HomeMy WebLinkAboutCITY_OF_IRVINE_MEA_MAP_ATLASS.
Map Atlas
i
Prepared For
City of Irvine
Community Development Department .
Prepared By
Community Planning Services
El Toro, Califbrnia
February 1986
•
I IV
Introduction
This Map Attas is intended for use in conjunction with the AMA User's Guide. The •Atlas .;;
includes both contraint and data maps covering the City's planning area. '
provide environmental resource and constraint information on thirteen topics:
Data maps provide additional environmental information for use by the- City.=°.Tn'some-'.:...`'-;, . .
cases; the data maps were used to model the information depicted on the envir6nmental,s
constrait maps.
The maps included in this Atlas are reproduced at a scale of 1" a 6000.' 'Eacii''maps
assigned an alpha numeric code depending upon its type.'
The orginal MEA maps were drawn on clear"accetate at a scale of 1:24:000 (1" = 2000').
These maps are on file with the the Environmental Services Division of the Community
Development Department, and are available for reference.
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MAP INDEX
B-1 Topographic Base.Map
0-1 Acetate Overlay
Constraint Maps.,,,`
C-1
Geologip Hazards
C-2
Flood/Dam Inundation_ Hazards
C-3-
Fire Hazards
C-4
Agricultural Capability
C-5
Water Resources.
C-6
Biotic Resources
C-7
Sand and Gravel Resources
C-8
Historical Resources
C-9
Archaeological Resources
C40
Paleontological Resources-
C-11
Aircraft Noise and Crash Hazards
C-12
Roadway and Railroad Noise
C-13
Special Districts
Data Mans
D-1
Landform
D-2
Slope Zones
D-3
Soils
D-4
Agricultural Preserves
D-5
Vegetation
D-6
Environmental Documents Index
D-7
Archaeological Documents Index
D-8
Statistical Areas & Residential Phasing
D-9
ITAP Zones
D-10
Census Areas
D-11
IRWD Token Zones
IRVIRR
IMA
Ui `I LO .I
3�-a Lif
IT
�FHF
s-
ENTER t� /
Gl '� r 1
�4
r v i n e Topographic Base
M E A
B-1
� l � TMOUGO
ON TOFEItA A RAN A FE eWUL
V�
�r
1U
0 2000 4000 6000 8000
Feat
Irvine Corporate Limits
"' Sphere of Influence
•
CONSTRAINT MAPS
,a,
•
L7�
i
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MAP NUMBER:
MAP TITLE:
MAP TYPE:
DATE PREPARED:
LAST UPDATE:
C-1
GEOLOGIC HAZARDS
CONSTRAINT
JULY 12,1985
NONE
Seismic Response Areatl)
Code Interpretation
1 Seismic Response Area (SRA) 1
2 Seismic Response Area (SRA) 2
3 Seismic Response Area (SRA) 3
4 Seismic Response Area (SRA) 4
5 Seismic Response Area (SRA) 5
1 See Appendix A for expanded code interpretation
V-10, vl---,
U-1,
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41.
IV RKY"I",
V
I r v i n e Geologic Hazards
AR 1U A
C-1
>40
t/V
elf-,
12.
'NIC/
0 2000 4000 6000 8000
Feet
— Irvine Corporate Limits
' " ' Sphere of Influence
P.p-d: My 12.1W
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MAP NUMBER: C-2
MAP TITLE:
FLOOD/DAM INUNDATION HAZARDS
MAP TYPE:
CONSTRAINT.
DATE PREPARED:
MAY 15, 1985
LAST UPDATE:
NONE
Floodplain Zones - 1st digit
Code Interpretation
1xx Area of Special Flood Hazard (100 Year Floodplain)
2xx Area of Special Flood Hazard (100 Year Floodplain) - County and City maps
3xx Area of Special Flood Hazard (100 Year Floodplain) - County map only(2)
4xx . Area of Special Flood Hazard (100 Year Floodplain) - City map only(2)
5xx Floodway
6xx Floodway Fringe.
9xx- Not within an area of Special Flood Hazard
Dam Inundation Areas - 2nd and 3rd digits
Code- Interpretation
x01 Rattlesnake Reservoir
x02 Santiago Reservoir
x03 Villa Park Reservoir
x04 San Joaquin Reservoir
x05 Sand Canyon Reservoir
x06 Syphon Canyon Dam
x07 Laguna Dam .
x10 Rattlesnake and Santiago Reservoirs
x12 Santiago and San Joaquin Reservoirs
x13 Santiago and Sand Canyon Reservoirs
x14 Santiago and Sand Canyon Reservoirs.
x20 Rattlesnake, Santiago, and Villa Park Reservoirs
x21 Santiago and Villa Park Reservoirs and Syphon Canyon Dam
x22 Santiago, Villa Park, and San Joaquin Reservoirs
x99 Not within Dam Inundation area
i Codes 3xx and 4xx refer to areas plotted -differently by Federal Insurance Administration on City and
County Flood Insurance Rate Maps.
2 Codes 3xx and 4xx refer to areas plotted differently by Federal Insurance Administration on City and
County Flood Insurance Rate Maps.
I r v i n e
M E A
C - 2
Flood/Dam Inundation
Hazards
P¢p—d May 15,1985
0 2000 4000 6000 8000
Feet
Irvine Corporate Limits
"' Sphere of Influence
•
i
1•
MAP TITLE:
FIRE HAZARDS
MAP TYPE:
CONSTRAINT
DATE PREPARED:
MARCH 5, 1985
LAST UPDATE:
NONE
Fire Hazard Severi - 1st digit
Code Interpretation
Ix None/low
2x Moderate
3x High
4x Extreme
9x Not Rated - Urban, fieldcrop, or orchard .
Fire Frequency (Since 1910) - 2nd digit
Code
Interpretation
xl
One Fire
x2
Two Fires
x3
Three Fires
x9
No Known Fires
M E A
C - 3
Fire Hazards
Prepared: M-h5,1985
0 2000 4000 6000 8000
Feet
Irvine Corporate Limits
"' Sphere of Influence
•
MAP NUMBER:
MAP TITLE:
MAP TYPE:
DATE PREPARED:
LAST UPDATE:
C-4
AGRICULTURAL CAPABILITY
CONSTRAINT
AUGUST 3, 1985 .
NONE
Class of Soils(')
Code Interpretation
1 Class I Soils
2 Class H Soils
3 Class.HI & IV Soils
5 Other than Class I thru7IV Soils
9 Water
1 See Appendix A for expanded code interpretation
i r v i n e
M E A
C - 4
Agricultural Capability
0 2000 4000 6000 6000
Feet
Irvine Corporate Limits
"' Sphere of Influence
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i
MAP NUMBER: C-5
MAP T=: WATER RESOURCES
MAP TYPE: . CONSTRAINT
DATE PREPARED: TUNE 12, 1985
LAST UPDATE: NONE
Groundwater Recharge Potential
Code Interpretation
lkx Restricted Recharge
2xx Partially Restricted Recharge: To Shallow Aquifers
3xx Partially Restricted Recharge to Deep Aquifers
4xx Unrestricted Recharge
9xx Not in Groundwater Basin
Master Plans of Drainage
Code Interpretation
x01 Irvine Ranch - Valencia
x05 Irvine Ranch - Bryan
x06 University Park
x07 Irvine Industrial
x15 Laguna Canyon
x16 Central Irvine Ranch
x19 East Irvine
x99 Not Included in Master Plan (State Property)
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I r v i n e I Water Resources
P.p-d: Tune 12,1995
0 2000 4000 6000 8000
Feet
Irvine Corporate Limits
"' Sphere of Influence
i
u
MAP NUMBER:
MAP TITLE:
MAP TYPE:
C-6
BIOTIC RESOURCES
CONSTRAINT
DATE PREPARED: DECEMBER 16, 1984
LAST UPDATE: JANUARY 30, 1986
Biotic Sensitivity(1)
Code. Area Name
01 Limestone Canyon
02 Bee & Round Canyons
03 The Sinks
04 - Borrego Canyon
05 Santiago Canyon
06 San Joaquin Freshwater Marsh
07 Sand Canyon Wash
08 San -Diego -Creek'
09 Bonita Reservoir
10 Sand Canyon Reservoir
11 Sand Canyon Reservoir Rare Plant Habitat
12 Shady Canyon Rare Plant Habitat
13 Shady Canyon
14 Bommer Canyon
15 Limestone -Canyon -buffer
16 Bee & Round Canyon buffers
-1.7. Aqua Chinon Wash
18 Borrego Canyon buffer
19 Rattlesnake Reservoir
20 Siphon.Reservoir
21 Lambert Reservoir
22 San Diego Creek -Downstream Reach
23 Woodbridge Lakes
24 San Diego Creek buffer
25 San Diego Creek = Irvine Center Reach
26 Sand Canyon Wash buffer
27 Laguna Reservoir
28 Bonita Reservoir buffer
29 Sand Canyon Reservoir'buffer
30 William R. Mason, Regional Park Lakes
31 Shady and Bommer Canyon buffers
32 - Shady Canyon tributary
33 Eucalyptus windrows
34 Sand Canyon Oak trees
35 Canada Geese Foraging Area(2)
Sensitivity
High
High
High
High
.High
High
High
High
High,
High
High
High
High
High
Moderate
Moderate
Moderate
Moderate
Moderate
Moderate
Moderate
Moderate
Moderate
Moderate
Moderate
Moderate
High
Moderate
Moderate
Moderate
Moderate
Moderate
Moderate
Moderate
High
1 See Technical Supplement # 2: Biotic Resources Element for additional information:regarding each of these areas.
2 This area has been designated based upon preliminary results of a study currently.underway. The designation and boundaries
of the area are subject to change.
I r v i n e
M E A
C - 6
Biotic
Resources
0 2000 4000 6000 8000
Feet
Irvine Corporate Limits
"' Sphere of Influence
htp-d• D—.b6 ,16, 1984
Updated. January 21, 1986
C7
MAP NUMBER: C-7
MAP TITLE: SAND AND GRAVEL RESOURCES
MAP TYPE: CONSTRAINT
DATE PREPARED: SEPTEMBER 4, 1985 _
LAST UPDATE: NONE
Code Interpretation
0 - Not Resource Area
1 Potential. Resources
2 - Known Resources
to
1 J
Sand And Gravel Resources
M E A
C - 7
Sand and Gravel Resources
0 2000 4000 6000 8000
Feet
Irvine Corporate Limits
Sphere of Influence
P,p=d Sq—ber4, 1985
i
0
MAP .NUMBER: C-8
MAP TITLE: HISTORICAL RESOURCES
MAP TYPE: CONSTRAINT
DATE PREPARED: AUGUST 12, 1985
LAST UPDATE: NONE
Historical Resources
Code Resource Title Tyne Status
01
High -line Canal
Structure
02
Irvine Ranch Headquarters & Employee Housing
Structure
_Existing
Existing
03
Irvine Community Church
Structure
Existing
04
Irvine's First Public School
Structure
Removed
05
Irvine Bean Warehouse
Structure
Existing
06
East Irvine Garage & Service Station
Structure
Existing
07
A.T. & SY Railway Station
Structure
Removed
08
Irvine General Store
Structure
Existing
09 -
Sand Canyon Oaks/Stage Coach Route
Place
N/A
10
Irvine - Laguna Stage Coach Stop
Structure
Removed
11
Bommer Canyon Cattle Camp
Structures.
Existing .
12
Urbanus Square (Old Buffalo Ranch)
Structures
Existing
13
Portola Campsite at Tomato Springs
Place
N/A
14
Route of Portola Expedition
Place
N/A
15
Tomato Springs Bandit
Place
N/A
16
Walnut Packing House
Structure
Removed
17
Francis Packing House.
Structure
Removed
18
Route of El Camino Real - "The.Kings Highway"
Place
N/A
19
"Swamp of the Frogs"
Place
N/A
20
Michelson Vacuum Tube Experiments
Place
N/A
21
Barton's Mound
Place ..
N/A
22
Don Jose Sepulveda's First Adobe
Structure
Removed
23
Rancho Headquarters
Structure
Existing
_
99
Remainder of Planning Area
N/A
N/A
Note: Circles on map represent approximate site locations.
I r v i n e
M E A
C - 8
Historical Resources
0 2000 4000 6000 8000
Feet
Irvine Corporate Limits
"' Sphere of Influence
Prepared. August 12,1995
•
i
0
MAP NUMBER: C-9
MAP TITLE: ARCHAEOLOGICAL RESOURCES,
MAP TYPE: CONSTRAINT
DATE PREPARED: ' JUNE.11, 1985.
LAST UPDATE: NONE'
THIS MAP CONTAINS SENSITIVE SITE LOCATION INFORMATION.
IT IS ON FILE WITH THE. DEPARTMENT OF COMMUNITY DEVELOPMENT
AND AVAILABLE FOR REVIEW BY QUALIFIED INDIVIDUALS.
Survey Status
Code Interpretation
0 Area Not Surveyed
1 Area Previously Surveyed
Archaeological Sites
Code Interpretation
Note: Map codes correspond to recorded site numbers (ORA-XXXX). -See Technical
Supplement 4: Archaeological Resource Element for a description and status of
each site.
MAP NUMBER: C-10
MAP TITLE: PALEONTOLOGICAL RESOURCES
MAP TYPE: CONSTRAINT
DATE PREPARED: JANUARY 4, 1985
LAST UPDATE: NONE
Sensitivity Zones - Large single digit
Code Interpretation
0 - None
1 Low Sensitivity
2 Moderate Sensitivity
3 High Sensitivity
Site Localities - Smaller 3 di itg code
Recorded Recorded Recorded
Code Locality # Code Locality # Code Locality
001 LACM 6666 026 UCLA 415 051 USES 509
002 USGS 106 027 UCRIYP 7898 052 USES 510
003 USGS 107 028 LC 613.1 053 USGS 512
004 USGS 11.1 029 JDC-BR-2 054 LC A535
005 USGS 112 030 JDC-BR-3 055 USGS 511
006 USGS 136 031 JDC-BR-4 056 NHF.54
007 USGS 137 032 JDC-BR-7 057 NHF 55
008 USGS -114B 033 UCLA 282 058 NHF 121
009 USGS 135 034 UCLA 413 059 LC A538
010 JDC-HC-6 035 LACM 4171 060 UCLA(CIT) 374
011 JDC-HC-1 036 RR 166 061 LACM 1067
012 JDC-HC-2 037 RR 161 062 LACM 3407
013 JDC-HC-3 038 LC 2337 063 LCAM 3877
014 JDC-HC-4 039 USGS 138 064 LACM 3980
015 JDC-HC-5. 040 USGS 192 065 LCAM 3866
016 JDC-BR-1 041 USGS 1 066 USGS'504
017 JDC-BR-6 042 USGS 193 067 LACM 1068
018 -JDC-BR-8 •043 UCLA 1534- 068 LACM 1069
019 JDC-BR-9 044 LACM(CIT) 449 069 LACM 3977
020 RR 153 045 LC A537 070 LACM 3978
021 RR 154 046 USGS 503' 071 LACM 3986
022 RR 155 041 USGS 505 072 NHF 96
023 RR 156 048 USGS 506 073 NHF 128
024 USGS 44 049 USGS 507 074 USGS 534
025 UCLA 414 050 USGS 508 075 RR 622
• (See Technical Supplement 5: Paleontological Resource Element fora description of each site.)
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I r v i n e Paleontologic Resources
A4 T A
C-10
Pmpar.d:7anuwy4,1985
0 2000 4000 6000 8000
Feet
Irvine Corporate Limits
Sphere of Influence
1, & S.M. M OP. Fnbcunrf 1986
MAP NUMBER: C-11
MAP TITLE: AIRCRAFT NOISE AND CRASH HAZARDS
MAP TYPE: CONSTRAINT'
DATE PREPARED: AUGUST 10, 1985
LAST UPDATE: NONE
Airport Crash Hazard Areas - 1st.digit
Code Interpretation .
Ox Not in Hazard Area
Ix Local Aircraft Traffic Zone
2x Accident Potential Zone 2
3x Accident Potential Zone 1
4x Airport Clear Zone
Noise Impacted Areas - 2nd digit
(Based upon existing noise. levels)
Code Interpretation
x0 Noise less than 60 CNEL
x1 Aircraft Noise Impacted Area (60 to 65 CNEL)
x2 Aircraft Noise Impacted Area (65 to 70, CNEL)
x3 Aircraft Noise Impacted Area (70 to 75 CNEL)
x4 Aircraft Noise Impacted Area (75 to 80 CNEL)
x5 Aircraft Noise Impacted Area(>80 CNEL)
0
I r v i n e
M E A
C - I I
Aircraft Noise
Crash Hazards
and
0 2000 4000 6000 8000
Feet
Irvine Corporate Limits
Sphere of Influence
Pmpamd• August 10, 1985
As Of:
MAP NUMBER:
C-12
MAP TITLE:
ROADWAY AND RAILROAD NOISE
MAP TYPE:
CONSTRAINT
DATE PREPARED:
DECEMBER 5, 1985
LAST UPDATE:
NONE
Roadway and/or Railroad Noise
Code Interpretation ;
1 Combined Noise Levels < 60 CNEL'
2 Combined Noise Levels > 60 CNEL or not plotted
I
0
I r v i n e
M E A
C-12
Roadway, and Railroad
Noise
P.p—d.D—be,5,1985
0 2000 400D 6000 8000
Feet
Irvine Corporate Limits
"' Sphere of Influence
•
MAP NUMBER: C-13
MAP TITLE: SPECIAL. DISTRICTS (Hillside, Coastal, AQMD)
MAP TYPE: CONSTRAINT
DATE PREPARED: AUGUST 22, 1985
LAST UPDATE: NONE
Hillside Overlay- District - 1st digit
Code Interpretation
Oxxx Not within Hillside Overlay District
1xxx Within Hillside Overlay -District
i
Code Interpretation
xOxx Not within Coastal Zone-
x1xx Within Coastal Zone
Coastal Zone - 2nd-digit
South Coast AQMD Subbasins - 3rd & 4.th .dig
Code Interpretation
xx19 Subbasin 19
xx20 Subbasin 20
•
I r v i n e
M E A
C-13
Special Districts
0 2000 4000 6000 6000
Feat
Irvine Corporate Limits
"' Sphere of Influence
Pmp=d. Au8-22,1985
r-
DATA. MAPS'
•
MAP NUMBER: D-1
MAP TITLE: LANDFORM
MAP TYPE: I DATA
DATE PREPARED: MARCH 21, 1985
LAST UPDATE: NONE'
Landform-Type(1)
Code
Interpretation
01
Lake
02
.-Reservoir
03
Coastal Lagoon/Estuary .
04
Depression
05
Delta
.06
- Beach
07
Dune
08
Cliffs
09
Gulley
10
Floodplain
11
Upland Valley
12
Marine Terrace Bench
13
Marine Terrace Sideslope
14
Alluvial Fan
15
Alluvial Terrace Bench -
16
Alluvial Terrace Sideslope
17
Alluvial Plain
18
Landslide
19
Rock Outcrop
20
Mountain Ridge Top
21-
Mountain Sideslope
22
Hilltop
23
Hill/sideslope -
24
Not used
25
Man-made/altered
i See Appendix for expanded code interpretations.
I r v i n e
M E A
D-1
x
Landform
Pmpamd: Much 21, 1985
0 2000 4000 6000 8000
Feet
Irvine Corporate Limits
'' Sphere of Influence
•
to
►i . ' ►t lul-0
MAP TIME:
D-2
SLOPE ZONES
MAP TYPE: I . CONSTRAINT
DATE PREPARED: JUKE 26, 1985
LAST UPDATE: NONE
Percent of Sloped)
Code Interpretation
1 0 -.5%
2 5 - 10%
3 10 - 15%-
4 -15- 20%
5 20.- 25%
6 25 - 30%
7 , > 30%
9 Urban/Regraded
i See Appendix for expanded code interpretations.
I r v i n e
M E A
D-2
x
Slope Zones
P.p—d:5um36,1985
0 2000 4000 6000 8000
Feet
Irvine Corporate Limits
"' Sphere of Influence
0
0.-
MAPNUMBER: D-3
MAP TITLE: SOILS
MAP TYPE: . DATA
DATE PREPARED: JUNE 2, 1985
LAST UPDATE: NONE
Code Interpretation
Soil TypescW.
100
Alo clay, 9 to 15 percent. slopes
101
Alo clay, 15 to 30 percent slopes
102
Alo clay, 30 to 50 percent slopes
103
Alo variant clay, 9 to 15 percent slopes
104
Alo variant clay, 15 to 30 percent slopes
105
Alo variant clay, 30 to 50 percent slopes
106
Anaheim loam, 1S to 30 percent slopes
107
Anaheim- loam, 30 to 50 percent. slopes
108
Anaheim clay loam, 15 to 30 percent slopes
109
Anaheim clay loam, 30 to 50 percent slopes
110
Anaheim clay loam, 50 to 75 percent slopes
111
Balcom clay loam; 9 to 15 percent slope
112
Balcom clay loam, 15 to 30 percent slopes
113
Balcom clay loam, 30 to 50 percent slopes
114
Balcom-Rock outcrop complex, 15 to 50 percent slopes
126
Bosanko clay, 9 to 15 percent slopes
127
Bosanko clay, 15 to 30 percent slopes
128
Bosanko clay, 30 to 50, percent slopes
129
Bosanko-Balcom complex, 15 to 30 percent slopes
130
Bosanko-Balcom complex, 30 to 50 percent slopes
131
Botella loam, 2. to 9 percent slopes
132
Botella clay loam, 2 to 9 percent slopes
133
Botella clay loam, 9 to 15 percent slopes
134
Calleguas clay loam, 50 to 75 percent slopes
135
Capistrano sandy loam, 2 to 9.percent slopes
136
Capistrano sandy loam, 9 to 15 percent slopes
137
Chesterton loamy sand, 2 to 15 percent slopes
138
Chesterton loamy sand, 15 to 30 percent slopes
139
Chino silty clay loam
140
Chino silty clay loam, drained
141
Cieneba sandy loam, 15 to 30 percent slopes
1 See Appendix for expanded code interpretations.
•
Soils (Cont)
Code Interpretation
142 Cieneba- sandy loam, 30 to 75 percent slopes, eroded
145 Cieneba-Rock outcrop complex, 30 to 75 percent slopes
-146 Corralitos loamy sand
147 Corralitos loamy sand, moderately fine substratum
148 Cropley clay, 0 to 2 percent slopes
149 Cropley clay, 2 to 9 percent slopes,
154 Gabino gravelly clay loam; 15 ',to 50 percent slopes
161 Marina loamy sand, 0 to 2 percent slopes
162 Marina loamy sand, 2 to 9 percent slopes
163 Metz loamy sand
164 Metz loamy sand, moderately fine substratum
165 Mocho sandy loam, 0 to 2 percent slopes
166 . Mocho loam; 0 to 2 percent -slopes
167 . Mocho loam, 2 to 9 percent slopes
172 Myford sandy loam, 0 to 2 percent slopes
173 Myford sandy loam, 2 to 9 percent slopes
174 Myford sandy loam, 2 to 9 percent slopes, eroded
175 Myford sandy loam, 9 to 15 percent slopes
176 - Myford sandy loam, 15 to 30 percent slopes
177 Myford sandy loam, 9 to 30 percent slopes-, eroded
178 Myford sandy loam, thick surface, 0 to 2 percent slopes
179 Myford sandy loam, thick surface,.2 to 9 percent slopes
182 Omni silt loam, drained
1-83 Omni clay
-184 Omni clay, drained
184 Pits
191 Riverwash
192 Rock outcrop-Cieneba complex, 30 to 75 percent slopes
193 San Andreas sandy loam, 15 to 30 percent slopes
194 San Emigdio fine sandy loam, 0 to 2 percent slopes
195 San Emigdio fine sandy loam, 2 to 9 percent slopes
196 San Emigdio fine sandy loam,' moderately fine substratum, 0 to 2 percent slopes
199 Soper loam, 15 to 30 percent slopes
200 Soper loam, 30 to 50 percent slopes
201 Soper gravelly loam, 15 to 30 percent slopes
202 Soper gravely loam, 30 to 50 percent slopes
203 Soper cobbly loam, 15 to 50 percent slopes
205 Sorrento sandy loam, 0 to 2 percent slopes
206 Sorrento loam, fl to 2 percent slopes
207 Sorrento loam, 2 to 9 percent slopes
208 Sorrento clay loam, 0 to 2 percent slopes
209 Sorrento clay loam, 2 to 9 percent slopes"
210 Thapto-Histic Rluvaquents
211 Title flats
221 Yorba gravelly sandy loam, 2 to 9 percent slopes-
• 222 Yorba gravelly sandy loam, 9 15 percent slopes
223 Yorba gravelly sandy loam, 15 to 30 percent slopes
Soils (Cont)
Code Interpretation
224 Yorba cobbly sandy- loam, 9 to 30 percent slopes
225 Yorba cobbly sandy loam, 9 to 30 percent slopes, eroded
998 Water
a,
0
/
X
I r v i n e Soils
M E A
D-3
Pmp=&J-2,1985
0 2000 4000 6000 8000
Feet
Irvine Corporate Limits
"' Sphere of Influence
•
MAP NUMBER: D-4
MAP TITLE: AGRICULTURAL PRESERVES
MAP TYPE: DATA
DATE PREPARED: DULY 11, 1985
LAST UPDATE: NONE
Preserve Contract Status = 1st and 2nd digits
Code.
Interpretation
00
Not Under Contract
88
Contract Expires in 1988
89
Contract Expires in 1989
90
Contract Expires in 1990
91
Contract Expires in.1991
94
-Contract Expires in 1994
99
No Contract Expiration Date' Set
NOTE: Some preserve areas extend beyond the boundaries of the &MA study area.
i
0,
MAP NUMBER:
MAP TITLE:
MAP TYPE:
Im
VEGETATION
DATA
DATE PREPARED: JULY' 29, 1985
LAST UPDATE: NONE
Vegetation Typescl)'
Code Interpretation_
010 Grassland
020 Coastal Sage Scrub
021 'Coastal Sage. Scrub -Sage
022 Coastal Sage Scrub -Mixed
030 Chaparral "
031 , Chamise Chaparral
032 Mixed Chaparral
040 Oak Savannah
050' Oak Woodland/Forest
051 Oak Woodland
052 Oak Forest
060 Riparian Woodland/Forest .
061 Riparian Woodland
062 Riparian Forest
070 Conifer Woodland/Forest (Not Used).
071 Conifer Woodland (Not Used)
071 Conifer Forest (Not Used)
080 Marsh
081 Saltwater Marsh
082 Freshwater Marsh.
090 Barren
100 Agriculture
101 Orchard
102 Fieldcrop
103 Windrow
104 Sand Canyon Oaks
110 Urban/Cultural Altered
120 Water
1 See.Appendix for expanded code interpretations.
I r v i n e
M E A
D - 5
X
Vegetation
P.P-,:7uly 11, 1985
r
■yE
_-Nov— w \
0 2000 4000 6000 8000
Feet
Irvine Corporate Limits
Sphere of Influence
•
i
MAP NUMBER: " D-6
MAP TITLE. ENVIRONMENTAL DOCUMENTS INDEX,
MAP TYPE: DATA
DATE PREPARED: SEPTEMBER 5, 1985
LAST UPDATE: NONE
Major Environmental Documents
Lend
IS -
Initial Study
ER -
Environmental Impact Report
EA -
Environmental Assessment
MEA' -
Master Environmental Assessment
ES -
Environmental Impact Study
Type
Code
Document
Project Title,
-
EA/MEA
General Plan Amendment # 40)
-
EA/MEA
IRWD Master Environmental Assessmentci)
-
MEA
Orange County Master Environmental Assessment(2)
001
ER .
Bee and Round Canyon Landfill
002
ER
Irvine Lake Pipeline and Treatment Facility
003
ER
Foothill Transportation Corridor.
004
ER
Foothill Transportation Corridor
ER
Bee and Round Canyon Landfill
005
ER
North -Irvine Precise Land Use Plan
ER
IRWD Improvement District 75-1
006
EA
Irvine Blvd. Widening.
007
ER
North Irvine Precise Land Use Plan
008
ER
Northwood Parcels 2 & 3
.000
ER
Saddleback College Site Selection
ER
IRWD Improvement District 75-1
ER
North Irvine Precise Land Use Plan
010
ER
Saddleback College Site Selection
ER
North Irvine Precise Land Use Plan
Oil
ER
North Irvine Precise Land Use Plan,
ER
Northwood Parcel 2 and 3
• 1 This document encompasses the entire MEA study area and, therefore, has not been individually coded.
2 This document includes the city's entire northern sphere of influence and, therefore, has not been individually coded.
ENVIRONMENTAL DOCUMENTS INDEX (Cont.)
Type
Code Document Project Title
012 ER Northwood Parcel 4
ER Saddleback College Site Selection .
ER North IrvinePrecise Land Use Plan .
013 ER Saddleback College Site Selection
014 EA Myford/I 5 Interchange Improvements
015 EA - Yale Avenue Bicycle Overcrossing
EA . Yale Avenue Vehicular Overcrossing
016 EA Jeffrey Road Interchange Improvements
017 IS " Sand Canyon Business & Industrial Center
018 ER IIC-East Zoning
019 ER IIC-East Phase IV
020 ER IIC-East Phase III
ER IIC-East Zoning
021 IS IIC-East Phase II
ER IIC-East Zoning
022 ER Irvine Technology Center
ER IIC-East Zoning
023 ER IIC-East Phase I
ER IIC-East Zoning
024 IS Irvine Auto Center
ER IIC-East Zoning
025 ES Alton Pkwy & ICD Interchange-Irnprovements.
026 - ER Saddleback College Site Selection
ER . Walnut Village General Plan Amend. -
027 ER - Walnut Village General PlanAmend.
028 ER Walnut Avenue Extension
029 ER Eastern Corridor Trans. Corridor
030 ER Village of Valley View
031 ER Heritage Park Stadium
032 ER East Irvine Historical District
033 ER AT& SF Railroad Lowering Project
034 ES Moulton Parkway/ICD Realignment
035 ER Home Improvement Center "
ER Eastern Corridor Trans. Corridor
ER Village of Valley View
036 ER Village of Valley View
ER North Irvine Precise Land Use Plan
037 BR Yale Avenue%AT&SF Railroad Overcrossing
038 ER Smoketree Townhomes
ER North Irvine Precise Land Use Plan
039 ER Irvine Corporate Yard
040 IS Irvine Center CUDP Phase II
ER Irvine Center Zoning
ER Irvine Center Development Agreement
041 IS Irvine Center CUDP Phase I
ER Irvine Center- Zoning
ER Irvine Center Development Agreement
042 IS Agua Chinon Channel Realignment
043 IS Irvine Center Drive Widening
ENVIRONMENTAL DOCUMENTS INDEX (Cont.)
Type
Code
Document
Project Title
044
IS
121 Acre Medium Industrial Zoning
ER
Irvine Business Complex
ER
Irvine Business Complex (Supplement)
ER
II-C West 15th Amendment
.045
ER,
Sunset Fibre Waste Transfer Station
ER
Irvine Business Complex
ER
Irvine Business Complex (Supplement)
ER
H-C West 15th Amendment
.046
ER
Irvine Business Complex
ER
Irvine Business Complex (Supplement)
ER
II-C West 15th Amendment
047
ER
Park Redhill Industrial Center
ER
Irvine Business Complex
ER
Irvine Business Complex (Supplement)
ER
H-C-West 15th Amendment
048
IS
Foodpark Development
ER
Irvine Business Complex
ER
Irvine Business Complex (Supplement)
ER
H-C West 15th Amendment
049
IS'
Koll Center Irvine
ER
Irvine Business Complex
ER
Irvine Business Complex (Supplement)
ER
II-C West 15th Amendment,
050
IS
Main Street Trunk Sewer
051
ER
Main. and Jamboree P.C.
ER
Irvine Business Complex
ER
Irvine Business Complex (Supplement 6/85),
ER
II-C West 15th Amendment
052
ER
Village 14 Rezoning
ER
Village of Westgate'Environmental Data
053
ER
Central Irvine GPA
ER
Village 14 Rephasing
ER
Village of Westgate Environmental Data
054
ER
Village of Westpark
ER
Village 14 Rephasing
ER
Village of Westgate Environmental Data
055
ER
Central Irvine GPA
ER
Village of Westpark
ER
Village of Westgate Environmental Data
ER
Village 14 Rephasing
056
EA
Harvard Avenue/I-405 Overcrossing
057
ER
Woodbridge Village Phase I
ER
Housing & Urban Development Review
ER
Woodbridge Village Zoning
058
IS
Woodbridge Village NE Quad.
ER
Woodbridge Village Zoning
ER
Housing & Urban Development Review
059
ER
Central Irvine GPA
ER
Woodbridge Village Phase I
ER
Woodbridge Village Zoning
ER
Housing & Urban Development Review
ENVIRONMENTAL DOCUMENTS INDEX (Cont.)
Type
Code
Document
Project Title
060
IS
Woodbridge Village SW Quad.
ER
Woodbridge Village Zoning
ER
Housing & Urban Development Review
.061
IS
Woodbridge Village SE Quad
ER
Woodbridge Village, Zoning
ER
Housing & Urban Development Review
062
EA
Yale Ave/I-405 Bicycle Overcross.
EA
Yale Ave/I-405 Vehicular Overcross.
063
ER
Saddleback College Site Selection .
ER
Village 12 Concept Plan
064
ER
Orangetree Planned -Community
ER
Village 12 Concept Plan
065
ER
Village 12 Concept Plan
066
ER
Central Irvine GPA
ER
Village 12 Concept.Plan
'067
ER
Transmission Line (San Onofre to Santiago Substation)
068
ER'
Irvine Medical Center
ER
Irvine Medical & Science Complex
069
ER
Saddleback College Site Selection
ER
Irvine Medical & Science Complex
070
ER
Irvine Medical .& Science Complex
071
EA
Culver Dr./I-405 .Interchange Improvements
072
EA
San Canyon/I-405 Interchange Improvements
073
ER
Douglas Crow -Irvine Development
074
ER
Michelson Drive Extension
075 -
IS
San Joaquin Commercial Recreation'Center
076
ER
Expansion of Wastewater Reclamation Facilities
077
IS
Irvine Equestrian Center
078
ER
Rancho San Joaquin P.C.
079'
ER .
University -Town Center Zoning
080
IS
University Town Center Core
ER
University. Town Center Zoning
'
081
ER
Campus Drive Extension
082
IS
Tentative Map-10484
083
IS
Tentative Map 10483
084
ER
Saddleback College Site Selection
085
EA
University Drive Widening
086
ER
Turtle Rock Village Zoning
087
ER
Turtle Rock Apartments
ER
Turtle Rock Village Zoning
088
ER
Christ College Irvine
ER
Turtle Rock Village Zoning
089
ER
Turtle Rock Enclave VI[
ER
Turtle Rock Village Zoning
090
ER
Turtle Rock Enclave II
ER
Turtle Rock Village Zoning
091
- ER
Turtle Rock Enclave IV
092
ER
IS
Turtle. Rock Village Zoning
Turtle Rock Enclave III
ER
Turtle Rock Village Zoning
ENVIRONMENTAL DOCUMENTS INDEX .(Cont.)
Type
Code
Document
Project Title
093 -
IS
Turtle Rock Enclave V
ER
Turtle Rock Village Zoning
094
ER
Quail Hill P.0
095
ER
Bommer Canyon GPA
096
ER
Western Worlds Borrow Site
097
-ER
San Joaquin Hills Trans. Corridor
098
ER
Coyote Canyon Landfill - Genstar Gas Recovery
ER
Coyote Canyon Landfill - Borrow Site
ER
San Joaquin Hills Trans. Corridor
099
ER
Coyote Canyon Landfill - Genstar Gas Recovery
ER
Coyote Canyon Landfill - Borrow Site
1-00
ER
Bommer Canyon GPA
ER
San Joaquin Hills Trans. Corridor
101
EA
San Diego Freeway Widening
102
ER
Bonita Canyon Road
103
ER
Conjunctive Use Water Wells and Pipeline
11
I r v i n e
M E A
D - 6
Environmental Documents
Index
0 2000 4000 6000 8000
Feet
Irvine Corporate Limits
Sphere of Influence
P.pa d• Sq—bv 5, 1985
MAP NUMBER:
MAP TITLE:
MAP TYPE:
D-7
ARCHAEOLOGICAL REPORT INDEX
DATA
DATE PREPARED: TUNE 6, 1'985
LAST UPDATE: NONE
Archaeological Reports
Code Reports Included Within Coded Area
1 Padon, Beth and Bill Breece,.Arc*ha6ological Resource Inven-
tory, 1984, City of Irvine and_Its Sphere .of Influence.
2 Scientific Resource Surveys, Inc., 1978, Archaeological and
Historical Report on the Proposed Bee & Round Canyons Landfill
Disposal Station.
Steve E. Colegrove, 1972, Village of Valley View (letter
report).
Public Antiquities Salvage Team, California State University
at Fullerton, 1976, -Archaeological. Resources of the Tentative
Coyote Canyon Landfill Replacement Site in Central Orange
County.
Scientific Resource Surveys, Inc., 1978, Cultural Resources
Report - Preliminary Assessment on the San Diego'Creek Water-
shed in Hicks Canyon, Rattlesnake -Creek Wash, San Diego Creek,
and the San Joaquin Marsh.-
Bill- Breece and Beth Padon, 1982, Cultural Resource Survey of
Archaeological Resources, Foothill Transportation Corridor,
Phase II.
E. Gary Stickel, 1979, Evaluation of Cultural Resources at the
City of Los -Angeles Hyperion Water Facilities and the County
of Los Angeles, and Orange County Sanitation District Proposed.
Round Canyon Site.
3 (El Toro Marine Base)
,184
.4 N..Nelson Leonard III; 1975 Archaeological Impact Evaluation:
Park Place.
Scientific Resource Surveys, Inc., 1976, Archaeological Survey
Report on Tentative Tract No. 9379,' Lots A-G and A-5 of Tract
No. 282 in the City of Irvine.
0.-
Archaeological Surveys (Cont.)
Code Reports Included Within Coded Area
Scientific Resource Surveys, Inc., 1,976, Archaeological Survey
Report on a Four Acre Parcel of Land Located in Irvine Indus-
trial Area, Irvine, California.
Scientific Resource Surveys, Inc., 1976, Archaeological Survey
Report on The North' Irvine A-ssessment Di -strict Located in the.
"Frances" Area of the City of Irvine-.
Scientific Resource Surveys,. Inc.,.1977 Archaeological Survey
Report on Tentative Tract 9623 Located in the City of Irvine.
Archaeological Planning Collaborative, 1980, Archaeological
Records Search and Field Survey, Northwood Project Sites No. 1
and 2, City of Irvine.
Scientific Resource Surveys, Inc., 1976, Archaeological Report
on the Survey of Meadow Mobile Homes Proposed Development "The
Groves" Located.in the Frances Area, North Irvine.
Archaeological Planning Collaborative, 1979, Archaeological
Records Search and Reconnaissance Survey, .Orangetree Park
20-Acre Initial -Study, Irvine.
Michael L. Ahlering; A Discussion of Scientific Cultural
Resources in Relation .to the North Irvine Precise Land Use
Plan.
LSA,_ Inc., 1981; Cultural Resources Records Search and Field
Survey, Northwood Project Sites 3 and 4, City of Irvine.
LSA, Inc., . 1982, Historic Property Survey for Proposed
Improvements to Jeffrey Road and I-5, Irvine.
5 Marie G. Cottrell, 1976, Archaeological Record Search and
Field Survey of Sites N'o. 1, 2, and 5, North Irvine (letter
report).
Marie G. Cottrell, 1977, Village 10 - Records Search (letter
report).
Steve E. Colegrove, 1972, Village of Valley View (letter
report).
Archaeological Surveys (Cont.)
Code - Reports Included Within Coded Area
Michael L. Ahlering, A Discussion of Scientific Cultural
Resources- in Relation to the N.ort_h Irvine Precise Land Use
Plan.
6 Marie G. Cottrell, 1978, Archaeological Resources Located in
Village 14, Irvine (letter report).
Laura,Lee Mitchell, 1976 Woodbrige-Observer Survey Project.
Steve E. Colegrove, 1973, Central Village "A' East Irvine
Business -and Industrial Center and' Regional Commercial. Tr -
angle Scientific Resources -Survey (letter report).
Theo N. Mabry, 1979, Culver/I=405 and Harvard/I-405 Area
Arc-haeological Report"Inventory (letter report). -
Theo N: Mabry, 1979, Archaeological Record Search -and Recon-
naissance, Yale Avenue Rights -of -Ways,-, Irvine, CA,
Marie G. Cottrell, 1978,, Culver Drive/I-405 Interchange
Improvements (letter report).
Marie G. Cottrell, 1976, Walk -Over 'Survey Central Village "A"
(letter report).
Beth Padon, 1984, Archaeological Resource Assessment Irvine
Industrial Complex -East, Phase IV., Irvine,
N. Nelson Leonard III," 1975, Archaeological- Resources of
Rancho San Joaquin.
7 - Beth Padon, 1983, Assessment of Archaeological Resources, RV
Storage Project, Irvine.
Marie Cottrell, 1980, Walk-O-ver Survey of 25 Acres, Southwest
Corner of Sand Canyon and AT&SF Railroad in City of Irvine,.
8 Theo N. Mabry, 1979, Archaeological Records Search and Recon-
naissance Survey, Orange Tree Park 20-Acre Initial Study,
Irvine.
0
0
Archaeological Surveys (Cont.)
Code Reports Included Within -.Coded Area
LSA, Inc., 1981, Cultural Resource Assessment Village 12
Development Site.
Marie G. Cottrell, 1976, Walk -Over Survey Central Village "A"
(letter report).
Steve E. Col-egrove, 1973, Proposed Orange Tree Acres Planned
Community (letter report).
Marte G. Cottrell, 1976, Archaeological Survey on Sa,n Diego
Creek Flood Control' Channel -(letter -report). _
Marie G. Cottrell, 1977, Archaeological Survey Report on Vil-
lage 12 and Village 14.
9 Beth Padon, 1984, Cultural Resource Assessment,'Irvine Center
Project_, Irvine.
Marie G. Cottrell, 1978, Alton/Santa Ana Freeway Interchange
Construction and Irvine Center Drive, San Diego Freeway Inter-
change Expansion: Archaeological Resources Review (letter
report).
LSA, -Inc., 1981, Historic Property Survey, Alton- Parkway/I-5
Interchange and Irvine Center Drive/I-405 Interchange, Irvine. -
Theo Mabry, 1979, Archaeological Survey,. Alton and Irvine
Center.Drive Interchange Improvements (letter report)-.
Steve E. Colegrove; 1973, Central Village "A"' -East Irvine'
Business and, Industrial Center. and Regional Commercial Tri-
angle (letter report).
Jill Weisbord, 1981 Cul.tural Resource Survey of the Irvine
Center D.A. Village 13.
Beth Padon, 1.983, Assessment of Archaeological and Pal-eonto-
logical Resources, Irvine Medical Complex, Irvine.
Beth Padon, 1983, Assessment of Archaeological and Paleonto-
logical Medical Center, Irvine, CA.
•
Archaeological Surveys (Cont.)
Code Reports Included Within Coded Area
10 Theo N. Mabry, 1978, Archaeological Records Search and Recon-
naissance Survey, Irvine Industrial Complex -East, Phase 2 and
3 Areas, Irvine.
Beth Padon, 1984, Cultural Resource Assessment, Planning Area
34B.
Scientific Resource Surveys, Inc., 19.77, Archaeological' Survey
Report on a 34-Acre Parcel in the E1 Toro Area.
11 LSA, Inc., 198I Cultural Resource Assessment Irvine Meadows
Amphitheatre Development Site, Irvine.
Marie G. Cottrell, 1978, Report of Archaeological Resources
Survey on Laguna and Peters Canyons.
Charles N-. I'rwin; 1974, Laguna Canyon Su-rvey.
John Romani, 1984, Archaeological- Survey .Report -for the Widen-
ing -of Route Ora-133, Between Canyon Acres Drive and 1'405 PM.
12 Theo N.-Mabry, 1979, Updated Archaeological, Records Search and
Reconnaissance with Mitigation Recommendations, Quail Hill
Planning Area, Irvine.
Archaeological Pl-anning Collaborative, 19.79, Archaeological
Records Search and Reconnaissance Survey, Turtle,Rock Enclaves
6 and 7.
.Steve E. Col.egrove, 1973, Turtle Rock Planning Area (letter
report).
LSA, Inc., 1981 Archaeological and P-aleontological Resource
Assessment Turtle Rock Enclave 8, Irvine.
Steve E. Colegrove, 1973, Scientific Resources Survey on
Turtle Rock Planning Area; Irvine (letter report).
Raymond L. Bernor, 1977, Paleontological Resource Survey and
Impact Evaluation for Turti,e Rock Enclaves 3 and 5, Irvine.
•
0 ' I .
Archaeological Surveys (Cont.)
Code Rgports- Included Within Coded Area
Theodore Cooley, 1974, Archaeological Site Survey Records for
Bonita Canyon Extension (letter report). -
Marie G. Cottrell, 1976, Archaeological Survey' on Turtle Rock
Enclave 4 (letter -report).
13 Archaeological Resource Management, Corporation, 1978, Report
of Archaeological Resources Assessment conducted for the
Irvine Industrial Complex -West.
Beth Padon, 1984, Archaeological Field Review, Village 19A
Project, Irvine.
PBR and LSA, Inc., 1979, Wastewater Management and Action'P ro-
gram Draft Environmental & Action Program.
Theo N. Mabry, 1979, Archaeological Records- Search and Recon-
naissance, Upper Newport Bay,.Newport'Beach.
4 E. Gary Stickel and Jerry. B. .Howard, 1976, Cultural Resource
Survey of the -University of California, Irvine.
Thomas F. King, 1973, Archaeological Reconnaissance 'of the
Irvine Town Center Project.
Glen Rice, .1976, Systematic Surface Inspection -in Town Center
Area (l.etter report) ..
15 Theo N. Mabry, 1979, Archaeological Reconnaissance of it -Acre.
Bonita Canyon Baptist Church Site.
Ultrasystems, 1976, Archaeological, Historical, and Paleonto-
logical Resources Western World Medical Foundation Project,
Irvine.
Archaeological' Research, Inc.,- 1975, Preliminary Report -
Bonita Canyon.
Robert H. Crabtree, 1973, Harborview Hills Development Section
3 and 4, Sites 11, 13, and 14 (letter report).
is
Archaeological Survgys(Cont.)
Code Reports Included Within Coded Area .
Archaeological Research, Inc., 1977., Archaeological Resources
of the Coyote Canyon Disposal Station.
Marie G:: Cottrell, 1978, Preliminary. Archaeological Survey
Conducted for the San Joaquin Hills Transportation Corridor.
Marie G. Cottrell, 1983, Archaeological Resource Assessment,
Coyote Canyon Sanitary Landfill..
Edward B. Weil, 1981, Cultural Resource Survey of Proposed
Pelican Hill Road.
Jean & L. W. Lewis Tadlock, 1979, San Joaquin Hills Transpor-
tation Corridor Cultural Resources Study. -
David -Van Horn, 1983, A.Cultural/Scientific Resources Investi-
gatiorr of the Planned San ,Joaquin Hills, Transportation .Corrir
dor (.Phase II).
Beth Padon, 1982, Cultural Resources�'Survey for General Plan
.Amendment, Bommer and Shady .Canyons.
16 Theodore G. Cooley, 1974, Scientific.Resourcet Survey of Field
514' in Irvine Center (letter report).-
17 Theo N. Mabry,-1978, Archaeological Records.Search. and Recon-
naissance Investigation, Agua Chinon Flood Control Improvement
Project.
18 Theodore Cooley. and Adella- Schroth,' 1979, Archaeological
Resources Assessment., Irvine Ranch Water District Pipeline
Right -of -Ways.
19 Marie Cottrell, 1977, Santiago Aqueduct Parallel Reaches 2-6
(letter report).
20 Beth Padon, 1983, Hi sto.ri c Property Survey Report ,for Irvine
.Center Drive Widening,.
21 Theodore Cooley, 1974, Letter Report on Proposed Haul Road.
0
Archaeological Surveys (Cont.)
Code Reports Included Within Coded Area
22 Cottrell, Marie, 1978, Letter Report on Addendum to Previous
Report on Reach 4, Santiago Canyon Parallel Aqueduct.
23 Pat Sperry, 1972, Site Survey Report, U.S. Marine Hel'i-copter
Base: Tustin, CA.
24 Beth Padon, 1983, Historic Property Survey Report Proposed
Yale Avenue/I-5 Overcrossing.
25 LSA, Inc., 1982, Historic Property Survey for Proposed
Improvements_ to Jeffrey Road and I-5.
26 SRS, Inc., 1978, Cultural Resources .Report, San Diego. Creek
Watershed in Hicks Canyon, "Hicks Canyon Wash, Rattlesnake
Canyon Wash, San Diego Creek, and San Joaquin Marsh.
27 Marie Cottrell, '1976,, Walk -Over Survey of Irvine Boulevard
Between Sand Canyon and Jeffrey Road.
8- Archaeological Planning Collaborative, 1979., His"toric. Property
Survey, Moulton Parkway/ -Irvine Center Drive.
29 SRS, 1982, Cultural Resource Property Survey", Orange County
Rapid Transit Concept Design located in the Central Portion of
Orange County.
30 Pacific Coast Archaeological Society, -Inc.,- 1973, Walk -Over
Survey of Five" Miles Along North Side of San Diego Freeway-
0 etter report). On file at the PCAS Research Library..
31 Theodore Cooley, 1974, Field Survey of the -Proposed Right -of -
Way for the Extension of Michelson Drive (letter .report).
32 Ron Douglas, 1981, Historic Perspective" Survey, Harvard
Avenue/I-405 Overceo"ssing.
33 Theo Mabry, 1979, Records Searc-h "and -Reconnaissance, Harvard
Avenue Extension.
34 William A. Dodge, 1978, An Archaeological Assessment of Eight
Cultural Localities Along the San Qnofre/Santiago: 220-KY
Transmission Line.
ft-
Archaeological Surveys (Cont.)
Code Reports Included Within Coded Area
Lowell Bean and S. Vane, 1979, Cultural Resources and *the
High -Voltage Transmission Line From San Onofre to Santiago
Substation and Black Star Canyon..
Westec, Inc.; 1980, National Regi-ster Assessment Program of
Cultural Resources of the 230-KV Transmission Line Right -of -
Way From San OnofreNuclear. Generating Substation to Bl-ack
Star Canyon and Santiago Substation- and to E nci na and, M-i ssi on
Valley.
CSRI, Inc., '19K, Cultural- Resource- Data Recovery Program for
the 230-KV Transmission Line Right -of -Way From Sa-n O.nofre
Nuclear -Generating Station to Black Star Canyon and Santiago
Substation. and to Encina and- Mission Valley -Substation.,
Volumes 1 and 2.
0
b
w
L jLJ
L k
14
1NE
" V61
,.::'' •f
►.,`'-� M
:.........
MIN—
I r v i n e Archaeological Documents
M E A
Index M9 Unsurveyed Areas
D 7
Rep—d:dune 6,1995
0 2000 4000 6000 8000
Feet
Irvine Corporate Limits
"' Sphere of Influence
1
MAP TITLE: I STATISTICAL AREAS AND RESIDENTIAL PHASING
MAP TYPE: DATA
DATE PREPARED: AUGUST 26, 1985
LAST UPDATE: NONE
_
Statistical Areas - 1st and 2nd'digits
Code
Interpretation
Code
Interpretation
OOx
(Federal or state property)
Olx
Statistical Area 1
18x
Statistical Area. 18
02x
Statistical Area 2
Ox
Statistical Area 19
03x
Statistical Area 3.
20x
Statistical Area'20
04x
StatisticalArea 4
21x
Statistical Area 21
05x
Statistical Area 5
22x.
.Statistical Area 22
06x
Statistical Area .6
23x
Statistical Area 23
07x
Statistical Area 7
24x
Statistical Area 24
08x
Statistical Area 8'
25x
Statistical Area 25'
09x
Statistical Area 9
26x
Statistical Area 26
10x
Statistical Area 10
27x
Statistical Area 27
llx
Statistical Area 1 l'
28x
. Statistical Area 28
12x
-Statistical Area 12
29x
Statistical Area 29
13x
Statistical Area 13
30x
Statistical -Area .30
14x
Statistical- Area 14
31x
Statistical- Area-31 .
15x
-Statistical Area 15
32x
Statistical Area 32
16x
Statistical Area .16
33x
Statistical Area 33
17x
Statistical Area 17
34x
Statistical Area 34
35x
Statistical Area 35
Residential Phasing_-. 3rd digit .
Code Interpretation
xxO Not part of the Residential Phasing Plan
xxl Phase 1 (To 1974-75)
xx2.
Phase 2
(1974-75 to 1979-80) .
xx3
Phase 3
(1979-80 to 1984-85)
xx4
Phase 4
(1984-85 to 1989-90)
xx5
Phase 5
(1989-90 to 1994-95)
xxd
Phase 6
(Beyond 1994-95)
�..w�' �'���yGJj ,.'S(•xy�s�` 4y.F 1�' •. ����»n� ��.� {i \„ IR
�„ 'ice .,., -�� � � `-. ipt`= �Ot :: c.-• �•, _ -';�"�l<
'{.+�'� \�.•� R,:�`".: .4 its � '•J�,�,/�' 1 f
',+ . i • � � :lyd.
370 ll
� 0Owl r-h'i
66 I �!I
1 V-7,
•t � � �yp4.
IC3.D5+'"if�YZ%na.Y.—ice"--<.rrry
\7LGxAouw - - f•
�L i
`� ' x `�� I ] I ti / (—i- {ice-T-'i--
I r ° ' ° e Statistical Areas &
M E A
D 8 Residential Phasing
-
0 2000 4000 6000 8000
Feet
Irvine Corporate Limits
Sphere of Influence
Pmpamd:Au8ust26,1985
0
MAP TITLE: ITAP ZONES
MAP TYPE: DATA
DATE PREPARED: SEPTEMBER 12, 1985
LAST UPDATE: NONE
ITAP Zones
Map codes are equivalent to ITAP zone nuinerical designations. Some zones extend
beyond MEA study area, and some'lie entirely outside the ME study area resulting in
gaps in the numbering sequence.
- - -A
ra
w
"o) N1
X
43
YN
ni
_4 K�e , W6
�J
ILI
10TV 2
55 67, z?n
V�
F J5
�`.�;,�,
fill i!,5111 I Uq 2
lie _j
IF
JLII
21
It A
tip
A MIN PAN 7
55AQ XMZ \7 QQ
JUDIA'Ad"I'M h. 1, ME.I. aw29
g L
ZJ
2-
r 11"8
US N
4-
29
r4f!1L ki
—3 _3
442 130 1 I1C 136
j[-
1 s.
wall
'17- W41,
C
(D
RMIL 58 T-0--PtILL
g�
7
265
26
x-
281,;�
I r v i n e ITAP Zones
M E A
D-9
0 2000 4000 6000 8000
Feet
Irvine Corporate Limits
Sphere of Influence
Prepared September 12, 1985
r
MAP NUNVIBER: ' D-10
MAP TITLE:
CENSUS AREAS -
MAP TYPE:
DATA
DATE PREPARED:
AUGUST 28, 1985
LAST UPDATE:
NONE
Regional Statistical. Areas (RSA) - 1st & 2nd digits
Code Interpretation
39xx RSA Number F-39 (Central Coast)
44xx RSA Number E44 (El Toro)
CommunijAnalysis Areas (CAA) - 3rd & 4th digits
Code
Interpretation .
xx47
CAA Number 47
(North Newport Beach)
xx48'
CAA Number 48
(Airport Commercial)-
xx49
CAA Number 49
(Irvine Industrial Complex) .
xx50
CAA Number 50.
(South Irvine)
xx51.
CAA Number 51
(Central Irvine)
xx52
CAA Number 52
(North Irvine)
xx53
CAA Number 53
(East Irvine Industrial)
xx54
CAA Number 54
(MCAS, El Toro)
xx61
CAA Number 61
(Laguna Beach)
is
I r v i n e
M E A
D-10
Census Areas
0 2000 4000 6000 8000
Feet
Irvine Corporate Limits
"' Sphere of Influence
NcPamd' Au8urt28,1985
MAP NUMBER: D-11
MAP TITLE: IRWD TOKEN AREAS
MAP TYPE: DATA
DATE PREPARED: SEPTEMBER 8, 1985
LAST UPDATE: NONE
Token Areas
'Code. Interpretation Code Interpretation
O1 Not Used 38 Token Area 38
02 Not Used 39 Token Area 39
03 Token Area 03 40 Token Area 40
04 Token Area 04 41 Token Area 41
05 Token Area 05 42 Token Area 42
06 Token Area 06 43 Token Area 43
07 Token Area 07 44 Token Area 44
08 Token Area 08 45 Token Area 45
09 Token Area -09 46 Token Area 46
10 Not Used 47 Token Area 47
11 Not Used. 48 Not Used
12 Not Used 49 Not Used
13 Not Used 50 Not Used
14 Token Area 14 51 Not Used
.15 Token Area 15 52 Token Area 52
16. Token Area 16 53 ' Code Not Used
17 Token Area 17 54 Token Area 54
18 Not Used .55 Token Area 55
19 Not Used 56 Token Area 56
20 Token Area 20 57 Token Area 57
21 Token Area 21 58 - Not Used -
22. Token Area 22 - 59 Token Area 59
23 'Token Area 23 60 Token Area 60
24 Token Area 24 61 Token Area 61
25 Token Area 25 62 Token Area 62
26 Token Area 26 63 Not Used
27 Token Area 27 64 Not Used
28 Token Area 28 65 Token Area 65
29 Token Area 29 -66 Not Used
30 Token Area 30 67 Token Area 67
31 Token Area 31 68 Not Used
32 Token Area 32 69 Token Area 69
33 Token Area 33 70 Token Area 70
34 Token Area 34 71 Not Used
35 Token Area 35 72 Token Area 72
36 Token Area 36 '73 Not Used
37 Token Area 37 74 Token Area 74
Note: Codes not used represent token areas outside MEA 'boundaries. Some areas
within the MEA area also extent beyond the boundaries.
n
M E A
D-11
IRWD Token Zones
0 2000 4000 6000 8000
Feet
Irvine Corporate Limits
"' Sphere of Influence
Mp-d: &pt—ber 8, 1985
L 7_�
AD J0 0 Q 'JUEMA
EXPANDED CODE -DESCRIPTIONS
i
0
0
C ]
Expanded Code Descriptions
MAP C-1
GEOLOGICAL HAZARDS
1 Seismic Response Area (SRA) 1 Potentially soft or loose soils/high ground water.
This is one of the two areas considered to have --greater potential for ground failure in
the form of liquefaction, in' comparison to the other seismic response areas.
Liquefaction is not expected to occur for all earthquakes, nor over the whole of SRA
1.
2 Seismic. Response Area (SRA) 2 - Denser soils/deeper ground water. The
predominant potential seismic hazard in this area is ground motion. Ground
breakage, or ground failure is not expected to characterize this area. Localized
liquefaction potential is remote.
3 : Seismic Response Area (SRA) 3 - Shallow alluvium over and abutting bedrock.
Ground motion. is primary potential .seismic hazard. As slope increases, slope
instability potential increases. Localized liquefaction potential is remote.
4 Seismic Response Area (SRA) 4 - Highlands characteristically over , 20% slope.
Area is, in general, potentially less. stable -than SRA 3 due to the. larger incline.
Liquefaction potential is extremely remote.
5 Seismic Response Area: (SRA) 5 - Less stable geologic formations. These are -areas
representing existing mapped landslide areas. As such,, potential for slope instability
is higher than in SRA 4.
Expanded Code Descriptions
Page 3
MAP C-4
AGRICULTURAL CAPABILITY
1 Class I -Soils-- Soils with few limitations that restrict their use for,field crops.
2 Class II Soils - Soils- have moderate limitations that reduce the choice of plants or
that require moderate conservation practices, or both.
3 Class III*and IV Soils
Class III Soils - Soils have, severe limitations that reduce the- choice of plants
or require special conservation practices, or both.
Class IV Soils - Soils have very severe limitations that reduce the choice of
plants, require very careful management, or both.
5 Other than' Class I through IV Soils - Severe soil iimitations restrict their use
largely to uses such as pasture, range, woodland, wildlife,. recreation, water supply,
or aesthetic purposes.
9 Water - Reservoirs, small farm ponds and natural lakes. Flood control basins are not
included in this classification unless there are areas of permanent inundation.
0
•
i
0
Expanded Code Descriptions
MAP D-1
LANDFORM
01- .Lake -'A standing body of inland water.
P: age 4
02 Reservoir - An artificial standing body of inland water. The water may be supplied
by either natural stream flow into the depression -or by the importation of, water
through the -use of canals, pipes,. and .pumps. - .
'03 Coastal Lagoon/Estuar-y - Shallow water bodies which have a direct but restricted
connection to the sea. They contain ocean derived salts which tend to cause clay
minerals held in incoming fresh water to coagulate or flocculate and settle, gradually
filling the lagoon with sediment. Most southern California lagoons have been
dredged, to provide boat harbors and marina. Where such dredging has been carried
out and there is an unrestricted influx of ocean water subject to tidal flux and wave
.action, the area has nor been mapped as apart.:
04 -Depression - A low place of any size on -a plain surface, -with drainage underground
or by evaporation. It can also mean a hollow completely surrounded by higher
ground -and having no natural outlet.
05 Delta - Generally a prograding or building :marine shoreline. Deltas exhibit a variety
of '-forms but all of them are conspicuous seaward bulges on the shoreline at the
mouths of rivers where deposition of sediments -is, caused by the rapid reduction in
current velocity. Delta growth, while often rapid under natural conditions, has all but
ceased along the rivers and estuaries of .the southern California coast because of the -
effect of upstream flood control projects and because urban -land covers have acted to
limit the amount of sediments which reach the ocean coast. Where the lower portion
of a delta is overlain by a coastal lagoon or marsh/swamp, the latter take precedence
for mapping.
05 Beach : The zone of unconsolidated material that extends landward from the low
water line to where there is a noticeable change in material. or physiographic form, or
to where there is a line of permanent vegetation. In recent time the amount of
sediments reaching the beaches of southern California from streams has been greatly
diminished through a variety of man -mad- features such as flood control structures
and settling basins and through the construction of artificial surfaces in urbanized
areas; the net result has been a decrease in the, size of the beaches. .
l�
i
0
Expanded Code Descriptions
D-1 Landform (Cont.)
Page S
07 Dunes - Irregularly shaped hills and depressions paralleling the coastline. Coastal'
dunes are sometimes found landward of sand beaches, particularly where there is. a
coastal plain. Often these dunes have plant cover which helps. to stabilize the- dune.
A second type of sand dune is the climbing_ dune. which occupies hollows in the
mountain front inland from a "feeding" beach or other source of dune materiaL Here
the breezes blowing in from the sea carry sand and shell fragments and deposit them
along the foot of the mountain.
08 Cliffs - The steeply sloping zone between two flat or -shallowly sloping landforms,
such as between a beach and an elevated terrace.. Cliffs, are inaintairied by the erosion
and removal of material from the foot of the higher -landform by either wave or
stream action. Cliffs may be unstable, depending on the nature of the materials from
.which they are made. Where they are unstable they represent zones of potential
surface 1ailure. Erosion at the base of such cliffs often causes the cliff face to
collapse.
09 Gully-- Steep -walled, canyon -like trenches -whose upper- end grows progressively in.
an upslope direction. The distinguishing feature of a gully is that it cuts across a flat
surface such as a terrace. Gullies . are characteristically dynamic features, with
flooding and consequent erosion quite common.
10
F000dplain - A low, flat belt of land bordering most major .steams and rivers just
above the stream surface. In areas where there has been no interference by man, all
or part of this surface may be flooded annually, with -consequent erosion and
deposition. Because most major streams in southern California. have been
channelized and their flows regulated by dams, floods .no longer -regularly cover
floodplain surfaces.. However, even with all of the current flood prevention
measures, floods are much more likely
landforms.
to occur on floodplains than on most other
11 Upland Valley - The gently sloping surface at the bottom of mountain canyons and
coastal valleys and above the active floodplairi. Unlike an alluvial terrace, where the
terrace is separated from the floodplain by a cliff or terrace foreslope, the transition
between a floodplain and the valley -bottom is gradual. The valley bottom above the
floodplain is generally safe from flooding and landsliding.
12 Marine Terrace Bench - Old coastal plains or wavecut benches which now stand
above sea level and are separated from the ocean by a cliff or terrace sideslope.
Several marine terraces standing at different elevations and of different ages can
occur along the coast The seaward margin of marine terrace is frequently unstable
due to erosion; it is here that cliffs often occur.
0
i
is
Expanded Code Descriptions
D-I Landform (Cont.)
Page 6
13 Marine Terrace Sideslope - A transitional zone where a marine terrace is separated
from another flat landform at a different elevation. The separation is typically
marked by a grade of intermediate slope.
14 Alluvial Fan - Sands and gravels carried by a- steam and- deposited in a, fan shape
apron. Within the mountains, the stream's position is fixed -in its canyon, but upon
entering the plain the steam constantly shifts, sweeping back and forth in an arc,
depositing sediments in a cone with a. convex profile as the waters spread and seep
into the ground. Unless the steam has become entrenched or has been channelized by
Man, alluvial- fans present a potential for flooding.
15 -Alluvial Terrace Bench .-- Sediments which have been deposited along river
floodplains, in -valleys and at the foot -of mountain side slopes. These sediments are
often left as terraced deposits as. stream cut lower -beds and as orthographic uplift
raises the general level of the land. Because. these deposits are generally
unconsolidated to loosely consolidated they often exhibit instability, especially when
they occur adjacent to a.steeply sloping area.
16 Alluvial' Terrace Sideslope - A transitional zone where an alluvial -terrace is
separated from another- float landforin at a different elevation. The separation is
typically marked by a grade of intermediate slope.
17 Alluvial Plain - A flat to gently sloping surface formed of older alluvial sediments
deposited by water. This sedimentary material consists of fine mud, sand, or gravel
and generally fills former valleys. -
I& Landslide - A mass of rock that has moved downslope in one event. Landslode
includes all forms of land surface failures. The landslides mapped are of varying
ages, but all of them are Pleistocene or younger. Where the landslide mass moved as
one discrete unit there is a high potential 'for reactivation of the slippage ' planes.
Where the landslide fell as a crumbled mass with, many .slippage planes, renewed
movement can occur on any one of more of these plains.
19, Rock Outcrop - The above surface expression of a subsurface rock formation.
20 Mountain Ridgetop - The flat or nearly flat surfaces at the tops of mountains. These
generally are quite stable. Mountain ridgetops tend to form visual breaks in the
landscape, making them particularly sensitive areas in terms- of visual impacts.
21 Mountain Sideslope - All of the steeply sloping areas within the mountain ranges.
The stability of the mountain sideslopes varies widely with the geologic rock ,type
and internal structure.
Expanded Code Descriptions
D-1 Landform (Cont.)
•
Page 7
22 Hilltop - The flat or nearly flat surfaces at the topes of hills or foothills. Hill/foothill
tops tend to form visual breaks in the landscape, making them ,particularly sensitive
areas in terms of visual impacts. Hill/foothill tops differ from mountain ridgetops in,
that hill/foothills tend to be either isolated areas, of higher elevation or transitional
areas between the shallow plains, valley bottoms, and terraces; and the steeper
mountain sideslopes. Hills/foothills .are smaller than mountains and are: generally
less than 1000 feet above the surrounding terrain.
23 Hill/Sideslope - All of the steeply sloping areas within the hills and foothills tend to
be less severe than those found in' the mountain classification.
24 ' Man-made/Altered - This class applies to those areas where the natural landform no
longer exists.
•
Expanded Code Descriptions
MAP D-2
SLOPE ZONES
Angle of Gradient
Code % Slope Inclination. Slope Ratio- (Feet per Mile)
1 0-5% to 20 52' 20:1 264
2 5-10% to 50 43' 10:1 '528
3 10-15% to 80 35' 6.66:1 792
4 15-20% to 110, 26' 5:1 1056
5 20-25% to 140-17' 4:1 1320
6 25-30% to 170 11' 3.33:1 1584
7 >30%- over 17011' over:3.33:1 over 1584
Page 8
Expanded Code Descriptions
MAP D-3 AGRICULTURAL
BUILDING
SITE
o a
SOILSCAPABILITY
DEVELOPMENT
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Page .9
PHYSICAL AND c-a y
CHEMICAL PROPERTIES C H a
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1 Alo clay 415 2 315 611 6 6 6 6 6 1 1 4 03- 6 6 1 14 3 5 1
2 Alo variant -
clay 415 2 315 611 6 6 6 6. 6 1 1 4 03 6 6- 1 14 3 5 1
3 Anaheim loam 411 2 411 611 6 6 6 6 .6 1 1 5 09' 1 •1 1 25 3 4 1
4 Anaheim
clay loam 6-11 2 411 711 6 6 6 6 6 2 1 5 08 4 '4 1 22 3 4 1
5 Balcom
clay -loam 611 2 311 611 6 5. 6 5 6 2 1 5 08 4' 4 1 25 3 2 •1
6 Balcom-Rock .
outcrop
complex 631 1 631 631 6 6 6 6, 6 2 1 5' 08' 4 4 1 25 3 2 1
7 Beaches 821 1 821 821 -0 0 0 0 0 0 0 0 00 0 0' 0 00 0 0' 1
8'Blasingame
loam 411 1 -411 41.1 6 6 6 6 6- 2-- 1 5 09 2 2 2- 13 3 4 1
9 Blas-ingame
stony loam 731 2 631 731 6 6 6 6 6 2 1 5 09 1 2 2 09 3 4 1
lO.Blasingame—
Rock outcrop
-complex 631 1 631 631' 6 6 6 6 6 2 1 5 09 2 2. 2 13 3 4 1-
11 Blasingame—
Vista complex. 611 2 411 611 5 5 6 5 6 1 1 4 10 2 2 2 08 3 4 1
12 Bolsa '
silt loam .222 1 222 222 4 6 6 4 6 1 1 1 08 4 6 1 27 7 4 2
13 Bolsa silt
loam, drained 100 1 100' 100 4 6 6 4 6 1 1 1 08 4 6 1 27 7 4 2
14 Bolsa silty
clay loam 222 1 222 222 4 6 6 4 6 1 1 1 08 4, 6 1 27 7 4 2
15 Bolsa silty
clay loam,
drained 100 1 100 100 4 6. 6 4 6 1 1 1 08 4 6 1, 27 7- 4 2
16 Bosanko clay 415 2 315 611 6 6. 6 6 6 1 1 5 03 6 6 1 19 5 5 1
17 Bosanko—Balcom
complex 415 2 415 611 6 6 6 6 6 1 1 5 04 5 5 1 21 4 3 1
18 Botella loam 211 1 211 211 1 4 4 6 6 1 1 1 09 4 4 1 24 1 2 1
19 Botella
clay loam 211 2 211 311 4 4 5 6 6 1 1 1 OS .4 4 1 23 7 2 1
• 20 Cal] eas
loam,
clay loam,
eroded 711 1 711 711 6 6 6 6 6 1 1 7 09 4 6 1. 22 1 5 1
Expanded Code Descriptions
D-3 Soils (Cont.)
Page 10
AGRICULTURAL
BUILDING SITE
z m_
PHYSICAL AND
z
CAPABILITY
DEVELOPMENT
6'
CHEMICAL
PROPERTIES
WF4
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21 Capistrano
sandy loam 311 2 311 411 2 2 5 4 2 2 1 1 13 • 1 1 1 14 7 2 1
22 Chesterton
loamy sand 611 1 611- 611 .5 5 6 6 6 1 1 1 06 2 3 1 22 3 5 1
23 Chino silty
clay• loam - 222' 1 222 222 4 4 4 6 6 1 1 1 08 4 6 1 00 0 4 2
24 Chino silty
clay loam,
drained 100 1 100 100 4 4 4 6 6, 1 1- 1 08 4 5 1 00 0 4 1
25 Cieneba
sandy -loam 611 1- 611 611 6 6 6 6 6 1 1 8 13 1 1 1 14 1 4 1
26 Cieneba
sandy loam,
eroded 711 1 711 711 6- 6 6 6 6- 1 1 8 13 1 1 1 14 1 4- I
27 Cieneba-
Bl as ing amem-
Rock outcrop
complex 631 1 631 631 6 6 6 6 6 1. 1 6 10 2 2 2 12 2 4 1
28 Cieneba-.
Rock -outcrop
complex' 631 2- 631 731 6 6 6 6 6 1 1 8 13 1 1 '1 14 1 4 1
29 Corralitos
loamy sand 334 1' 334 334 _6 1 1 1 1 2 1 1 17 1 4 4 i9 7 1 1
30 Corralitos -
loamy sand,
moderately
fine sub-
stratum 234 1 234 234 6 1 1 1 6 2 1 -1 07 2 5, 4 07 7 1 3
31 Cropley clay 215 2 215 235 6 6 6 6 6 1- 1 1 03. 6 6 1 14 7 5 4
32 Escondido very
fine sandy
loam 611 2 411 611 5 5 6 5. 6 1 1 5 09 1 1 4 25 1 5 1
33 Exchequer -
Rock outcrop
complex 731 1 731 731 6 6 6 6 6 1 1 8 09 1 1 4 25 1 5 1
34 Friant - fine -
sandy loam 711 1 711 711 6 6 6 6 6 2 1, 8 13 1 1 1 22 1 5 1
• 35 Gabino gravelly
clay loam 631 1 631 631 6 6 6 6 6 1 1 4 03 5 5 2 16 5 5 1
Expanded Code Descriptions
Page 11
D-3 Soils (Cont.)
AGRICULTURAL
BUILDING
SITE
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AND
CAPABILITY
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<
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222-
222
6
6
6
6
6
2
1
.1
13
1
6
1
00
0
4
2
39 Hueneme fine
sandy loam,
drained
100
1
100
100
1
1
1
1
1
2
1•
1
13
1
6
1
00
0
2
1
40 Las Posas
gravelly loam
711
1
71.1
711-
6
6
6
6
6
1
1
4
09,
3
5
1
14
3
4
i
41 Laughlin
gravelly loam
711
1
711
711
6,
6
6
6
6
1
1
4
10
2
4
4
16
3
4:
1
42 Marina
loamy sand-
434
2
334
434
6
1
2.
1
1
.2
1
1
09
1
1
1
01
7
2
1
43 'Metz
loamy .sand-
334
1
334
334
6
1
1
1
1
2
1
1
11
1
6
.1.
03
7
1
1
44 Metz sandy loam,
moderately fine
sub —stratum
234
1
234
234
6
1
1
1
1
2
1
1
11
2
6
1
05
7
1
1
45 Mocho
sandy loam
100
1
100
100
1
4-
-4
4
4
1
1
1
09
2
6
1
18
7
2
1
46 Mocho, loam
100
2
100
211
1
4
4
4
4
1
1
1
09
2
6
1
27
7
2
1
47 '.T odjeska
gravelly loam
334
2
314
411
6.
3
3
3
3
1
2
1
14
1
1
4
04
3
2
1
48 Myford
sandy loam
413
2
413
611,
5
6
6'
6
6
1
1
1
02
3
6'
2
15
.3
5
1
49 Myford sandy
loam, eroded
711
2
611
711
5
6
6-
6'
6
1
1
1
02
3
6
2
15
3
5
1
50 Myford sandy
-
loam, thick
surface
333
2
313
333
4
6
6
.6
6
1
1
1
02
3
6
2
15
3
5
1
51 Nacimiento
clay loam
411
2
411
611
6
6
6
6
6
1
1
4
09
-4
6
1
22
3
4
1
52 Omni silt
•
loam, drained
233
1
233
233
6
6
6
6
6
l
1
1
OS
5
6
4
00
0
5
1
53 Omni clay
326
1
326
326
6
6
6
6
6
1
1
1
04
7
6
4
25
7
5
1
54 Omni clay,
drained
235
1
235
235
6
6
6
6
6
1
1
1
04
6
6
4
00
0
5
2
Expanded Code Descriptions,
Page 12
D-3 Soils (Cont.)
AGRICULTURAL
BUILDING SITE
z m
a
rHz�i�tw euvu
CHEMICAL PROPERTIES
Wes•
z w ra
CAPABILITY
DEVELOPMENT
ri
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55 Pits
831
1
831
831
0
0
0
0
0
0 0
0
00
0
0
0'
00
0
•0
1
56 Ramona fine
• sandy .loam
311
1
311
311
1
1
4
4
6
2 1_
1
10
1
2
2.
23
7
2
1
57 Ramona
gravelly fine
sandy loam
411
1
411
411,
4•
4
6
.4
6
2 1
1
10
1
2
2
22
7
2
1
58 Rincon
loam
213
2
213
413
5
6
6
6
6
1 1
1
06
5
5
2
26
6
4
1
.clay
59 Riverwash
821
1
821
821
0
0•
0
0
0
0 0
0'
00
0
0
0
00
0
0
1
60 Rock outcrop—
Cieneba
complex
731
1
731
731
6.
6
6
6
6
1. 1
8
13
1
.1
1
14
1 '
4
1
61 San Andreus
sandy loam
611
1
611
611
6
6
6
6
6
1 1
5
13
1
4
4
:02
3.
2
1
62 San Emigdio
fine sandy
loam
100
2
100
211
1
1
2
1
1
2 1
1
13
1-
6.
1
22
7.
2
1
63 San Emigdio
fine sandy
loam, mod—
erately fine
sub —stratum
100
2
100
100
1
1
1
1
6
2 1
1.
10
-1
6
1
17
7
2
1
64 Soboba
gravelly
loamy sand
631
1
631
631
6
1
1
1
1
`3 3
1
18
1
1
1-
02
7
1
1
65 Soboba cobbly
loamy sand
631
1
631
631
6'
4
6
4
4
3 3
1
18
1
1
1
02
7
1
1
66 Soper loam
611
2
41i
611
6
6
6
6
6.
1 1
5
09
2
4
2
20
5
4.
1
er
67 gravelly loam
711
2
611
711
6
6
6
6
6
1 1
5
09
2
4
2
20
5
4
1
68 Soper
cobbly - loam
731
1.
731
731
6
6
6
6
6
1 1
5
09
2
4
2
20
5
4
1
69 Soper=rock
outcrop
complex,
731
1
731
731
6
6
6
6
6
1 1
5
09
2
4
2
20
5
4
1
70 Sorrento
sandy loam
100
1
100
100
4
4
4
6
4
1 1
1
10
2
6
1
21
7
2
2
1
1
71 Sorrento loam
100
2
100
211
4
4
4
6
4
1 1
1
09
2
.6
1
25
7-
72 Sorrento
clay loam
100
2
100
211
4
4
4
6
6
1 1,1
09
2
6
1
23
7
2
1
Expanded Code Descriptions
D-3 Soils (Con,.)
Page 13
AGRICULTURAL
BUILDING SITE
x y
PHYSICAL AND
x y
CAPABILITY
DEVELOPMENT
6
CHEMICAL
PROPERTIES
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73 Thapto-Histic
Fluvaquents
326
1
326'
326
6
6
6
6
6
1
1
1
06
3
6-.
3 00
0
5 2
74- Tids]. flats
821
1
821
821
0
0
0
0
0
0
0
0
00
0
0
0 00
0
0 1
75 Tollbouse-
Rock outcrop.
complex
731
1
731.
731
6
6
6
6
6
2
2
8
17
1
1
4 14
1
5 1
76 Vista coarse
. sandy loam
711
2
411
711
5
5
6
5
6
1
i
4
13
1
4
4 19
3
4 1
77 Vista -
Rock outcrop
outcrop
complex
631
1
631
631
6
6
6
6
6
1
1
5
13
1
4
4 19
3
4 1
78 Xeralfi'c
Arents,-loamy
900
-1
-900
900
2
2
5
-2
6
1
1
1
00
0
0
0 00
0
2 1
79 Xerorth6nts,
loamy, cut &
fill areas
900
1
900
900
6
5
6
5
6
1
1
2
00
0
-0
0 00
0
4. 1
80 Yorba gravelly
sandy loam
413
2•
413
631
6
5
5
5.
6
1
1
1
06
2
2
4 11
1
5 1
81 Yorba cobbly
sandy loam
731
2
631
731
6
6
6
6
6
1
.1
1
06
2
2
4 11
1
5 1
82 Yorba cobbly
loam, eroded
731-
1
731
731
6.
6
6
6
6'
1
1
T
06
2
2
4 11
1
5 1
83 Water
000
0
000
000
0
0
0
0
0
0
0
0
00
-0
0
0 00
0
0 0
Expanded Code Descriptions Page 14
D-3 Soils (font.)
AGRICULTURAL CAPABILITY
Agricultural Capability for each soil series -is coded infourfields
representing the capability rating for the predominant phase, the existence
of aultiple phases 'within the series, the 'capability rating of, the highest
rated phase, and that of the lowest 'rated phase, respectively. Capability•
ratings (fields 1, 3, and 4) consist of three digit codes as defined below:
First Digit - Capability Classes
This one -digit code describes "the suitability.of soils for most -kinds of
field crops, according to the limitations imposed by those soils. The code
corresponds to standard SCS designations:
1 1i Class I - Soils have few limitations that.restrict their use.-
2 --Class II = Soils have moderate limitations that reduce the choice of
plants or that require moderate conservation practices, or -both.
3 - Class III - Soils have severe limitations that reduce the choice of
plants or require' special conservation practices, or both.
4 Class IV --Soils have very severe limitations that reduce the choice
of plants, require very careful management, or both.
5 - Class. V - Soils are not.likely to erode but have other limitations,.
impractical to remove, that limit their use largely to pasture
or range, woodland, or wild -life. (None in this survey area.)
6 Class VI - Soils have severe -limitations that make them generally
unsuited to cultivation and that limit their use largely to pas-
ture or range, woodland, or wildlife.
7 - Class VII - Soils have very severe limitations that make them
unsuited to cultivation and'that restrict their use largely to
pasture or range, woodland, or wildlife.
8 - Class VIII - Soils and landforms have limitations that preclude
their use for commercial production of crops and restrict their use
to recreation, wildlife,.or water supply, or to aesthetic purposes.
9. - Unit too varied to rate. The numerals indicate -progressively
greater limitations and narrower choices for practical use.
Second Digit - Capability Subclasses
This one digit code describes the primary limitation on a soil's
capability. This limitation is characterized by adding an alpha symbol to the
SCS capability rating; numerals corresponding to these are as follows:
•
a
E
Expanded Code Descriptions
D-3 Soils (Cont.)
1 e - Main limitation is risk of erosion.
2 w - Water in or on the soil interferes with plant growth or
cultivation.
3 - s-'Soil.is limited because it is shallow, droughty, -or stony-
4 -'c - Limitation is climate that is too cold or dry.
Third Digit - Capability Units
Page 15
This one digit code describes the basis for inclusion of a 'so•il into a
particular class and subclass; and allows grouping of soils into- groups.
requiring similar management. These are designated in -the SCS system by
numerical symbols following the subclass letter, as follows:
0 - A problem or limitation caused by sand and gravel in the sub
-
�stratum, which limits root penetration.
1 An actual or potential erosion'hazard.
2 A problem or limitation of wetness caused by poor drainage or
flooding.
3 --A problem or limitation caused by.slow or very slow permeability
of the subsoil or'substratum.
4 - A problem or limitation caused by coarse soil texture or
excessive gravel._
5 - A problem or limitation caused by a fine textured or very fine
textured soil.
6--A,problem or limitation caused by salts or alkali.
7 - A problem or limitation caused by cobbles, stones, or -rocks..
8 - A problem or limitation caused by nearly impervious bedrock
or a hardpan within the effective -rooting depth.
9 - A problem or limitation caused by low fertility or by toxicity.
(None in this survey area).
This existence of multiple phases within a.series is shown by a
one -digit code in field 2 as follows:
1 - Only one phase within the series.
2 - Two or.more phases/variants within the series.
Expanded Code Descriptions Page 16
D-3 Soils (Copt.).
BUILDING SITE DEVELOPMENT
Limitations on development have been evaluated fo'r-four different
building considerations: shallow excavation, dwellings wiihdtit'basements,
small commercial buildings, and local roads and streets. Limitations on
septic tank absorption fields have.also been.evaluated. Limitation ratings
represent the value assigned -by SCS.to the soil phase which occupies the
largest amount of acreage in the County relative to other phases within the
series..
Shallow Excavations
This one digit code describes'soil limitations influencing excavations
for pipelines, sewerlines, communications and power transmission lines,
basements, and open ditches. Codes 2, 3 and 5 represent series with a range
of ratings.
1 - Slight limitation - Conditions are generally favorable for the -
specified use, and- any limitation is easily overcome.
2 - Range 1 to 4
3 - Range 1 to 6 -
4 = Moderate limitation - Conditions are unfavorable for.the specified
use, but limitation can be overcome or minimized by special
planning or design.
5 = Range 4 to 6
6 Severe limitation - Conditions are so unfavorable or difficult
-to overcome that a major increase.in construction effort, special
design, or intensive maintenance is required.
Dwellinst Without Basements
This one digit code describes soil limitations influencing construction
of dwellings no more than three stories tall on undisturbed soil,. For such
structures, soils must be sufficiently stab -le that cracking or subsidence of
the structure from settling or shear failure of the foundation does not
occur. Codes 2, 3, and 5 represent series with a range of ratings.
1 - Slight limitation —Conditions are generally favorable for
the specified use-, and any limitation is easily overcome.
2 - Range 1 to4
3 - Range 1 to 6
Expanded Code Descriptions
D-3 Soils (Cont.)
4 - Moderate Limitation - Conditions are unfavorable for'the
specified use, but limitations, can be overcome or minimized by
special- planning 'or design.
S - Range 4 to 6
6 - Severe limitation , Conditions are so unfavorable'or difficult to
overcome that a -major increase in construction effort, special
design, or intensive maintenace is required..
Small Commercial Buildings
Page 17"
This one digit code describes soil limitations influencing construction
of commercial -buildings no more than three stories tall on undisturbed soil.
For such structures, soils must be sufficiently s'table'that cracking or
subsidence of the structure from setting or shear failure of the foundation
does not occur. Codes 2; 3, and 5 represent series with a range of ratings.
1 - Slight limitation - Conditions are.generally favorable for the
specified use; and any limitation is easily overcome.'
2 - Range 1 to 4-
3 - Range 1 to 6
4 - Moderate limitation - Conditions are unfavorable for the specified
use, but limitations can be�overcome or minimized by special
planning or design.
5 - Range 4 to 6
6 - Score limitation - Conditions are so unfavorable.or difficult to
.overcome that a major increase in construction effort, special
design, or intensive maintenance is required.
Local Roads and Streets
This -one digit code describes soil limitations influencing the
construction of all-weath'er;.light to medium duty roads, graded with soil
material at hand, with most cuts and fills less than six feet deep. Codes
2, 3, and 5 represent series with a range of ratings.
1 - Slight limitation - Conditions are generally favorable for the
specified use, and any limitation is easily overcome.
2 - Range 1 to 4
3 - Range 1 to 6
4 - Moderate limitation - Conditions are unfavorable for the specified
use, but limitations can be overcome or minimized by special
planning or design.
0
Expanded Code Descriptions
D-3 Soils (Cont.)
5 - Range, 4 to 6
6 - Severe Limitation - Conditions are_ so unfavorable or difficult to
overcome that a major increase in construction effort, special
design, or intensive maintenance is required.
Septic Tank Absorption Fields
Page 18
Limitations on construction of sanitary facilities have been evaluated
heie only for septic tank absorption fields; other considerations are
included in the, SCS Soil Survey. ' Th•e one digit code expresses the
limitations of the predominant soil phase within the series for construction
of fields consisting of subsurface systems of til& or perforated pipe that
distribute effluent from a septic tank into the natural soil at a depth of '18
to 72 inches. Codes 2, 3, and 5 represent series with a range of ratings.
1 - Slight limitation - conditions are generally favorable for the
specified use, -and any limitation is easily overcome.
2 - Ranged to 4
3 - Range 1 to 6
4 - Moderate limitation - Conditions are unfavorable for the specified
use, but limitations can be overcome or -minimized by special
planning or design:
5 - Range 4 to 6
6 -•Severe Limitation - Conditions are so unfavorable or difficult
to overcome -that .a major increase in construction effort, special
design, or intensive maintenance is required.
CONSTRUCTION MATERIALS
Soil series have been rated by SCS based upon the probability that soils
in a -given area will contain sizable deposits of sand.or gravel.
Source of Sand
This one dig -it code expresses the potential suitability of a soil as a
source for sand.
1 - Unsuitable - Soil has little potential as a source of sand.
2 - Poor - Soil contains sand, but it is in spotty deposits or
contains large amounts of finer material.
• 3 - Fair - Soil has 'a layer of suitable material at least 3 feet
thick, the top of which is within 6 feet of the surface=; however,,,
a large percentage of fine material may be included.
Expanded Code Descriptions
D-3 Soils (Cont.)
Page 19
Source of. Gravel
This one digit code expresses the potential suitability, of a soil as a
source for gravel.
1 - Unsuitable - Soil has little potential' as a source .of gravel.
2 Poor - Soil contains gravel, but it is in spotty deposits or
contains large amounts of finer materials.
3 = Fair - Soil has a layer•of suitable material at least 3 feet thick,
*,which is -wi'thin 6 feet of the surface; however, a large percen-
tage -of fine material may be -included.
PHYSICAL AND CHEMICAL -PROPERTIES
'Seven soil properties -are evaluated:
Depth
- -Permeability
- Shrink/Swell Potential
- Corrosivity to Untreated Steel
- Corrosivity to Concrete
- Erosion K Factor
- Erosion T Factor
Depth
This one digit code describes the average depth of the entire soil
profile. Codes 2, 4, 6,_and 8 represent series in Which -the range of soil
depth exceeds that shown within the individual classes below.
1'- Very deep - Over 60 inches
2 - Range 1 - 7
3 - Deep - 36-60 inches
4 - Range 3 to 5
5 - Moderately deep - 20-36 inches
6- Range 5 to 7
7 - Shallow 10-20 inches
8 - Range 7-9
9 - Very shallow - Less than 10 inches
•
i
Expanded Code Descriptions
D-3 Soils (Cont.)
Page 20
Permeability
This two digit code describes the permeability of the soil, estimated on
the basis of known relationships among the soil characteristics observed in
the field, particularly soil structure, porosity, and gradation or texture
that influence the downard movement of water in the.soil: Codes 2, 4., 5,
7, 9, 10, 11, 13, 14, and 17 represent series with a range of permability
ratings.
01 Very slow - Less than-0.06 (inches per,hour)
02 - Range 01 - 16
03 - Slow - 0.06 to 0.20
04 - Range 03 -.8
05 - Range 03 - 12
06 - Range 03 - 16
07 - Range 03 = 18
08 - Moderately slow - 0.20 to 0.80
09 -.Range .08 - 12
10 = Range 08 - 16
11 - Range 08 - 18
12 - Moderate - 0..80. to 2.50
13 - Range 12 - 16
14 - Range 12 - 18
15 - Moderately rapid.- 2.50 to 5.00
16 - Rapid - 5.00 to 10.00
17 -'Range 16 to 18
18 - Very rapid- Over '10.00'
Shrink -Swell Potential
This one digit code describes the expainsivity or shrink -swell potential
of each soil - that quality of the soil that determines - -its volume change
with change in moisture content. Codes 2, 3, and 5 represent series with a
range of shrink -swell potential ratings. -
Expanded Code -Descriptions
D-3 Soils (Cont.)
Page 21
1 Low - Soils range from sands to silt'loams with any clay mineral,
and sandy clay loams if the clay is kaolinitic..
2 - Range 1 to 4
3 Rang e 1 to 6
4 Moderate - Soils include the silty clay loam to clay textures
if the clay is kaolinitic, and heavy silt losms, light sandy
clays, and silty clay loams with mixed clay minerals.
5- Range 4-to 6
6- High - Soils include clay loans to clays with mixed or
montmorillonitic clays.
7. - Very High
Corrosivity to -Untreated- Steel
This one digit code describes the. potential .'for soil -induced chemical
action on untreated steel. Codes 2, 3, and 5 repr.esent series with a range
.of risk ratings.
1 - Low risk of corrosion
2 --Range 1 to 4
3 - Range 1 to 6
4 - Moderate risk of corrosion
5 - Range 4 to 6
6 - High risk of corrosion
Corrosivity to Concrete
This one. digit code describes the potential f or soil -induced chemical
action on concrete. Codes 2, 3, and 5 represent series with it range- of risk
ratings.
1 - Low risk of corrosion
2 - Range 1 to 4
3 - Range 1 to 6
4 - Moderate risk of corrosion
• 5- Range 4 to
6 - High risk of corrosion
Expanded Code Descriptions
D-3 Soils (Cont.)
Page 22
Erosion K
This two -digit code describes the erodibility of a soil. This factor
(K). is a measure of the susceptibility of- the soil to erosion by water. R
values range from 0.10 to 0.04, with soils having'the-highest K values being
those most erodible. As noted below, a number of the series are represented
by a range of K values.
01 = 0.10
02 = 0.15
03 = 0.15, 0.17
04 = 0.15, 017, 0.20
05 = 0.15, 0.17, 0.28, 0.49
06 = 0.17
07 = 0.17,
0.24
08 = 0.17,
0.28,
0.37
09 0.17,
0.37
10 0.20
11 = 0.20,
0.24,
0.32
12 = 0.20,
0.24,
0.43-
13 = 0.20,
0.43
14 0.24
15 = 0.24,
0.28,
0.32
16 0.24,
0.32
17 = 0.24,
0.32,
0.49
18 = 0.24,
0.43
19 = 0.28
20 = 0.28, 0.32
21 = 0.28, 0.37
22 = 0.32 -
• 23 = 0.32, 0.37
0
i
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Expanded Code Descriptions
D-3 Soils (Cont.)
24 - 0.32, 0:43
25 - 0.37
26 - 0.37, 0.43
27 0.43
28 - 0.43, '0.49
29 0.49
Page 23
Erosion T
This one digit code represents the soil -loss -tolerance factor'(T)• This
is the maximum rate of soil erosion- whether from rainfall or soil blow-ing,
that can occur without reducing crop production or environmental quality; and
is expressed in tons of soil loss per acre per year. Codes 2 and 4 represent
series with a range of T factors.
1-1ton
2 - Range 1 to 3
3 - 2 tons
4- Range 3 to
5 -- 3 -tons
6-4tons
7 - 5 tons
SOIL AND WATER FEATURES
Two ,soil water features have been evaluated, hydrologic group and
presence of seasonal high water table.
Hydrologic Group
This one digit code describes hydrologic soil group, u-sed to estimate
runoff from precipitation. Code 3 represents series with a range of ratings.
1 - Group A - Soils having a high infiltration rate (low runoff
potential) when thoroughly wet.
2 - Group B - Soils having a moderate infiltration rate when
thoroughly wet.
Expanded Code Descriptions
D-3 Soils (Cont.)
3' - Range 2 to 5
4 in Group c - Soils having a low infiltration rate when,thoroughly
wet.
5 - Group D - Soils having a very slow infiltration rate (high
runoff potential)- when thoroughly wet.
Page 24
Seasonal High Water Table
This one digit code incidates the existence and ,type of high water
table. This is defined as the -highest level of a saturated zone more than 6
inches thick for a continuous period of more than 2 weeks during most.years.
1 - No high water table
2 - Apparent high water table
3 - Perched high water table -
NOTE: A "0 " in any code except agricultural capability unit indicates that no
rating has been given.
0
0
Expanded Code Descriptions
MAP D-5
VEGETATION
Page 25
010 Grassland - Consists mainly of introduced grasses most of which are annuals.
Grasslands may contain, species of oak or walnut; however, the tree canopy is under
10 %. - Grasslands in Orange, County usually occur on hills and. low foothills,
alluvial plains and disturbed areas.
020 Coastal Sage Scrub - A low - but moderately dense community of drought
deciduous shrubs occurring on moderately steep to steep south and west facing
slopes. Grasses and forbs are numerous within this community. - Oaks are
occasionally found in the coast sage. scrub; however, density is .less than 20%.
Dominant plants include California sagebrush and numerous species of Eriogonum,
Salvia, Baccharis and Encelia.
021 Coast Sage Scrub -Sage - More than 75% California sagebrush.
022 Coast Sage Scrub -Mixed - A mix of Salvia, Eriogonum, Artemisia and other low
shrubs with no one species truly dominating.
030 Chaparral - A dense community of needle -leafed and broad leafed evergreen
sclerophylus shrubs occurring on the higher mountains of Orange County. Forbs or
grass understories are rare except -in areas of fairly recent burn. Dominant shrubs
include chamise, manzanita, ceanithus, and scrub oak.
031 Chamise Chaparral - Adenostoma fasciculatum (Chamise) is the dominant
species. This vegetation usually occupies south and west -facing slopes in the Santa
Ana Mountains just above the Coastal Sage community.
032 Mixed Chaparral - Contains Chamise, Ceanothus, Scrub Oak, Rhus, and
Manzanita with no one species truly dominant. This community usually occurs in
cooler and moister locations than Chamise Chaparral and Coastal Sage Scrub. -
040 Oak Savannah - An .area of annual grassland with 10-30 % tree cover usually,
consisting of oak or walnut. Density of trees increases toward riparian Tones and
towards woodlands on north facing slopes.
050 Oak Woodland/Forest - A community consisting of a tree density of over 30%
usually containing Coast live oak and Walnut. The ground layer is usually
grassland where the canopy is open. 'Oak woodland and forests usually occur in
valley areas where the- water table is nearer the surface and on moist north and east
facing slopes of the Santa Ana Mountains and Laguna Hills.
•
Expanded Code Descriptions
D-5 Vegetation (Cont.)
Page 26
051 Oak Woodland - Consists of trees occupying ->30%, but not over 70%, crown
cover - with the understory usually consisting of grasses and forbs. Woodland
communities usually -occur above riparian zones on cooler north facing slopes.
052 Oak Forest - A community, of trees occupying >709o' 'canopy cover typically
occurring on steep north facing slopes usually above riparian habitat.
060 Riparian Woodland/Forest - Consists of trees and shrubs with an open to dense
canopy. The vegetation is at or near the water table. Understory may consist of
gravelly to rocky riverwash, emergent vegetation, or on " the dryer fringes, annuals
may- occur.
061 Riparian Woodland - Consists of a community of trees, or shrubs with a canopy
density of 30-70% -occupying the fringes of the wetter riparian forests. Riparian
woodland often occurs a few meters up the slopes where. it merges with savannah
vegetation. Riparian woodlands consisting of cottonwood species occur along
major washes. Upstream, dominant species are oak and sycamore.
062 Riparian Forest - Consists of a community of trees with a close canopy occurring
along perennial and major seasonal steams. . Understory often consists of willow
and emergent vegetation. Dominant. trees include sycamore, .cottonwood, ' black
willow and alder.
080 Marsh - This community is the vegetative part of the coastal estuaries; the wetter
portions containing Salacorniaa-and-Spartina, with saltgrass along the drier fringes
where tidal inundation does -not occur regularly.
082 Freshwater Marsh - Consists of emergent vegetation occurring along perennial
streams, interspersed occasionally with pools of open water. 'Dominant plants
include Typha, Scirpus, Carex, and Salix. Drier meadow communities where the
watertable is not at the surface may support species of. Juncus.
090 Barren - Areas where vegetation is largely or entirely absent. If plants occur they
are usually members of the surrounding community.
110 Urban/Cultural Altered - Areas in -which urban development or agriculture is the
dominant feature of the landscape. Such areas include commercial, residential,
industrial, and governmental complexes; agriculture of any type and pasture.
120 Water - This classification includes reservoirs, small farm ponds and natural lakes.:
Flood control basins are not included in this classification unless there are areas of
permanent inundation.
0
I
0
"TIF
3\
\
(/}
\\
/ !�
BACKGROUND '1'3%J"L",:fP LvjLORT
PHASE I
Technical Supplement 1
0
a
BACKGROUND REPORT
PHASE I
Prepared For
City of Irvine
Community Development Department
Prepared By
Community Planning Services
El Toro, California
January 1986
•
CONTENTS
I INTRODUCTION ................................. 1
II STUDY METHODOLOGY .......................... 4
k IM[PLEMENTING.
IV REFERENCES ................................... 23'
APPENDICES
A DATA AND CONSTRAINT MAPPING
B MITIGATION MEASURE SOURCES
C DATA CLASSIFICATION SYSTEM
v
•
•
LIST OF EXHIBITS
A MEA Applications and Benefits ........................ 3
B MEA Project Team ............................... 5
CMEA Development ........................ . ...... 6
D Land Use Intensity Categories ......................... _ 11
E Development Review Process ......................... 15
4
ii
0
i
0
INTRODUCTION
PURPOSE
This supplement discusses the technical aspects related to development of phase I of the
Irvine Master Environmental Assessment (kMA). It presents the development of the
various MEA components, and how these components integrate with the City'.s existing
environmental and project review processes.
BACKGROUND
Interest in master environmental assessments among public agencies has grown over the
past several years. Not only have an increased number of assessment systems been
developed; but the trend toward computerized systems has increased. This trend has been
facilitated by an enhanced awareness by public agencies of computers and their
capabilities, and recent advancements in both hardware and software systems.
One of the first, and most sophificated assessment systems was developed by the
University of Illinois for use by the Army Corps of Engineers. At the local agency level,
the City of Bellevue, Washington has implemented an integrated land use and
environmental assessment system. And closer to home, the County of Orange has
prepared a MEA covering the unincorporated areas of the county. While there are
differences among these systems, a= common objective of each has been a desire to
improve the management of environmental information, and to expedite the project
.review process.
In California, projects are required to undergo environmental review in accordance with
the California Environmental Quality Act (CEQA). The provisions of CEQA are further
supplemented by guidelines promulgated by the Secretary'' for Resources. According to
these guidelines, a public agency may prepare an MEA in order to identify and organize
envirbnmental information for an area or region. This information can then be used by the
agency in the environmental evaluation of projects, and in the preparation of
environmental impact reports (EIR), and negative declarations. The guidelines leave the
decision to prepare a MEA, as well as the method of preparation and its' form, to the
discretion of each public agency.'
' CEQA Guidelines Section 15169
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Introduction
Page 2
The City of Irvine adopted its first MEA in 1977. This. MEA was originally prepared as
an Environmental Impact Report addressing the effects of the city's General Plan
Amendment #4. Following adoption, the MEA was used .extensively in evaluating the
environmental effects of development proposals. As time passed, and the city grew, the
utility of the MEA declined as the information it contained became dated and, less
relevant.
Recognizing the usefulness of an MEA, a task force2 charged with assessing the city's
environmental review procedures recommended in 1982 that the city's MEA be revised
and updated. By 1984, the City had developed a program for the preparation of a new
computerized MEA. This program envisioned the preparation occuring in two phases.
Phase I would entail the design, development and preparation of all documentation.
During phase II, the hardware and software would be selected, and the actual automation
process completed.
In late 1984, the City commissioned the firm of Community Planning Services (CPS) to
complete the Phase I work program. The primary objectives established for Phase I
included the following:
o - Update and expand the city's environmental information base
o Model environmental impacts of various land use types for each of the City's
project review steps
o Prepare "standard" mitigation measures to reduce or avoid adverse
environmental effects of development proposals
o Design an MEA system suitable for subsequent automation
An overview of Phase II is presented in Section II of this report. The City expects to
complete Phase II once Phase I has been fully implemented.
APPLICATIONS AND BENEFITS
As an analytical tool, the MEA is expected to be of benefit .to, a wide range of users
including members of the city council, commissions, residents, to
and city staff.
Table A identifies each of these user groups, how they might apply the MEA, and the
resulting benefits. As the primary user, city staff will find the most applications. for the
system, and receive the majority of the benefits. Several of these benefits will be
enhanced through system automation planned as part of phase H.
• a
2 Community Development Task Force, CEQA Subcommittee
EXHIBIT A
MEA APPLICATIONS AND BENEFITS
APPLICATIONS BY USER
Council/Commissions City Staff Residents Developers
o During consideration of
project proposals and
associated environmental
documents
o During environmental
policy consideration
Council/Commissions
o Promotes uniform policy
guidance on.environmental
issues
o Facilitates attainment of
community goals and
objectives
•
o During initial study
analysis
o During preparation of neg-
ative declarations and en-
vironmental'impact reports
o As input during prepara-
tion of community plans
o In evaluating other
agency's projects and en-
vironmental documents
o In reviewing development
proposals, and associated
environmental documents
BENEFITS BY USER
City Staff
o Enhances knowledge of the
area's environmental re-
sources and constraints
o Reduces time needed to
evaluate a project's effects
and prepare mitigation
measures
o Promotes evaluation of
cumulative effects
o Fosters consistency in envi-
ronmental evaluation, and
mitigation strategies
o Enhances coordination
among city departments and
other agencies
Residents
o Enhances knowledge of the
area's resources and
constraints
o Promotes increased under-
standing of the city's envi-
ronmental review process
and policies
o Helps protect quality of life
o Reduces cost of environ-
mental review for public
projects
o During project planning
Developers
o Promotes understanding of
the city's resources and en-
vironmental policy require-
ments
o Expedites the project review
process by focusing on.:
project specific issues
0
H
STUDY METHODOLOGY
THE PROJECT TEAM
Phase I of the MEA was prepared over the course of several months by a team of
environmental planners assisted by technical consultants with expertise regarding specific
environmental issues. This team was augmented by key staff members from various
divisions within the Department of Community Development. The primary individuals
participating on the team are listed in Exhibit B.
PHASE I DEVELOPMENT
41 Development of the MEA involved completion of nine tasks. These tasks, and, their
relationship to one another, are illustrated in the flow diagram shown in Exhibit C. Each
of these tasks is discussed separately below.
Task 1 Acquisition and Evaluation of Existing Environmental Data
At the outset of the project, the consultant team acquired and inventoried all relevant
environmental resource and constraint data available for Irvine's planning area. Sources
consulted included the City of Irvine, County of Orange, The Irvine Company, :Irvine
Ranch Water District, various special districts, State and Federal agencies, and local
organizations, such as the Irvine Historical Society. Information not available locally was
acquired by the consultant team.
Once assembled, this information was catalogued by type, geographic coverage, scale,
source, publication date and availability. The information was then evaluated to identify
outdated data, conflicts among sources, and gaps in geographic coverage. Areas where
further additional data were needed, were flagged for supplemental analyses in subsequent
tasks. The documents acquired, and inventory prepared was presented to city staff at the
conclusion of the study for their use in updating the MEA.
. EXHIBIT B
MEA PROJECT TEAM
City Staff
Mr. Ed Moore, AICP
Environmental Services Division
Principal Planner
Mr. Dain Anderson,
Environmental Services Division
Senior Planner
Mr. Mike Thiele,
Planning Services Division
Principal Planner
Mr. Steve Haubert,
Planning Services Division
Senior Planner
Consultants
Mr. Tom Miner,
Community Planning Services (CPS)
Principal
Mr. Eric Hernden,
Aerial Information Services (AIS).
Principal
Ms. Janet Reyes
Aerial Information Services
Senior Analyst
Mr. Steve Nelson,
Nelson Biological Consulting
Biologist
Mr. Rod Raschke,
RMW Paleo.Associates.
Paleontologist
Ms. Beth Padon,
Larry Seeman Associates
Archaeologist
•
A
EXiiiBIT C
MEA DEVELOPMENT PROCESS
PHASE I
MODEL
CONSTRAINTS
PREPAREIMPACT
.MODEL
A
ACQUIRE AND
EVALUATE
EXISTING DATA
DEFINE SYSTEM
COMPONENTS
COMPLETE
SUPPLEMENTAL
STUDIES
PREPARE MAPS
INTREGRATE
SYSTEM'
COMPONENTS
COMPLETE USERS
MANUAL, MAP
ATLAS AND
TECHNICAL REPORTS
PUBLIC REVIEW
DEVELOP
CODING SYSTEM
FORMULATE
MITIGATION
MEASURES
MEA
PHASE II
0
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Study Methodology
Task 2 System Definition
Page 7
This task focused upon selection of the environmental topics to be include in the NSA,
and how the information would-be classified within each topic. The primary objective of
this task was to ensure that 1) all critical environmental topics were included, and 2)
extraneous information not satisfying a clearly identified need was eliminated. Based on
the project team's analysis, the following subjects were ultimately selected for inclusion
in phase I.
Geologic Hazards
Flood/Dam Inundation Hazards
Fire Hazards
Agricultural Capability
Water Resources
Biotic Resources
Sand and Gravel Resources
Historical Resources
Archaeological Resources
Paleontological Resources
Aircraft'Noise and Crash Hazards
Roadway and Railroad Noise
Special Districts
Once the subjects to be included were deemed, an explicit data classification system was
developed. This classification system was -used to organize the environmental information
within each of the selected environmental topics. This system would guide later activities,
including the mapping effort. Criteria used to define the classification system included
consideration of 1) the City.'s established environmental objectives and policies, 2) the
format and availability.of existing data, 3) map preparation and maintenance costs, and 4)
compatibility of the City's MEA with the system adopted by the County of Orange. To
ensure broad based input into the classification process,, potential users were contacted to
identify their speck needs. Because of its length, the classification system has been
included separately as Appendix C.
Task 3 Supplemental Studies Preparation_
The consultant team completed supplemental technical studies where earlier tasks had
determined existing environmental information was either lacking, or inadequate in its
present form, and the information was deemed critical in the development of the MEA.
Three separate studies were completed addressing biotic, archaeologic, and paleontologic
resources. The scope of each study was tailored to the MEA's specific data requirements.
Study Methodology
Page 8
The information obtained through these studies greatly enhances the City's overall
knowledge regarding the occurrence and value of these resources within the city's
planning area. The utility of this informationextends beyond the MEA, and it is already
finding important applications in association with a proposed revision to the Conservation
Element of the City's General Plan.
The supplemental studies are included in the MEA as Technical Supplements 2, 3, and 4,
and are on file with the City of Irvine. The reader is referred to each study for information
beyond that provided in the MEA User's Guide and Map Atlas.
Task 4 Data and Constraint Map. Preparation
The data collected in the earlier phases of the study were mapped during this task
according to the classification system developed under task 2.
The first step was the preparation of a cartographically accurate base map for the study
area. Selection of the base map scale was an important consideration, and included
consideration of 1) consistency with existing environmental data, 2) compatibility with the
city's general plan mapping system, and 3) legibility of the maps in their pre -automated
form. Based upon these criteria, a scale of 1:24,000, or 1" = 2000' was -selected.
Six USGS 7.5 topographic quadrangle maps cover the study area: _
El Toro Black Star
Tustin- San Juan
Laguna Beach Orange
These quadrangles were photographically combined to produce a single map
encompassing the entire planning area. This map was then reproduced on a stable mylar
base. Boundaries of the study area were drawn on the base map using administrative and
planning boundary information provided by the city.
Once the base map was completed, the next step was to assemble and rescale, where
necessary, the environmental data to be used to compile each of the data and constraint
maps. Resealing was -accomplished via an optical/manual technique. This procedure
involved the use of an optical pantograph, an instrument similar to a rear screen projector
which is used to project an enlarged or reduced image onto a drafting surface. Using the
pantograph, the image is first brought to the proper scale by projecting it onto a
transparent mylar copy of the base map, and then matching locations of recognizable
Study Methodology
Page 9
linear. or point features with known locations on the base map. The image is then
transferred manually onto translucent drafting film. The specific device used in
conjunction with the- MEA was a ME kargl reflecting projector, with an overall
distortion of less than 0.01 percent.
Not all of the information needed for the study had been previously mapped in a
satisfactory format. In these cases, the data had to be photo -interpreted. Aerial photos
were used, and included high altitude Earth Resources Technology Satellite (ERTS) color
infrared imagery, and low level black and white photography at a nominal scale of
1:24,000. The features mapped were plotted by drafting lines on a piece of transparent
acetate fastened to the imagery while it, and the adjacent photos, were viewed in stereo.
Once delineations were made, the data was transferred onto the base maps using the
pantograph. Use of the base map in the process ensured not only that the- photo -
interpreted information was drawn to the scale of 1:24,000, but also provided a means for
correcting the distortion inherent in stereo photo pairs.
The product of this effort. was a uniform, set of twenty four environmental data and
constraint maps, with minimum mapping resolution of 5 acres. The original maps are
available for use by city staff at a scale of 1"=2000'. Because . the size of these maps
makes their use somewhat cumbersome, a reduced set of maps has been published for use
'in phase I and are included in the.. Map Atlas. These maps are reproduced at a more
manageable scale of 1"= 6000' (11" by 1711).
Appendix A has been prepared to assist the city in maintaining these maps in a current
status. This appendix includes the sources of. the data for each map, and the method -of
preparation.
Task 5 Impact Model Development
Impact models were developed to identify -potential environmental effects of various land
uses. The purpose of these models was not to identify specific environmental impacts,
but instead to provide a means by which to associate potential environmental impacts with
proposed mitigation measures.
The consultant team completed a series of matrices to analyze the potential impacts
resulting from different land use types. Each of the City's General Plan land use
categories was tested against each of the resource and constraint categories defined during
Task 2. This effort revealed that impacts were influenced more by the intensity of
development than by the specific type of land use. In other words, whether a project was
industrial, commercial, or residential is less important than its overall intensity. This
Study Methodology
Page 10
conclusion lead to development of the five Iand use impact intensity categories shown in
Exhibit D. Each of the categories is explained below.
The No Impact category is restricted to certain types of open space uses.. Because these
uses would maintain the natural conditions of a site, they would be expected to have no
appreciable adverse environmental impacts, and have not been considered further in the
The low, medium, and high intensity categories reflect a range in intensity encompassing
the most commonly used land use designations found in the City's General Plan Land Use
Element. Uses within these three categories are potentially affected by environmental
hazards, and also can be expected to result in impacts on environmental resources.
The Special intensity category was established- to recognize uses with low human
habitation. These uses are not importantly influenced by hazard considerations, but their
development may nevertheless result in substantial effects on a number, of sensitive earth
based resources.
To'evaluate the effect -of alternative intensity groupings on the MEA output, the consultant
team completed a -sensitivity analysis. This analysis showed only slight changes in model
output when a land use was shifted one intensity category within the low to high range.
The reader can verify this through a detailed examination of the MEA impact models and
mitigation measures.
Task 6 Mitigation Measures Preparation
The consultant team formulated mitigation measures for each of the environmental
constraint topics. This task was completed concurrently with the development of the
impact models so that as potential impacts were identified, measures were developed to
address the identified impacts. The actual mitigation measures were formulated based
upon a comprehensive inventory of existing City policies and regulations, a review of
state and federal laws, appropriate technical literature, recognized environmental criteria,
and interviews - with the individuals from other public :. agencies and ,environmental
planning firms. A draft of each measure was reviewed by city staff, and appropriate
representatives of other organizations and agencies to assure that the proposed measures
were considered feasible, and all reasonable measures had been included. The
environmental policy inventory completed in support of this task is included in Appendix
B. City staff will find it useful in confirming, the currency of the mitigation measures
during future updates. Other sources consulted during this task are also documented in
Appendix B.
EXHIBIT D
LAND USE IMPACT
INTENSITY CATEGORIESW
No Impact
Open Space(2)
Wildlife habitat
Wildlife Reserve
Water
Low
Rural Density Residential ' (<0.1 Dwelling Units/Acre)
Estate Density Residential (0.1 to 1.0 Dwelling Units/Acre)
Medium
Low Density Residential (1.0 to <5.0 Dwelling UnitslAcre) "
Medium Density Residential (5.0 to <10 Dwelling UnitslAcre)
High
Meduim High Density Residential (10 to 25 Dwelling UnitslAcre)
High Density Residential (25 to 40 Dwelling UnitslAcre)
Airport
Multi-Use(3)
Commercial -
Industrial
Landfill
Sand and Gravel Operations
Institutional
Special
Open Space(2) _
General
Cementary
Agriculture
Regional Park
Community Park
Nature Center
Roadway Projects
1 Land use categories adapted from the Irvine General Plan Land Use Element
2 This category has been subdividdd due to the wide range of uses included.
3 Mixed or multi use projects must consider each use separately.
Study Methodology
Page 12'
The mitigation. measures included in the MEA can be divided into two categories. One,
referred to as decision criteria, include specific standards, or planning policies, to which
projects are expected to comply. These measures have been keyed to the level of project
review at which the decision criteria should be applied. In many cases, these measures
may apply to more than one level of review. Where this is the case, the measures are
identified at each level in the impact models. The following is an example of a decision
criteria measure.
All stationary emission sources shall comply with the regulations- adopted
by the South Coast Air Quality Management District.
The second mitigation category includes compliance notification measures. These are
intended to notify an applicant that speck mitigation requirements must be met at a
subsequent level of project review. These measures can be easily distinguished by an
introductory phrase which begins "Prior to -- ." These measures are generally keyed to the
level of review immediately preceding the level of review at which compliance would be
required. An exception applies to measures associated with- concept plan. This is because
1) many projects may not require a general plan amendment (the normal compliance
notification point -for concept plans); and 2) conditions of approval (mitigation measures)
are frequently not adopted in association with general plan amendments, thus the requisite
preceding review level is not consistently available for adoption -of the notification
measures. Consequently, these measures have been written to provide both notification
and compliance during concept plan review.
Finally, each mitigation measure was coded according to the primary constraint topic to
which it relates, i.e., Geologic Resources (C-1): 1.1, 1.2, etc.
Task 7 System Components Integration
The above tasks resulted in the development of the individual components of phase I of
the MEA.. These components were integrated during this task to form* a coherent
assessment system which could be used temporarily in a manual form until system
automation was completed.
The objective of this task was to establish a. system which focused on increasing the
efficiency of the environmental review process, and which could be put to immediate use
by each of the intended user groups identified in Exhibit A. The system arrived at
• includes a Users Manual and Map Atlas, plus supporting technical documentation for use
by those in need of additional background information. The Users Manual"and Map Atlas
Study Methodology Page 13
are the primary system components and contain all of the elements needed to use the.
system under phase I. It should be noted that because the MEA has been designed and
structured for automation, its manual implementation can not fully exploit the system's
benefits in terms of improving the efficiency of the environmental review process, or ease
of use.
Task 8 System Documentation
This task included preparation, and publication of the User's Guide, Map Atlas, and
'technical supplements. As part of this task, the consultant team also conducted two
training sessions for city staff in the use of the MEA.
Task 9 Public Review Process
-The final task of phase I is intended to provide ' the public, and other agencies an
opportunity to review and comment on the MEA. Both the User's Guide and Map Atlas
were distributed for consideration. Revisions to the documents will be made based upon
the comments received. The MEA will be presented to the Irvine City Council for
consideration following- the public review period. Once approved by the city, the MEA
will be implemented as discussed in the next section.
0
IMPLEMENTING THE MEA
OVERVIEW OF THE DEVELOPMENT REVIEW PROCESS
Development proposals in Irvine are required to undergo both project and environmental
review. The project review process is a decision -making system established by the city to
ensure the community grows in a desirable and orderly fashion. In accordance with this
process, each, development proposal must undergo several levels of review before final
approval is granted to proceed with actual construction. This multi -level review process
is depicted in Exhibit E. As Exhibit E shows, development review begins at the general
plan level, where project proposals are considered at the conceptual planning stage, and
proceeds through subsequent levels of review where more detailed plans are scrutinized.
Each review is founded on the assumptions, allowances and limitations of preceding.
approvals. The process concludes when construction approvals are granted.
The primary documents governing each step in the decision making process are also
shown in Exhibit E. Typically, these documents define- the manner of the review, as well
as the planning criteria by which projects are evaluated. Of particular note here, is the
general plan. This document establishes policies intended for implementation over a wide
range of project review levels.
The environmental review process is intended to supplement the project review process.
It is essentially an information system designed to inform the public and decision -makers
of the environmental consequences of development proposals as they proceed through .the
project review process.
This process is established by the state under the .California Environmental Quality Act
(CEQA) and CEQA Guidelines. It is -implemented by the�city of Irvine through locally
adopted implementation guidelines (City of Irvine CEQA Procedures). Procedurally,
these regulations require that the city complete an initial study to determine a project's
environmental effects at each discretionary level of project review (See Exhibit E). If the
analysis -shows that a proposed project may have a significant effect on the environment,
the city must prepare an Environmental- Impact Report (EIR) addressing the significant
effects, mitigation measures and project alternatives. If on the other hand, the
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EXHIBIT E
PROJECT REVIEW PROCESS
Project
Primary
Definition Review Process
Governing Regulations
General General Plan Amendment,
General Plan
Concept Plan,
Zoning Ordinance,
General plan
Change of Zone,
Zoning Ordinance,
General Plan
Tentative Map/Parcel.Map'
Subdivision Map Act,
Subdivision Manual
Master Plan,
Zoning Ordinance
Conditional Use Permit,
Zoning Ordinance
Code Compliance/
Zoning Ordinance
Specific
Discretionary level of review.
Zoning Determination
Grading Permit, Grading Ordinance
Building Permits Uniform Building Code
Certificate of Occupancy Uniform Building Code
Implementing the MEA
Page 16
analysisdemonstrates that the project's effects will not be significant, the city prepares a
Negative Declaration.
To augment the established procedures, the city has adopted an Environmental Review
Matrix. This document assists city staff by identifying the type environmental
information required at each stage of the city's project review process.
INTEGRATING THE MEA WITH EXISTING PROCESSES
This section discusses how the MEA integrates with the existing environmental and
project review processes outlined above. It is organized according to the four principal
user groups identified in Exhibit A. As discussed in Section I, each user will have a
somewhat different application for the MEA. Emphasis here is on the primary .user: city
staff. For the actual steps involved in_ using the system, refer to the User's Guide.
While not discussed in this section, the consultant team has suggested revisions to city
ordinances, policies and procedures, necessary to assure full implementation of the MEA
in the context of the city's current project and environmental regulations -and procedures.
These recommendations have been forwarded to the city under separate cover.
Developers
The primary use of the MEA by developers during a project's planning and design stages.
Because the MEA reflects adopted environmental policy, it is expected that project
applicants will consult the MEA 'in the same manner that they would consider .other
important planning documents, such as the city's General Plan or Zoning Ordinance.
The MEA can play an important role in shaping a project's design before it reaches the
point of formal submittal to the city. As a centralized source of environmental
information and policy, it can serve as an important element during a project's conceptual
design. Typically projects are planned by a multi -disciplinary team. In this context, the
MEA can serve as a common source of officially adopted constraint information and
planning criteria for use by members of the project team. Because the MEA spans all of
the project review levels from General Plan to construction permits, and because it
provides mitigation measures associated with each, the developer can proceed with
project planning beyond the current application with some certainty, as to the
environmental issues and expectations of the city.
Implementing the MEA
City Staff
Page 17
At the staff level, the MEA will be used, in association with 1) initial study analysis, 2)
preparation of negative declarations and environmental impact reports, 3) formulation of
project recommendations and conditions of approval, 4) review of other agency's
environmental documents, and 5) preparation of various planning studies. Each of these
applications is discussed further below. It is anticipated that the staff of the
Environmental Services Division will have primary responsibility for the majority of
these activities. Specific procedures to implement the MEA at the staff level will be
established by the Director of Community Development.
Initial Studies: As. an environmental planning and analysis tool, the MEA is intended for
use as an integral component of the initial study process. CEQA requires the completion
of an initial study for every project at each discretionary level of review (See Exhibit E).
The city's CEQA Procedures Manual, Section 5, governs how the initial study is to be
conducted. In accordance with these procedures, - the staff members utilize an
Environmental Analysis form to evaluate a project's environmental effects, and document
the conclusions of the analysis.
The MEA will assist staff in this evaluation process. First, it provides a central source of
current environmental information which can be used to identify the environmental
resources and constraints which apply to a particular project site. Second, the MEA
identifies established environmental criteria against which to judge the potential
environmental effects of the project. Third, it identifies mitigation measures which can be
used to reduce or avoid any potential adverse impacts.
Since the MEA considers all levels of project review, the environmental planner has
ready access to a broad spectrum of mitigation measures. Thus, he is not only able to
identify those measures which are relevant to the current level of'review, but also those.
associated with all preceding. and succeeding levels as well. The ability to identify a
coherent mitigation package for implementation at each . stage of the review process is
expected to. lead to an increased use of negative declarations, and environmental impact
reports focused more on project specific issues. Thus, in most cases the mitigation
measures included in the MEA would normally be expected to mitigate a project's
potential adverse effects to insignificant levels (for those topics addressed in the MEA).
A project may, however, present unique or,unusual issues which can not be foreseen by
the MEA. Such issues are deal with through the inclusion of measures which provide a
framework for identifying and implementing project speck measures. This approach
1 An initial study is a preliminary analysis prepared by the lead agency to determine
whether an EIR or a negative must be prepared or to identify the significant
environmental effects to be analyzed in an EIR.
Implementing the MEA
Page 18
assures the appropriate analysis will be completed, .and that specific measures will be
given timely consideration during.the initial study.
Negative Declaration and EIR Preparation: Where staff concludes, as a result of the
initial study, that a Negative Declaration is appropriate, the mitigation measures
identified through use of the MEA can easily be appended to the Negative Declaration
form as required by the CEQA Guidelines:. If an EIR is necessary to address the
environmental effects of' a project, the MEA provides environmental information and
mitigation measures which can be incorporated directly into the EIR. This should permit -
those preparing the EIR to concentrate their analysis on the unique aspects of the -project
at hand.
Formulation of Project Recommendations and Conditions of Approval. The decision
criteria included in the MEA will assist the staff of the Planning Services Division in their
evaluation of the appropriateness of projects which come before them. Additionally, the
compliance notification measures are provided in a form which, in many cases, will
permit their use as conditions of project approval without modification. With each
measure keyed to a specific level of project review, staff will always know which
measures are typically applied at each step in the review process. The task of preparing
staff reports is also expected to be less time consuming with each of .the "standard"
mitigation measures readily available on the city's word processing equipment.
Review of Other Agencies' Environmental Documents: The City of Irvine is frequently
call upon to consider the information and analyses .included in the environmental
documents of other agencies. Where the city has a decision making role in these projects,
its responsibility in the review process is governed by 'the city's CEQA Procedures,
Section 10. The environmental information contained in the MEA, and its mitigation
measures will assist staff in focusing attention _ on the environmental issues . important to
the City of Irvine. In many cases, the MEA will suggest specific mitigative wording
which staff can forward to the lead agency for incorporation in the environmental
document, and use as conditions of project approval.
City Planning Studies: In the normal course of their duties, the Community
Development Department staff prepares numerous -planning studies .and analyses. Many
of these studies require consideration of environmental issues. In these instances, use of
the MEA and its relevance to the study will be dictated by the particular needs and
objectives of each study. It should be noted that the MEA is already serving as important
input to a study currently involving the Conservation Element- of the General Plan.
Implementing the MEA
City Council and Commissions
Page 19
The primary use of the MEA by members of the City Council and Commissions will
likely be in association with their consideration of - development- proposals, and
corresponding environmental documents. Through reference to the User's Guide and
Map Atlas, the MEA can serve as source of current environmental information, and a
means of conforming compliance with the city's adopted environmental objectives and
policies. Since the MEA provides a compendium -of adopted environmental, policies, it
also establishes a reference point from which members of the Council and Commissions
can monitor and reevaluate the continued appropriateness' of these policies. These uses
will be implemented in an informal manner, with the frequency of use dependent upon
the individuals and circumstances involved.
Residents
Irvine residents with an interest in a particular development proposal will. now have a
central source of environmental- resource information which - they, can refer to in
considering the environmental merits of a development proposal. Copies of the phase I
User's Guide and Map Atlas will be available for reference at the Irvine City Hall, and
public library branches. Copies are also available at the Department of Community
Development for purchase by residents.
LIMITATIONS OF PHASE I
While the MEA is considered an important and useful element in the city's_ overall
planning and environmental processes, it is appropriate to point out its limitations as well.
For example, it must be remembered that while a. major effort, has been devoted to
preparing a comprehensive document the system is intended only to assist the user. It is
not intended as a pure "cookbook" approach to environmental ' analysis. For example,
while the mitigation measures proposed by the-MEA may be applicable in most cases,
circumstances related to a specific project should dictate whether a particular measure is
modified to fit the project, or perhaps not applied at all. In some cases, MEA measures
may need to be expanded, or additional measures added. These adjustments are
appropriately handled by the city staff during .the initial study analysis.
Another limitation relates to the number of environmental topics included under phase I.
While a broad range of issues are addressed, topics such as traffic and circulation, public
services, energy, and hazardous materials have not been included. Until the MEA is
• expanded to include these areas, staff must continue to be addressed them separately
during the initial study analysis without the assistance of the MEA.
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Implementing the MEA
UPDATING
Page 20
If the MEA is to be useful, it is imperative it be kept current. Because the MEA
incorporates a substantial- amount of information, constant vigilance by staff will be
required. Consequently,. it is recommended that a careful review of the MEA be
completed every six months with updates prepared as warranted. The following MEA
features will facilitate keeping the MEA current:
L. The sources of all data used in the mapping process, and the methods of map
preparation, have been carefully documented (Refer to Appendix A).
2. Preparation and revision dates are included on all maps, impact models and
mitigation measures -to assure currency.
3. An inventory of existing environmental policy documents used in preparation of
the mitigation measures is provided (Refer to Appendix B). Additionally, the
sources of all mitigation measures have been identified in parenthesis following
each measure.
4. The text, impact models and mitigation measures have been prepared on word
processing equipment compatible with that used by the city. Thus, revisions can
be- made easily.
5. The User's Guide and Map Atlas will be printed in a three ring notebook format to
permit easy replacement of pages.
PHASE II
Phase II is expected to provide efficiencies in the application of the MEA through .
development of a computerized data base management system. The system currently
envisioned will permit a user to enter a project's location and general characteristics into a
computer terminal, and have tle program search through the applicable environmental
categories and list, or print, the appropriate mitigation measures. As an option the user
may also have the computer print portions of individual data or constraint maps,. or
prepare composite constraint maps covering the project site or entire-MEA study. _
Three primary tasks support completion of phase H. They are discussed here simply to
provide an overview of the work necessary. to automate the MEA. Refinement of these
tasks is expected at the time the city is actually prepared to proceed with phase H.
Implementing the MEA
Task 1 Select Hardware and Software Systems
Page 21
The Community Development and Administrative Services Departments will research
and evaluate alternative hardware and software systems for selection and acquisition.
Emphasis would be placed on use of existing city equipment and "off the shelf' software
programs which are cost effective and readily available. The city may choose to retain an
outside systems analyst to assist staff with this task.
Task 2 System Programming and Input
Development of application programs will need be completed to adapt the acquired
software for use with the MEA. Once this is completed, a geo-based grid or polygon
format will be defined, computer. files containing the MEA data created and edited, and
the system tested.
Task 3 Documentation and Training
As a final task, documentation for the automated system will to be prepared, and staff
trained in the use and maintenance of the system.
41 FURTHER SYSTEM ENHANCEMENTS
As the MEA demonstrates its value, ways will likely be suggested to further enhance the
system.. Some of these potential enhancements have already come to light in association
with development of phase L They are briefly discussed below.
Inclusion of Additional Environmental Topics
As noted under the discussion on limitations, not all environmental issues are included in
the current version of the MEA. Future revisions should give consideration to adding as
many of these issues as is practical.
Additional Analysis of Existing MEA Topics
While the MEA provides substantial environmental information regarding the area's
resources, additional analysis would further enhance the utility of the system. As an
example, a comprehensive survey of historical resources; including an evaluation of
tenant farm homes, would be useful. Inclusion of helicopter flight corridors, and new
roadway noise contours currently under preparation, should also be considered during
future updates.
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Implementing the MEA
0' - Inclusion of Planning Issues
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The MEA establishes a system which could readily be expanded to include additional
land use planning issues. Such a system is currently, under preparation by the city of
Bellevue, Washington. Under such a system, all of the city's land use planning policies,
regulations, and adopted conditions of project approval could be automated. Such a
system would provide a user with immediate access to all relevant land use regulations
and planning policies for a specific project proposal. As a minimum, development
standards should be considered for. incorporation during a subsequent update, once the
city fias clearly defined its overall planning data base objectives.
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REFERENCES
Aircraft Environmental Support Office; Naval Air Support Facility, 1977. Noise
Monitoring MCAS (Hi Santa Ana, California, North Island, CA.
Anderson, J. R., Hardy, E. E., Roach, L T., and Witmer, R. E., 1976. A Land Use and
Cover Classification System for Use with Remote Sensor Data, U.S. Geological
Survey Professional Paper 964.
Association of Engineering Geologists, 1973. Major Earthquakes and Recently Active
Faults in the Southern California Region. Scale 1" = 20 miles.
California Division of Forestry. Fire Hazard Severity Classification System for California
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California Division of Mines and Geology, 1974. Geology of the South Half of the El
Toro Quadrangle Orange County, California. Special Report 110.
California Division of Mines and Geology, 1976. Environmental Geology of Orange
County, California. open Fire Report 79-81A.
California Division of Mines and Geology, 1981. Mineral Land Classification of Greater
Los Angeles Area, Part III. Classification of Sand and Gravel Resources Areas,
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Report 143.
California Resources Agency, Department of Parks and Recreation,1979. California
Historical Landmarks, Sacramento, CA.
Christiansen and Associates, 1971. Master Plan. of Drainage for Laguna Canyon, San
Juan Capistrano, CA.
City of Irvine, 1975. Historical. Archaeological and Paleoniological Policy and Program.
City of Irvine, 1984. Paleontological Survey Records File.
City of Irvine, 1985. General Plan, including all elements
City of Irvine, 1985. California Environmental Quality Act Procedures.
City of Irvine, 1985. Zoning Ordinance.
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References
Page 24
City of Irvine, 1980. Flood Insurance Rate Map, Panels 1-7. National Flood Insurance
Program. U.S. Dept. of Housing and Urban Development, Washington, D.C.
City of Orange, 1978. General Plan, Seismic Safety Element; Orange, CA.
Community Planning Services, 1983. Environmental Review Matrix. Prepared for the
City of Irvine.
Corps of Engineers, 1969. Flood. Plain Information Report In Laguna. Canyon,
Washington D.C.
Corps of Engineers, 1972. Flood Plain Information Report for San Diego Creek and
Peter's Canyon Wash, Washington, D.C.
Corps of Engineers, 1973. Survey Report for Flood Control: Laguna Canyon, Orange
County. California, Washington, D.C.
Corps of Engineers, 1974. Flood Plain Information: Tributaries- of Upper San Diego
Creek, Orange County, California, Washington D.C.
Corps of Engineers, 1974. Flood Plain Information Report for Upper Peters Canyon
'Wash, Washington, D.C.
County of Orange, Planning Department, 1968. Historical Landmarks of Orange County,
Santa Ana, CA.
County of Orange, 1969. Historical Landmarks of Orange County. Orange County
Planning Department, Santa Ana, CA.
County of Orange, 1970. Proposed Increments of a Master Plan of Drainage for the
Unincorporated Areas of Orange County, California, Plate 1. Dwg. no.;-Misc. - 106-
41. Scale 1"-2 miles.
County of Orange, 1973. Slone Stability. Report, Santa Ana, CA:
County of Orange, Flood Control District, 1974. Primary Facilities and Drainage Areas,
Scale 1"-8000'
County of Orange, 1977a. A Report on Cultural/Scientific Resources. for County of
Orange. Cultural/Scientific Resources: Policy Task Force, .Santa Ana, CA.
County of Orange, Environmental Management Agency, 1976. Hdrology Report, San
1 Joaquin Channel Facility N. F14, Entire Drainage System, Santa Ana, CA.
County of Orange, 1976. Fire Protection Planning Task Force Report.
References
County of Orange,1979. San Joaquin Hills Transportation Corridor Route Location
Study, Environmental Impact Report # 267.
Page 25
County of Orange, 1983. Foothill Transportation Corridor, Final Environmental Impact
Report # 423.
County of Orange, 1984. John Wayne Airport Master Plan and Santa Heights Land Use
Compatibility Program. Final Environmental Impact Report # 508.
County of Orange, No Date. Noise Element of the General Plan. Ultimate Noise
Contours.
County of Orange,. Office of Emergency Services, 1978. Evacuation Plan for Areas
Below Dams. Santa Ana, CA.
Division of Mines and Geology,1976a. Active Fault Mavping and Evaluation Program.
Special Publication 47. Sacramento CA.
Division of Mines and Geology, 1976b. Geology and Engineering Geolo .ig'c Aspects of
the Laguna Beach Quadrangle, Orange County, California. Special Report 27.
Sacramento, CA.
E.L. Pearson and Associates, 1969. Master Plan of Drainage for the El -Modena - Irvine
Area, Newport Beach, CA.
El Toro USMCAS, 1980. El Toro APZ. Scale 1"=2000'.
Evans, Goffman, & McCormick, 1973.
and East of JeffreyRoad. Santa Ana, CA.
Federal Law, 1906. The Antiquily Act of 1966. (Public Law 59-209, 34 stat. 225; -16
U.S.C. 431-433), Washington, D.C.
Federal Law, 1935. The Historic Sites Act of 1935, (Public Law 74-292, 49 stat. 666; 16
U.S.C. 461-467), Washington D.C.
Federal Law 1960. The Reservoir Salvage Act of 1960. (Public Law 86-523, 74 stat. 220;
16 U.S.C. 469-469c), Washington D.C.
Federal Law 1966. The Historic Preservation Act of 1966. (Public Law 89-665, 80 stat.
915; 16 U.S.C. 470), Washington D.C.
Federal Law 1969. The National Environmental Policy Act of 1969, Executive Order
11593 (Public Law 209), Washington, D.C.
References
Page 26
Federal Law 1974. The National Archaeological/Historical Preservation Act of 1974,
(Public Law.93-291, 88 stat. 174; 16 U.S.C. 469-a-1 et seq.), Washington, D.C.
Frederick, D. G., and Anderson, K. Eric, 1983. The Collection and Analysis of Natural
Resource Data in the 1980's: Fifth International Symposium on Computer -assisted
CartographX. Crystal City, Virgina.
Friis, L.J., 1965. Orange County Through, Four Centuries,, -Pioneer Press, Santa Ana, CA.
Geotechnical Survey, 1973. Geohydrology and Artificial Recharge Potential of the Irvine
Area, Orange County, California. Washington, D.C.
Goldman, Harold B., 1968. Sand and Gravel in California, an Inventory of Deposits.
Part C--Southern California. California Division of Mines -and Geology, Bulletin
190-C. Scale 1:500,000.
Guptill, S, C.,1978. "The Impact of Computer Graphics, Data Manipulation Software,
and Computing Equipment on Spatial Data Structures," First International Advanced
Study Symposium on Topological Data Structures for Geographic Information
Systems. Cambridge, Massachusetts.
Irvine Blue Ribbon Committee, 1982. Report of the City's East Irvine Blue Ribbon
Committee.
Interagency Fire Prevention Group, 1978. Fire Safety Considerations for Developments
in Forested Areas - A Guide for Planners. and Developers. Portland, Oregon.
Kuchler, A. W., 1967. Vegetation Mapping. "The Ronald Press Company.
Lowry Engineering -Science, 1971. A Preliminary Investigation of the Feasibility of
Providing Works of Improvement within San Diego Creek Watershed in'Orange
County, California, Santa Ana, CA.
Meadows, Don,1975. Irvine - A City on Rancho San Joaquin, The First National Bank
of Orange County, Costa Mesa, CA.
Mitchell, W. B., et. al., 1977. GIRAS -- A Geographic Information Retrieval and
Analysis System for Handling Land Use and Land Cover Data: U.S. Geological
Survey Professional Paper 1059.
Morton, P.K. and Miller, R.V., 1973. Geo-Environmental Maps of Orange County,
California, CDMG Preliminary Report 15, Sacramento, CA.
O'Neal, Stephen, 1985. Letter dated November 21 regarding historical sites in the Irvine
planning area.
References Page 27
Oppenheimer, Carl H_., 1983. Environmental Data Management, Plenum Press, New York
and London.
Ploessel et.al.,1972. Seismic Environment of the Southern California Coastline I: Palos
Verdes to Dana Point. (preprint) Dallas, Texas.
Poland, J.F. et.al., 1956. Groundwater Geology -of the Coastal Zone Long Beach, Santa
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RBF, 1973. Master Plan of Drainage for the East Irvine Area, Irvine, CA.
R. Dixon Speas and Associates, Inc., 1976a. Air In Compatible Use Zone
Study, WAS El Toro, prepared for Western Division, Naval Facilities Engineering
Command, Los Angeles, CA.
R. Dixon Speas and.Associates, Inc., 1976b. Air Installation Compatible Use Zone
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References
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Soil Mechanics and Foundation Engineers, Inc., 1968. A Reconnaissance Investigation
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The Irvine Company, 1978. Land Use Information, System, Newport Beach, CA.
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Area. Santa Ana, CA.
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112584
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APPENDIX A
DATA AND► CONSTRAINTS
MAPPING
0
DATA AND CONSTRAINTS MAPPING
Overview
This appendix documents the methodology used in preparing the data and constraint
maps. The consultant team prepared a base map, eleven data maps, and thirteen
constraint maps suitable for automation or for manual interpretation in the Irvine MEA.
Aerial Information Systems (AIS) was responsible for the majority of this task, with
assistance provided by Community Planning Services.
General Mapping Procedure
Each map was compiled in reference to the others, so that the data categories- show some
degree of integration of polygon boundaries. The constraint maps were either prepared
from -models derived from the data maps, or were compiled from existing published
maps. The methodologies used to prepare the topographic base map, and the data and
constraint maps are described below.
The base map was prepared on a topographic base. It also included the City corporate
limits; sphere of influence boundaries; I-5, I-405, and SR-133 Freeways; tic marks
indicating the corners of each USGS 7.5 minute topographic quadrangle map; and
reference marks used to align each map. Parts of the following six USGS quad sheets fall
within the study area: Orange, Black Star Canyon, Tustin, El Toro, Laguna Beach, and _
San Juan Capistrano. Topographic reference for registering data consistently was
provided by a mylar copy of a topographic map supplied by the Irvine Company. This
mylar was placed underneath the Irvine MEA base map and registered using the .common
registration marks. All data was plotted at a scale of 1:24,000 (1" = 2,000') on
transparent mylar sheets.
Each map was pin -registered to the base map to ensure proper alignment. Where data
classification categories between the City of Irvine MEA and the Orange County MEA
were identical, the polygon data within the sphere of influence were traced for use in the
Irvine MEA. Delineations for data within the City boundaries, and where the data
classification categories differed, were plotted from other sources.
•
A-1
Data and Constraints Mapping
0 Sources - All mans
EDAW Inc. and ESRI for County of Orange. Master Environmental Assessment, Phase
I: Constraints Mapping and Analysis. Vol. III: Technical Report. 1980.
The Irvine Company. Topographic map. Scale 1:24,000. January 1982.
U.S. Geological Survey. Black Star Canyon 7.5 minute topographic quadrangle map.
Scale 1:24,000. 1967, Photorevised 1973.
U.S. Geological Survey. El Toro 7.5 minute topographic quadrangle map. Scale
1:24,000. 1968.
U.S. Geological Survey. Laguna Beach 7.5 minute topographic quadrangle map.
Scale 1:24,000. 1965, Photorevised 1972.
U.S. Geological Survey. Orange 7.5 minute topographic quadrangle map. Scale
-1:24,000..1964, Photorevised 1972.
U.S. Geological Survey. San Juan Capistrano 7.5 minute topographic quadrangle map.
Scale 1:24,000. 1968:
U.S. Geological Survey. Tustin 7.5 minute topographic quadrangle map. Scale 1:24,000.
1965, Photorevised 1972.
DATA MAPS
Photo -interpretation played an important role in the data map preparation, particularly in
regard to landform and vegetation. The imagery utilized included high -altitude color
infrared photography (1:126,500 scale) and •low-level black -and -white photography
(1:24,000 scale). Both sets of photography provided stereoscopic coverage of the study
area. Additionally, a black -and -white mylar copy of a photomosaic of the area was
available. The mosaic was placed underneath the topographic map, facilitating the
transfer of data from stereoscopic interpretation to the data maps.
The minimum mapping resolution was five acres. The actual procedures used for
mapping each of the data items varied somewhat depending on the format of the source
data utilized. These procedures are briefly summarized below.
A-2
Data and Constraints Mapping
0 D-1 Landform
This map was interpreted using topographic maps, the aerial black -and -white photos, and
landslide collateral maps. Landslide boundaries were transferred visually from the source
collateral to the preliminary landform overlay.
Sources
American Aerial Surveys, Inc. Photo set no. 80033. Flown 2/25/80 and 2/26/80. Black
and white paper print. Scale 1:24,000 (approx.).
Fife, Donald L. Geology of the South Half of the El Toro Quadrangle, Orange County,
California. California Division of Mines and Geology, Special Report 110. Plate 1.
Scale 1:12,000. 1974.
The Irvine Company. Photomosaic. Scale 1:24,000. September 1982.
Miller, Russell V., Ran, Siang S. Geology and engineering geologic aspects of the South
Half Tustin Quadrangle, Orange County, California. California Division of Mines
and Geology.. Special Report 126. Plate 1. - Scale 1:12,000. 1976.
Morton, P.K., Edgington, W.L., Fife, D.L. Geology and Engineering Geologic Aspects
of the San Juan Capistrano Quadrangle, Orange County; California. California
Division of Mines and Geology, Special Report -112. Plate 1. Scale 1:12;000. 1974.
NASA. Scene ID No. 5780025815165. Frame nos. 5167 and 5168. Flown 2/14/78.
Color infrared paper prints. Scale 1:126,500.
Tan, Siang S., Edgington, William J. Geology and engineering geologic aspects of the
Laguna Beach Quadrangle, Orange County, California. California Division of Mines
and Geology. Special Report 127. Plate 1. Scale 1:12,000.
D-2 Slope Zones
This data map was interpreted from the USGS topographic maps by visual inspection of
the contour line densities. A slope map was prepared by delineating units of five acres or
larger where contour line densities fell within preset slope class limits. The percent slope
class assigned to any unit represented the modal value for the unit. Local variations of
less than five acres do occur within units. Where large areas have been regraded for
development (most notably in the Turtle Rock area), a code of Urban Regraded was
assigned.
A-3
•
Data and Constraints Mapping.
Sources
American Aerial Surveys, Inc. Photo set no. 80033. Flown 2/25/80 and 2/26/80. Black
and white paper print. Scale 1:24,000 (approx.).
The Irvine.Company. Photomosaic. Scale 1:24,000. September 1982.
The Irvine Company. Topographic map.. Scale 1:24,000 January 1982.
U.S. - Geological Survey. Black Star Canyon 7.5 minute, topographic quadrangle map.
Scale 1:24,000. 1967, Photorevised 1973.
U.S. Geological Survey. El Toro 7.5 minute topographic quadrangle map. Scale
1:24,000. 1968.
U.S. Geological Survey. Laguna Beach 7.5 minute topographic quadrangle map. Scale
1:24,000. 1965, Photorevised 1972.
U.S. Geological Survey. Orange 7.5 minute topographic quadrangle map. Scale
1:24,000. 1965, Photorevised 1972.
U.S. Geological Survey. San Juan Capistrano 7.5 minute topographic quadrangle map.
Scale 1:24,000. 1968.
U.S. Geological Survey. Tustin 7.5 minute topographic quadrangle map. Scale 1:24,000.
1965, Photorevised 1972.
D-3 Soils
This data was mapped using the Orange County Soil Survey which shows soil series and
variant at a scale of 1:24,000. No reformatting was. necessary. Boundaries were adjusted
to the topographic base map where necessary. Several inconsistencies were noted in the
Soil Survey data. These were clarified through direct discussions with Soil Conservation
Service personnel.
Sources
U.S. Soil Conservation Service. Soil Survey of Orange County and Western Part of
Riverside County, California. Washington, D.C.: U.S. Government Printing Office.
Scale 1:24,000. 1978.
Y
A-4
Data and Constraints Mapping
D-4 Agricultural Preserves
This map depicts the status of agricultural preserve contracts executed in accordance with
the provisions of the Williamson Act. Agricultural preserve maps were provided by Mr.
Gary Weber of The Irvine Company. Based upon these maps, areas under- contract were
mapped according to the year of contract expiration. Some areas under contract within.
the planning area extend beyond the study area and, therefore, these polygons do not
always close at the study area boundary. The preserve boundaries were visually
transferred from the maps supplied by the landowner.
Sources
Agricultural Preserve, The Irvine Company, Scale 1:24,000. Last updated September
1984.
D-5 Vegetation
This data 'map was photo -interpreted using the color. infrared and black -and -white
photography. The phot.omosaic, being the most recent photo coverage available for this
study, was used -to update areas mapped for the Orange County IVMA where development
had clearly altered vegetation patterns. Windrows and the oak trees along Sand Canyon
Avenue were added as linear features after all other vegetation data. had been mapped.
They were delineated in a manner that did not create additional polygons. A field check -
was conducted in August 1985 to confirm the status of the windrows shown on the aerial
photographs.
A comparison of this map with the vegetation map prepared for the 1971 Irvine General
Plan, will show much smaller areas mapped as "woodland". This difference is primarily
due to. the classifcation schemes used in preparing each map. The woodland
classification used in the MEA is defined in the expanded code descriptions found in the
Map Atlas. This definition requires a substantial percentage of trees for an area to qualify
as woodland. While a definition of the classification scheme used for the 1973 map is not
available, re-examination of the original map confirmed that areas with only a low
number of trees were mapped as woodland
Sources
American Aerial Surveys, Inc. Photo set no. 80033. Flown 2/25/80 and 2/26/80. Black
and white paper print. Scale 1:24,000 (approx.).
The Irvine Company. Photomosaic. Scale 1:24,000. September 1982.
A-5
Data and Constraints Mapping
6, NASA. Scene ID No. 5780025815165. Frame nos. 5167 and 5168. Flown 2/14/78.
Color infrared paper prints. Scale 1:126,500.
D-6 Environmental Documents Index
This map depicts the areas which have been subject to detailed environmental review by
the City of Irvine and other agencies. Project boundaries were taken from the project site
maps included within each environmental document. In most cases these maps were
prepared on a USGS topographic base map. This facilitated transfer of the, project
boundary lines using visual methods. The following types of environmental documents
were mapped:
Initial Studies (CEQA)
Environmental Impact Reports (CEQA)
Environmental Assessments (NEPA)
Environmental Impact Studies (NEPA)
The map legend identifies the document type and project title. In all, over one hundred
41 documents were indexed. Iri many ' cases, several documents covered one geographic
area. In these cases, the boundaries of each project were mapped separately. This
approach results in multiple document listings within many of the polygons.
In addition to the document types identified- above, three Master Environmental
Assessments also cover all or substantial portions of the study area. These documents are
noted on the map legend, but were not mapped.
Sources
The documents mapped are listed on the map legend, and have not been repeated here due
to their number.
Ms. Linda Rios, Environmental Services Division
Mr. Mike Kellog, Irvine Ranch Water District
Mr. Daniel L. Fricke, Planner, Orange County Environmental Management Agency
D-7 Archaeological Documents Index
This map geographically indexes all archaeological reports completed within the MEA
• study area. As with the Environmental Documents Index map, the same area is
A-6
Data and Constraints Mapping
frequently addressed by more than one report. In these cases each report is listed.. The
original reports were used as the source for mapping the areas covered. The boundary
data was transferred visually.
Sources:
Ms. Linda Rios, Environmental Services Division
Larry Seeman Associates, Archaeological Survey Report Notebooks, 1985.
D-8 Statistical Areas and Residential Phasing
Statistical areas are established by the City's General Plan Land Use Element. They
represent residential villages, and other logical planning areas. In all 36 statistical areas
were mapped for the N EA using visual methods from maps supplied by the City.
Residential phasing areas are established by the General Plan to guide the timing of
residential development within the planning area. Six phasing areas were mapped
visually from those adopted by the City. .
Sources
01
City of Irvine, General Plan Land Use Element Figure A-2, 1985 Scale 1:24,000
City of Irvine, General Plan Land Use Element,, Figure A-3, 1985 Scale 1:24,000
D-9 ITAP Zones
ITAP is an acronym for the Irvine Traffic Analysis Program: This program has divided
the planning area and surrounding areas into -the analysis zones shown on this map.
While this phase of the MEA work effort only identified the ITAP zones, the City is
considering expanding the scope of the system during future updates to integrate ITAP
analysis into the automated system.
Sources
City of Irvine, Irvine Traffic Analysis Program Zone Map, 1985 Scale 1:24,000
•
D-10 Census Areas
Both Regional Statistical Areas (RSA), and Community Analysis Areas (CAA) were
plotted on this map. These areas are established by the Federal Bureau of the Census in
cooperation with state and local agencies. The boundaries of each area were rescaled
A-7
Data and Constraints Mapping
using manually techniques from maps supplied by the Orange County Forecast and
Analysis Center.
Community. Analysis Areas (CAA) were taken from "Community Analysis Areas" map
(no date) published by the County of Orange, and were rescaled photographically.
This map serves as an index to relate available census data to geographical areas within
the study area. Future updates of the MEA may expand the system to include the actual
demographic information as part of the automated system.
Sources
County of Orange, Regional Statistical Areas, 1984 Scale 1:12,000
County of Orange, Community Analysis Areas, 1984 Scale 1:12,000
D-11 IRWD Token Zones
Token zones are areas representing local planning units used by the Irvine Ranch Water
District for capital improvement programing. They are used in conjunction. with the
District's land development, water use, and sewage flow computer program, and were
01 included in the MEA at the request of the Community Development Department,
Advanced Planning Section to enhance the City's geographic base of administrative
boundary information. The source map for these areas was . provided by Mr. Bob
McGrew,, Senior Engineer with the Irvine Ranch Water'District. The boundaries of each
area were rescaled from 1:48,000 to 1:24,000 using visual techniques.
Source
Irvine Ranch Water District, Token Map, Revised June 1983, Scale 1:48,000.
Once the preliminary versions of each data map had been prepared, the final versions
were drafted using a modified integration process. The purpose of integration is to reduce
the time needed to digitize the maps during the subsequent automation process. Given
that boundaries between many natural features are often coincident (i.e., changes in slope
and soil often correspond with changes in landform), the integration process typically
involve the delineation of a single line in place of three of four separate, but generally
consistent lines which appear on each of the individual preliminary maps. -
In the Orange County MEA, a high degree of integration was used to produce one
Integrated Terrain Unit Map (ITUM) containing all the lines created by all the data
categories. While an ITUM was not produced for the Irvine MEA, each final data map
Was drafted in reference to the others, in order to standardize the delineation of essentially
A-8
Data and Constraints Mapping
coincident boundaries. The soils map was drafted first and modified the least, so that it
closely resembles the published soil survey. Slope, vegetation, and landform were
subsequently drafted in that order. The result is a reasonably good "fit" when the data
maps are superimposed.
ENVIRONMENTAL CONSTRAINT MAPS
Constraint maps. were derived from the data maps, or from various published maps.
Baseline data were modeled to produce the Agricultural Capability, and' Fire Hazard
Severity maps. Floodplain Boundaries, Dam Inundation Areas, Fire Frequency,
Groundwater Recharge, and Drainage Area maps were drafted by reformatting existing
maps. When necessary, data were rescaled to 1:24,000 by use of the optical pantograph;
or by visually comparing the topographic base of the source map to the Irvine topographic
map. The procedures used for each map are described further below.
C-1 Geologic Hazards
The geologic hazards map depicts various seismic response zones within the study area.
These areas were originally established based upon a comprehensive technical _report
completed by the geological engineering firm of Woodward McNeil Associates as part of
the development program for the City's original General Plan completed in 1973. This
map is currently included in the General Plan Seismic Element as Figure M-1.- The
interpretation of each Seismic Response Area (SR.A) is found in the expanded code
descriptions provided in the appendix to the MEA Map Atlas. The boundaries of each
SRA were visually transferred to the MEA map.
Sources
City of Irvine, General Plan Seismic Element, Figure M 1, 1985. Scale 1:24,000
C-2 Flood/Dam Inundation Hazards
The following two issues were drafted on one mylar overlay to facilitate evaluation of .
overall Flood/Inundation Hazards.
Floodplain Boundaries
Floodplain boundaries were derived from United States Federal Insurance Administration
(FIA) maps. Areas within city boundaries were mapped by tracing polygons from a map
supplied by the City. Areas within the Sphere of Influence were mapped using Orange
County MEA delineations, which in turn had been drafted from photographically rescaled
A-9
i
is
Data and Constraints Mapping.
(FIA) maps. It should be noted that there is an unresolved discrepancy in the floodplain
boundaries between the FIA maps published for the City of Irvine, and those published
for the County of Orange. These discrepancy occurs in the area of the Santa Ana
Freeway and Jeffrey Road, and were plotted on the constraint map. Resolution of these
differences will have to await publication of corrected Flood Insurance Rate Maps by
FIA.
A-10
Data and Constraints Mapping
0 Sources
1�
City of Irvine. Map of 100 Year Floodplain.
U.S. Federal Insurance Administration. Flood Insurance Rate - Map, Orange County,
California (Unincorporated Areas). Scale 1" = 700'. 1979. Community Panel Number
060212, Map Number 0030, 0031, 0039, 0040,0049, 0050.
Dam Inundation Areas
This data item was derived .from several dam- inundation maps. These maps were
provided. by Ms. Sharon Franks, Program Coordinator with the Orange County
Emergency. Management Office. The maps were rescaled using the optical/manual
method for reformatting data, and by visual transfer of data.
Sources
Boyle Engineering Corp. Inundation Map of Laguna Dam. Draft. Scale 1" = 1,000'.
Boyle Engineering Corp. Inundation Map of Syphon Canyon Dam. Scale 1" = 1,000'.
1983.
V.T.N. Consolidated Inc. Inundation Map for Rattlesnake Reservoir. Scale 1"=- 1,000'.
1973.
V.T.N. Consolidated Inc. Inundation Map for Sand Canyon Reservoir. Scale 1" _
1,000'. 1973.
V.T.N. Consolidated Inc. Inundation Map for San Joaquin Reservoir. Scale 1" = 1,000'.
1973. -
V.T.N. Consolidated Inc. Inundation Map for Santiago Reservoir. Scale 1:24,000. 1973.
V.T.N. Consolidated Inc. Inundation Map for Villa Park Reservoir. Scale 1:24,600.
1975.
C-3 Fire Hazards
Fire Hazard Severity and Fire Frequency were drafted on one overlay.
�I
A-11
0
i
•
Fire Hazard Severity
The fire severity model assigns a rating to an area based on the combination of several
environmental factors which contribute to the risk associated with wildland fires. It is
derived from a system - developed by the California Division of Forestry. Three
environmental factors are considered as input in the fire hazard model: fuel loading, fire
weather, and slope steepness.
Fuel loading was derived from vegetation information as mapped for this study (see map
D-5). Four fuel loading categories were assigned:
a. - -None - Barren Areas, Water, Row Crops, Orchards, Plantations
b. Light - Grassland, Marsh (Saltwater and Freshwater)
c. Medium - Coastal Sage Scrub, Oak Savannah, Oak Woodland, Riparian
Woodland, Coniferous Woodland
d. Heavy - Chaparral, Oak Forest, Riparian Forest, Coniferous Forest
Urban areas and fieldcrops were excluded from consideration in this evaluation.
Fire weather was defined, using information from the State's Wildland Fire Danger
Rating System, for each USGS quadrangle with wildland vegetation. Each quadrangle. is
rated in one of the three categories of fire weather categories:
a. Class I (Low) - Fire weather- either in the "extreme" or "high" range on the
average of less. than one day per year (none in study area).
b. Class II (High) _ Fire weather in either the "extreme" or "high" range on the
average of one to 9.5 days per year (El Toro, Laguna Beach, Orange, San Juan
Capistrano, Tustin).
c. Class III (Extreme) - Fire weather in either the "extreme" or "high" range on the
average of more than 9.5 days per year (Black Star Canyon).
The slope categories utilized in this model were:
< 45% 45 - 65%
> 65%
These slope categories were mapped as part of the Orange County MEA, but were not
part of the Irvine MEA classification system. Thus, within the sphere of influence the
A-12
Ll
•
Data and Constraints Mapping
County MEA maps were used to delineate the appropriate slope categories,, while within
the City, additional analysis of contour line density was completed to determine the
location of these slope divisions.
• To produce the fire hazard severity map, the vegetation and slope maps were
superimposed and the resulting polygons formed wereevaluated according to the model
shown below.
Fire Weather
Class II
Fire Weather
Class III
Fuel
% Slope
% Slope
Loading
<45
45-65
>65
<45
45-65
>65
None
1,
1
1
1
1
1
Light
2-
2
2
2
2
3-
Medium
3
3-
3
4
4
4
High 3 4 4 4 4 .4
Hazard Severity Index:
1= None/Low 2 = Moderate 3 = High 4 = Extreme
This model expresses the overall fire hazard severity. It is an adaptation of the the model
used by the.Division of Forestry, with minor changes made to account for input data in a
slightly different form than that typically used by the Division. These adjustments did not
materially affect the outcome of the modeling process.
Sources
California Division of Forestry. Fire Hazard Severity Classification System for California
Wildlands. 1973.
Mr. Hamilton Mills, California Department of Forestry. Riverside, CA.
Fire Frequency
This item was derived from maps showing the fire history of the area. The data was
rescaled using the optical/manual method of reformatting data. Only the last three
decades of fire were mapped for any one area.
�I
A-13
Data and Constraints Mapping
0 Sources
Orange County Fire Dept. Fire History Map. Scale 1:66,000 (approx.). 1985.
U.S. Forest Service. Trabuco District Fire Mosaic by decades. Scale 1" = 2 miles.
Mr. Dave Hubert; Orange County Fire Department. Orange, CA
C-4 Agricultural Capability
This map describes the suitability of soils for most kinds of field crops, according to the
limitations imposed by those soils. The following codes corresponds to standard Soil
Conservation Service designations:
Class I - Soils have few limitations that restrict their use.
Class II - Soils have moderate limitations that reduce the choice of
plants or that require moderate conservation practices, or both.
Class III - Soils have severe limitations that reduce the choice of plants or
require special conservation practices, or both.
Class IV - Soils have very severe .limitations that reduce the choice of
plants, require very careful management, or both.
Class V - Soils are not likely to erode but ' have other limitations,
impractical to remove, that limit their use largely to pasture or
range, woodland, or wildlife. (None in this survey area).
Class VI - Soils have severe limitations that make them generally
unsuited to cultivation and that limit their use largely to
pasture or range, woodland, or wildlife.
Class VII - Soils have very severe limitations that make them unsuited to
cultivation and that restrict their use largely to pasture or
range, woodland, or wildlife.
Class VIII - Soils and landforms have limitations that preclude their use for
commercial production of crops and restrict their use to
recreation, wildlife, or water supply, or to aesthetic purposes.
In this study, soils in Classes III and IV were grouped together, as were those in Classes IS V through VIII. The Agricultural Capability map was produced by registering a sheet of
A-14
Data and Constraints Mapping
mylar to the final soils map and tracing only the boundaries that separated soils of
different classes as modeled for this study.
Additional soil management considerations are possible. These have been included as
oart if the expanded code descriptions included in Appendix A of the the Map Atlas.
Sources
U.S. Soil Conservation, Service. Soil Survey of Orange County and Western Part of
Riverside County, California. Washington, D.C.: U.S. Government Printing Office. Scale
1:24,000..1978.
C-5 Water Resources
The following two issues were drafted on one map since they both deal with water
resource information. Each variable was mapped from source maps more recent. than
those used in the.Orange County NSA.
Groundwater Recharge
The groundwater basin, and areas of groundwater recharge were delineated using
so collateral data and adjusted using the topographic map. Data were rescaled using the
optical/manual method of reformatting, and by visual transfer. Where necessary, lines
were adjusted to the base map.
Sources
Harvey O. Banks, Consulting Engineer Inc. High Ground Water Problem Areas in the
Irvine Area. Plate 12. Orange County Water District Irvine Area Groundwater
Management Study. Scale .1:48,275 (approximate). 1984.
- Drainage Areas by Increment
These areas were visually transferred from a map depicting the master plan of drainage
boundaries for the Irvine study area. Codes are related to the drainage increment names.
Sources
City of Irvine. Areas for Joint Drainage Program Administration. Exhibit A to
Agreement No. C689. Scale 1" = 4,000. 1972.
Proposed Increments of a Master Plan of Drainage for the Unincorporated Areas of
Orange County, California. Plate I. Dwg. No. Misc. - 106-41. Scale 1" = 2 miles. May
1968, revised May 1970.
A-15
Data and Constraints Mapping
0 C-6 Biotic Resources
Biotic resources were identified and mapped by Mr. Steve Nelson in conjunction with the
development of the Biotic Resources Element (Technical Supplement 2). The original
mapping was completed on USGS Quadrangle base maps. In all 35 areas with either
moderate or high resource potential were identified. Each was .transferred visually to one
map covering the entire study area. 'Please refer to Technical Supplement 2 for additional
information regarding the designation of individual areas.
Sources
MEA Biotic Resource Element field maps (six quad sheets), November 1984. Scale
1:24;000.
C-7 Sand and Gravel Resources
Known and potential sand and gravel locations were plotted on this map. Geologic
formations with the potential deposits were interpreted from geologic information based
upon evaluation criteria.and ratings given in: Environmental Geology of Orange County,
California, 1176. Only formations with a rating of "fair" or better were mapped. These
included the Sequel member of the Puente formation, the Sespe and Vaqueros formations,
and the undifferentiated members of the Sespe formation.
Known resource areas were plotted from geologic maps recently published by the
California Division of Mines and Geology. The Mines and Geology map was
photographically rescaled, and the data plotted directly onto the MEA map sheet. Mr.
Gary Weber of The Irvine Company was also consulted for additional information
regarding any sand and gravel resources located on the Irvine Ranch.
It is noteworthy that the areas identified as potential resource areas in the Irvine MEA do
not coincide directly with those mapped as part of the County of Orange MEA program.
This is because the County mapped geologic formations with ratings less than "fair", and
in part due to the "integration" process which adjusted the polygon boundaries.
Sources
Division of Mines and Geology, Map of Orange County Showing Mines and Mineral
Deposits, 1981, Scale 1:48,000.
Division of Mines and Geology, and County of Orange, Environmental Geology of
Orange County. California, 1976, Scale 1:24,000.
0
A-16
Data and Constraints Mapping
Division of Mines and Geology, 1981. Mineral Land Classification of the Greater Los
Angeles Area, Part III. Classification of Sand and Gravel Resource Areas, Orange
County-Tesmescal Valley Production -Consumption Region. Scale of origins 1:24,000.
C-8 Historical Resources
As .part of the MEA, a records check was completed to locate known'historical resources
within the planning area. The following institutions were consulted during, the records
check:
California Historic Preservation Office
Orange County Historical Commission
Irvine Historical Society
City of Irvine Historical, Archaeological and Paleontological Committee
The following publications were also reviewed for historical resource information:
California History. Plan
California Inventory of Historical Resources
National Register of Historic Places
California Historical Landmark Register
California Points of Historical Interest Register
�1
Historical Landmarks of Orange County
Irvine General Plan, Cultural Resources Element
East Irvine Historical Area, by the Irvine Blue Ribbon Committee
Historical resources officially recognized by federal, state, or local agencies were
mapped. - While additional, potentially significant, historic resources exist within the
study area, no comprehensive study has been undertaken to identified or evaluated their
significance, thus they have not been mapped. Tenant farm homes fall within this
category. Since the City's Cultural Resources Element identifies all officially recognized -
sites, it was used to plot the site locations by visually transposition. The approximate
location of each resource is denoted by a circular polygon.
A-17
Data and Constraints Mapping
0 Sources
City of Irvine, General Plan Cultural Resources Element Figure N-1, 1985, Scale of
original 1:24,000.
C-9 Archaeological Resources
Archaeological resources were mapped by the firm of Larry Seeman Associates during
preparation of the Archaeological Resources Element. * This Element is included as
Technical Supplement 3. -It provides a further discussion of the methodology used in
preparing -this map. Because of the sensitivity -of. site location information of
archaeological sites, this map is considered confidential, and has not been published as
part of the Map Atlas.
Sources
Refer to Technical Supplement 3.
C-10 Paleontological Resources
This map depicts the paleontological sensitivity of the planning area's rock units. It also
identifies the location of all recorded paleontological sites. The final MEA map was
compiled from . draft maps prepared on USGS Quad sheets by the firm of RMW
Associates. The criteria used to map -the sensitive zones, and adescription of the recorded
sites is presented in the Paleontological Element, Technical Supplement 4.
Sources
Refer to Technical Supplement 4.
C-11 Aircraft Noise and Crash Hazards
As the title indicates, this map is a composite depicting both aircraft noise and crash
hazard information.
Of all three aviation facilities within or surrounding the planning area, crash hazard zones
have only been established at one: Marine Corps Air Station, El Toro. At this installation,
accident potential zones (APZ) include Clear Zones, APZ 1, and APZ 2. While not
strictly an accident potential zone, local pattern aircraft corridors are also established.
The definition of these zones is found in the expansion code descriptions included with
the Map Atlas. With the exception of the local pattern aircraft corridors, these areas were
• transposed from maps provided by the City of Irvine. The local pattern aircraft corridor
boundaries were rescaled from Exhibit V-10 of the AICUZ Study for El Toro.
A--18
Data and Constraints Mapping
Noise
Noise contours were mapped -in increments of five using Community Noise Equivalent
Levels (CNEL), the standard used by the City of Irvine. The contours for El Toro were
transposed directly from General Plan Noise Element Figure F-2. Noise contours for
John Wayne Airport were derived from 1984 Noise Contour maps provided by the airport
manager's office. The noise contours for MCAS', Tustin Helicopter Facility were
rescaled from the 1976 AICUZ for that facility. Because all noise contour locations are
heavily influenced by such factors as the level of • aircraft operations and mix of aircraft
types, the contour locations are subject to change, and will require updating as
circumstances change.
Sources
City of Irvine, Map of El Toro Crash Hazard Zones, 1985, Scale 1:24,000.
U.S Department of the Navy, Air Installations Compatible Use Zones Study, MCAS El
Toro, Exhibit V-10, 1981. Scale 1"=4500' (approximate)
U.S Department of the Navy, Air Installations Compatible Use Zones ' Study, MCAS,
Santa Ana, 1976. Scale 1"=4500' (approximate)
County of Orange, John Wayne Airport Noise Contours for 1984. Scale approximately
1:48,000.
C-12 Roadway and Railroad Noise
The 65 CNEL noise contour for combined future noise levels resulting from roadway and
railroad noise sources was mapped based upon maps provided by the City. The noise
contour was visually transposed from a current 1:24,000 map to the MEA map sheet.
Sources
City of Irvine, General Plan Noise Element, Figure F-3: Future Highway/Railroad Noise,
1985. Scale 1:24,000.
C-13 Special Districts
This map is a composite of three special district designations: Hillside District, Coastal
Zone, and Air Quality Source/Receptor Areas. The Hillside District depicts an overlay
district established by the City's Zoning Ordinance. This area was visually te-scaled
from maps district boundary maps included in the Zoning Ordinance. The Coastal Zone
designation denotes the area subject to special land use regulations associated with the
A-19
•
Data and Constraints Mapping
California Coastal Conservation Act. This area also was -re-scaled visually from a map
provided by the City. Air Quality Source/Receptor areas are -boundaries established by
the South Coast Air Quality Management District for air quality data collection and trend
analysis. Two such areas span the study area. The boundaries of these areas were plotted
by visual transposition of the boundaries from maps .supplied by the AQMD.
Sources
City of Irvine, 1984. Zoning Ordinance, Hillside Overlay District, V.E. 502, Figure 500-
City of Irvine, 1984. Zoning Ordinance, "Special Regulations for Development in the
Coastal Zone, Figure 814-1.
South Coast Air Quality Management District, 1983. Air Quality Handbook, Figure 4 -
Source/Receptor Areas.
A-20
APPENDIX B
MITIGATION MEASURE SOURCES.
6
•
•
APPENDIX B
MITIGATION POLICY INVENTORY
The following inventory was prepared in support of the Irvine MEA. It is current as of July
1985. In addition to the documents listed below, the Urban Design Implementation Plan was
reviewed. This document has not been listed separately, however, ' since the environmental
policies contained in the UDIP are also found within the documents.
Map TitlelReference Document Applicable Policies
C-1 Geologic Hazards
General Plan Policies: J=1b; M-la; M-2a,d,f,g;
Zoning Ordinance:
Environmental Review Matrix:
Subdivision Manual:
Standard Subdivision Conditions:
Landscape Manual:
Hillside Development Manual:
General Plan Amendment # 4 EIR:
C-2 Flood/Dam Inundation Hazards
General Plan Policies:.
Zoning Ordinance:
Environmental Review Matrix:
Subdivision Manual:
Standard Subdivision Conditions:
Seismic Element Standards
V.E. 733.5 (4)
Earth Resources (page 4) and
Appendix A
Section 4.4 a
Conditions 2.2; 2.7; 3.2
Guideline IF
Mitigation measures page 157
B-2g; L-3f, L-4b,g,h,i,n,o,
q,tu
V.E. 503; 700.2 (6); 713.4
(4), (6),(7),(9); 733.5
(7),(11).
Water Resources (page 6)
Section 4.3 a (36) and (37)
Conditions 1.1 b; 1.3; 2.5
�1
B-1
J
Mitigation Sources
Map TitlelReference Document Applicable Policies
a
•
Landscape Manual:
Hillside Development Manual:
General Plan Amendment #-4 EIR:
C-3 Fire Hazards
General Plan Policies:
Zoning Ordinance:
Environmental Review Matrix:
Subdivision Manual:
Standard Subdivision Conditions:
Landscape Manual:
Hillside Development Manual:
General Plan Amendment # 4 EIR:
C-4 Agricultural Capibility
.General Plan Policies:
Zoning Ordinance:
Environmental Review Matrix:
Subdivision Manual:
Standard Subdivision Conditions:
Landscape Manual:
Hillside Development Manual:
General Plan Amendment # 4 EIR:
Guidelines 4 A - H
Mitigation measures pages 158, 159
J-lc; J-2a-b,d
Conditions 2.1; 3.3
Guidelines 7 A; 8 C
Mitigation measures pages 159
L-3a-g,i-o
V.E. 201; 733.5 (3)
Mitigation measures pages 167-169
B-2
Mitigation Sources
Map Title/Reference Document Applicable Policies
C-5 Water Resources
General Plan Policies:
Zoning Ordinance:
EnvironmentarReview Matrix:
Subdivision Manual:
Standard Subdivision Condition:
Landscape Manual:
Hillside Development Manual:
General Plan Amendment # 4 EIR:
C-6 Biotic Resources
General Plan Policies:
Zoning Ordinance:
Environmental Review Matrix:
Subdivision Manual:
Standard Subdivision Conditions:
Landscape Manual:
Hillside Development Manual:
General Plan Amendment # 4 EIR:
Eculyptus Windrow Policy (Reso 1036):
•
A-2p; L-ld,f.--m,o; L-4c,p
V.E. 700.2 (6);736.4 (15),
(16), (17).
Water Resources (page 6)
Section 1.3
Conditions 1.2;1.3; 2.3
Page 43 (#6); Page 39 (#5)
Guidelines 2 C,I; 3 D
Mitigation measures pages 145, 148
A-2p; L-la-g, r; L-2a-h
V.E. 708.4 (7); 713.2 (5);
713.4 (8),(1.6).
Biotic Resources (page 7)
Section 3.6-c (5); 4.3 a
(40), (41); 4.3 a (42);4.6
(23)
Conditions 2.4
Section I. 1.
Guidelines 1 C, E, E; 3 A-B,
E;4A;8A,B
Mitigation measures pages 153-155
Entire document
e
B-3
Mitigation Sources
Map TitlelReferencebocument Applicable Policies
C-7 Sand and Gravel Resources
General Plan Policies: A-ld
Zoning Ordinance: --
Environmental Review Matrix: --
Subdivision Manual: --
Standard Subdivision Conditions: --
-Landscape Manual: --
Hillside Development Manual: Guideline 2 G
General Plan Amendment # 4 EIR: --
C-8 Historical Resources
General Plan, Policies:
N-1,a d, N-2,a-c,f-h;
Cultural Resources Element
Standards
Zoning Ordinance:
V.E. 713.4 (20); 719.4 (2)
Environmental Review Matrix:
Cultural and Scientific
Resources (page 9) and
Appendix D
Subdivision Manual:
--
Standard Subdivision Conditions:
--
Landscape Manual:
--
Hillside Development Manual:
Guidelines 1 G;8 B
General Plan Amendment # 4 EIR:
Mitigation measures pages 161
•
C-9 Archaeological Resources .
General Plan Policies: N-la-d; N-2a-c,f-h; Cultural
Resources Element Standards
10
B-4
Mitigation Sources
0 Map Title/Reference Document Applicable Policies
Zoning Ordinance: V.E. 5002.3 (c); 700.2 (14);.
708.4 (10); 710.4 (5); 714.3
(17); 724.5 (13); 733.5 (10);
736.4(3)
Environmental Review Matrix: Cultural and Scientific
Resources (page 9) and
Appendix D
Subdivision Manual:
Standard Subdivision Conditions: Conditions 2.6
Landscape Manual: --
Hillside Development Manual: Guidelines 1 G;8 B
General Plan Amendment # 4 EIR: Mitigation measures pages 162
C-10 Paleontological Resources
General Plan Policies: N-la-d; N-2a-c,f-h; Cultural
Resources Element Standards
Zoning Ordinance: V.E. 708.4 (10)
Environmental Review Matrix: Cultural and Scientific
Resources (page 9) and
Appendix D
-Subdivision Manual:
Standard Subdivision Conditions: Condition 2.6
Landscape Manual: --
Hillside Development Manual: Guidelines 1 G;8 B
General Plan Amendment # 4 EIR: Mitigation measures pages 163
C-11 Aircraft Noise and Crash .
General Plan Policies: A-if--hj; B-2m,; F-la-d,f-
k,m-o; F-2a; Noise Element
Standards
B-5
Mitigation Sources
Map Title/Reference Document Applicable Policies
Zoning Ordinance:
Environmental Review Matrix:
Subdivision Manual:
Standard Subdivision Conditions:
Landscape Manual:
Hillside Development Manual:
General Plan Amendment # 4 EIR:
Noise Ordinance:
C-12 Roadway and Railroad Noise
General Plan Policies:
Zoning Ordinance:
Environmental Review Matrix:
Subdivision Manual:
Standard Subdivision Conditions:
Landscape Manual:
Hillside Development Manual:
General Plan Amendment # 4 EIR:
Noise Ordinance:
Stationary Sources:
• General Plan Policies:
V.E. 301.4; 301.7; 700.2 (2);
708.4 (6); 709.3; 713.3;
713.4 (2), (21); 733.3 (a4,
b4,c5,e); 733.5 (5),(13);
(14),(15),(16); 735.3; 736.3;
801.2 Al
Noise (page 12) and Appendix E
Conditions 3.4; 3.5 (proposed)
Mitigation measures pages 209, 210, 213
Entire document
A-lf.hj; B-2m; F-la-c,e-
k,p,r,t; Noise Element
Standards
V.E. 700.2 (8); 713.4 (18),
(19); 733.5 (14),(15),(16);
801.2 Al
Noise (page 12) and Appendix E
Conditions 3.4; 3.5
Mitigation measures pages 209,210, 213
Entire document
F-2a-c
B-6
Mitigation Sources
Map TitlelReferenceDocument Applicable Policies
Noise Ordinance:
C-13 Special Districts
Hillside District
General Plan Policies:
Zoning Ordinance:
Environmental Review Matrix:
Subdivision Manual:
Standard Subdivision Conditions:
Landscape Manual:
Hillside Development Manual:
General Plan Amendment # 4 EIR:
Coastal Zone
General Plan Policies:
Zoning Ordinance:
Environmental Review Matrix:
Subdivision Manual:
Standard Subdivision Conditions:
Landscape Manual:
Hillside Development Manual:
General Plan Amendment # 4 EIR:
Entire document
A-2k; Land Use Element
Standards for rural
residential; B-2g; B-4
a-c; L-1n,p-u; L-3e
V.E. 502; 721.4 (2).
Project Description (page 1),
Earth Resources (page 4),
Water Resources (page 6),
Biotic Resources (page 7),
Cultural and Scientific
Resources (page 9)
Section 4.4 g
Conditions 3.7
Entire Manual
Mitigation measures pages 135-137
V.E. 814
0
B-7
Mitigation Sources
Map TitlelReference Document Applicable Policies
AQMD
General Plan Policies:
Zoning Ordinance: -
Environmental Review Matrix:
Subdivision Manual:
Standard Subdivision Conditions:
Landscape Manual:
Hillside Development Manual:
General Plan Amendment # 4 EIR:
Other
Phasing
General Plan Policies:
Zoning Ordinance:
Environmental Review Matrix:
Subdivision Manual:
Standard Subdivision Conditions:
Landscape Manual:
Hillside Development Manual:
General Plan Amendment # 4 EIR:
•
B-8
A-le,g,hj; A-2b, A-5g; B-3c;
C-3e; D; D-1 all; I-1 all; L-
4 a-m,n-v
V.E. 700.2(7),(11),(13),(15);
735.3 (2); 736.4 (2), (5).
Air Resources (page 8)
Section 4.4 d
Mitigation measures pages 143, 144, 223
A-2c; A-3 all(14); A-4 all
(IBC); J-2d; L-3a; L-3o
V.E. 700.2 (4),(5).
0
11
is
Mitigation Sources
This -section 'lists
inventory which
The source of a
ADDITIONAL MITIGATION SOURCES
the sources in addition to those identified in the preceding policy
vere consulted during preparation of the MEA mitigation measures.
speck measure can be found in the User's. Guide in parenthesis
following each measure.
C1 Geologic Hazards
Chapter 70, Uniform Building Code
California Subdivision Map Act
Mr. Tony Slunka, Irvine City Engineer
Mr. Loran Anderson, Principal Engineer
C-2 Flood/Dam Inundation Hazards
Dam Inundation
California Government Code 8589.5
Mr. Keith Harrison, California Office of Emergency Services
Sylvan Hersh, PhD., Emergency Services Coordinator, City of Irvine
F1'oodina
Mr. Ed Moore, Principal Planner
Mr. Dain Styles, The Irvine Company
Mr. Mark Wildermouth, Camp Dresser and McKee
Ms. Diane Dzerske, The Irvine Company
C-3 Fire Hazards
Mr. Tony Slunka, Irvine City Engineer
Mr. Gene Hutain, Fire Protection Analyst Orange County Fire Department
Mr. Daniel Fricke, Orange County MEA
Fire Safety Considerations for Development in Hillside Areas = A Guide for Planners and
Developers
C4 Agricultural Capability
Ed Moore, Community Development Department .
Dain Anderson, Community Development Department
B-9
0
Mitigation Sources
Steve Haubert, Community Development Department
C-5 Water Resources
Groundwater
Mr. Bob Storhheim, Manager Inspection Services
Mr. Nereus L. Richardson, Assistant Manager and District Engineer, Orange County
Water District
Harvey O. Banks, 1984. Ground Water Management Irvine Area Orange County, CA.
Prepared for the Orange County Water District
Master Plan Areas
Mr. Tony Slunka, City Engineer
Mr. Loran Anderson, Principal Engineer
C-6 Biotic Resources
Refer to the Biotic Resources Element, MEA Technical Supplement 2
C-7 Sand and Gravel Resources
Environmental Geology of Orange County, California,1976.
Air. Daniel Fricke, Orange County EMA
Mr. Gary Weber, The Irvine Company
C-8 Historical Resources
Ms. Judy Liebeck, past president of the Irvine Historical Society
Ms. Ann Johnson, member of the Irvine Historical Society
Mr. Cliff Boderman, Curator of the Irvine Historical Museum
Irvine Historical, Archaeological and Paleontological Committee, meeting of December
12,1985
C-9 Archaeological Resources
Mr. Ed Moore
Irvine Historical, Archaeological and Paleontological Committee, meeting of December
12, 1985
Beth Padon, Larry Seeman Associates, County Certified Archaeologist
C-10 Paleontologicaf Resources
isMr. Rod Raschke, RMW Associates, County Certified Paleontologist
B-10
1 0
•
Mitigation Sources
Irvine Historical, Archaeological and Paleontological Committee, meeting of December
12,1985
C-il Aircraft Noise and Crash Hazards
Eve Frost, General Plans Section
Ed Moore, Environmental Services Section
Mike Thiele, General Plans Section
Irvine, City Council Resolution - 1090
Irvine Noise Ordinance
C-12 Roadway and Railroad Noise
Mr. Mike Thiele, General Plans Section
Mr. Ed Moore, Environmental Services Section
Mr. Dain Anderson, Environmental Services Section
C-13 Special Districts
Hillside District
Mr. Mike Thiele, General Plans Section
Mr. Ed Moore, Environmental Services Section
Mr. Dain Anderson, Environmental Services Section
Coastal Zone
Mr. Mike Thiele, General Plans Section
Mr. Ed Moore, Environmental Services Section
Mr. Dain Anderson, Environmental Services Section
Air Quality Management Districts
City Council Resolution 1171
South Coast Air Quality Management District, Air Quality Handbook
Mr. Brian Farris, South Coast Air Quality Management District
Mr. Mike Thiele, General Plans Section
Mr. Ed Moore, Environmental Services Section
Mr. Dain Anderson, Environmental Services Section
B-11
0
APPENDIX C
DATA CLASSIFICATION SYSTEM
i
•
•
APPENDIX C
DATA CLASSIFICATION SYSTEM
Introduction
The MEA data classification system serves several important functions. First, it divides a
resource with a continuous spectrum of values or interpretations into separate categories.
For example, slope is divided into specific increments such -as 5, 10, or 20 percent so that
these areas may be mapped in a polygon format. Second, the classification system
describes already mapped, readily distinguishable units such as geologic formation or soil
types. These units are typically mapped by name or number with the classification
system serving as an enumeration of these previously defined units. Finally, the
classification system delineates natural, cultural, 'and administrative boundaries, such as
those associated with census or planning areas. The delineations of these areas serves as
an index for examination of related information or environmental issues.
Definition of the classification system was guided by considerations similar to those
employed in the selection of the environmental topics themselves. Namely, the data
category had to be broad enough to produce legible maps with sufficient detail to. be
useful, it had to be available throughout the study area in published form or be capable of
being interpreted from aerial photography, and it had to respond to environmental issues
considered important to the City.
Many of the data categories are self explanatory, while others tend to be somewhat
cryptic. For example, "mixed chaparral' does not immediately suggest the individual
plant species which comprise this biotic community. In these instances, an expanded code
description has been prepared. These expanded descriptions are found as an appendix to
the Map Atlas.
C-1
0
•
CLASSIFICATION SYSTEM
The following presents the data classification system used for the Irvine MEA.
Data Maps
Mau Title Data Categories
1. Landform Lake
Reservoir
Coastal Lagoon/Estuary
Depression
Delta
Beach
Dune
Cliffs
Gully
Floodplain
Upland Valley
Marine Terrace Bench
Marine Terrace Sideslope
Alluvial Fan
Alluvial Terrace Bench
Alluvial Terrace Sideslope
Alluvial Plain
Landslide
Rock outcrop
Mountain Ridge Top
Mountain Sideslope
Hilltop
Hill/sideslope
Man-made/altered
C-2
Data Classification
0
Ma Title Data Categories
2. Slope Zones
3. Soils
4. Agricultural Preserves
5. Vegetation
a, -
0-5%
5 -10%
10 - 15%
15-20%
20 - 25%
25 - 30%
>30%
Mapped by U.S. Soil Conservation
Service Soil series
Areas under contract by year of expiration
Grassland
Coastal Sage Scrub
-Coastal Sage Scrub -Sage
Coastal Sage Scrub -mixed
Chaparral
Chamise Chaparral
Mixed Chaparral
Oak Savannah
Oak Woodland/Forest
Oak Woodland
Oak Forest
Riparian Woodland/Forest
Riparian Woodland
Riparian Forest
Windrow
Sand Canyon Oaks
Marsh
Saltwater Marsh
Freshwater Marsh
Barren
Agriculture
Orchard (type)
Fieldcrop
Urban/Cultural-Altered
ft
C-3
0
Data Classification
Map Title Data Categories
6. Environmental Documents Index
7. Archaeology Documents Index
S. Statistical Areas and Residential Phasing
9. Irvine Transportation Analysis Program
10. Census Areas
Major environmental documents
indexed by geographic coverage.
Reports indexed by geographic coverage.
Statistical areas and phasing mapped according
to established general plan categories.
Analysis zones mapped according ITAP
By Regional Statistical Areas and
Community Analysis Areas
11. Irvine Ranch Water District Token Areas By established IRWD. zones
Environmental Constraint Maps
1. Geologic Hazards
2. Flood/Dam Inundation Hazards
Seismic Response Area 1
Seismic Response Area 2
Seismic Response Area 3
Seismic Response Area 4
Seismic Response Area 5
100 Year Floodplain
Floodway
Floodway Fringe
Dam inundation areas by reservoir
C-4
Data Classification
16
Map Title Data Categories
3. Fire Hazards
4. Agricultural Capability
i
5. Water Resources
•
Fire Hazard Severity
None
Low
Moderate
High
Extreme
Not Rated
Fire Frequency
No Known Fires
One Fire
Two Fires
Three Fires
Agricultural Capability
Not agricultural Soils
Class III & IV Soils
Class II Soils
Class I Soils
Groundwater Recharge
Not in basin
Restricted recharge
Partially restricted recharge
Unrestricted recharge
Drainage Areas by increment
vp
C-5
Data Classification
Mau Title Data Categories
6. Biotic Resources No Significance:
No resources
Moderate Significance:
Buffer area
Link between habitat areas of
high significance and locally
significant habitats
Locally significant riparian habitats
Locally significant freshwater
marsh habitats
Locally significant stands of
native vegetation
Open water/shoreline with local
value as waterfowl habitat
High Significance:
Rare/endangered/unique species
Regionally -significance riparian
habitat
Open water/shoreline with
regional significance as
waterfowl habitat
Prime bird of prey nesting/roosting area
Prime bird of prey foraging/wintering area
Prime bird of prey
nesting/roosting area
Major wildlife movement corridor
Regionally significant
freshwater.marsh
Regionally significant oak
woodland
Woodland/brushland/grassland
ecotone
C-6
11
r-7
Data Classification
.Man Title Data Categories
7. Sand and Gravel Resources
8. Historical Resources
9. Archaeological Resources
(Confidential Map)
10. Paleontological Resources
11. Aircraft Noise and Crash Hazards
12. Roadway and Railroad Noisr,
13. Special Planning Areas
Not resource area
Potential resources
Known resources
Recognized sites plotted
Recorded site locations and status plotted
Mapped by Sensitivity Zone:
None
Low sensitivity
Moderate sensitivity
High sensitivity
Recorded sites
Airport Noise Contours (CNEL)
<60
60-65
65-70
70-75
75-80
>80
Airport Crash Hazards
Not in a crash hazard
Local aircraft traffic zone
Accident Potential Zone 1
Accident Potential Zone 2
Airport clear zone
65 CNEL Railroad and roadway noise
contour plotted
The following area boundaries plotted:
Hillside Overlay District
Coastal Zone
Air Quality Management District Subbasins
C-7
i
•
BIOTIC RESOURCES
ELEMENT
Technical Supplement 2
•
BIOTIC RESOURCES ELEMENT
Prepared For
COMMUNITY PLANNING SERVICES
EL TORO, CALIFORNIA
Prepared By
STEVEN G. NELSON
CONSULTING BIOLOGIST
August 1985
Revised January 1986
•
0
CONTENTS ,
I. INTRODUCTION
A. Overview of Biotic Resources .. . ... .. .... ......... 1
B. Purpose, Scope and Objectives ......... , ............... 1
II. APPROACH
A. Current Practices and Problems ............. .......... 4
B. The Application of Commonly Accepted Criteria - A
Uniform Procedure for Resource Assessment :................. 4
III-. FINDINGS
A. Biotic Communities ......... .......... .......... 9
B. High Interest Species ................................. 9
C. Areas of High Significance ......... ..................... 11
D. Areas of Moderate Significance ....... ...:........a... 20
E. Areas of Low Significance ............................. 20
IV. WHY PRESERVE BIOTIC DIVERSITY? .......... I. .... `....... 21
V. REFERENCES AND PERSONS CONSULTED ................... 25
APPENDICES
A. Applicable Laws and Planning Policies
B. Sources Reviewed for Assessment Criteria
C. Individuals or Groups Consulted in the Development
of Assessment Criteria
D. Evaluation Criteria
E. Descriptions of Biotic Communities
F. Areas of High and Moderate Significance
G. Mitigation Program
H. Glossary
i
r
L--j
TABLES
A Total County Coverage and Percent of County Total for Major
Community Types within the Study- Area. ................... ' 10
B Species of Special Status and/or Concern and Representative Examples
of Their Occurrence within the Study Area .. .... ........... 12
FIGURES
1 Study Area ....... . ................ .............. 2
2 Biotic Resources Map ............. ........................ 18
ii
L INTRODUCTION
A. Overview of Biotic Resources within the Study Area
The study area, including -the City of Irvine and its sphere of influence lies within the -
coastal and foothill region of central Orange County: Ecologically, the area encompasses
a wide range of physical habitats including flatlands, hills and mountains. These habitats
support a diverse collection of grassland, brushland and woodland vegetation types which,
in turn, support a wide variety of wildlife.
As is typical of most of the Southern California coastal region, past agricultural activities
and more intense urban development have taken place over most of the study area and
have resulted in the removal of natural habitats from the landscape.. As a consequence,
large areas 'of native vegetation and wildlife habitats have also been lost and, today,
remain relatively undisturbed only .in the steeper hills and mountains. -
Man's impact on the landscape and biotic resources within the _study area has not been
limited to habitat loss. Man has also made a contribution to the landscape in the form of
reforestation and the creation of lakes, ponds and reservoirs in an otherwise semi -arid
landscape. Right or wrong, these contributions are a part of the ecological "fabric" which
covers the study area today.
This ecological fabric contains eight major vegetation types, six of which are native or
naturalized and two of which are man -created. Associated with -these are hundreds of
plant and wildlife species,' many of which have become very. restricted in their
distribution. Along with their inherent natural resource value, some of these resources
possess cultural value, being representative of the area's agrarian history and heritage.
Almost certainly, the need to actively plan and manage this biotic resource base will
increase as the City of Irvine annexes additional land and continues to grow and expand.
B. Purpose. Scope and Objectives of the Study
The purpose of this study is to lay the groundwork and provide a working tool for the
planning and management of the City's biotic resources. The scope of this, study includes.
the entire existing resource base encompassed by the City limits and the City's sphere of
influence which may eventually be .annexed to the City (Figure 1). Recognizing,
however, the fact that biotic resources within a single jurisdiction cannot always be
managed in a "vacuum" due to their being part of larger, regional ecological systems, this
study is designed to interface and work with the County of Orange Master Environmental
1
•
11
•
•
Assessment. Phase I of the county study, completed in 1981, covered the unincorporated
lands surrounding the City and overlaps this study within the City's sphere of influence
(1).
In accordance with its purpose -and scope, this study has the -following objectives.
o To document the existing- biological resource base within the study area at a
scale appropriate for general planning purposes.
o To define and delineate areas of high, moderate and low biological
significance, as an "overlay" to the existing resource base; whereby ongoing
resource planning review and management activities can be focused.
o To outline and discuss management considerations -for the various areas of
significance identified, whereby City planners will have, in hand, guidelines
to direct their planning -and management activities.
Through the accomplishment of these objectives, this=study- is intended to have utility to
planners and decision makers, as well as to landowners, developers and the general public.
If consistently applied, it will serve as a basis for the common understanding of land use
capabilities and suitabilities for future growth within the city.-
A cautionary note should be made concerning the types of uses to which this analysis can
be put. This study represents a first level constraints analysis. It may be used to identify
key biological constraints and general management guidelines for further detailed study as
part of the planning and environmental review processes. Furthermore, this analysis is not
static. As additional information is generated through subsequent- more detailed 'on the
ground investigations, the findings of- this study should be refined and updated. It is not
anticipated, however, that this process will result in changes in sensitivity levels. Rather,
it is expected to provide detailed information on the distribution and interrelationships of
key resources within the designated management units so that they may be properly
managed at the appropriate level of detail.
3
•
H. APPROACH
A. Current Practices and Problems
A recurring question which arises in land- use planning, resource management and
environmental review is what constitutes a significant biological resource? Surprisingly
even more than a decade after the California Environmental Quality Act of 1970 (CEQA)
was enacted, .there is no universally accepted answer. CEQA- established a procedural
structure for environmental review to ensure that. the long-term protection -of the
environment is a guiding criterion in public decisions. However, consistently within this
structure there is, the need to determine whether or not a resource is significant.
For many of the factors customarily considered in land use planning and management the
intent of the term "significant" is readily discernible as the result of laws, codes-. and
ordinances written specifically to address public health, and safety: For these factors,
including for example, geotechnical hazards, flood hazards and .ambient noise levels, the
determination of significance is fairly clear and basic. This is not, however, the case with
biological resources. Rather than being a -basic determination founded on legal
requirements, the assessment of biological resource significance has largely been- -a
subjective determination based on individual -interpretation. Although some selected
biological resources are addressed by laws, codes and policies, they are limited to legally
protected rare and endangered species, . riparian 'habitats and wetlands. Appendix A
provides an annotated listing of applicable laws and policies. These address only a
fraction of the biological resources which exist in our environment and in. no way
represent the only significant resources given any reasonable interpretation.
The. lack of broader criteria with which to determine significance has been a fundamental
problem in managing biological resources. Principally, this problem has manifested itself
in several ways, including unpredictable findings and conclusions; widespread
disagreement on resource values; and, an inconsistent planning perspective within which
sound goals and planning decisions have been difficult to make.
B. The Application of Commonly Accepted Criteria - A Uniform Procedure for Resource
Assessment
As mentioned above, current practices of biological resource assessment have resulted in
an undisciplined, vaguely defined activity which often results. in unworkable concepts for
regionwide resource planning and management. What is needed, is a set of evaluation
criteria for defining biological significance which are commonly accepted within the
4
scientific, governmental and private communities. The central element and strength of
such criteria should be that they are well enough defined to allow their. application to
specific resource types, yet are broad enough to encompass all resource types. In addition,
these criteria should remain fixed to ensure consistency and objectivity.
Following is a description of how this concept was applied --to the City of Irvine Master
Environmental Assessment. There were four basic phases involved: 1) the research phase,
where the evaluation criteria were developed; 2). the -inventory phase, where the resource
base was defined; 3) the interpretive phase, where the evaluation criteria were applied to
the resource base; and 4) the analysis -phase, wherelogical management units were
delineated in a manner which best allows for the planning and management -of resources
according to their degree of significance. .
1. The Research Phase
As the logical first step of any study like this one, the research ' phase consisted of
reviewing relevant literature and canvassing a body of biologists involved in planning and
resource management activities. For the most part, this particular task was accomplished
by the author during co -preparation - of' the 1976 Los ,Angeles- County Significant
Ecological -Area Study for the Los.Angeles County Department of Regional Planning as
part of their general plan update program (2).
During the Los Angeles County Study some.40 to 50 resource management and planning
documents and reports were reviewed to understand how significance had previously been
defined. In addition, over 150 individual biologists representing some 62 governmental
agencies, private conservation groups and academic institutions responded to a request for
-their input. Appendices B and C provide lists of sources reviewed and persons contacted,
respectively, for the Los Angeles County Study. - Interestingly enough, a more recent
review of literature discovered a similar, totally independent approach developed for
environmentally sensitive area planning in Ontario, Canada, for use by municipalities
across that province (3). Many of the specific criteria promoted by the Ontario. study were
nearly identical to those used. for the Los Angeles County study.
The intent of the Los Angeles County study (and the Ontario approach) was to identify
significant ecological areas for a comprehensive planning program, and the input received
was translated into only the highest level of concern. However, since resource
significance is seldom a "black and white" issue it was later recognized that a more useful
set of criteria would be one which would assess resources according to either high,
moderate or low significance. Further, it was recognized that these rankings should reflect
and dictate the level of concern and attention resources should receive in the land use
planning and management process.
5
•
The use -of criteria defining high, moderate and low.. levels of significance was precisely
the approach taken in the biological assessment for the 1981 County of Orange Master
Environmental Assessment, also prepared by the author (1). In this regard, the approach
used for the County study was viewed as superior to its Los Angeles 'County and .Ontario
predecessors and was the model for the approach used for the preparation of .this report.
Thus, the research phase was largely completed and'is well -documented in the previously
cited studies with only an update of the literature review and canvassing efforts required.
The reader should note that this study refines the previous approaches, particularly the
County of Orange MEA. This is reflected in- the categorization of resources. Whereas,
the classification scheme includes the same types, of resources as those identified in the
County report, their definition is more specific. That is, this study generally "split" or
expands upon resources, which were "lumped" in the County report. For example-, the
County, report -included a classification of "ecotone of oak/riparian woodlands, brushland
and grassland habitat". This report is, more specific in its classification delineating this
same resource type a& "regionally significant oak woodland", "regionally significant
riparian habitat" and "woodland/brushland/grassland ecotone." In addition, the
significance of the Bommer Canyon management area, of which only a small portion was
evaluated in the County study, was upgraded from moderate to high.
A detailed description of each of the evaluation" criterion is .provided in Appendix. D.
Briefly, however, the criteria andrationale defining "high significance" relate to resources
that are generally limited in distribution -and whose contribution to biological diversity
and/or productivity is critical within their regional context. In most cases, the term
"regional" refers 'to Southern California. For purposes of the Irvine Master
Environmental Assessment, these resources include:
o The habitat of state and federally sanctioned rare, endangered and -threatened
plant and animal species.
o Biotic communities, vegetative associations and habitats of plant and animal
species that are highly restricted in distribution on a regional basis.
o Habitat, that at some point in the life cycle of a species or group of species,
serves as a concentrated breeding, feeding, resting or migrating grounds, and -is
limited in availability.
o Biotic resources that are of scientific interest because they are either an extreme
in physical/geographical limitations, or they represent an unusual variation in a
population -or community.
R,
o Areas that serve as "core" habitats, to regional plant, wildlife, and game.
populations and fisheries.
The criteria for defining "moderate significance" relate to 'resources whose contribution to
native biological diversity and productivity is limited to their local context and/or which
support the - functioning and integrity of adjacent areas of high significance. Such
resources are:
o Habitats that are key to the maintenance of localized plant and animal
populations but are not significant on a regional basis.
o Areas which act to buffer and protect resources of high significance.
o Corridors and zones which serve to link areas of high significance and facilitate
their ecological -interaction.
o Biological resources which are noteworthy for their educational and/or,
horticultural value.
Remaining. biological resources fall within areas of "low significance". The single
criterion for determining these resources is:
o Areas where biological resources have been removed or significantly altered
and/or none of the above criteria apply.
2. The Inventory Phase
This phase' consisted of reviewing all available information .on existing resources,
supplementing these with additional field investigations, and compiling this information
into a. preliminary data base.
The compilation of existing information was as complete as available information
permitted, including previous planning and environmental studies in and around the study
area, literature in scientific journals, natural resource surveys published by local
environmental management agencies, publications, on, rare and endangered species and
areas of special biological significance by State and Federal wildlife agencies and private
conservation groups, regional field guides and floras, papers and dissertations frorn local.
colleges and universities, and any other source available.. The -interpretation of aerial
photographs and consultation with biologists having a first-hand knowledge of the. study
area was also a part of this effort (4 thru 18 and Appendices B and Q.
7
Following compilation, the data was mapped,. in preliminary form, as accurately as the
scale of study allowed. _ Mapping categories were. defined by the evaluation criteria
themselves. For example, the habitats of rare, endangered and high interest species, the
distribution of common and uncommon biotic communities, and the locations of high
wildlife use areas were typical information mapped.
After the preliminary mapping was completed, the data base was verified, refined and/or
supplemented in the field. The extent to which this was. done depended upon the level of
detail needed for the study and -the coverage and level of detail of available information.
At a minimum, the veracity of the information was checked. This was the case for
example, where a previous- study of adequate detail had been completed and overlapped
or was adjacent to the area under study and included similar biological resources. At a
maximum, a complete biological inventory was generated, as in the case where little or no
information was available. Following these procedures, the entire study area was
examined, the results of which formed the resource base for use in the next phase.
3. The Interpretive Phase
Following the compilation of the data base, biological resources over the study area were
examined and interpreted with respect to the speck evaluation criteria.- Areas of high,
moderate and low sensitivity were identified in this manner which lent themselves to
being mapped in an overlay_ system with the baseline inventory. In this regard, this phase
combines the two preceding phases into a single product leading to the final plan - and
involved no new data gathering.
4. The Analysis Phase
The product of this- phase was an analysis,_ including maps and supporting data, of
biological resource areas possessing varying degrees of significance. Most commonly,
these areas took the form of polygons having natural features, such- as watershed
boundaries, riparian zones, the base of slopes, and lake- shorelines as their boundaries.
Occasionally, boundaries were defined by the presence of cultural features, such as a
dam, roadway, or urban edge. In no case, however, did boundaries intentionally conform
to political jurisdictions.
Each polygon essentially related the evaluation criteria to specific resource types, and by
their nature, to meaningful resource management units. Thus, adjacent resource areas, or
units, were often assigned the same level of sensitivity, yet were found to be distinct
because, they contained different types of resources and/or- they represented individual
management areas. As such, each management unit received specific treatment in the
• formulation of management considerations, tailored to the resources it contained.
H
•
IIL FINDINGS
A.' Biotic Communities
Biotic. communities are assemblages of plant and animal species'that are found in specific
physical habitats. They are ecological units containing a diverse group of organisms that
exist -together in an orderly predictable manner and have ' a very close and, complex set of
interrelationships. These communities are commonly identified and discussed with
reference to one or two dominant plant, species and the nature of the vegetation. For the
most .part, the community classification system used in this report follows that of
Cheatham and -Haller (19).
Eight major biotic communities exist within the- study area. These include freshwater
marsh, coastal sage scrub, introduced grassland, rural -agricultural, urban, chaparral,
riparian, and oak woodland (See Appendix E). 'In 1963, the California Department of
Fish and Game inventoried the natural communities of -the State (20).. Table A shows the
coverage and 'percent of total cover for the major community types within Orange
1k County. Undoubtedly, the distributions. of natural communities, have been reduced since
1963 by urban .and agricultural expansion. Today,. three of these communities, riparian,
oak woodland and marsh are highly restricted in their distribution.
Appendix E provides a discussion of the general ecology of the major biotic communities
found within the study area. Each community description includes information on the
significance, physiognomy, characteristic plant species, representative wildlife,
distribution, and. wildlife value, as well as brief descriptions of any sub -communities..
Although insects and other invertebrates are generally omitted from the discussion, they
play an important role in the ecology of each community by providing a vital link in food
chains. Because the definitions of .biotic communities are .largely based on vegetation
types, their - distribution follows the vegetation types mapped separately as, part of the
overall MEA effort (See MEA Map Atlas).
B: High Interest Species
Widespread habitat loss and degradation in Southern California is now indicated by the
relatively high number of rare; endangered, or protected, plant and animal species found
here. Numerous species which are known or are expected to occur within the study area
have been given special status. designations by Federal (21,22) and State agencies (23,14)
• and private organizations (25,26). The reader should note that those designations from
V]
0
TABLE A
TOTAL COUNTY COVERAGE AND. PERCENT OF COUNTY TOTAL
FOR MAJOR COMMUNITY TYPES FOUND WITHIN THE STUDY AREA, 1963
Percent of
Community Type
Coverage
County Total
Urban
169,719 acres.
34.0
Coastal Sage Scrub
103,280, acres
20.6 -
Rural -Agricultural
85,401 acres
17.0
Introduced Grassland
74,906 acres
.15.0
Chaparral
52,381 acres
10.5
Riparian
3,673 acres
0.7
Marsh'
2,150 acres
0.4
Oak Woodland
5,107 acres
10
Total
= 496,617 acres2
99.22
•
' Includes fresh and saltwater marshes.
2 The remaining 3,863 acres, or 0.8 percent of Orange County are represented by lakes,
bays and reservoirs, and'by coniferous forest.
10
private groups are advisory only and include: 1) bird species which are of special concern
to the National Audubon Society and have been "blue listed" due to recent or' current
declines in their population numbers; and 2) plant species- which are native and
considered "rare and endangered" by the California Native Plant Society. Table B lists
those plant and animal species which have received special status designations, and may
occur within -the study area. Additional information regarding the range, regional
distribution, and habitat requirements of these species may be obtained from the
aforementioned literature plus regional field guides and floras (27,28,29,30).
C. Areas of High Significance
Based on the evaluation criteria for determining biological resource significance, there are
fifteen areas of high biological significance within the study area. Each area has been .
assigned a number (code) as follows:
01.
Limestone Canyon
02.
Bee & Round Canyons
03. '
The Sinks
04.
Borrego Canyon
O5.
Santiago Canyon
06.
San Joaquin Freshwater Marsh
07.
Sand Canyon Wash
08. San Diego Creek
09.. Bonita Reservoir
10. Sand Canyon Reservoir
11. Sand Canyon Reservoir Rare Plant Habitat
12.
Shady Canyon Rare Plant Habitat
1.3.
Shady Canyon
14.
Bommer Canyon
21.
Laguna Reservoir
35.
Canada Geese Foraging Area
Each of these areas is described "in Appendix F, including the specific criteria each area
meets, a brief discussion of the resources each area contains, and an outline of appropriate
management considerations for each area.
Figure 2 delineates the areas of high significance. As shown, most of the areas are
entirely contained within the study area. "Some areas, however, extend outside of the.
study area. Although these areas were included in the County Master Environmental
• Assessment, and may overlap only a small portion of the study area, they are discussed in
this report due to the importance of a coordinated, regionwide resource management
strategy.
11
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Biotic
P®p-d• December 16, 1984
Updated: January 21.1986
Resources
0 2000 4000 6000 8000
Feet
Irvine Corporate Limits
"' Sphere of Influence
i
6
•
D. Areas of Moderate Significance
Based on the evaluation criteria, there -are nineteen areas of .moderate biological
significance. Each area has been assigned a number (code) as follows:
15. Limestone Canyon buffer
16. Bee & Round Canyon buffers
17. Aqua Chinon Wash
18. Borrego Canyon buffer
19. Rattlesnake Reservoir
20. Siphon Reservoir
21. Lambert Reservoir
22. San Diego Creek -_ Downstream Reach
23. Woodbridge Lakes
24. San Diego Creek buffer
25. San Diego Creek - Upstream Reach
26. Sand Canyon Wash buffer
28. Bonita Reservoir buffer
29. Sand Canyon Reservoir buffer
30. William R. Mason Regional Park Lakes
31. Shady and Bommer Canyon buffers
32. - Shady- Canyon tributary .
33. Eucalyptus windrows
34. Sand Canyon Oak trees
Each. of these areas is also described in Appendix F, and is also delineated in Figure 2.
Here again, some of the delineated areas extend outside of the study area and are
consistent with the County Master Environmental Assessment.
E. Areas of Low Significance
All remaining areas not delineated as either high significance .or- moderate significance,
are of low significance. No further discussion of these: resource areas is provided since
these areas do not contribute importantly to the continuance of biological diversity and
productivity; thus, they do not require management considerations.
20
•
IV: WHY PRESERVE BIOTIC DIVERSITY?
The underlying goal -of the evaluation criteria, is, to provide direction and guidelines for
preserving biotic diversity, as it exists today in. the county and the region. But why
preserve biotic diversity? What is its value? Why should it weigh in land use decisions?.
These are questions that are often asked by developers who must "satisfy a myriad of
environmental concerns before obtaining a building permit, by land owners who may be
asked to sell their land for a new park or natural area,, and by tax -payers who must pay the
bill.
Die-hard environmentalists often respond that man has a moral commitment. to preserve
these'resources; that- these resources have their own inherent right to survive, regardless of
their apparent degree -of usefulness to man. The belief that biotic resources should. be
preserved for their own sake has .been transformed into an official policy by the California.
State Legislature in the Fish and Game Code:
"The Legislature finds and declares ..... that' -it is the policy of this state......to
perpetuate all species of wildlife for their intrinsic and ecological values, as
well as for their direct benefits to man."
Although this argument has its merits, it is not convincing to most people who- mise
questions about biological significance. However, there are reasons for preserving
biological diversity that are based on ,current scientific evidence, and should be of utmost
concern to -the public and its representatives.
Biological diversity must be preserved to maintain natural ecosystems, many of which -are
of direct benefit to man. Natural vegetation slows runoff velocities during heavy storms,
preventing severe erosion problems and flooding. Slower moving water can infiltrate the
soil more easily, thus increasing groundwater recharge. This is a:direct economic benefit
of natural ecosystems. Another direct benefit is the production of -game and fish species.
In Orange County, hunting and fishing are primarily recreational activities, but they are
still pursued by thousands of County residents. Coastal wetlands are important links_ to
marine ecosystems. They act as natural filters, removing many pollutants before exiting
to the sea; These areas also serve as breeding grounds for the majority of marine fish that
are commercially harvested. Natural habitat adjacent to agricultural areas supports insects
thatpollinate crops and others that prey on crop pests. Riparian habitat supports hawks.
and owls that help control populations of rodents and rabbits, in and around agricultural
areas. Natural communities are also important in recycling nutrients, decomposing
21
0 . _
organic material, and maintaining and producing healthy top soils, all of which are
important to man. These are just a ,few of the direct benefits received from healthy
ecosystems.
The natural environment contains a plethora of -plant and animal species. Each one
possesses certain genetic and biochemical characteristics that .make it unique, and
therefore a potentially priceless resource. The unique features of each species are
available to be used by, man as his needs demand and his technology evolves. •These
qualities may someday be transformed into important chemical, medical, commercial,
industrial, and agricultural products or practices that could significantly benefit man.
An excellent example of this is the fungus Penicillium. Today it is common knowledge
that the antibiotic, penicillin, is produced by .this organism, and that it has saved millions
of lives as well as revolutionized the medical profession., When and where such an
important species may be found is absolutely impossible to predict.. It could be as rare as
the California condor or as common as the :housefly. It could be as yet undiscovered iri.
the heart of the Amazon rain forest, or found* world' -wide. It could even be the Orange
County turkish rugging, California least tern, Laguna Beach liveforever, or light-footed
clapper rail, all of which are found in Orange County,_ 'and are on rare or endangered
species lists. Research is going on throughout the world to uncover the secrets that plants
and animals possess, and to use this information to benefit mankind.
Along the. -same lines, there is a need to preserve biotic diversity for agricultural research.
It should be remembered that our entire food supply comes from plants and animals that
were once part of the natural world. We have taken these organisms_ and selectively bred
them for desirable features. As a result, we have produced crop strains that are highly
productive, disease resistant, and adapted to the rigors of the climates in which they grow.
To do this, man has continually had to go back_ to :nature and find, wild -growing strains
possessing traits .that could be used to produce .crops with higher yields. The ability to do
this has allowed our agricultural productivity to rise by ,continually remaining one step.
ahead of the pests and diseases that destroy crops, and by increasing efficiency of growth.
However, man has only been able to do this because wild strains _of old crops and
undiscovered new crops still exist in the wild. This would not be possible if areas did not
exist in their natural state. Since it is not possible to predict when, or where these species
will be found, the most prudent action is to preserve as much of the existing. biotic
diversity as possible. Whenever a species becomes extinct, a potential reservoir of
information is lost.
Another agricultural aspect of preserving diversity that has become increasingly important
• in recent years is biological control. Most of today's ecologists would agree that the
simpler an ecosystem, the more likely it is to be upset and undergo drastic rises and
22
declines in productivity. Agricultural fields are monocultures with little diversity. They
have traditionally been maintained by the application of insecticides and fungicides that
control pests and diseases. However, two important changes are taking place that are
gradually changing the situation. First, some pests and diseases are developing resistances
to chemical control which may eventually leave them ineffective and require that stronger,
toxins be developed. Second, it has been discovered that harmful insecticides and
fungicides accumulate in the food chain and have widespread effects. Biological control
can accomplish the same effects without the application'of these artificial substances. The .
technique involves the identification of'organisms that prey 'on the pest in question. The
predator can then be raised in captivity in large numbers and released into the field. The
method has been used successfully in the past, and shows great potential. However, the
scientist must be able to go into the wild and locate natural predators. If enough natural
areas do not exist, it might not be possible to find such a species, and the method cannot
be used.
A less dramatic but still important.- reason for preserving natural -areas ' is 'for their
recreational and aesthetic qualities. A large percentage of suburbanites exit the cities on
Weekends and vacations to escape into more natural surroundings. The fact that this use is
real and growing becomes obvious when one tries to get a campground in a state park or
finds out at a trailhead in the Sierra Nevada that the number of people in the backcountry
is regulated and a wilderness permit is required.
Perhaps the most important reason for attempting to preserve natural diversity is that man
exists as a part of the world-wide ecosystem. He is not a separate entity that functions on
an independent plane, but is a part of all the pathways, food. webs, and nutrient cycles of
the ecosphere. As such, he is dependent on them for his survival and should be concerned
that they remain intact. As urban and agricultural growth continues; species become
extinct, and areas of natural habitat are lost. The net result is that local, regional, and
world ecosystems become a little less complex and more likely to undergo fluctuations.
At some point in the future, too much habitat or too many species maybe lost, and the
pathways, webs, and cycles that support the ecosystem may collapse. Nobody can predict
what these levels are or when they might be reached. The way to prevent this possibility
is to preserve as much biotic diversity as possible.
From these arguments, it should be evident that there are important reasons for preserving
diversity that go beyond a moral commitment. Natural areas provide many direct and
indirect benefits to man. They provide a place to pursue recreational activities, and they
help maintain the balance of the ecosystem in which we all live. In addition, they serve as
outdoor classrooms where children from urban areas can be taught about their natural
• environment. In the future, these areas may serve as important ecological laboratories that
can be used by man to better understand the world around him. They can be used as
23
s
•
environmental monitoring stations to detect the impacts that man is having on his
environment, and may even serve as models for man-made ecosystems if population
growth and resulting expansion should upset critical environmental forces. Which
communities and which species have the potential to provide us with valuable information
cannot be predicted. This is often used as an excuse to avoid the- question of preserving
diversity by those who do not understand its values. Instead, it should be the grounds for
a policy of attempting to preserve as much diversity as possible.
Every habitat thavis destroyed and every species that is lost is information that cannot be
regained. This is part of the reason for concern -over the fate of rare and endangered
species. _ In order to see the need for preserving species and communities, regardless of
-their currently recognized value, we should ask ourselves these, questions. Would it have
been possible to foresee the future value of the common bread mold, Penicillium, sixty
years. ago? Without knowing this, would it have been possible to save it if it had been a
rare or endangered species? Can we predict the potential value of any species or
ecosystem? And finally, shouldn't biotic diversity be preserved? Whetherthe final
answer is based on moral commitment, scientific interest, ecological principles; or sound
economic sense, the answer�is yes.
24
V. REFERENCES AND PERSONS CONSULTED
References
1. Edaw, Inc. 1981. County of Orange Master Environmental Assessment Phase.I -
Constraints Mapping 'and Analysis. County of Orange, EMA, Santa Ana, CA.
2. England and Nelson. 1976. Los Angeles County _Significant Ecological Area
Study, Land Capability/Suitability Analysis, Vol. III, Los Angeles County Dept.
Regional Planning, Los Angeles, CA.
3. Eagles, P.F., J. 1981. "Environmentally ' Sensitive Area Planning in Ontario,
Canada', Journal of the American Planning Association, No. 47, pp 313-323:
4. California Department of Fish and Game, 1985. Letter dated February 15, 1985
from Mr. Fred A Worthley regarding biological resources within the Irvine
planning area.
.5. England and Nelson, 1976. Coyote Canyon Sanitary Landfill Replacement Site
Biologist's Report. - Prepared for the Orange County Environmental Management
Agency.. - Prepared for the County of Orange, Environmental Management
Agency.
6. England and Nelson, 1976. Peters's Canyon Reservoir Regional Park Bound=
Study Biological Assessment. Prepared for the Orange County Environmental
Management Agency. Prepared for the County of Orange, Environmental
Management Agency,
7. Jones and Stokes, 1975.' Irvine .Coastal Project Area Wildlife Habitat and
Corridors System,. Vegetation/Wildlife Habitat. Prepared for the County of
Orange, Environmental Management Agency.
8. Jones and Stokes, 1975. Irvine Coastal Project Area: Vegetation/Wildlife Habitat
Maps. Prepared for the County of Orange, Environmental Management Agency..
9. Jones and Stokes, 1974. Preliminary Biological Inventory and, Management
Recommendations, Irvine Coastal Project .Area. Prepared for the County of
Orange, Environmental Management Agency.
25
0
b
•
10. Phillips Brandt Reddick Inc., 1979. -Trabuco Unit Specific Plan. Biological
Assessment. Prepared for the County of Orange, Environmental Management
Agency.
11. Marsh; Gordon, 1973. Wildlife and Habitat Inventory Irvine General Planning
Program. Prepared for the City of Irvine.
12. .Larry Seeman Associates and Phillips Brandt Reddick, 1979, Master
Environmental Assessment for the Irvine Ranch Water District. Prepared for .the
Irvine Ranch Water District.
13. Phillips Brant Reddick, 1979. Conrock-Trabuco Resources Biological
Assessment. Prepared for the County of Orange, Environmental' Management
Agency.
14. Phillips Brant Reddick, 1980. Biological Resources of the Foothill Transportation
Corridor. Prepared for the County of Orange, Environmental Management
Agency.
15. EDAW Inc:, 1982. Foothill 'Corridor Biological Assessment. Prepared for the -
County ,of Orange, Environmental Management Agency.
16. EDAW Inc., 1982. Irvine Coast Planning Unit Development and Dedication Plan
Biological, Assessment. Prepared for the County of Orange; Environmental
Management Agency.
17. EDAW Inc., 1982. Bommer and Shady Canyons General Plan Amendment
Biological Assessment. Prepared for the Irvine Company.
18. Community Planning Services, 1985. Environmental Documents Index. Irvine
Master Environmental Assessment. Prepared for the City of Irvine.
19. Cheatham, N.A. and J.R. Haller. 1976. "An Annotated List of California Habitat
Types." Unpublished
20. California Department of Fish -and Game, 1966. California Fish and Wildlife Plan
3 Vol., Sacramento, CA.
26
21. -U.S. Department of the Interior, Fish and Wildlife Service. 1976. Code of Federal
Regulations, Title 50 Wildlife and Fisheries, Washington, D.C.
22. U.S. Department of the Interior, Fish and Wildlife Service. 1973. Threatened -
Wildlife of the United States. Washington, D.C-.
23. California Department of Fish and Game, 1977. Status Designations of California -
Animals. Sacramento, California.
24. California Department of Fish and Game. 1980. At The Crossroads: -A Report on
California's Endangered and Rare Fish and Wildlife. Sacramento, CA.
25. Smith, J:P.; Jr., and York, R., 1984. InvenIM of Rare and Endangered Vascular
Plants -of -California. California Native Plant Society, Spec. Publ. No..1. Berkeley,
CA.
26. Arbib, R. 1-980. "The Blue List for 1981". American -Birds.
27. Stebbins, R.C. 1966. A Field Guide to Western Reptiles and Amphibians.
Houghton Mifflin Co., Boston, MA.
28. Burt, W.H. and R.P. Grossenheider: 1976. A Field Guide- to- the Mammals. -
Houghton Mifflin Co., Boston, MA.
2-9. -Peterson, R.T. 1941. A Field Guide to Western Birds. Houghton Mifflin Co.,
Boston, MA.
30. Munz, P. 1974. A Flora of Southern California. Univ. of Calif. Press, Berkeley,
CA.
Persons Consulted
The following people are credited with having provided information and ideas which
contributed to the preparation of this report.
1. Mr. Jack Fancher, U.S. Fish and Wildlife Service
2. Mr. Steve Kimple, California Department of Fish and Game
27
i
3. Mr. Carl Wilcox, California Department of Fish and Game
4. Mr. Eric Jessen, County of Orange Environmental Management Agency
5. Mr. Pete Bloom, Raptor Biologist
6.- Ms. Karlin Marsh, Biologist
28
APPENDIX A
APPLICABLE LAWS AND PLANNING POLICIES
Federal Endangered Species Preservation -Act of 1966
This act -gave authority to the Secretary of the Interior to. declare as, endangered those
wildlife species which are native to the United States and are ,threatened with extinction.
Federal Endangered Species Act of 1913
This act strengthened many of the provisions - set forth in the Endangered Species
Preservation Act of 1966. Administered by ,the United States Fish- and Wildlife Service,
this legislation charges all Federal agencies with the direct responsibility for ensuring that
actions authorized, funded, or carried out by them do not either,jeopardize the continued
-existence of Endangered or Threatened -Species, or, result in the destruction or adverse
modification of the habitats of Endangered or Threatened Species. State, local, and
private: actions that do not involve Federal funding or approval do not fall under the .terms
of this act.
Should the City of Irvine become involved in an action coming under the terms of this act,
the" action must involve consultation with .the United States Fish and Wildlife Service
pursuant to the ,Interagency Cooperation Regulations set forth in the act. Briefly defined,
consultation involves examination of -the action to determine whether or not it will
jeopardize the species or its "critical habitat". Once this determination has been, made,
modifications to the action may be required to receive Federal monies and/or -approval.
The greatest likelihood of this occurring, exists- within the San Joaquin Marsh. where
Federally funded or approved actions may jeopardize light-footed clapper rail, _California
brown pelican and California least tern populations. The, possibility also exists within
potential habitat for Laguna Beach live -forever, many -stemmed live -forever, and salt
marsh bird's beak, where undiscovered populations of these plants- may exist within the
study area. No other Federally recognized Endangered or Threatened Species are known
or are expected to occur within the study area.
Listings of Endangered and Threatened .Species of plants and animals are revised and
amended at irregular intervals in the Federal Register. The most current listings may be
obtained from the Federal Office of Endangered Species.
A - 1
Other Federal Species Designations
tions
Since 1965, . several reference documents regarding Endangered and Threatened Species
have been published by the Department of the Interior. These publications contain .
information on native wildlife species that -are either Endangered or are- candidates for
Endangered Species status. Categories used in these documents include "threatened";
"peripheral", and "status undetermined". These are not official status designations and are
used only for reference purposes as a means to stimulate interest, impart knowledge, and
solicit data about species of special concern which may be used to -compile the official list.
Also, Federal protection is given to migratory birds through the Migratory Bird Treaty
Act, as amended; to bald and golden eagles through the Bald Eagle Act, as amended; and
to marine mammals through the Marine Mammal. Protection Act. Basically, these acts
make it unlawful to "take" or possess any species afforded such protection. It is highly
.doubtful that actions undertaken by the City should constitute a taking or possession of
such species. Additionally, there are no provisions for habitat protection under these acts.
Federal Wetlands Protection Policies
The Federal Water Pollution Control Act, P.L. 92=500, and the Clean Water Act, P.L. 95-
217, and specifically Section 404, regulate the: discharge of any pollutant or the discharge
of dredged or fill material into all waters of the United -States including adjacent wetlands.
The Section 10 permit program of the River and Harbor Act of 1899 authorizes works or
structures in navigable waters. The Section 10 and 404 permit programs are administered
by the Corps of Engineers in consultation with the U.S. Fish and Wildlife Service. In
essence, the' discharge of dredged material, the placement of fill and structures, or the
conduct of activities that could impact or obstruct the navigable capacity of a waterway or
alter its chemical, physical and biological integrity is prohibited unless permitted by the
Corps of Engineers..
On May 24, 1977, Executive Orders 11988, Flood Plain Management, aiid' 11990,
Protection of Wetlands, were issued. These orders directed all Federal agencies to avoid,
to the extent possible, all actions associated with the modification or destruction of
floodplains and wetlands, or actions that may, increase the risk of loss of life or property,
resulting from flood or storm damage. This protection effort was necessary because
man's continued alteration of, and ,presence within, floodplains has resulted in property
damages in excess of 3 billion dollars annually. Disaster relief and rehabilitation often
exceeded I billion dollars annually. These damages continue to occur despite substantial
expenditures for structural flood control measures.
. Federal wetlands protection policies would apply to actions undertaken within the San
Joaquin Marsh and San Diego Creek inland to the area around the Laguna Freeway.
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California Species Preservation Act of 1970
Prior to the enactment of this bill, California law had fully protected a limited number of
birds and mammals. Such- protection was granted only through legislative approval and
included unique or attractive species which were not necessarily threatened with
extinction. This act provided that the California Department of Fish and Game shall
prepare biennial inventories and reports on the status of the State's threatened birds,
mammals, reptiles, amphibians, and fishes, and establish criteria for the classification, of
these -species as Rare or Endangered. The act also revised the list of fully protected birds
and mammals and added fully protected fishes, amphibians and reptiles. Under this law,
no such designated species or parts thereof may- be taken, possessed, or sold within the
State of California without authorization by the California Fish and Game Commission
and/or the Department of Fish and Game. There is no provision for the preservation of the
habitat of these species under this act. As a result, the City of Irvine is not likely to fall
under the provisions of this -law..
California Endangered Species- Act of 1970
This act defines Rare and Endangered Species and gives the Fish and Game Commission
the authority to declare which species fall into these categories. - The law prohibits the
taking, possession, or selling of any bird, mammal, fish, amphibian .or reptile, or -parts
thereof, that the Commission determines to be Rare or Endangered. Many of these had
already received. protection under the California Species- Preservation Act. The act has
recently been amended to include plant species, and .an Endangered P1ant.Program was
recently initiated.
Unlike the Federal Endangered Species Act, the California law does not currently include
consideration for the habitat of Rare or Endangered Species. However, the only species
designated by the State that is not also found on the Federal list is the Belding's savannah
sparrow, which occurs at the San Joaquin Marsh.
Other California Fish and Wildlife Protection and Conservation Laws,
Under the provisions of the State Fish and Game Code, Chapter 6, Sections 1601 and
1.603, actions which may alter streariibeds or lakes from which fish and wildlife resources
derive benefit requires the review and approval of the Department of Fish and Game.
Briefly, the process involves submitting plans indicating the nature of a project to the
Department. These are submitted .as 1601 or 1603 permit applications. Normally, within
thirty days the Department will return the plans with a proposal for reasonable
modifications in the project which would allow for the protection and continuance of fish
• and wildlife resources. Within fourteen days of receipt of the Department's proposal, the
affected party notifies the Department as to the proposal's acceptability; if unacceptable,
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-arbitration is necessary. All major drainages, generally defined as a. "blue 'line" on
U.S.G.S. 7 1/2 minute quad sheets, within the study area fall under the provisions of this
chapter.
California Coastal Act
Sections 30230, 30231 and 30236 of this act requires that marine resources be preserved
and restored; that special protection be given to areas of special_ biological .significance;
and that the quality of coastal water be maintained for the protection of -human health.
This act also requires the control of runoff,. the prevention of ground water depletion, the
prevention of interference with surface flow, the encouragement of waste water
reclamation, and the maintenance of riparian buffers along drainages and mitigation when
natural drainages are significantly altered.
Additionally, Section 30240 .of the Coastal Act requires -that sensitive habitat areas be
protected against 'significant disruption and that projects .in adjacent areas be designed to
prevent the degradation of these habitats. All portions of the coastal area falling within
the jurisdiction of the California Coastal Zone Conservation Cominission are subject to
these policies:
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APPENDIX B
SOURCES REVIEWED FOR ASSESSMENT CRITERIA
1976 LOS ANGELES COUNTY SIGNIFICANT ECOLOGICAL AREA STUDY
American Association for the Advancement of Science. 1963.. Natural Areas as Research
Facilities. American Association for the Advancement of Science,_ Wash:, D.C.
Anonymous., 1.975. Code of Federal Regulations - Title 43 - Public Lands:. Interior. U.S.
Government Printing Office, Wash., D.C.
Association of Bay Area Governments..1975. Areas .of Critical Environmental Concern.
Association of Bay Area Governments, Berkeley, Ca. 83pp.
Bartholomew, G.A., T.R. Howell, J.G. Morin, M.E. Mathias, and H.J. Thompson. 1972.
Statement to -the Los Angeles County Regional Planning Commission on
Preservation of Natural Areas. Los Angeles County Regional Planning
Commission. 4pp.
Bury, R.B. 1975..Conservation of Non -Game Wildlife in California: A Modef
Programme. Biol. Conserv. 7:199-210.
California Coastal Zone Conservation Commission. 1974. The Coastal Land
Environment. Calif. Coastal Zone Conserv. Comm., -Long Beach, -Ca.
California Coastal Zone Conservation Commission. 1974. The Marine Environment.
Calif. Coastal Zone Conserv. Comm., Long Beach, Ca.
California Department of Fish and Game. 1974. Supplement toFish and Game Code.
Calif. Dept. General Services, Documents Section, Sacramento, Ca. 53pp.
California Department of Fish and Game. 1973. -Fish and Game Code. Calif, Dept.
General Services, Documents Section, Sacramento; Ca. 239pp.
California Department of Fish and Game. 1966. California Fish and Wildlife Plan. Calif..
Dept. Fish and Game, Sacramento, Ca. 3 vols.
California Governor's Office of Planning and Research. 1974. Maps and Publications for
Areas of Potential Environmental Critical Concern. Calif. Governor's Office of
Planning and Research. Sacramento, Ca.
California Natural Areas Coordinating Council. 1975. Inventory of California Natural
9 Areas. Calif. Natural Areas Coordinating Council.
B - 1
California Water Resources Control Board. 1974. Resolution No. 74-28. Designating
Areas of Special Biolo ig cal Significance ,ABAS). Calif. Water Resources Control
Board.
Center for Geographic Analysis, Institute for Environmental Studies. 1975. Data Needs
and Data Gathering for Areas of Critical Environmental Concern. Univ. of
Wisconsin, Madison, Wis. EIS Rep. Nos. 53-55.
Center for Natural Areas. 1975. A Conservation and Recreation Plan for Santa Catalina
Island. Center for Natural Areas, Wash., D.C. 71pp.
Duncan, Jones, Ribera, and Sue. - 1972. Parks, Recreation, and Open Space Plan, Santa
Cruz County, California. Santa Cruz Co. Planning- Department.' Santa Cruz, Ca.
Gehlbach, F.R.. 1975. Investigation, Evaluation, and Priority Ranking of Natural Areas.
Biol. Conserv. 8:79-88.
Goldsmith, F.B. 1975 The Evaluation of Ecological Resources in the Countryside for
Conservation.Purposes. Biol Conserv. 8:89-96.
Kunit, E.R., and K.S. Calhoon. 1973. Landscape Preservation Study for the- Southwest_
Mountain and Valley Province. Calif Dept. Parks and Rec. 69pp.
Kunit, E.R., and K.S. Calhoon. 1973. Landscape Preservation StudyAppendix: The
Southwest Mountain and Valley Province. Calif. Dept. Parks and Rec. 154pp.
Los Angeles County Department of Regional Planning. 1976., Conservation Element:
Statement of Needs Opportunities, and Goals. L.A. Co. Dept. of Regional
Planning.
Los Angeles Department of Regional Planning. 1975. La Habra Heights- Community
General Plan and EIR. L.A. Co. Dept. of Regional Planning.
Los Angeles County Department of Regional Planning. 1975. Preliminary Draft; -
Conservation Element, Los Angeles County General Plan. L.A. Co. Dept. of
Regional Planning. 57pp.
Los Angeles County Department of Regional Planning. 1965. The Malibu Area. L.A.
Co. Dept. of Regional Planning. 57pp:
Los Angeles County Environmental Resource Committee. 1,973. Interim Report on the
Status of Natural Areas in Los Angeles Countv, and Recommendations for Their
Conservation. Los Angeles County Dept. of Regional Planning. 5pp.
Los Angeles County Environmental Resource Committee., 1973. Rare, Endan eg red,
Depleted, and/or Protected Vertebrates Occurring in Los Angeles County.. Los
• Angeles County Dept. of Regioynal Planning. 7pp.
B-2
Los Angeles County Environmental Resource Committee. 1973. (Significant Ecological
Areas -Final Report.) Los Angeles County Dept. of Regional Planning.
Los Angeles County Nature Unit. 1974. Flora and Fauna of Devil's Punchbowl County
Park, Los A aeles Co., _Calif. Whittier Narrows Nature Center. El Monte, .Ca.
Los Angeles Department of City Planning. 1973. Open Space Plan. City of Los Angeles.
L.A. Ca.
Los Angeles Department of City Planning. 1973. Proposed Conservation Plan. City of
Los Angeles. L.A. Ca.
Los Angeles Regional Planning Commission-. 1973.. Los Angeles County General Plan
Conservation Element Technical Report. L.A. Co. Regional Planning
Commission.
Marin County Planning Department. 1973. Countywide Plan--Marin County. Marin Co.
Planning Dept. San Rafael, Ca. 144pp.
Marin. County Planning Department. 1971. Can the Last Place Last?-- Preserving the
Environmental Quality ofMarin. Marin County Planning Department, San Rafael,
Ca. 144pp.
National Forest Service; Land Use Planning Group. 1976.' Land Use. Planning- in the _
California Re ion. U.S. Forest Service. S'aii Francisco, Ca.
National Forest Service, Land use Planning Group. 1976. Synopsis of Formal
Classification Action_ s and Listing of Designated Areas. U.S; Forest Service. San
Francisco, Ca.
National Forest Service. 1973. New Wilderness Study Areas - Roadless Area Review
and Evaluation. U.S. Forest Service, CI. Report No. '11. 21pp.
National Park Service. 1975. Management Policies. National Park Service. 16pp,
Nature Conservancy, The. 1975. The Preservation of Natural Diversity A Survey and
Recommendations. The Nature Conservancy, San Francisco; Ca. 212pp.
Office of Land Use and Water Planning and United States Geological Survey, Resource
and Land Investigations Program. 1975. Critical Areas: A Guidebook .for
Development of State Programs. U.S.D':I., Wash., D.C.
Quinton-Redgate. 1975. North Los Angeles County General Plan. Los Angeles County
Planning Commission,
Santa Clara County. 1973. A Plan for the Conservation of,Resources : An Element of the
General Plan of Santa Clara -County. Santa Clara County Planning Commission.
49pp.
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Santa Barbara County. 1974. Santa Barbara County Comprehensive Plan: Conservation
Element. Santa Barbara County Planning Department.
Stanislaus Area Association of Governments. 1974. Wildlife and Vegetation:
Environmental Resources Mana eg ment, Element. Stanislaus .Area Association of
Governments, Modesto, Calif.
Tans, W. 1974. Priority Ranking of Biotic Natural Areas. Michigan Botanist 13: 31-9.
Thorne, R.F. 1972. Priorities - San Gabriel Mountains. Los Angeles County Dept.:of
Regional Planning.
United States Department of Agriculture. 1973. The National Forests, National Forest
Wilderness and Primitive Areas. U.S. Forest.Service, San Francisco, Ca: FS-25.
United States Department of Agriculture and United,States Department of the Interior.
1970. Guidelines for Evaluating Wild. Scenic, and Recreational River Areas
Proposed for Inclusion in the National Wild and Scenic Rivers System Under
Section 2. Public Law 90-542. U.S. Government.Printing Office. 12pp.
B-4
APPENDIX C
INDIVIDUALS OR GROUPS THAT EITHER RECEIVED. A SIGNIFICANT
ECOLOGICAL AREA. NOMINATING FORM OR WERE INTERVIEWED
1976 LOS ANGELES COUNTY SIGNIFICANT ECOLOGICAL AREA STUDY
PREPARED BY ENGLAND & NELSON
Legend
x = Response received
ERC = Los Angeles County Environmental Resources Committee Member
RAC = U.C.L.A. Resources Advisory Committee Member
Government Agencies
x Association of Bay Area Governments
x Chris Hartzel - Planner
x Bureau of Land Management
Bakersfield District
x Terril King - Chief of Resource Management
Desert Planning Staff
x Robert Badaracco - Outdoor Recreation -Planner
x Kristin Berry - Wildlife Biologist
Hyrum Johnson - Plant Ecologist
Riverside District
x Allen Cooperrider - Wildlife Biologist
x Mark Dimmitt - Animal Ecologist
x John Hall - Botanist
x Bureau of Outdoor Recreation
x Ray Murry - Planner
x California Coastal Zone Conservation Commission
South Coast Regional Commission
x Margot Feuer
x Dave Smith
x Gregg Van Orman
x California -Department of Fish and Game
Region 5 Office, Long Beach
x Peter Gelfand - Wildlife Supervisor of L-A: County
x Chuck Hooker - Marine Biologist
x Earl Lauppe - Wildlife Biologist
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• Rolf Mall - Environmental Sciences Manager
for Marine Resources
x Charles Marshall - Fisheries Biologist
x Peter Phillips Marine Biologist
x Gary Stacey - Wildlife Biologist
x Jim St. Amant - Region 5 Fisheries Supervisor
x California Department of Parks and Recreation
x Alan Kolster - Associate Landscape Architect
x La Verne, City of
x Ruth Hogan - City Clerk
x Los Angeles County Department of Beaches
Joe Chesler - L.A. Co: Beach Advisory Council Member
x Dick Fitzgerald - Director
Paul Pettite
Los Angeles County Department of Parks and Recreation
Seymour Greben - Director
-x Whittier Narrows Nature Center
x Dean Harvey - ERC
Los Angeles Department of Environmental_Quality -
Roger Fontes _
x Los Angeles County Museum of Natural. History
x Charles Hogue - ERC
x Lan Lester - ERC
x Camm Swift - ERC
x Marin County Planning Department
x Kathleen Ohlson - Environmental Planner
x National Forest Service
Angeles National Forest
x Margie Brayton - Wildlife Biologist
California Region
x Charles Joy - Land Classification Specialist
x National Park Service
x Nicholas Weeks - Landscape Architect
x Santa Clara County Planning Department
x Don Weden - Associate Planner
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x Santa Cruz Countyu Planning Department
x Dennis Pisila - Planner
x-Stanislaus Area Association of Governments
x Greg. Steel - Area Coordinator
x U.S. Fish and Wildlife Service
California Condor Recovery Team
k Sanford Wilber
Academic Institutions
x Antelope Valley College
x Gail Newkirk - Biologist
x Biola College
x Raphael Payne - Chairman, Biology Department
Cabrillo Marine Museum
Suzanne Miller - Marine Biologist
California Institute of Technology
Wheeler. North - Marine Biologist, Kelp
Habitat Restoration Project
RoberfSinsheimer - Chairman, Division of Biology,
California, Lutheran College
Curtis Nelson = Chairman, Biological Sciences
Department
x California State College, D6minguez1iills
x Gregory Smith - Marine Biologist
x California State Polytechnic University, Pomona
Jonathan Baskin - Icthyologist
Ken Brown - Vertebrate Ecologist
Timothy Brown - Biologist
Gilbert Brum - Botanist
x Peter Castro - Marine Biologist
Marion Harthill - Plant Ecologist
Harold Lint - Field Ecologist
x Edward Mercer - Freshwater Biologist -
Ronald Quinn Zoologist
x Glenn Stewart - Zoologist, ERC
• Martin Stoner - Mycologist, Plant -Pathologist
Laszlo Szijj - Ornithologist
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California State University, Fullerton
Michael Horn - Marine Biologist
Gene Jones - Botanist
x California State University, Long Beach
Philip Baker - Botanist
x Charles Collins Ornithologist.
Charles Galt - Marine Biologist.
David Huckaby. - Mammalogist
Richard Loomis - Herpetologist
Greayer Mansfield --Jones - Plant Ecologist
Alan Miller - Biologist
Dennis Rainey = Biologist
Donald Reish - Biologist
Donald Shipley - Biologist
Stuart Warter - Ornithologist
William Wellhouse = Biologist
California State University, Los Angeles
Dudley Thomas - Chairman, Biology Department .
Richard Vogl - Botanist
California State.University, Northridge
Andrew Starrett - ERC Chairman
Cerritos College
Louis Wilson - Chairman, Science, Engineering
Mathematics Division
Chaffey College
. . . Richard Becks - Chairman, Division of Life Sciences
x Chapman College
x Cheng--Mei Fradkin. - Biologist
Claremont Men's College
Clyde Eriksen - Biologist
Robert Feldmeth - Biologist
College of the Canyons
James Boykin - Biologist
Donald Takeda - Biologist
Compton Community College
0 Frisby Lockard
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0 Cypress College
Bob Vandergrift
East Los Angeles College
George Wistreich.
x El Camino College
x Carl Meadows - Dean, Division of Natural Sciences
R.C. Stephens - Zoologist
Glendale Community College
James Bouey
Golden West College
Norman Rich - Division of Mathematics and Sciences
x La Verne College
Harvey Good - Biologist
x Sheridan Merritt - Zoologist
Robert Neher - Chairman, Division of Natural
Sciences and Mathematics
Long Beach City College
Barbara Kalbus'- Chairman, Division of Mathematics and Sciences
x Los Angeles City College
Gerhard Bakker- Biologist
x Barbara Joe Hoshizaki - Botanist
Robert Lyon - Chairman, Department of Life Sciences
x Los Angeles Harbor College
x Arnold Small - Zoologist
Herbert Thomas - Botanist
x Los Angeles Pierce College
x Barbara Hopper - Biologist
Los Angeles Southwest College
Biology Department Chairman
x Los Angeles Valley College
x David Dixon - Chairman, Department of Biological Sciences
Mount San Antonio College
J. Robert Thomas - Chairperson, Department of Biological Sciences
x Occidental College
Louis Baptista - Biologist
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William Hand = Biologist
x John Stephens Jr. - Icthyologist
Robert Stockhouse Il - Biologist
Pasadena City College
John Babel - Chairman, Department of Life Sciences,
Pepperdine University
Chairman, Department of.Natural Sciences and Mathematics
x Pomona College
Thomas Mulroy - Botanist
x Larry, Oglesby - Zoologist
Edwin Phillips.- Chairman, Botany Department
William Wirtz - Zoologist
Rancho Santa Ana Botanic Gardent
. Robert Thorne - Herbarium Curator
x Rio Hondo College
John Hole - Biologist
Don Jenkins - Chairman, Biology'Department.
x Ray Williams - Biologist
San Bernardino County Museum
Gene Cardiff - Curator
x Santa Monica College
x Jeremy Ward - Chairman, Department of Life Sciences
x State Extension Services
Maynard Cummings - Unit Coordinator, Wildlife
and Marine Resources Extension,'and State-
wide Coordinator Sea Grant Advisory Programs
x Christopher Dewees - Marine Resources Specialist
Robert Laacke - Extension Forester
Lewis Nelson - Wildlife Specialist
Jerome Siebert - Associate Director Cooperative
Extension
Dale Wade - Wildlife Specialist
University of California, Berkeley
Robert Stebbins - Herpetologist
University of California, Irvine
Gordon Marsh - Museum of Systematic -Biology
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x University of California, Los Angeles
x George Bartholomew - Zoologist, RAC
x Glen Egstrom - Marine Biologist
x Thomas Howell - Zoologist, RAC
x Mildred Mathias - Botanist, RAC
x'Norman Miller - Biologist
x Henry Thompson - Botanist, RAC
x David Verity - Museum Scientist
x University of California, Riverside
x Oscar Clarke - Herbarium Director
x Wilber Mayhew - Zoologist,
Rodolfo Ruibal - Herpetologist
x Frank Vasek - Botanist
x University_ of Redlands
Lowell Smith - Chairman, Biology Department
x Robert Wright - Biologist-
x University of Southern California
x Susan Anderson - Marine Recreation -Specialist
Gilbert Jones - Zoologist
Louis Wheeler - Botanist
x Southern California Academy of Sciences
x Dick Frizsen
x Roberta Greenwood
Conservation Groups
American Cetacean Society
Bill Samaras - President
x Audobon Society
Conejo Valley Chapter
x Jessie Smith - President
El Dorado Chapter
Barbara Massey
.Los Angeles Chapter
x Barry Clark - Editor, "Western Tanager"
Jerry Maisel - President
Pasadena Chapter
Arden Brame Jr.
Michael Long - Conservation Chairman
Pomona Valley Chapter
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x Larry Oglesby - President
San Fernando Valley Chapter
Judy Howard
Robert,Smith
Santa Monica Chapter
x Pamela Axelson - President
Sea and Sage Chapter
Margaret Carlberg
Whittier Chapter
x Norma Allen
x J.H. Comby
H.R. Gable
x California Association of Resource Conservation Districts'
Alex Adams - President
x Lorin Trubschenck - First Vice President
California Conservation Council
J.B. Atkisson - Executive Secretary
Edward Doldet - President
William Wake - Vice President
Californians for Environmental Quality
Conservation Director
x California Forest Protection Association
x John Callaghan : Executive Vice President
x Fred Landenberger - Assistant Manager, Land Use and Environment
x California Native Plant Society
Sier-ra--Santa Monica Chapter
x Grace Heintz - President.
Southern California Botanist Chapter
x June Latting - Past President
Jim Shevock Treasurer
V. Walton. Wright - President
x California Natural Areas Coordinating Council
x Leslie Hood - Executive Director
x California Tomorrow - Southern California Office
x Richard Grant Jr. - Director
California Trout Incorporated ' '
Richard May - President
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x California Wildlife Federation
x Sam Baker - President
Center for Natural Areas
Stephen Keiley - Chairman of the Board and President
Council for Planning and Conservation
Ellen Harris - President and Executive Secretary
x Desert Bighorn Council
x Bonnar Blong - Chairman
x Desert Fishes Council
x Edwin Pister, - Secretary --Treasurer
x Desert Protective Council, Incorporated, The
x Norwood Hazard - Vice President
x Jane Pinheiro - High Desert Chairman
Dean Slaughter - Secretary
Glenn Vargas - President
x Ecology Center of Southern California
x Nancy Pearlman - Executive Director
x Environmental- Policy Committee
x Roberta Greenwood - Chairman -
Friends of Charmlee Park
John Hollinrake - President
Friends of Griffith Park
Conservation Chairman
Friends of the Earth
Conservation Chairman
Friends of the Santa Monica Mountains and Seashore
Conservation Chairman
x Great Western Boy Scouts
x Bob Hawkins - Director of Camps
High Desert Environmental Defense Fund
Charles Bell - President
Izaak Walton League of America, Incorporated
Art Harvey - President, California Division
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x Jenner Ecological Foundation
x Mrs. William Jenner
x Las Virgenes Resource Conservation District
x Helen Funkhouser
Los Allsos Beach Association
Michael Palecki
x Los Angeles County Beach Advisory Committee
x Ken Kvammen
x Dorothy Leconte
x Ann Shaw '
Malibu Citizens for Good Community Planning
Mrs. Elmer Callen Jr.
National Waterfowl Council Pack Flyway
John McKean - Chairman
x Nature Conservancy, The
State Office
x Peter Seligman - Staff Biologist
Southern California Chapter
Frank Boren - Chairman
x Fred, Botine
National Wildlife Federation
Western Region
William Reavley - Executive Director
North Valley Ecology Council
Conservation Chairman
Ocean Fish Protective Association, Incorporated
Conservation Chairman
Planning and Conservation League
'David Hirsch - President
x Resource Conservation Districts -- Los Angeles
x Joy Picus
x Santa Susana Mountain Park Association
x Jan Hinkston - President
x Save Malibu Canyon Committee
x Mrs. Warren Cappel
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0 Save Our Coastline
Mirian Murphy,- Secretary
Save the Oaks
Conservation Chairman
x Sierra Club
Los Angeles Chapter
x Doug & Naomi Farr - Co -Chairman; _Conservation Committee
Conservation Chairman - High Desert Angeles Group
Conservation Chairman - SanTernando Valley Group
Southern California Regional Conservation Committee
Ted Trzyna - Chairman
Small Wilderness Area Preservation
Emily Polk - President
Paul Lippe - Ballona Creek Section
Conservation Chairman - Glendale Section
x Southern.California Camping Association
x Grant Gerson
Southern Council of Conservation Clubs
M. Doornbos = President
Tarzana Property Owners Association, Incorporated
Recreation and Parks Chairman
Theodore Payne Foundation for Wildflowers
Conservation Chairman
Topanga--Las Virgenes Resource Conservation District
Robert Mann
x Topanga State Park Citizen- Advisory Committee
x Harvey Anderson
Western Bird Banding Association
Michael San Miguel - President
Shirley Wells - First Vice President
Wildlife Society
Conservation Chairman, Southern California Chapter
0
Individuals
x Pete Bloom - RaP for Bander
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x David Brown
x Rimmon Fay - Marine Biologist
x Susan Nelson
G.S. Suffel - Ornithologist
x Tim Thomas
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APPENDIX D
EVALUATION CRITERIA
High Significance .
The criteria and.rationale defining High Significance relate to resources that are generally
limited in distribution and whose contribution to biological diversity,and/or.productivity, is
critical within their regional context. In most cases, the term regional will refer to an area
the size of a county, geographical subregion, national forest, or- larger. The criteria for
High Significance are:
o The habitat of State and Federally sanctioned Rare, Endangered and Threatened
plant and animal species._ ;
These areas are important to the preservation of plant and animal species that -are
recognized as being either extremely low in numbers or having a very, limited
amount of habitat available. The terms Rare, Endangered and Threatened have
precise meanings defined in .both state and federal law. These areas would include
the "critical" or "essentiaP_ habitat' -for such a species where this designation has
been made, as well as areas which, have not been designated as such but are used
by these species as an important part of their habitat.
o Biotic communities, vegetative associations and habitats of plant and animal
Mecies that are highly restricted in distribution on a regional basis.
The purpose of this criterion is to identify resources -that .are unquestionably
uncommon on a regional basis. This criterion is particularly applicable to those
resources that may have been more common at one time, such as riparian habitats
and coastal wetlands, but have been greatly reduced due to urban and agricultural
expansion. Also included under this criterion is the habitat of non -government
sanctioned rare and endangered species recognized by private conservation groups,
such as the California Native Plant Society and Smithsonian Institute. In addition,
resources that are limited in distribution, in the region being considered, but
common elsewhere, fall into this group.
o Habitat that at some point in the life cycle of a species or group of species, serves
as a concentrated breeding, feeding, resting, or migrating grounds, and is limited
in availability.
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Certain areas tend to concentrate a species or group of species at various points in
their life cycles. These areas possess specific characteristics that are essential to
the maintenance of fish and wildlife. This criterion is intended to identify -such
areas that are limited in distribution in the region and not the specialized habitat of
a common species or group of species.-
o Biotic resources that are of scientific interest because then are either an extreme
in, pb1sicallgeogMphical limitations, or tha represent an unusual variation in a
population or community.
Scientists often, learn the most about a species or biological phenomenon by
studying it at an extreme in its distribution. This reveals what the extremes are
under which it can survive. In addition, isolated.populations and communities are
often relics of what was present in an area of some previous time, and often show
genetic traits .not found elsewhere in the species. These characteristics may be
useful in determining taxonomic relationships.
o Areas that serve as core habitats to regional plant, wildlife, and game -populations
and fisheries.
Certain characteristics of habitats, their geographical location; and their
topographical configuration make them particularly important to plant and wildlife
resources within - an entire region. An example' would be a watershed containing
an "ecotone", or high diversity of habitats with an extraordinarily high species
holding capacity which serves to replenish and maintain healthy plant and wildlife
populations throughout the surrounding area. Areas that are critical to the
maintenance of game and fish populations in the same. manner also fall under this
criterion.
Moderate Significance
The criteria defining Moderate Significance relate to resources whose contribution to
native biological diversity and productivity is limited to their local context .and/or which
support the functioning and .integrity of adjacent areas of high significance. The criteria
and the rationale for determining Moderate Significance are:
o Habitats that are key to the maintenance of localized plant and animal
populations but are not significant on a regional basis.
These would include relatively small undisturbed habitats, such as in canyons or
on steep hillsides, which are isolated by surrounding urban and agricultural land
D-2
uses and do not function as an interacting part of regional wildlife and vegetation
systems.
o Areas. which act to buffer and protect resources of high significance.
Commonly, areas of high significance will be� defined by ridgelines, the physical
extent of habitats, and the edges of urban and agricultural development. In most
cases, the areas immediately adjacent to these borders, while not displaying high'
significance in themselves, interrelate enough that their ultimate disposition will
have- an influence on adjacent resources. Thus, it may be necessary to provide
setbacks from intense development to prevent adverse impacts from "spilling
over" into areas of high. significance.
o Corridors and zones which serve to link areas of high significance and facilitate
their ecological interaction.
While not ,possessing high significance in themselves, such corridors and zones
would support and protect the functioning of .areas of high significance in- the
context of regional- ecosystems. In this regard they are like buffer areas. They are
usually -larger, however, not only protecting areas of high significance from impact
but also :facilitating population exchange between them. Such areas are intended
to prevent . areas of high significance from. becoming geographically isolated- by.
development whereby a gradual decline in their integrity and value would be
expected.
o" Biological resources which are noteworthy for their educational andlor-
horticultural value.
This criterion applies to resources which do not contribute to regionally 'significant
ecological functions, but do contribute to the overall biological diversity of a -
particular locale. An example of this type of resource would be introduced or
native trees with exceptional specimen quality.
Low Significance
Remaining biological resources fall within areas of Low Significance. The single
criterion for determining these areas is:
o Areas where biological resources ,have been removed or significantly altered and
is
none.of the above criteria apply.
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In general, these. areas are highly disturbed and/or lack importance in the
continuance and preservation of local or regional native biological diversity and
productivity. Urban and agricultural land uses -are usually associated with areas of
low significance..
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APPENDIX E
DESCRIPTION -OF BIOTIC COMMUNITIES
FOUND WITHIN THE IRVINE STUDY AREA
Freshwater Marsh. This community is composed of emerged aquatic plants and is
found in permanently saturated soils where the water, table is at or above the ground
surface. In the study area it exists along several stream courses, along the shorelines of
ponds, lakes, and reservoirs, and most extensively -at the San Joaquin Marsh .(area #6).
Normally, it is dominated by tall reed -like species, including cattail (T)tha latifolia) and
Olney bulrush (Scirpus olneyi). Willows are also common. In. general, this habitat
remains in good condition over most of the study area. However, the distribution of the
community is limited, In most areas it exists as a very thin band along stream courses.
As a result, it is highly susceptible to disturbances. Uncontrolled access and invasion by
non -natives has seriously degraded this community in some areas.
The freshwater marsh community serves as- the entire habitat or the critical component of
the habitat for a. great variety of faunal species. Amphibian species include several frogs,
salamanders, and newts. Most of these spend their entire' life cycle in freshwater aquatic
and semi -aquatic habitats, and could not otherwise survive. Only -two reptiles, the
western pond turtle and the western aquatic -garter snake are expected in this habitat with
any regularity. This community is equally critical for them.
Rodent populations can be found on the outside edge of the .habitat,, and medium to large
sized mammals use the marsh for cover while watering; feeding and resting: These
include the coyote, gray fox, mule deer, Virginia opossum, long:tailed weasel; and
raccoon. Several bird species found here are also specialized for this type of habitat and
can be found nowhere else. They include the Virginia rail,, sora rail,. American bittern,
common yellowthroat, _and long -billed marsh wren. There is an additional avifaunal
component that requires the cover of the marsh and the open water of the intermittent
ponds. These include American coot, common gallinule, green heron, great blue heron,
grebes, and several species of ducks. Species within this 'community with special status,
and the areas within the planning area in which they are found, are listed in Table B.
Commonly found in association with marsh areas .are bodies of open water. These occur
at the Sand Canyon, Laguna,. Bonita, Rattlesnake, Lambert, and Siphon Reservoirs, as
well as the Woodbridge Village and William Mason Park Lakes. This habitat is
E-1
important to migrating ducks, geese, loons, and grebes. Most bodies of freshwater are.
used by these species as wintering and resting areas during their migrations.
Most reservoirs and drainages are used for irrigation or flood control, and the periodic
rapid fluctuations of water levels prevents the formation of well -developed mature
lakeside marsh that can be used by waterfowl for forage and cover. Therefore, few
reservoirs offer more than marginal wildlife habitat. Those that 'do contain water year-
round have developed aquatic corrimunities.
Coastal Sage Scrub. Coastal sage scrub is the characteristic plant community of the
lower elevation hillsides and ridges of coastal Southern California where it occupies dry,
rocky, or gravelly soils. Within the study area this community is ' found scattered .
throughout the San Joaquin Hills and at elevations .generally below 1500 feet on the
Lomas Ridge. Typically, it is present on steep hillsides and in narrow canyons which are
unusable. for grazing and agriculture.
Coastal sage scrub is an open shrub community. The dominant species are shrubs that
grow two to five feet high, but do not normally form a closed canopy. However, bare
ground is not common. Rainfall. and soil moisture are sufficient to support a rich variety
of forbs and grasses. Growth of the dominant vegetation occurs in late winter and spring,
following the onset of winter rains. Most flowering will occur in spring, but some shrub
species continue into summer. The vegetation becomes .dormant and -more or less
deciduous in summer and fall.
Natural seeding rapidly reestablishes this community-, after fire, which normally consumes
this vegetation type entirely. Ground cover is usually reestablished within one year after
a burn.
The .composition of this community varies considerably within .the study ,area and two
sub -communities, "sage" and "mixed", can -be identified. This is"the result of the diversity
in climate, soils, and topography found among the .coastal and inland mountain
environments. The sage sub -community is relatively homogeneous in its species
dominance. Generally, this vegetation is, dominated. by California sagebrush ,(Artemisia
californica) and a variety -of grasses. In .fact, it often occurs in association with
introduced grassland. Floral species commonly comprising mixed coastal sage scrub
communities include California sagebrush (Artemisia californica), coastal goldenbush
(Happlopappus venetus), California encelia (Encelia californica), deer weed (Lotus
scoparius), black sage (Salvia mellifera), and California buckwheat (Erigonum
fasciculatum). Within both the sage and mixed subcornmunities, larger shrubs such as
lemonadeberry (Rhus integrifolia), laurel sumac (Rhus laurina), and toyon (Heteromeles
• arbutifolia).are also common on north -facing slopes and in drainages where coastal sage
scrub resembles chaparral in growth pattern and appearance. Common groundcover
E-2
species are annual grasses and forbs introduced by man through, grazing and agriculture.
These include red -stemmed filaree (Erodium cicutar-ium), foxtail chess (Bromus rubens),
soft chess (Bromus mollis), and wild oat (Avena fatua). Remnant perennial grasses (Stipa
spp., Elymus condensatus) may also be found.
Coastal sage scrub is highly _productive and supports a surprising diversity and abundance
of . wildlife. Amphibians are generally absent; however, several reptiles, including
western lizard, side -blotched lizard, gopher snake, red diamond rattlesnake; common
kingsnake,, and red racer are commonly found.
Rodents and small mammals are very abundant and include dusky -footed woodrat, deer
mouse, western harvest mouse, pacific kangaroo rat, California pocket -mouse, and
Beechey ground squirrel. Audubon cottontail and brush, rabbit are also numerous. The
large number of smaller mammals supports a relatively large number of predators. These
include those snakes mentioned above, and in addition, -fox, coyote, bobcat, and raptorial
birds (hawks, eagles, owls). Larger maminals, represented by niule deer and mountain
lion (in the Lomas. Ridge area) also commonly utilize this habitat within their ranges.
Characteristic bird species include the brown towhee; ,several sparrow species,. California
.thrasher, blue -gray gnatcatc her, and roadrunner. Other small "migratory -birds become
common in the winter and wide-ranging predatory birds are frequently seen overhead.
These raptors roost in nearby oak and riparian woodland, and on cliffs and rocks.
Chaparral. Chaparral is widely _distributed throughout California on dry slopes: and -
ridges at low and medium elevations where it occupies thin, rocky, or heavy soils. A
well -developed chaparral cover is found in the extreme northeast corner of the study area
and both "mined" and "chamise" chaparral types are found within the study area.
Vegetative composition varies considerably; however-, most species posses small -,-broad,
hard leaves. These characteristics allow plants to photosynthesize and transpire under
semi -arid conditions without wilting by reducing their evapo-transpiratory water losses.
Most plants, are evergreen, growing and flowering primarily im late winter and spring and
becoming somewhat dormant over the summer and fall. Chaparral species commonly
grow six to ten feet high and often form dense nearly impenetrable -stands.
Chamise chaparral communities are dominated by _chamise (Adenostoma fasciculatum)
which grows in relatively non-specific, uniform stands. Within mixed chaparral, this
species is joined in dominance by other species which include California sagebrush,
lemonadeberry, laurel sumac, black sage, scrub : oak (Quercus dumosa), and toyon.
Typically, a large accumulation of litter is found surrounding the base of shrubs ,and is
important to the overall ecology of the chaparral community. It- functions as a
• . "groundcover" in place of grasses and forbs to retard rainfall runoff, thereby inhibiting
erosion and enhancing percolation of water into the soil.
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Additionally, the leaf litter is highly flammable and readily burns during the drier parts of
the year: Periodic burning (every twenty years or so) is a key element to the maintenance
of a healthy, productive chaparral cover. The plants of this community are adapted to
recurrent fires and either produce seeds that-require� high temperatures before germinating
(scarification) or possess root crowns that send up sprouts following fire. Furthermore,
fires recycle nutrients held.in the plants back to the soil in the form of ash.- If fire does not
occur, the soil becomes sterile and -plants eventually become decadent and die without
replacement: This can lead to problems in. wildlife. and watershed management.
Following a fire, annuals produce a dense- groundcover that holds the soil in, place until
the- larger shrubs and the litter are reestablished.
The diversity of wildlife in pure. unbroken stands of chaparral :is limited. However,
community productivity is high and large numbers of individual species are often present.
Under natural conditions of recurring fire, the chaparral is regularly burned, thus creating
openings that often support many grasses and coastal- sage scrub -species. This process is
extremely important to wildlife: These openings provide an edge between the
successional vegetation and chaparral that is much more diverse and able to support a
greater number of species than either habitat type alone. These animals are -able to utilize
this interface as an entrance to dense chaparral in areas that would otherwise be- closed- to
them. The characteristic wildlife species found in this plant community are virtually the
same as those found in coastal -sage scrub. -
Introduced Grassland. Introduced grassland, also referred -to as valley grassland, is. a
vegetation type that replaces native communities- following dryland farming, heavy,
grazing, and other artificial clearing. Natural plant species are - either cleared or are
destroyed and are replaced by adventitious species that can withstand constant
disturbance. As a result, the flora of this .community is dominated by annuals and
perennial herbs that grow one to three feet high. The majority of these are non-native and-,
are often considered to be "weeds".. The vegetative cover of this 'community
characteristically germinates during the late fall rainfall, with most growth, and flowering
occurring from winter through spring. Plants then die and persist as seeds through
summer and early fall. These characteristics are in contrast to - native grasslands of
Southern California which are composed of perennial bunchgrasses (Stipa spp., Poa spp.,
Aristida spp.).
Relatively large introduced grasslands are found primarily in the broader valleys and on
the more gentle hillsides of the Lomas Ridge and on ridgelines of the San Joaquin Hills.
Presumably, these areas were once covered by a -native coastal sage scrub or native
grassland community. However, as ranching, and agricultural practices grew in the
region, these areas were either mechanically cleared or treated with herbicides and were
either converted to grassland to improve livestock grazing or plowed for farming.
E-4
Dominant species include various introduced grasses (e.g., .Brome* spp., Avena spp.,
Festuca spp., Hordeum spp., etc.) and mustards (Brassica spp.). Numerous spring -
flowering native wildflowers are also present in limited numbers. These are rapid-, .
growers, shooting up out of the soil in a matter of a week:or two under the proper climatic
conditions and adequate rainfall.. When the weather becomes hot and, dry, they disappear
with the same rapidity.
Introduced grassland is easily reestablished after fire; and . on -going grazing and
agricultural practices will continue to promote this vegetation. However, if left
undisturbed, these areas will eventually revert back to their native conditions, of native
grasslands or coastal sage scrub.
Large open expanses of grassland support a limited diversity of wildlife, but those that are
present.are normally abundant. No amphibian species are expected, in this dry, disturbed
habitat. The side -blotched -lizard, western fence lizard, red diamond rattlesnake, and
gopher snake are the characteristic reptiles of this community. The latter two species -as
well as larger mammalian predators, .such as coyote, fox and bobcat, are supported by
abundant populations of rodents and. small mammals, including meadow mouse, deer
mouse, Botta pocket gopher, Beechey ground squirrel, and Audubon cottontail.
'Two groups of birds dominate the avian fauna in this community.. Grassland birds such:
as the western meadowlark, water pipit; savannah sparrow, lark sparrow, and horned lark
forage for seeds and insects on the ground. Several of these species . Will nest here l'f not'
disturbed. The second group of birds are the. predators. These species .are expected` to
include the red-tailed hawk, marsh hawk, black -shouldered kite, turkey vulture,, American
kestrel, barn owl, and great horned owl. For, these organisms, grasslands serve as
important feeding grounds where "they prey on small .mammals, lizards, and small birds.
However, they depend on woodland habitats in. the region :for nesting and ,perching .sites.,
Riparian. Riparian communities are found along drainage courses throughout California
where moisture is at or near the surface- on a year-round basis. These conditions_ are
favorable for the establishment of a rich cover of trees;, shrubs, herbs, and grasses. This
community type is found along numerous drainage courses. in -the .study area.. It was once
much more extensive in the region; .however, flood control and irrigation .projects have
severely restricted its distribution. Due to the wide variation in the intensity and extent of
man's activities adjacent to and within these areas, species composition and growth .form
vary considerably. Community associations within the study area consist of two types,
"Woodland" and "forest".
Riparian forest refers to riparian community associations which have a dense vegetative
• cover. These areas are dominated by western sycamore and coast live oak-(Quercus
agrifolia). A dense understory of large shrubs, including toyon, elderberry (Sambucus
E-5
mexicana), laurel sumac, and lemonadeberry, is. commonly present: The groundcover is
usually a thick layer of leaf litter. Aquatic and , semi -aquatic plants,, such as algae and
water -cress (Rorippa nasturtium-aquaticum) are found where surface water is present on
a year round basis. Poorly developed examples of- this association are scattered
throughout the study area where it occurs as a narrow band or as scattered clumps along
drainage courses. Only where it occurs. interspersed 'or intermixed with oak woodland
(see below) is it well developed. These areas include Shady, and Bommer Canyons in the
San -Joaquin Hills and in Bee and Round Canyons in the Lomas Ridge.
Riparian woodland occur in localities with permanently wet soil; thus, they are usually
found near seeps'or.at the margins of perennial streams and marshes where drainage is too
poor for the development 'of a riparian forest. Characteristically,, this association is
dominated by dense stands of willows (Salix spp.) nine'to fifteen feet tall. These plants
reproduce readily from- seeds, broken branches and underground shoots. Understory.
vegetation is normally lacking. Willow thickets are found along irrigation ditches and
streamcourses throughout the study area. The most significant of these are found at
Bonita Reservoir, Sand Canyon Wash and along portions of the San Diego Creek,
particularly where it mixes with the SanJoaquin Marsh. Much smaller examples are
found scattered throughout the study area surrounding reservoirs,, and in the larger
drainage ditches.
Due to the similarity of wildlife habitat provided by riparian communities :and oak
woodland, this aspect of this community is discussed in the next section.
Oak Woodland. Major oak woodlands are found in Bee and Round Canyons in the
Lomas Ridge and in Shady and Bommer Canyons within the San Joaquin -Hills. ' Minor
woodlands can be found in numerous other canyons within the study area, however, most
of these were not mapped due to their small size. These communities, consisting of either
open "savannah" or more dense forest, are solely dominated by coast live oaks ten to_
twenty feet tall with an understory of grasses and scattered shrubs. The only significant
difference -between these sub -types is the density of oak trees. Large shrubs characteristic
of the chaparral and coastal sage scrub communities, such as toyon, laurel sumac,
lemonadeberry, Mexican elderberry and coffeeberry (Rhamnus californica) commonly
occupy the openings between the oak trees. The majority of the oak woodland
communities within the study area are in good -to excellent condition despite the fact that
the native understory vegetation of most has been heavily disturbed by recreational use
and/or heavy grazing pressure.
Fire results in the clearing of litter and dead vegetation, and loss of approximately 50% of
living material on oaks. Rejuvenation of the woody vegetation will occur after a fire.
E-6'
Annual grasses and chaparral type shrubs in the understory will reseed and resprout after
a burn.
Oak and riparian woodlands are very uncommon in Southern California., In 1963, these
habitats were estimated by the California Department of Fish and Game to cover less than
1.7%-of Orange County (Table A). This figure has undoubtedly been reduced since then
by urban and agricultural expansion, particularly residential development and flood
control improvements. This is contributing to the loss of regional wildlife •, resources
because woodland habitats* are of high ecological value. For a given. number of acres of
habitat, they support, higher population densities of wildlife than any other terrestrial
habitat.
Oak and riparian woodland habitats normally possess a high. diversity of plant types
enhanced by their overlap with surrounding vegetation types (edge effect or, ecotone),
.which in turn support abundant and diverse wildlife resources-. All woodlands should be
viewed as components of a. regional system of woodland "island" habitats. The number
Of wildlife species each woodland island can hold is- a function of its size and its isolation.
'Larger woodlands, and woodlands located close to other woodlands' (such as in the same
canyon or in adjacent canyons), can hold more species than smaller or isolated ones. If an
individual woodland or a large portion of a woodland ' is removed, the diversity and
abundance of wildlife there; as well as in surrounding woodlands, will decrease: These -
habitats normally support relatively high, numbers of amphibians .beneath leaf litter and
along moist stream banks. Several reptile species are also common here. Rodents .are
common along the _edge of .neighboring habitats and in areas where seasonal flooding
does not occur. Particularly in lowland areas; woodlands are very important to furbearers
(rabbits, raccoons, skunks, foxes, coyotes, weasels, bobcats) which use these habitats .for
cover., food, and denning.. Populations of furbearers commonly reach their greatest
densities in and around these areas.
Woodlands are very important to bird: species. Nearly all *the species, found in,
surrounding habitats can be found here. In addition, it supports. others, that require the
moist vegetation and/or trees. Hummingbirds, woodpeckers,, many flycatchers, thrushes,
- vireos, warblers, and most finches forage and nest in this habitat. Many of these. species
are migratory, and utilize this habitat for over -wintering. Hawks, owls; falcons, kites; and
doves specifically require the trees as perching .and, nesting sites , and forage in
surrounding vegetation. Some predatory species such as Cooper's. hawk and , sharp -
skinned hawk forage in the habitat itself.
These habitats also serve as wildlife dispersion corridors important ' to regional wildlife
populations. Many wildlife species, particularly medium and large forms, must move
from place to place to forage for food or meet other requirements necessary for their
E-7
survival. In addition, the dispersion of young after reproduction- is essential -to prevent
local population crowding and to maintain genetic variability and numbers throughout
regional populations. Wildlife dispersion usually takes place along, canyon drainages and
streamcourses, not only because topographic resistance is -minimized, but also because
they commonly support woodland habitats which provide cover, food, and/or water
during movement.
Agriculture Generally, this community is comprised'of orchards, cultivated croplands
and scattered residential and farm structures, and is found mostly on valley floors where
land is suitable for agriculture and where irrigation is available. This community is found
over much -of the Tustin Plain and the broader foothill canyons- where agricultural land
uses have a fairly long history.
The prevailing orchards and row -crops found here are 'far :removed from natural
: conditions and represent environmental simplifications which are artificially managed.
Eucalyptus windrows composed of single'rows of blue gum (Eucalyptus globules) fifty to
seventy-five feet high, are commonly aligned between fields and orchards.. These were
originally intended to reduce crop damage and excessive evaporative water loss due to
wind. These windrows visually dominate the existing landscape and are currently being
retained in . urbanized areas as a visual amenity (Appendix G - III). A wide variety of
roadside and irrigation ditch weeds complete the vegetation of this community.
The native flora in rural communities has been heavily impacted, and' natural habitat
diversity and productivity has been greatly reduced. Consequently, the diversity and
abundance of fauna is very limited. Croplands and orchards are capable of supporting a
relatively small number -of -wildlife species. These include several perching birds
(starling, mourning dove, western meadowlark, horned lark, several sparrow species) and
birds of prey (red-tailed hawk, turkey vulture, black -shouldered kite), few reptiles (gopher
snake, side -blotched lizard), a number of small rodents and medium sized mammals
(meadow mouse, house mouse, beechey ground squirrel, Audubon cottontail), and an
occasional larger mammalian predator (coyote). The type and number of wildlife vary
with the crop present and the season. Adjacent eucalyptus windrows are frequently used
by birds of prey for roosting and"occasionally for nesting.
The use of the numerous flood control channels and irrigation ditches by wildlife depends
largely on their location, design, substrate, presence or absence of surface water, and the
degree and frequency of weed control and silt removal. Most are dry for the greater part
of the year and/or are frequently managed. Thus, permanentresident wildlife populations
are limited. Others support a surprising number of species including, `those species found
in adjacent croplands, plus, several shorebirds, waterfowl, and amphibians which depend
• on surface water and/or moist soil and vegetation. Perhaps most notable in this regard is
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•
the San Diego Creek Channel which in the past possessed considerable lateral vegetation
along its margins.
Urban/Cultural. Urban communities are located within cities and towns with residential
subdivisions, parks, golf courses, commercial areas, and industry. Within the study area-,
this community is represented over much of the Tustin Plain which is rapidly urbanizing.
Notable urban features of the area include MCAS El Toro, MCAS- - Tustin and .the
scattered residential developments of .the Irvine Villages. Gener-ally, all native vegetation
in these areas has been removed and replaced with non=native ornamental species which
are frequently manicured.
Faunal diversity is extremely low. However, several ,animal species thrive under these
conditions. They include Anna's hummingbird, starling, mockingbird, house, sparrow,
house finch, -Brewer's blackbird, common crow, house mouse, and Botta's-pocket gopher.
The house sparrow, the starling and the house mouse are introduced European species and
are considered to -be "zoological weeds' that compete with -native species.
E-9
APPENDIX F
AREAS OF HIGH AND MODERATE SIGNIFICANCE
Area of High Significance #1 .
Limestone Canyon
Classification: -Prime bird of prey nesting/roosting area.
Prime .bird of prey foraging/wintering area.
Major wildlife movement corridor.
Regionally significant oak woodland..
Woodland/brushland/grassland ecotone.
Description: This area, defined by the entire watershed of Limestone Canyon
overlaps the extreme northern boundary of the study area. -With
the exception of several unimproved 'dirt roads. and limited
agricultural activities, the area has retained most of its natural
character.
A mosaic of native and naturalized habitats are present, including
extensive oak woodland onthe floor of the canyon and its major
tributaries; coastal sage scrub on steeper hillsides.and in narrower
drainages; and, introduced grassland throughout the- broader
canyons and on -the more gentle rolling"hillsides. Elements of
riparian habitat are also found- along the mainstern drainage.
These habitats create an -"edge effect" which support diverse and
abundant populations of mammals, birds, reptiles and
amphibians. In particular, the combination of larger trees and
adjacent open areas creates an important habitat area for resident
and migratory birds- of prey. In addition, the canyon provides, an
important link between Santiago. Canyon downstream and the
interior habitat areas of Lomas Ridge upstream.
As a wildlife movement corridor, this area.is used by a number of
larger mammals and medium sized furbearers, including
mountain lion, coyote, bobcat, striped skunk and mule deer. The
combination of open foraging habitat in proximity to woodland
nesting and roosting sites: also makes this area very important to
birds of prey. Several raptor species are. found here including
black -shouldered kite, cooper's hawk, sharp -shinned. hawk, marsh
hawk, red -shouldered hawk, ferruginous hawk, golden eagle,
prairie falcon, merlin, American. kestrel and barn owl, all of
which are afforded special status designations. Other species of
special status which occur within this area are ring-tailed cat,
black -tailed gnatcatcher, cactus wren, hairy woodpecker,
Bewick's wren, western bluebird, loggerhead shrike, vesper
sparrow and coast horned lizard.
• Overall, this area ranks as one of the more significant 'habitat
areas remaining in Orange- County.
F-1
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•
Management
Considerations: The goal for managing this area should be to -prevent any .,loss, of
the existing resource value within the "core" oak woodland area
and minimizing/limiting the loss .of ' resource values, throughout
the remaining area. The most effective action to achieve this goal
is to preserve the oak woodland areas in their entirety and to
retain large interconnected blocks of contiguous coastal : sage
scrub and grassland habitats adjacent to' the woodland. (Note:
The vast majority of- this area is outside the City's sphere of
influence).
F-2
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•
Area of High Significance 42
Bee & Round Canyons
Classification: Regionally significant oak woodland.
Woodland/brushland/grassland ecotone.
Description: This area encompasses the entire upper watersheds .of Bee and
Round Canyons. Except for several unimproved dirt roads and.
limited grazing in both canyons, this area is natural, and has
retained most of its native character.
The area supports a mosaic of habitat and vegetation types,
including extensive oak woodland, well developed riparian,
coastal sage scrub and introduced grassland. The oak woodland
and riparian vegetation are found in the mainstein canyon
bottoms with the hillsides. of these drainages supporting coastal
sage scrub. Limited .areas; of 'introduced grassland are found on
the more level ridgelines- and more gentle hillsides of the
uppermost watershed, particularly Bee Canyon.
The variety and mix of vegetation types create a diverse habitat
for wildlife.. Populations of mammals, - birds, reptiles and
amphibians are.diverse and abundant :This area represents one of
the more important habitats found on the south side of Lomas
Ridge.
Several "wildlife species of special concern. are found here
including ring-tailed cat, black -shouldered kite, Cooper's hawk,
golden eagle, prairie falcon, merlin, American kestrel, barn owl,
black -tailed- gnatcatcher, cactus wren, hairy woodpecker,
Bewick's wren, western bluebird, loggerhead shrike, Vesper
sparrow and coast horned lizard.
Management
Considerations: The goal for managing this area should be to prevent any loss of
the existing resource value within the "core" oak woodland and
riparian habitat. In addition, the loss of resource values through
other areas should be minimized and limited by preserving large,.
interconnected blocks of contiguous coastal sage scrub and
grassland habitats, particularly adjacent to the woodland. (Note:
a major portion of this area is planned .as a sanitary landfill by the
County of Orange):
F-3
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•
Area of High Significance #3
The Sinks
Classification: Regionally significant oak savannah.
Woodland/brushland/grassland ecotone.
Description: This area encompasses a portion of the upper Agua Chinon
Watershed. -Except for several unimproved dirt roads and limited
grazing in the area, this area is natural, and has retained most of
its native character.
The - area supports a mosaic of habitat and vegetation types,
including extensive, well developed oak savannah, riparian,
coastal sage scrub and introduced grassland. The oak savannah
and riparian vegetation - are found- throughout . the various
drainages in the area with the hillsides of these drainages
supporting coastal sage scrub. Limited areas ,of introduced
grassland are found on the more level ridgelines and more gentle
hillsides.
This area represents one- of -the more important. habitats found on
the south.side of Lomas Ridge.
This area also supports .a number of plant species, in abundance,
which are normally found- in the .desert regions and ,more interior
regions of Southern California. Thus, ,certain floral components
may represent the western most extremes in .their distribution and
are of potential scientific interest..
Additionally, -several wildlife species of "special concern are found
here including ring-tailed cat; black -shouldered kite, Cooper's
hawk, golden eagle, prairie falcon, merlin, .American kestrel,,barn
owl, black -tailed gnatcatcher, cactus wren, hairy woodpecker,
Bewick's wren, western bluebird, loggerhead shrike, Vesper
sparrow and coast horned- lizard. - Also, due to the presence -of "
cliff roosting sites, American peregrine falcon -may also visit this
area during periods of migration.
Management
Considerations: The goal for managing this area should be to prevent any loss of
the existing resource value within the "core" oak savannah and
riparian habitat. In addition, the loss of resource values through
other areas should be minimized and limited by preserving large,
interconnected - blocks of 'contiguous coastal sage scrub and
grassland habitats, particularly adjacent to the woodland.
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Area of High _Significance #4
Borrego Canyon
Classification: Regionally significant oak woodland.
Woodland/briishland/grassland ecotone.
Major wildlife movement corridor.
Description: This area encompasses the entire upper watershed of Borrego
Canyon. Except for several unimproved, dirt roads and limited
grazing, this area is natural, and has retained most -of its native
character. This area overlaps the. extreme northeast edge of the
study area.
The area supports ..a mosaic of habitat and vegetation types,
including extensive oak woodland, well developed riparian-,
coastal sage scrub -and introduced grassland: The oak woodland
and riparian vegetation are found in the mainstem canyon bottom
with the hillsides of this drainage supporting coastal sage scrub.
Limited areas of introduced grassland are found on the more level .
ridgelines and more gentle hillsides.
The variety and mix- of vegetation types create a diverse habitat
for wildlife. Populations of -mammals, birds,, reptiles and
amphibians are diverse and abundant Larger and medium sized
mammals and ,birds are believed to _use this canyon as a major
wildlife movement ,corridor :due .to, the presence of breeding;,
feeding, nesting and coven habitat.
This area represents one of the more important habitats found on
the south side of Lomas Ridge.
Several wildlife species of special concern are found here
including ring-tailed cat, black -shouldered kite, Cooper's hawk,
golden eagle, prairie falcon, merlin, American kestrel, barn owl;
black -tailed � gnatcatcher, cactus wren, hairy woodpecker,
Bewick's wren, western bluebird, loggerhead shrike, Vesper
sparrow and. coast homed lizard.
Management
Considerations; The goal for managing this area should be to prevent any loss of
the existing resource value within the. "core" oak woodland and,
riparian habitat. In addition, the loss of resource values through
other areas should be minimized and limited,by preserving.. large,
interconnected blocks of contiguous coastal sage scrub and
grassland habitats, particularly adjacent to the woodland.
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Area of High Significance #5
Santiago Canyon
Classification: Regionally significant riparian habitat.
Prime bird of prey nesting/roosting area.
Major wildlife movement corridor. "
Regionally significant oak woodland.
Woodland/brushland/grassland ecotone.
Description: Santiago Canyon is a major topographical and ecological feature
of the Santa Ana Mountains. - This area, overlapping the extreme
northern boundary of the study area, encompasses a large portion
of the canyon where sand and gravel operations and rural
development has not occurred... Although Santiago Canyon Road,
agricultural activities, grazing and limited rural development has
taken place in this area, the canyon remains natural overall and
supports significant native vegetation.
The habitats present continue to support extensive and well
developed riparian, scattered oak woodland, coastal sage scrub,
chaparral and introduced grassland communities. Dense, wooded
areas remain throughout the broad canyon floor and on many
north -facing slopes. Dense chaparral and. coastal sage- scrub are
found on most hillsides and ridgelines. Introduced grassland is
present over the canyon bottom and in many broader, more level
areas where tributary drainages . intersect with the mainstem
canyon. ,
Wildlife is both abundant and diverse in the area which provides
a wide variety of breeding, foraging and cover habitats. A. year
round source of surface water is also present in most years,
adding to the importance of this area. Mammals,, birds, reptiles
and amphibians are all represented in high -numbers. Larger more
mobile species of birds and mammals use the canyon as a major
movement corridor, utilizing the variety of habitats as they move.
Such species. include mountain lion, bobcat, mule deer, -coyote
and a variety of furbearers (skunks, ring-tailed cat, raccoons, etc.)
Sensitive species which are found in this area include several
species of birds of prey.. These are black -;shouldered kite,
Cooper's hawk, sharp -shinned hawk, marsh hawk, red -shouldered
hawk, golden eagle, prairie falcon, merlin, Americankestrel, barn
owl, and -possibly American peregrine falcon. Additional species
of special status found in the chaparral, coastal sage scrub, and
open areas are black -tailed, 'gnatcatcher, Bewick's wren, hairy
woodpecker, cactus wren, western bluebird, loggerhead shrike,
yellow warbler, grasshopper, sparrow, Vesper sparrow, and coast
horned lizard.
Historically, the area- is believed to have been extremely
important to nesting birds of prey due to the availability of tree
and cliff nest sites. This feature -has diminished somewhat due to
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the, encroachment of man. However, it remains to a significant
degree.
Within a regional context, 'the broader alluvial woodlands and
more dense. oak and riparian.forests are found in only a few
drainages within Orange County.
Management
Considerations: Resource "management -for this area should have as its goal the
prevention of any :loss to. existing woodland values, preferably,_
through riparian and oak woodland preservation. Additionally,
large blocks of contiguous chaparral, coastal _sage scrub and
introduced grassland should be .preserved so as to minimize and
limit the- loss of these habitat values, (Note: The majority of this
area is outside the City's sphere of influence).
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Area of High Significance'#6
San Joaquin Freshwater Marsh
Classification:.. Rare/endangered/unique species.
Regiorially significant riparian habitat.
Open water/shoreline with regional significance as waterfowl
habitat.
Regionally significant freshwater marsh. _
Description: This area is a .remnant of the extensive wetlands that once
covered the entire upper Newport Bay and San Diego Creek delta
area. . Today, former areas of this. habitat have been filled,
drained, and lost to development.
Excellent examples of lowland riparian and regionally limited
freshwater marsh habitats are present; most of which have been
set aside as part of the University of California reserve system.
Freshwater marsh habitat supports a great diversity of wildlife.
Most of the many bird species found here are dependent in some
way on the surface moisture and vegetation.. It is also habitat that
supports several species of amphibians -(including California red -
legged frog), reptiles and mammals.
The San Joaquin freshwater marsh is, -most important to resident
and migratory waterfowl and shorebirds, which- either breed here
or are found in very high numbers during the spring and fall
migration periods.' Such species include western grebe, double-
crested cormorant, canvasback, . black -crowned night heron,
American bittern, least bittern, white-faced ibis, California black
rail, mountain plover, snowy plover; long -billed curlew, short -
billed dowitcher, and elegant tern all of which have special- status..
Still other non -water bird species found here are black -shouldered
kite, marsh hawk, ferruginous, hawk, American osprey, American
kestrel, burrowing owl, barn owl, and yellow -breasted chat.
Five rare/endangered species are also -found here on. a regular
basis. These are Belding savannah sparrow, light-footed clapper
rail, California least tern, , California brown pelican, and possibly
Bell's least vireo. -These species are more common within the
Upper Newport Bay saltmarshs, but occasionally use -the
freshwater marsh for habitat as well.
This area is the only large area of this habitat remaining in the
county.
Management
Considerations: There should be no loss of existing resource values from within
this area. Preferably, this goal should be -achieved through total
preservation; however, should some, limited loss be unavoidable,
restoration is acceptable if restored habitat is equal in. value 'to
• that lost. -
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Area of High Significance #7
Sand Canyon Wash
Classification: Regionally significant riparian habitat:
Regionally significant freshwater marsh.
Description: This area includes the. reach of Sand Canyon Wash between Sand
Canyon Reservoir and the Culver Drive crossing; The upstream
portion of this area consists of dense riparian thickets which have
reestablished themselves along the improved channel. The lower
portion of this area is considerably wider, and consists of -both
riparian and freshwater marsh habitats within the -undeveloped
portion of William R. Mason Regional Park. Flood control
improvements in the- lower portion appear to have been minimal.
Although this area has experienced some alteration, the
vegetation is primarily native and characteristic of natural,
lowland riparian habitats, and, is significant within: a regional
context. Some of .the species which use this area are sensitive
based on various status designations. These include black-,
shouldered kite, marsh hawk, American kestrel, black -crowned
night heron; American bittern, least bittern, loggerhead shrike,
and yellow warbler.
Due to, the extensive and well developed native vegetation, this
area serves as an important habitat. for .a. wide variety of birds,
small and medium sized mammals, reptiles and amphibians..
Today, it is one of. the few, relatively large areas of riparian and
freshwater marsh , areas remaining in the study area. It is also
noteworthy on a county-wide.basis.
Both resident -breeding and seasonal -migratory birds benefit. from
this area. Being one of � the few habitats of its type remaining in
the region, it serves as a refuge for those species. requiring
riparian vegetation within their habitat areas.
Overall, the area has high integrity as a predominantly native
habitat.
Management
Considerations: The underlying management goal for this area should -.be to.
prevent any loss of existing resource value. Preservation of
existing habitats and vegetation is the preferred objective;
however, on -site enhancement and/or restoration of a portion of
existing habitat to equal the total existing habitat value is
acceptable.
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Area of High Significance #S
San Diego Creek - Upstream Reach
Classification: Regionally significant riparian habitat.
Description: Within the study area, .this segment of San Diego Creek supports
a good example of a lowland riparian community.- This type of
vegetation was once found along all,of the drainages crossing the
Tustin Plain which has now been developed or converted to
agricultural use. As a consequence, most of the drainages have
been improved and their native riparianhabitats have been lost.
This reach of San Diego Creek supports. a number of native
riparian tree, shrub, and groundcover species. Although they
grow along. the immediate drainage course only, they usually
create dense stands.
The habitat here is important to many smaller birds, medium and
small mammals, reptile and amphibians. Cover, breeding and
foraging habitat requirements are all met for -these wildlife. Some
of the species which use this area are sensitive based on various
status designations. These include black -shouldered kite, marsh
hawk, American kestrel, black -crowned night heron, American
bittern, least bittern, loggerhead shrike, and yellow warbler.
This area's greatest value lies in its being the habitat for - a
so . regionally limited biotic community, and it being a refuge for
wildlife within an otherwise developing area.
Management
Considerations: The goal for managing this area should be -that there is no .loss of
existing resource value. This goal should be met through the
preservation of existing, habitat and - vegetation and/or
enhancement and restoration. of existing habitat after any
disturbance.
•
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Area of High Significance #9
Bonita Reservoir
Classification: Regionally. significant riparian habitat.
Regionally significant freshwater marsh habitat.
Description: This area essentially encompasses the designated impounded area
upstream from Bonita Reservoir dam: It is a man-made habitat
which is seasonally flooded by impounded run-off, but maintains
saturated. soil throughout most years. Although an artificial
habitat, the vegetation found here is native.
Dense stands of both native riparian and freshwater marsh
vegetation are present. -This vegetation provides valuable habitat .
for a. wide variety of birds, mammals, reptiles and amphibians
including many resident and migratory species.
Bonita Reservoir represents one of the few sizable riparian and
marsh habitats remaining in the study area, and county.- _In
addition to- ` wildlife -requiring dense riparian and marsh
vegetation; -the area serves- as habitat for a limited number of
waterfowl which use a small area of .open water within the area..
A number -of -wildlife with special status designations are found
here. These include western grebe, canvasback, black -shouldered
kite- marsh hawk, black -crowned night- heron, American bittern,
least bittern, yellow warbler, yellow -breasted chat and California
red -legged frog.
The area has high integrity as a. habitat- and, is limited in the
region.
Management
Considerations: The management goal for this area should be to preserve existing
habitat -value, with no loss. Direct preservation of existing habitat
and vegetation should be the primary objective ,with restoration
and/or enhance-ment being secondary and used only if some loss
of existing habitat is unavoidable.
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Area of High Significance #10
Sand Canyon Reservoir
Classification: Open water/shoreline with regional significance as waterfowl
habitat.
Rare/endangered/unique species.
Description: This area is defined by the reservoir and shoreline upstream from
Sand Canyon Reservoir dam. ..It is a man-made habitat area
which has gained value and importance by way of the loss of
natural open water and shoreline habitats throughout the region.
Sand Canyon Reservoir is valuable as .an area of undisturbed
waterfowl habitat. It is used by a relatively. -large number of
migratory waterfowl. Most noteworthy, it:is the winter habitat for
several thousand Canada geese (up to 3000 geese have been
observed) who are otherwise -relatively unknown 'in Orange
County in high, concentrated numbers. Additionally, as many as
400 double -crested -cormorants have been seen using the open
water and riparian habitat for foraging and roosting, respectively.
The riparian habitat appears to be suitable for nesting for this
species as well. For waterfowl species, and in- particular the
Canada geese, this area serves as ovef-wintering and resting
habitat. Other species of note which use this area are western -
grebe, canvasback,,and California red -legged frog.
Management
Considerations: The management goal for this area should be no net ,loss- of in -
kind resource value; while minimizing Ithe -loss of existing
resource values. Preservation is the preferred objective; however,
restoration and/or enhancement of remaining habitat following
any unavoidable loss of existing resource base is acceptable.
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Areas of High Significance #11 and #12
Rare Plant Habitat
Classification: Rare/Endangered/Unique Species.
Description: These areas represent known habitats 'and populations of the
Orange County turkish ragging (Chorizanthe staticoides var.
compactd). One area is found on the earthen dam and adjacent
hillsides of Sand Canyon- Reservoir the other area is found along
a roadside in a major tributary to Shady Canyon. Orange County
turkish rugging is a species recognized as rare and endangered by
the California Native Plant Society. Typically, it is -found in
sandy soil and, is most commonly associated with coast sage
scrub. Orange County turkish rugging is reported to occur only
along the Orange County coast, and has its population center in
the San Joaquin Hills.
Management -
Considerations: The management goals of these - areas should be no loss of
existing resource value with in -place preservation of existing
habitat areas being the most effective means of achieving this
goal.
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Area of High Significance #13
Shady Canyon
Classification: Regionally significant riparian habitat.
Prime bird of prey nesting/roosting area.
Prime bird of prey foraging/wintering area.
Major wildlife movement corridor.
Regionally significant oak woodland.
Woodland/brushland/grassland, ecotone.
Description: This area encompasses the ,entire middle and upper, watershed ,of
Shady Canyon. Small portions of this area extend beyond the
extreme southeast boundary of the study -area. With the exception,
of several unimproved, dirt roads and on -going grazing activities,
this area is natural and has -retained its native character.
There are a variety, of physical habitats present which, .in turn,
support excellent .examples of a variety of vegetation types.
These -include well developed riparian, extensive oak woodland;
coastal sage scrub and introduced :grasslands, Well- developed
riparian ,woodland and forest follow ,the mainstein drainage.
Often mixed with- the riparian vegetation, and found by itself on
adjacent north -facing hillsides is. oak woodland. Intermixed
throughout the hillside areas 'is coastal sage scrub. Introduced
grassland predominates the level areas of the canyon floor,
ridgelines and lower hillsides.
The physical features and vegetation mosaic of this area, make it
very important to a wide variety of wildlife forms. Diverse
populations of mammals, birds, reptiles, and amphibians are found
in abundance. Larger and medium=sized mammals and birds .are
believed to use the canyon as a major movement corridor due to
the presence of breeding, feeding, resting and cover habitat.
Noteworthy species which use habitats in the area are ringtailed
cat, barn owl, black -tailed gnatcatcher,. - cactus - wren, hairy
woodpecker, . Bewick's wren,, western bluebird, loggerhead
shrike, yellow warbler, grasshopper sparrow, Vesper sparrow and
coast horned lizard.
The area is also important to birds of prey due - to the numerous
cliff and tree nesting and -roosting sites and nearby foraging
habitat provided by grassland and open coastal sage scrub.
Significant raptor species found Here are black -shouldered kite,
Cooper's hawk, sharp -shinned_ hawk, marsh hawk, red -shouldered
hawk, prairie falcon, merlin, American kestrel, barn owl, and
possibly American peregrine falcon.
The integrity of this canyon, as a habitat area is high and it
represenfs one of the most important biological features of the
San Joaquin Hills.
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Management
Considerations: This area should be managed so as to prevent any loss of existing
riparian and oak woodland resources and to minimize ,the loss of
other resources, -including ,grassland and coastal , sage scrub.
These goals should be met by, preserving existing riparian and
oak woodland vegetation and by retaining large, interconnected
areas of contiguous grassland and coastal sage scrub vegetation.
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Area of High Significance #14
Bommer Canyon
Classification: Regionally significant riparian habitat.
Prime bird of prey nesting/roosting area.
Prime bird of prey foraging/wintering area.
Major wildlife movement corridor.
Regionally significant oak woodland. -
Woodland/brushland/grassland ecotone.
Description: This area encompasses the entire middle and upper watershed of
Bommer Canyon. Small portions of this area extend beyond the
extreme southeast boundary of the study area. With the exception
of several unimproved, dirt roads and on -going grazing activities,
this area is natural and has retained its native character.
There are a variety of physical -habitats present which, in turn,
support excellent examples . of a variety of vegetation, types.
These include riparian, oak "woodland, coastal sage scrub and
introduced grasslands. Well developed riparian woodland and
forest follow the mainstem drainage. Often -mixed with, the
riparian vegetation, and found by itself on adjacent north -facing
hillsides is oak woodland. Intermixed throughout the hillside
areas is coastal sage scrub.- Introduced grassland .predominates
the level areas of the canyon floor, -ridgelines-and, lower hillsides.
The physical features and vegetation mosaic of this area make it
very important to: a wide variety of wildlife forms. Diverse
populations of mammals, birds, reptiles and amphibians -are found
in abundance. Larger and medium-sized mammals and birds are
believed to use the canyon as a major movement corridor due to
the ' presence 'of breeding, feeding, -resting, and ,cover. habitat.
Noteworthy, species which use habitats in the area are ringtailed
cat, barn owl, black -tailed -gnatcatcher, cactus 'wren, hairy
woodpecker, Bewick's wren, western bluebird, loggerhead
shrike, yellow warbler, grasshopper sparrow, Vesper sparrow and
coast horned lizard.
The area is also important to birds of prey due to the numerous
cliff and tree nesting and roosting sites and nearby foraging
habitat provided by grassland- .and open coastal sage scrub-.
Significant raptor species found here are black -shouldered kite,
Cooper's hawk, sharp -shinned hawk, marsh hawk, red=shouldered
hawk, prairie. falcon, merlin, American kestrel, barn owl, _-and
possibly American peregrine falcon.
The integrity of this canyon as a habitat area is high and it
represents- one of the most important biological features .of the
San Joaquin Hills.
Management
Considerations:' This area should be managed so as to prevent any loss of existing
riparian and oak woodland resources and to minimize the loss of
other resources, including grassland and coastal sage scrub.
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These goals should. be met by preserving existing riparian and
oak woodland vegetation and by retaining large, interconnected
areas of contiguous grassland and coastal sage scrub vegetation.
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Area of Moderate Significance #15
Limestone Canyon Buffer
Classification: Buffer -area.
Description: This area represents a "buffer strip", generally' following the
watershed boundary delineating the - adjacent area of high
significance. Occasionally, the strip also follows. a tributary
drainage, or minor ridgeline in order to cross the canyon.
Mostly, the buffer strip. is 300 feet wide. However,. the strip is
wider in some areas to include broader ridgelines and/or relatively
small stands of native vegetation which enhance the area
buffering capacity.
The native character of this area is often diminished significantly.
However, buffers are an integral part of avoiding the impacts of
future development at the edge of areas of high significance from
"spilling over" into important resources.
Management
Considerations: Management of thisarea- should focus on the goal of minimizing
the loss of the buffering function. This should be accomplished
through the retention. of -'a portion of the buffer area in its natural
condition. (Note: The majority, of resources within this area are
outside the City'.s sphere of influence).
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Area of Moderate Significance #16
Bee and Round Canyons Buffer
Classification: Buffer area.
Description: This area represents a "buffer .strip", generally following the
watershed boundary delineating. the adjacent area of high
significance. Occasionally, the strip also follows a tributary
drainage, or minor ridgeline in order tocross the canyon.
Mostly, the buffer, strip is 300 feet wide. However, the strip is
wider in- some areas to include broader.ridgelines and/or relatively
small stands of native vegetation which enhance the area
buffering capacity.
The native character of this area is often diminished significantly.
However, buffers are an integral part of avoiding the impacts of
future development at the edge of areas of. high significance from
"spilling over" into important resources.
Management
Considerations: Management of this area should focus on the goal of minimizing
the loss of the buffering function. This should be accomplished
through the retention of a portion of the buffer area in its natural
condition.
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Area of Moderate Significance- #17
Agua Chinon Wash
Classification: Buffer area..
Locally significant stands of native vegetation.
Link between habitat areas- of high significance and locally,
significant habitats.
Description: This area encompasses stands of coastal sage scrub and scattered
oak trees which are significant within their local context. The
area also abuts an area of high significance. and, therefore, -serves
as a buffer area. Generally, the area has retained most of its
native character despite several unimproved, dirt roads and on-
going grazing activities. .
The physical features and native or- naturalized- vegetation present
represent marginal habitat areas in comparison to habitats of high
significance within the study area. Nevertheless,.a-relatively full
complement of wildlife characteristic of .coastal sage scrub and.
introduced grassland are present, including red -shouldered hawk,
American kestrel, bam owl, black -tailed gnatcatcher, cactus wren,
hairy woodpecker, Bewick's wren, loggerhead shrike,- and coast
horned lizard, all of which are sensitive species. Several species
less tolerant of human disturbances .as well as those species
requiring woodland or riparian habitat are absent, however.
In addition to the locally significant habitats, this area also serves
as a buffer to an adjacent- area of high significance. As such, it is
an integral part of regional resource management by providing the
opportunity to prevent the `impacts. of future nearby developments
from "spilling over" into highly important resource areas.
Management
Considerations: The goal for managing this area should be to minimize the loss of
existing resource values. This should be accomplished through
the retention of a portion of the area in its existing condition as
natural open space.
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Area of Moderate Significance #18
Borrego Canyon Buffer
Classification: Buffer area.
Link between habitat areas of high significance and locally
significant habitats.
Description: This area represents a "buffer, strip," gendrally following the
watershed. boundary delineating the adjacent area of high
significance. Occasionally, the strip also follows a tributary
drainage, or minor ridgeline in order to cross the canyon.
Mostly; the buffer strip is. 300 feet wide. However,- the 'strip is
wider in some areas to include broader ridgelines and/or relatively
small stands of native vegetation which, enhance the area
buffering capacity and are enhanced by their proximity to Borrego
Canyon, Agua Chinon and the Sinks.
The native character of this area is often diminished significantly.
However, buffers are, an integral part of avoiding the impacts of
future development at the- edge of areas of high -significance from
"spilling over into important resources.
Management
Considerations: Management of this- area should focus on' the goal of minimizing
the loss of the buffering function: This should be accomplished
through the retention of a portion of the buffer area in its
naturalized condition.
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Area of Moderate Significance #19
Rattlesnake Reservoir
Classification: Open water/shoreline with local values as waterfowl habitat:
Description: This area includes a body of man-made, impounded water- devoid
of significant shoreline or backwater vegetation. The shoreline is
not intensely used or developed -by, humans, and disturbances to
the area are limited.
The availability of open water represents an, opportunity for
waterfowl habitat. Several species of -waterfowl -and other water
birds use this area as resting habitat during the fall and spring
migration periods. During .these periods. and the winter- months,
fairly, large numbers of birds use the reservoir, including western
grebe and canvasback which -are sensitive species.
The moderate importance of . this area: is derived primarily from
the overall lack of open water habitat in general within the study
area and region.
Management
Considerations: Minimized loss of resource value should be the management goal
-for this area. This should be accomplished by. retaining this
resource in -its entirety, or nearly so, in- its existing condition as an
open space feature.
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Area of Moderate Significance #20
Siphon Reservoir
Classification: Open water/shoreline with local values as waterfowl habitat:
Description: This area includes a -body of man-made, impounded water devoid
of significant, shoreline or,.backwater vegetation. The shoreline is
not intensely used ' or developed, however, and on -going
disturbances to the area are limited.
The availability of open. water represents an opportunity for
waterfowl habitat. Several species of waterfowl and other water
birds -use this area as resting habitat during- the fall and spring
migration periods. During these periods .and the winter months,
fairly large numbers of birds use the reservoir; including western
grebe and canvasback which are sensitive species.
The moderate importance of this area is: derived primarily from
the overall lack of open water habitat in general within the study
area and region.
Management
Considerations: Minimized loss of resource value should be the management goal
for this area. This should be accomplished by retaining this
resource in its entirety; or nearly so,: in its existing condition as an
open space feature.
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Area of Moderate Significance #21
Lambert Reservoir
Classification: Open water/shoreline-with local',values as waterfowl habitat.
Description: This area includes a body of man-made, impounded water devoid
of significant shoreline or backwater vegetation. The shoreline is
not intensely used or developed-, however, and - on -going
disturbances to the area are limited.
The availability, of open water represents an opportunity for
waterfowl habitat. Several species of waterfowl and other water
birds use this area as resting habitat during the fall and spring
migration periods. During these periods and the winter months,
fairly large numbers of birds use the reservoir, including wester-n
grebe and canvasback which are sensitive species.
The moderate importance of this area is derived primarily from
the overall lack of open water habitat in general within the study
area and region.
Management
Considerations: Minimized loss of resource value should be the- management goal
for this area. This should be accomplished by retaining this
resource in its entirety, or nearly so, in its .existing condition as an
open space feature.
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Area of Moderate Significance #22
San Diego Creek - Downstream Reach
Classification: Locally significant freshwater marsh habitats
Description: This stretch of San Diego _Creek ptovides an effective wetland
corridor between the San Joaquin freshwater marsh and Upper
Newport Bay.. This .area is an. -improved flood control and is
completely altered from its native condition. It is a soft, bottom
channel, however, and considerable wetland vegetation
reestablishes itself almost immediately after channel maintenance.
Particularly during the winter months when large numbers of
migratory waterfowl and shorebirds are in the area, this corridor, is
intensely used. Some species of birds- also use the channel as a
foraging area. Some of these are sensitive, including mountain
plover, snowy plover, long -billed curlew, and short -billed
dowitcher.
Management
Considerations: This should be managed so as to minimize any loss of resource
value: Maintenance should not preclude the reestablishment of a.
wetland character to the area. '(Note: The San Diego Greek
Channel along this reach is owned and maintained by the County
of Orange and under.their jurisdiction).
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Area -of Moderate Significance #23
Woodbridge Lakes
Classification: Open water/shoreline with local values as waterfowl habitat.
Description: This area includes two bodies of .man-made, impounded water
devoid of significant shoreline or backwater vegetation: The
shoreline is not intensely used or developed.
The availability of -open water- represents an opportunity for
waterfowl habitat. Several species. of waterfowl 'and other water
birds use this area as resting habitat during the fall and spring
migration periods. During these periods and the winter months, .
fairly large numbers of birds use the lakes, including western
grebe and canvasback which are sensitive species. .
The moderate importance of this area is derived primarily from
the. overall -lack of open water habitat in general within the.study
area and region.
Management
Considerations: Minimized loss of resource value should be the management goal
for- this area. This should 'be' accomplished by,, retaining this
resource in its entirety,:or nearly so, in its existing condition as an
open space feature.
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Area of Moderate Significance #24
San Diego -Creek Buffer
Classification: Buffer area.
Descriptions This area consists of a thin strip, approximately 300 feet wide,
representing a setback from the edge of an area :of , high
significance. Generally, the buffer area is extensively altered
from its native conditions by agricultural use or -clearing and
native vegetation is generally lacking.
The importance of this area lies in its capacity to prevent future
development impacts from "spilling over' and affecting 'resources
of high significance.
Management
Considerations: Management of this area should focus on the goal of minimizing
the loss. of the buffering function. This should be accomplished
through the retention of the area in -extremely low intensity uses
with -minimal development.,
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Area of Moderate Significance 425
San Diego Creek - Irvine Center Reach
Classification: Locally significant riparian habitats.
Description: This relatively short reach of San. Diego Creek located within
Irvine Center exhibits a moderately high degree of disturbance
which has resulted in the loss of considerable native riparian
vegetation from this area. As a consequence, this area is not as
significant as the reaches of San Diego Creek both upstream and
downstream of Irvine'Center.
This area does, however, possess enough native vegetation and
native riparian character to- make it useful, as a link between .the
areas of high significance upstream and downstream Not only is
this area a valuable means of interaction between upstream and
downstream areas; it also has the :potential to restore itself to a
level of high significance by the growth and reestablishment of
native riparian vegetation given enough time.
Some of the wildlife found here are sensitive. These include
yellow warbler and Bewick's wren.
Management
Considerations: This area should be managed so as- to minimize the loss of
resource value by the retention of this area in entirety, or nearly
so, as natural open space.
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Area of Moderate Significance #26
Sand Canyon Wash Buffer
Classification: Buffer area.
Description: This area consists of a =thin strip, approximately 300 feet- wide,
representing a setback from the edge of an area of high_
significance. Generally, the buffer area is extensively altered
from its native conditions by agricultural use or clearing and
native vegetation is generally lacking.
The importance of this area lies in its capacity to prevent future
development impacts from "spilling over". and affecting resources
of high significance.
Management
Considerations: Management of this area should focus, on the goal of minimizing
the loss of the buffering function. This should be accomplished
through the retention of the area in ' extremely low intensity uses
with minimal development.
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Area of High Significance #27
Laguna Reservoir
Classification: Open water/shoreline with regional values as waterfowl habitat.
Rare/endangered/unique species
Description: This area includes a body, of man -made, -impounded water devoid
of significant shoreline or backwater vegetation. 'The shoreline is
not intensely used' or developed, however, and on -going
disturbances to the area are limited.
The availability of open water represents an opportunity for
waterfowl habitat. Several species of waterfowl and other water
birds use this area as testing habitat during -the fall and spring
migration periods. During these periods and the winter months,
fairly large numbers of birds use the reservoir, including western
grebe and canvasback which are sensitive species. Also
noteworthy, as many as 150 Canada- geese have been recently
counted on the reservoir and the surrounding slopes... .
The importance of this area is derived primarily from the overall
lack of open water habitat in general within the study area and
region.
Management
Considerations: The management goal for -this - area should 'be no net loss of in -
kind resource value, while minimizing the loss of existing
resource values. Preservation is the preferred objective; however,
restoration and/or enhancement of remaining habitat following
any unavoidable loss of existing resource base is acceptable.
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Area of Moderate Significance ##28
Bonita Reservoir Buffer
Classification: Buffer area.
Description: This area consists of a thin strip, approximately 300 feet wide,.
representing a setback from 'the edge of an area of high
significance. Generally, the buffer area -is extensively, altered
from its native conditions by agricultural use - or clearing -and
native vegetation is generally lacking.
Management
Considerations:
The importance of this area lies in _its capacity to prevent future
development impacts from "spilling over." and affecting resources
of high 'significance.
Management of this area should focus on the goal of minimizing the loss of the buffering function_. -This should be accomplished
through the retention of the area in extremely low intensity uses
with minimal development.-
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0 Area of Moderate Significance #29
Sand Canyon Reservoir Buffer
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Classification: Buffer area.
Description: This area consists of a thin strip, approximately 300 feet wide,
representing a setback from the edge of an area of high
significance. Generally, the buffer area is extensively altered
from its native conditions by agricultural use or clearing and
native vegetation is generally lacking.
The importance of this area lies in its- capacity to prevent future
development impacts from "spilling over" and'affecting resources
of high significance.
Management
Considerations: Management of this area should focus on the goal of minimizing
the loss of the buffering function. This should be accomplished
through the -retention of the area in extremely low intensity.uses
with minimal development..
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Area of Moderate Significance #30
William R. Mason Regional Park Lakes
-Classification: Open water/shoreline with local values as waterfowl habitat.
Description: This. area includes two bodies of man-made, impounded. water
devoid of significant shoreline or backwater vegetation. The
shoreline is not intensely used .or developed.
The availability of open water represents- an opportunity for
waterfowl habitat. Several species of waterfowl and other water
birds use this area as resting habitat during the fall and spring
migration periods. During these periods and the winter months,
fairly large numbers of birds use the lakes, including western
grebe and canvasback which are sensitive species.
The moderate importance of this area is derived ,primarily from
-the overall lack -of open water -habitat in general within the study
area and region.
Management
Considerations: Minimized loss of resource value should be, the management goal
for this area. This should be accomplished by retaining this
resource in its entirety, or nearly so, in. its existing condition as an
open space feature. (Note: These lakes are under the jurisdiction
of the County of Orange).
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Area of Moderate Significance #31 .
Shady and Bommer Canyon Buffers
Classification: Buffer area.
Description: This area represents a "buffer strip", -generally following the
watershed boundary. delineating the adjacent .area. . of high
significance. Occasionally, the strip also .follows a tributary
drainage, or minor ridgeline in order to cross the canyon.
Mostly, the buffer strip is 300, feet wide. However, the strip is
wider in some areas to include broader ridgelines and/or relatively
small stands � of native vegetation which enhance the area
buffering capacity.
The native charactdr of this area is often diminished significantly.
However, buffers are an integral. part of, avoiding the .impacts of
future development at -the -edge of 'areas of high significance from
"spilling over" into important resources.
Management
Considerations: Management. of this area should focus on the goal of minimizing
the loss of -the buffering function. This should be accomplished
through the retention of a portion of the buffer area in its natural
condition.
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Area of Moderate Significance #32
Shady Canyon Tributary
Classification: Buffer area.
Locally significant stands, of native vegetation.
Description: This area encompasses stands of coastal sage -scrub and scattered
oak trees which are significant within their. local context. The
area also abuts an area of'highsignificance and`, therefore, serves
as -a buffer area. Generally; -the area -has retained most of its
native character despite several, unimproved, dirt roads and on-
going grazing activities.
The physical features and native or naturalized vegetation present
represent marginal habitat areas in comparison to habitats of.high
significance -within the study area. Nevertheless, a relatively full
complement of wildlife characteristic of coastal sage scrub and
introduced grassland are present, including red -shouldered., hawk,
American kestrel; barn owl,, black -tailed gnatcatcher; cactus wren,
hairy woodpecker, Bewick's wren, loggerhead shrike,, and. coast
horned lizard, all of which are, sensitive species. Several species
less tolerant of human disturbances as well as : those species
requiring woodland or riparian habitat are absent.
In addition to the locally significant habitats, this _area also serves
as a buffer to an adjacent area of high significance.. As such, it is
an integral part of regional resource management by providing the
opportunity to prevent the impacts of future' nearby developments
from "spilling over" into highly important resource. areas.
Management
Considerations: The goal for managing this area should be to minimize the loss, of
existing resource values. This should be accomplished, through
the retention of a portion of the area in its naturalized condition' as
natural open space.
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Area of Moderate Significance #33
Eucalyptus Wind Breaks
Classification: Locally significant vegetation.
Description:. This area actually ' consists of .numerous sub- areas- representing
eucalyptus wind breaks. These wind .breaks are well developed
and visually dominate the landscape. In some cases -these wind
breaks have been extensively trimmed and thinned, presumably,
for reasons of public health and safety. Many remain in their
unaltered condition.
While not important in strict biological terms, these windbreaks. .
are reflective of the area's 'agrarian heritage and have' a cultural
significance. In addition, they, serve a. .moderately important
ecological function in that several species of raptorial, birds use
these as roosting sites. included among these are the red tailed
hawk, American kestrel, black -shouldered kite, and turkey
vulture.
Management
Considerations: These resources should be managed so as to retain their existing
cultural value. This should be accomplished by continuing to
incorporate these areas into the- landscape of developed areas. It
is preferred, however, that required maintenance be minimized by
the use of setbacks, from roads and structures, to reduce public
health and safety hazards. This is in :contrast to, current practices
of extensive pruning which significantly diminishes the value of
these resources.
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Area of Moderate Significance #34
Sand Canyon Road Oak Trees
Classification: Locally significant vegetation.
Description: This area consists of the oak trees lining Old Laguna Road- and
both sides rof Sand Canyon Road- between I-5_ and I-465. In
general, these trees are of horticultural origin and a number of
them are specimen.quality.
While not important in strict biological terms,, -these. trees are
reflective of the area's heritage; and thus have a cultural
significance.
Management
Considerations: These resources should be managed so as 'to retain their existing
cultural value. This should be accomplished by incorporating
these trees into the development for the area. It is preferred that
maintenance be minimized by the use of setbacks from roads and
structures.
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Area of High Significance #351
Canada Geese Foraging Area -
Classification: Rare, Endangered and Unique Species Habitat.
-Description: This. area, encompassing the northern flank of Quail Ridge. and is:_
a key component of the habitat for the wintering population of
Canada geese at Sand Canyon Reservoir. This large population
of geese is a regionally .significant wildlife resource found
nowhere else in Orange County.. While the reservoir ,itself serves
as the resting and night habitat for the winter population of as
many as 3,000 geese, this area serves as the foraging and daylight
habitat for these birds. Early every morning of their winter stay,
these birds Ieave the reservoir and, travel the short distance to this
area and forage until the late evening, then return to the reservoir
This area is critical to the geese wintering habitat. Without this
forage habitat, it is .not known whether .the geese would continue
to overwinter in the study area. At a minimum, the loss of this
area would represent. a serious interruption to 'the established
behavior of the population found here.
Management
Considerations: This resource area, due to the unknown - consequences of
disturbance or alteration should be preserved with no loss of
existing resource. value.
. Designation of this area is. based upon preliminary information from a study
currently underway. The description found here, and the area boundaries shown on
the Biotic Resources map are, therefore; subject to- change pending the conclusion of
the study.
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APPENDIX G
MITIGATION PROGRAM
•
CONTENTS
I INTRODUCTION .. . ..... ......... . .............. G-1
II APPROACH.................... .. ........... G-2
III ' STUDY LEVIITATIONS ...................... ... G-4
IV EXISTING PRACTICES AND PROCEDURES ................ G-5
V MITIGATION PLANNING GOALS ........ ........... : G-8
VI RVIPLEMENTATING ACTIONS .... ...... ......... 0-10
VII -REFERENCES .................................. G-19
APPENDICES
G-I Summary of Conservation and Open Space Goals, Objectives and Implementing
Actions Pertaining to Biological Resources
G-II Summary of Hillside Development Manual Policies Relating to Biological
Resources.
G-III Resoultion 81-7, Eucalyptus Windrow Preservation Policy
•
INTRODUCTION.
Theinventory and analysis of biological resources found within the preceding sections. of
this report broadly accomplished two tasks:, 1) The determination and development of
evaluation criteria with which to define various levels of ecological
significance/sensitivity; and 2) the application of these criteria to the study area in order to
locate and map significant/sensitive biological resources which represent potential
constraints to. development.
This study is intended to -provide information and planning ,guidelines fundamental to the
management of these sensitive and significant biological resources. It -provides specific
mitigation measures. by which biological resources can be protected in light of anticipated
impacts from various types and intensities of development. In addressing these measures,,
this report: 1) briefly reviews practices at the local, state -and federal levels; 1) suggests
basic mitigation planning goals and discusses the rationale for these; and 3) makes
recommendations for appropriate mitigative actions and their implementation.
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APPROACH
-As in the case of determining the level of resource significance itself, the question of what
constitutes appropriate mitigation is a difficult one to answer. More often. than not local,
state and federal agencies are not consistent in either the type of resources protected or. the
-manner and degree to which resources are protected and managed.
For many of the factors customarily, considered in land use planning, the intent of
mitigation is readily known as the result of laws, codes and ordinances written specifically
to protect the public from health and safety hazards. This is not, however, the case with
biological resources. . Rather than being a basic determination founded on legal
requirements and sound engineering principles, the mitigation of impacts to, biological
resources has largely been a . subjective matter based on individual experience and
interpretation. Although some related biological resources are addressed in terms of their.
protection and management by laws, codes and .policies, they are limited to legally
protected rare and endangered - species, riparian habitats,' wetlands and certain other
resources of aesthetic/cultural value, such as eucalyptus windrows.
The lack of a broader program to conserve and protect biological resources has been a
fundamental problem in managing ecological systems. Too often, this problem has
resulted in piecemeal attempts at resource management and the loss of overall resource
integrity. � What -is needed is a program which will lead to the management of the full
spectrum of biological resources on a consistent basis. The central element and strength
Of such a program should be that it is broad enough to encompass all resources types and
therefore allow a regional application, yet specific enough to provide meaningful
guidelines to planners and decision -makers on a local basis.
The inventory and analysis phase of the MEA identified a limited number of mitigation
guidelines, policies and requirements for those specific resource types now being
protected and managed by local, state and federal agencies. In' addition_to these, the City
of Irvine General Plan Conservation and Open Space Element, and the Hillside
Development Manual identified broader based objectives,. guidelines and implementing
actions for biological resource.protection. Still, the necessary specifies are not provided to
guide planners and decision -makers on a consistent, regionwide basis.
G-2
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The approach to developing this mitigation program was intended. to close the gap
between general objectives and guidelines, .and their specific implementation. Whereas,
the existing City .programs and plans were used as,. the basis for this program, the
mitigations contained herein are intended to specify, as much as possible, exactly how the
City programs and plans should be implemented,, if they are to be effective 'in meeting
established conservation and open space goals and objectives: Iii order to' achieve this
intent, it was necessary to elaborate, expand.upon and add to the existing programs, and
plans, information obtained from scientific reports, state- and -federal programs, the
author's experience and persons consulted.
G-3
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III
STUDY LIMITATIONS
This study represents a first level mitigation program. It is intended to. provide
management guidelines for use in the City's project planning. and review process..
Whereas, these guidelines are often fairly, speck in their description, they are not
intended to be applied so strictly and rigidly so as to preclude the reasonable and balanced
development of land. Rather, the findings presented above should be , applied and
evaluated on a site specific basis through further study. Furthermore, this analysis is not
static. As additional information becomes available through research on resource
management -techniques, the findings contained herein should be refined and updated.
G-4
EXISTING -PRACTICES AND -PROCEDURES
Existing practices and procedures for the mitigation of adverse impacts to biological
resources are generally deficient and ineffective- in providing adequate resource
management and protection within the City. Primarily, this is,due.to.a lack of consistency
among the various levels. of government in their regulation and, more importantly, a lack,
of protection for the full range of resources that occur within the City.
At the federal level, protection of biological resources is provided principally by the
Federal Endangered Species Act of 1973, the Clean Water Act (Section 404) of 1977, and
the National Environmental Policy Act. The first pieceof legislation affords protection to
individual species designated as either "Endangered" or "Threatened!'. and has the U.S.
Department of the Interior, Fish and Wildlife Service as its. implementing authority. In
addition to providing- protection -for a very limited number, of species only, the Act in its
literal interpretation pertains only to projects which require some -type of action by a
federal agency (i.e., funding, permit approval, sponsorship).
The second piece of legislation provides protection for major riparian wetland; aquatic and
marine environments. Although the U.S. Department of Defense,. Army Corps of
Engineers is the implementing agency for this Act, the U.S. Fish and Wildlife Service is
the advising authority to the Corps in matters 'dealing specifically with biological
resources. Here again, the resources given protection are very -narrow In -scope.
The third piece of legislation is considerably broader in scope. It gives the U.S. Fish and
Wildlife Service review authority for all federal projects. During the review process the
Service makes recommendations for the mitigation of impacts to biological resources.
The Service recently adopted a mitigation policy which includes a standard and consistent
tool for this purpose (Federal Register Vol. 46, No. 55, January 1981). � However,, it is
applied to federal projects only and is not used for other public and private projects which
make up the majority of those within the City of Irvine.
A similar situation exists at the sate level. There are two primary pieces of legislation
which specifically apply to biological resources. These are the California Endangered
Species Act of 1969 and the California Fish and Game Code, Sections 1600, et. seq. Both
laws are implemented by the California Resources Agency, Department of Fish and
• Game. Like the Federal Endangered Species Act, the California Endangered Species Act
G-5
pertains to a limited number of plant and wildlife species which meet criteria of
"'Endangered!' or "Rare." Here again, the Act pertains only to public projects where there
is direct public.agency involvement. Sections 1601-6 of the Fish and.Game Code'applies
to both private and public projects; however, it remains narrow in the .range of resources
protected, applying only to riparian, aquatic and wetland habitats within the high water
mark of major rivers, lakes and streams from which wildlife and fish .derive significant
benefit. In addition, a third_piece of legislation, the California Environmental Quality Act,
gives 'the California Department of Fish and Game -the opportunity to review and,
comment upon public and private projects. While the, Department can make
recommendations for effective and comprehensive mitigation, there may not be the means
to implement these- at the local level. Actions that are taken are usually reactionary and
too late to be fully effective.
: Within:the purview of the City, there are existing programs and plans which provide the
basis for the protection of biological resources. First, there is the ability of the City to
exact mitigation measures ' during the environmental review process pursuant to the
California Environmental Quality Act. Historically, the problem here- has been that
specific measures have not been incorporated into projects until late in the- design and -
implementation phase. Additionally, such measures do not necessarily reflect long range,
region -wide resource management goals effectively.
Second; the City's General Plan Conservation and Open Space Element provides the City
with the necessary direction towards the preservation and enhancement of the City's
natural environment. It follows from the many functions of open space, that this element
is strongly related to other elements in the general plan. The Conservation and Open
Space Element is. important in providing input into the land use, circulation, and urban,
design elements. A summary of the goals, objectives, and implementing actions of the
Conservation and Open Space Element which apply to biological resources are
summarized in Appendix G-I.
Third, the City has a Hillside Development Manual which sets forth fairly specific
policies as' well as -the timing for their implementation with regard to biological resources.
These policies are outlined in Appendix G-II.
Fourth, the City adopted Resolution 1036 (see Appendix G-III, the Eucalyptus Windrow
Preservation Policy which serves to protect and preserve the extensive network of
eucalyptus windrows ,existing in the City.
From the discussion and information presented above, it is clear that the :federal, state and
City have developed- and established a sound foundation for the conservation and
• preservation of biological resources. In fact, at the City- level, there exists programs to
preserve not only the narrow range of rare, endangered and threatened biological
G-6
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resources, but a more comprehensive range of .resources as well. Despite past efforts,
however,, there remains a general. lack of specific implementation actions with which to
implement and monitor the effectiveness of conservation and preservation practices.
As discussed in the approach to this study, the measures and actions contained herein are
intended. not to change but to augment existing programs. Through. the more specific -
measures and actions provided in this report, 'it is felt that the City can more effectively
and consistently achieve the goals and objectives they have establish for. the protection of
its natural biological environment.
G-7
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MA
MITIGATION PLANNING GOALS
The criteria used to define biological sensitivity in the first phase of the City MEA were
developed as an outgrowth of the overall goal of preserving the existing diversity of
biological resources found within the City and -its sphere of influence. This is based on
the premise that stability of ecosystems is directly .related to diversity. The .overall
mitigation planning goal for this phase is the same, that is the preservation of diversity.
Included areconsiderations for both the variety of vegetation and wildlife resources -
existing in the City and its sphere and, as much as. possible, their present distribution and
relative abundance. The overall goal is not, to merely preserve one or - two of each type,
but to preserve as many of each kind as is possible: Within the overall goal of preserving
biological- diversity, more specific objectives are outlined for individual .resource types.
Conceptually, these objectives were adopted from the US. Fish and Wildlife Service
Mitigation Policy mentioned earlier. That policy establishes guidance -for. U.S. Fish and,
Wildlife Service personnel involved in making recommendations to protect or conserve
fish and wildlife resources. Explicitly, the policy is used to: 1) ensure consistent- and
effective recommendations; 2) allow government agencies and private developers to
anticipate mitigation recommendations and plan for -them early; 3) reduce agency and
developer conflicts as well as project delays.
The fundamental principle which guided the application of these objectives .to the City
MEA is that. the degree of mitigation correspond to the scarcity of the resource .at risk.
Within the high, moderate and low rating, system for biological sensitivity three mitigation
objectives based on levels of decreasing sensitivity were identified. These were:
1. No loss of existing resource value - intended to protect resources which are unique
and/or irreplaceable in the region. (The term "existing resource value" refers to
the nature, extent and condition of the resource, as it exists.)
2. No net loss of in -kind resource value (while minimizing loss of existing resource
value) - intended to protect resources which are relatively scarce, or are becoming
scarce on a regional basis. (The term "in -kind" means "the same as, or similar
to.")
G-8
3. Minimize loss of resource value - intended. to, protect resources which are
relatively abundant, but are important, or are of moderate value to, regional
ecosystems. (Here "resource value" means "of equal importance or value, but not
necessarily the same as.")
Each resource type and their corresponding ,objectives, are listed in the following section.
Included also are specific implementation actions designed to augment those contained in
the City Conservation and Open Space Element.
As noted, the biological mitigation program should be applied, as early in the planning and
review process as is possible. The program should not react to a ,particular proposed plan;
rather, the plan should be responsive to the mitigation program. The. two- primary
determinants of exactly when the application should take place are the types of:resource at
risk, and the intensity of land use proposed. For example, the incorporation of mitigation
measures. for buffer areas under conditions of low intensity. development need not occur
until later in the implementation phases of project .planning since- both the'recommended
action and listing of development areas remain flexible up to this point. On the other
hand, the successful incorporation of recommended actions . to - protect the habitat of an
endangered species under conditions of high intensity development depends on their early.
input to the planning phase. - That way, they are considered - early and . planned . around
throughout the planning and implementation process.
It is suggested that the biological mitigation program be applied as part of the normal City
environmental review process. Using these procedures, the applicant would be made
aware of constraints and recommended actions at the time of. pre -filing, or, "the EIR or
mitigated Negative Declaration pre -preparation discussions.. The applicant would then be
responsible for incorporating mitigations into his project and the, environmental
documentation prior to approval and certification,. respectively.
Further, it is suggested that the applicant include an open space management plan as part
of the project plansubmittal. This plan should detail, in graphic and narrative formats, -
how the project will incorporate and accomplish themitigative action required of the
project. This need not be a lengthy document, but should contain enough information to
clearly demonstrate the project's responsiveness and key, features related to the
management of biological resources as directed by the mitigation program. Also, it
should be prepared with the assistance or input of a qualified biologist, if necessary, either
directly or indirectly (such as through the EIR process). Guidelines for the preparation of
open space management plans are presented in Appendix G-IV.
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VI
IMPLEMENTING ACTIONS
Introduction
Each area of moderate -or high significance within the study area has .been identified by
name and number and discussed in preceding sections of this report.. Within the
description of each area, the nature or type of resources of significance contained in that
area were identified (ie, buffer area, regionally significant riparian habitat, etc.).
Recommended mitigative actions for each of these resource types is outlined beginning on -
the following page. Because most areas contain more than one. resource type, more than
one mitigative action will apply to each area in most cases. In these situations, it is the
most strict of the actions which should be.considered first.
For example, if an area contains a regionally significant -oak woodland and a
woodland/brushland/grassland ecotone, the recommended actions for mitigation would be -
to preserve the woodland in place and retain 60 percent of the, ecotone, respectively. In
this case, the woodland should be first delineated and designated for preservation in. its
entirely, and areas of brushland and grassland .habitats should .then 'be. added to the
woodland to make up the 60 percent of the total to be retained.
With regard to the specific recommended actions; percentages -and/or minimum areas of
resource types to be protected are often used. The reader should note that this attempt at
qualification is based on- -scientific study - where available. In most cases, however,
empirical data is just not available and the numbers used are the opinions of the. author
and other biologists consulted, based on their years of experience in the field. This: is not
pointed out to dilute or question the findings contained hereunder. Rather, it notifies the
reader as to the prudence and care with which significant biological resources should be
managed, protected and conserved.
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IlaLEMENTING ACTIONS BY RESOURCE TYPE
1 BUFFER AREA (Areas 15, 16. 17, 18.24, -26, 28, 29, 31-, 32)
Objective: Minimize loss of resource value (i.e., as buffer area).
Recommended Action: Retain 20 percent of area in -existing condition, preferably by
preserving natural open space adjacent to borders or areas possessing high sensitivity.
Where required, fuel modification zones employing -a graduated clearing approach may
make up a portion of the buffer zone. Recreation open space, agriculture and greenbelts -
may also be substituted as a portion of the zone however, dense tree and shrub plantings at
the edge of areas of high'sensitivity should be included. Overall this.* zone should provide
a 300-foot development setback from the edge of high ecological sensitivity areas.
2 LINK BETWEEN HABITAT AREAS. OF HIGH, SIGNIFICANCE AND
LOCALLY SIGNIFICANT HABITATS (Areas
Objective: Minimize loss of resource value. (i.e., as link).
Recommended Action: Retain 20 percent of area as natural open space in the form of a
network of contiguous corridors, preferably around :and along drainage courses.
Individual corridors to be retained in, natural condition must be no less than 100 feet wide
in order to be effective.
3 LOCALLY SIGNIFICANT RIPARIAN HABITATS (Area 25)
Objective: Minimize loss of resource value.
Recommended Action: Retain as part of open space in entirety, or nearly so. Also, it is
recommended. that the California Department of Fish and Game (DFG) be contacted to
determine if a 1601 notification should be filed (see California Fish and Game Code,
Sections 1601-1606).
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Note: Unless . 80 percent can be retained, preservation efforts will probably not be
worthwhile due to the typically small, isolated nature of these resources.
4 'LOCALLY SIGNIFICANT FRESHWATER MARSH HABITATS (Area 22)
Objective: Minimize loss of resource value.
Recommended Action: Retain in entirety, or nearly so, as natural open space. Also, it is
-recommended that the California Department of Fish and Game (DFG) be contacted to
determine if a 1601 notification should be filed (see California Fish and Game -Code,
Sections 1601-1606).
Note: Unless 80 percent can be retained, ,preservation efforts will ,probably not be
worthwhile due to the typically small, isolated nature of these resources.
5 LOCALLY SIGNIFICANT STANDS OF NATIVE VEGETATION/OTHER
VEGETATION (Areas 17, 32, 33. 34)
Objective: Minimize loss of resource value (i.e., as habitat).
Recommended Action: Retain 20 percent of areas 17 and 32 as -natural open space in the
form of a network of contiguous corridors, preferably around and along drainage courses.
Individual corridors to .be retained in natural condition must be no less than 100 feet wide
in order to be effective. Windrows located within agricultural areas, and the oak trees
lining Sand Canyon Avenue,'should be retained.for their aesthetic and cultural value in
accordance with established planning policies (see Appendixb-III).
6 OPEN WATER/SHORELINE .WITH LOCAL VALUES- AS WATERFOWL
HABITAT (Areas 19, 20, 21, 23, 30)
Recommended Action: Retain -in entirety, or nearly so, as natural open space: Also, it is
recommended that the California Department of Fish and Game (DFG) -be contacted to
determine. if a 1601 notification should be filed (see California Fish and Game -Code,
Sections 1601-1606).
Note: Unless at least 80 percent can be retained preservation efforts will probably not be
• worthwhile due to the typically small, isolated nature of these resources.
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7 RARE, ENDANGERED AND UNIQUE SPECIES HABITAT (Areas 6, 10, 11, 12,
Objective: No loss of existing resource value.
Recommended Action: Identify/delineate extent of existing -habitat area and preserve in
place as permanent open space.
Consult DFG, U.S Fish and Wildlife Service (USFWS), in accordance- with the intended
goals of the Federal Endangered Species Act of 1973 and California Endangered 'Species
Act of 1970, and other qualified biologists to determine -the need for additional species -
specific actions, such.as:
o Screening and setbacks from habitat areas,- as in the case of highly sensitive
wildlife species, to allow continued use of entire habitat available;.
o The use of fencing or other means of controlling access to habitat -areas; as in the
case of fragile flora or wildlife habitat'.
8 REGIONALLY SIGNIFICANT RIPARIAN HABITAT (Areas 5, 6, 7, 8, 9, 13, 14)-
Objective: No loss of exiting resource value.
Recommended Action: Prepare riparian preservation and . management plan to
identify/delineate extent of existing habitat and provide specific guidelines to preserve in
place as permanent open space.
Preparation of the plan should include consultation with DFG through, required
notification process (Sections 1601-1606, California Fish and Game Code) and the U.S.
Fish and Wildlife Service pursuant to the U.S. Army Corps of Engineers (COE) permit
process (Section 404, Clean Water Act), if applicable, to determine additional protective
actions, such as:
o Setbacks and edge screening of adjacent development to allow continued use of
entire habitat available by wildlife;
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0 o The use of fencing and other means of controlling access and disturbance to
maintain values;
o Diversions or control'of increased flood runoff from adjacent and upstream urban
developments to prevent the scouring of bottom and bank°vegetation; ,
_ o Maintenance of existing water supply for the continued support of habitats.
Note: In some -cases, these measure may not be adequate due to 'the presence of
irreplaceable flora or physical habitat features.
9 REGIONALLY SIGNIFICANT OAK WOODLAND/SAVANNAH (Areas 1. 2.3.4,
5 1• 3. 14)
Objective: No loss of exiting resource value.
Recommended Action: Prepare oak tree. preservation and management plan to
identify/delineate extent of existing. habitat and provide specific guidelines to preserve in
place as permanent open space.
Preparation of the plan should include consultation with DFG through required
notification process (Sections 1601-1.606, California Fish and -Game Code) and the U.S.,
Army Corps of Engineers (COE) permit process (Section 404, Clean Water Act), if
applicable, to determine additional protective actions,'such as:
o Setbacks and edge screening of adjacent :development. to allow continued use of
entire habitat available by wildlife;
o The use of fencing and other means of controlling access and" disturbance to
maintain values;
o Diversions or control of increased flood runoff from adjacent and upstream urban
developments -to prevent the scouring of bottom,and bank vegetation;
o Maintenance of existing water supply for the continued support of habitats.
Note: In some cases, these measures may not be adequate due to the presence of
irreplaceable flora or physical habitat features.
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10 REGIONALLY SIGNIFICANT FRESHWATER MARSH HABITAT (Areas 6, 7, 9)
Objective: No loss of exiting resource value.
Recommended Action: Prepare freshwater marsh preservation and management plan to
identify/delineate extent of existing habitat and -provide specific guidelines to preserve in
place as permanent open space. .
Preparation of the plan should include consultation with DFG through required
notification process (Sections 1601-1606, California Fish and Game Code) and the U.S.
Fish and Wildlife Service pursuant to the U.S. Army Corps of Engineers (COE) permit
process (Section 404, Clean Water Act), if applicable, to determine additional protective
actions, such as:
o Setbacks and edge screening of adjacent development to allow continued use of
entire habitat available by wildlife;
o The use of fencing and other means of controlling access and disturbance to
maintain values;
o Diversions or control of increased flood runoff from adjacent and upstream urban
developments to prevent the scouring of bottom and bank vegetation;
o Maintenance of existing water supply for the continued support of habitats.
Note: In some cases, these measures may not be adequate due to the presence of
irreplaceable flora or physical habitat features.
11 OPEN WATER/SHORELINE WITH REGIONAL SIGNIFICANCE AS
WATERFOWL HABITAT (Areas 6, 10, 27)
Objective: No --net loss of in -kind resource value (while minimizing loss of exiting
resource values).
Recommended Action: Prepare open water/shoreline habitat preservation and
management plan to identify/delineate extent of existing habitat and provide specific
guidelines to preserve in place as permanent open space.
Preparation of the plan should include consultation with DFG through required
• notification process (Sections 1601-1606, California Fish and Game Code) and the U.S.
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Fish and Wildlife Service pursuant to .the U.S. Army Corps of Engineers (COE) permit
process (Section 404, Clean Water Act), if applicable, to determine additional protective
actions, such as:
o Setbacks and edge screening of adjacent development to allow continued use of
entire habitat available by wildlife;
o The use - of fencing and other, means of controlling access and disturbance to
maintain values;
o Diversions or control of increased flood runoff from adjacent and upstream urban
developments to prevent the scouring of bottom and bank vegetation;
o. Maintenance of existing water supply for -the continued support of habitats.
Note: In some cases, these measures may not be adequate due to the presence of
irreplaceable flora or physical habitat features. While open water habitats are fairly easy
to accomplish, even within urban areas, they are- seldom of high value to most wildlife due
.to high intensity human use and manicured shorelines which preclude their use by many
sensitive species. To be effective, enhanced or restored habitats should be primarily
intended for wildlife, and any secondary uses should be consistent with this objective.
12 PRIME BIRD OF PREY FORAGING/WINTERING AREA (Areas 1, 13,14)
Objective: No net loss of in -kind resource value (while minimizing loss of existing
resource value).
Recommended Action: Preserve large blocks of grassland - (20 acres and greater). and
open brushland foraging area (50 ,percent of the site at ' a, minimum) as, permanent open
space. To achieve the maximum value, this area should be contiguous and -not broken up
by roads or scattered dwellings; therefore, clustering of development with interspersed
open space of. -the type described above is preferred. Where prime nesting/roosting sites
are also present, these areas should include the spatial buffer zone recommended for that
resource (see # 13,. below). Artificial clearing of areas to create forage may be used as
part of this action, providing revegetation with grasses and low, open brush species is
accomplished immediately following clearing activities.
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13 PRIME BIlZD OF PREY NESTING/ROOSTING AREAS. (Areas 1. CO. 14)
Objective: No loss of existing resource value.
Recommended Action: Identify/delineate prime oak/riparian woodland and cliff nesting
and roostings sites and preserve as permanent open space. In conjunction with-- # 12
above, establish a spatial buffer/feeding zone for a distance of 1/2 . mile around
nesting/roostings- sites, and preserve as permanent open space. If necessary, clear portions
of this area, especially in canyon bottoms, of dense brush to maximize its value as forage
for birds of prey (this could be done as part of fuel modification -procedures.). Use buffer
zone edge treatments to discourage or prohibit access to nesting- and roosting areas.
Methods up to and including fencing should be considered; natural. barriers, such as
rugged terrain and dense vegetation should also be taken into account. A qualified
biologist or DFG should be consulted if necessary on a site 5pectBc basis.
Note: Mitigative actions for this resource should be consistent/complimentary with the
action exercised for resource # 12, if also present.
14 MAJOR WILDLIFE MOVEMENT CORRIDOR (Areas 1, 4, 5, 13, 14)
Objective: Not net loss of in -kind resource value (while minimizing loss of -existing
resource value).
Recommended Action: Preserve vegetation along contiguous corridor in canyon bottoms.
Corridor should generally - . conform to native vegetation existing along drainages,
including riparian habitat, oak woodland and dense brush. Minimum width should be 300
feet, unless existing vegetation is narrower, in which case additional buffer areas should
be provided in the form of bordering greenbelt/recreation open space, areas. Fencing or
otherwise controlling access is not necessary, however, there should be no extensive
clearing of vegetation within the corridor. If clearing is required for road crossings fire
safety clearance, etc., landscape materials,. should be introduced for screening and/or
widening the corridor to retain the corridor's original value.
15 WOODLAND/BRUSHLAND/GRASSLAND ECOTONE (Areas 1, 2, 3, 4, 5, 13,
14)
Objective: No loss of existing resource value within. "core" oak/riparian woodland areas
while minimizing/limiting loss of remaining existing resource value.
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Recommended Action: Preserve 60 percent of brushland and grassland habitats,
according to the following guidelines:
o Retain in large (20 acres minimum), contiguous habitat configurations.
o Retain corridors/links of native vegetation between habitat enclaves.
o Include oak/riparian buffer zones as a portion of area preserved:
o Place lowest intensities of use, greenbelts,, recreation open space - adjacent to
preservation areas.
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all
REFERENCES
California Resource Agency, Department of Fish and Gave, California Fish and Game
Code, 1977.
California Resources Agency, Department of Fish and Game, California Endangered
Species Act of 1970, 1970.
California Resources -Agency Department of Fish and Game, California Fish and_ Wildlife
Plan; 1966.
City of Irvine, Environmental Review Matrix, City of Irvine; 1983
City of Irvine; Hillside Development Manual, City of Irvine, "1977.
City of Irvine,.General Plan Conservation and Open Space�Element, City of Irvine, 1985.
City -of Irvine, Resolution 1036, Eucalyptus Windrow Preservation Policy, City of Irvine,
1981.
EDAW, Inc., Master Environmental Assessment County of Orange: Phase I Constraints
Mapping and Analysis. Prepared for the County of Orange, Environmental
Agency, 1980.
LSA, Inc./Van Dell & Associates, Master Environmental Assessment County of Orange:
Phase II Mitigation Measures. Prepared for the County of .Orange, Environmental
Agency, 1982:
U.S Department of the Interior, Fish and Wildlife Service, U.S. Fish and Wildlife Service
Mitigation Policy. Federal Register, Vol. 46, No. 15, 1981.
U.S Department of Defense, Army Corps of Engineers, Clean Water Act of 1977, 1977.
U.S. Department of the Interior, Fish and Wildlife Service, Federal Endangered Species
Act of 1973, 1973.
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C�
U.S Department of Defense, Army Corps of Engineers, Clean Water Act of 1977, 1977.
U.S. Department of the Interior, Fish and Wildlife Service, Federal Endangered Species
Act of 1973, 1971
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APPENDIX G-I
SUMMARY OF CONSERVATION AND OPEN SPACE GOALS, OBJECTIVES AND
IMPLEMENTING ACTIONS PERTAINING TO BIOLOGICAL RESOURCES
GOAL L:
Maintain the natural environment as a major
element in the ,development -of the City.
Objective L-1:
Maintain designated natural areas
in their undeveloped state.
Implementing Actions:
a. 'Natural. vegetation should be maintained in areas where significant stands can be
identified. Particular attention shall be given to bottom canyon tree stands of
California Live Oak, Emeroy Oak, Scrub Oak, Sycamore, and Holly.
b. Windrows should remain an integral part of the open space system.
C. Landscape plantings should complement or enhance the native material and be _
continuously maintained.
d. Use native trees,. shrubs, and grasses with low maintenance costs.
e. Prohibit development and- intensive human use in areas which sustain rare or
endangered species, including migratory bird species and rare plant species:
f. Where possible and practicable, the appearance and ecology of certain existing
natural channels shall be studied to determine ' which channels, or portions
thereof, conservation measures shall be applied. Channels, or portions of
channels, delineated for preservation in the future shall not be altered in. any way
except for general maintenance to preserve.their natural amenities.
g. Require the maintenance of existing natural water sources in the design of
surrounding development.
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r. Building development should be located on sites which minimize- the need for
grading partly moving or the removal of native plant material (except -for fire
trails).
S. Any access roads or highways ' that must pass through hillside areas are to be
designed so as to not damage their ecological and/or aesthetic characters.
Objective L-2:
Develop a program of preservation, enhancement for educational or recreational
purposes, or development restraint of designated wildlife habitat.
Implementing Actions:
a. Preserve the San Joaquin Marsh in its existing condition, and allow development
to occur only as an. enhancement for its, role. as an environmental education and
research center. Study the possibility of increasing the size of the existing wildlife
preserve. Areas adjacent to the existing preserve located on either side of Campus
Drive may be appropriate to, be designated wildlife preserve if the proposed study
warrants such action.
b. Promote the designation of the area of the Santiago- Hills as the "Sinks" as a
regional wildlife preserve.
C. No development will be allowed except that designed to enhance the habitat in
designated wildlife habitat areas.
d. Inclusion areas shown in Figure L-1 (of the Conservation and Open Space
Element) will be preserved with no development except for hiking and equestrian
trails.
e. Development that occurs at the edge of -the inclusion areas will be designed in
such a manner as not to substantially alter the drainage pattern of surface water
runoff into the primary habitat area.
f. Areas designated for primary preservation in Figure L-I (of the Conservation and
Open Space Element) will be maintained without change from their existing
condition and development adjacent to these areas will be of the lowest density
possible.
g. Areas designated for enhancement for recreational and educational purposes will
• be more carefully analyzed and a plan for their development and use established
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for each area. Priority uses should be for environmental education areas, to be
used in conjunction with other community education 'and information programs.
h. Areas designated for preservation of wildlife habitat should be primarily managed
for their wildlife and open space values with recreation and park uses clearly a
subordinate and secondary activity. The use of hiking and equestrian trails should
constantly be monitored for their impact and viability as a compatible use with
wildlife habitat.
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APPENDIX G-II
SUMMARY OF HILLSIDE DEVELOPMENT MANUAL
POLICIES RELATING TO BIOLOGICAL RESOURCES'
1C. No development shall be -permitted within the main habitat portions of designated
wildlife habitats as defined by the City's General Plan. -
1D. Development shall preserve existing areas of vegetation identified as significant at
the. Planned Community Zoning level. Additionally, development shall attempt to
preserve other existing trees, riparian vegetation, native plant communities and
significant rock outcroppings within the context of the development plan.
1E. Development should be set back a minimum of 50' feet from existing lakes,
reservoirs and significant natural drainage courses identified at the Planned
Community zoning level, unless it is demonstrated that the environmental function
of the water- feature is not impaired and that -public access is not restricted.
3A. Development shall attempt to preserve and protect existing trees, riparian
vegetation and native plant communities within the context of the development
plan.
3B. New landscape materials introduced as transition plantings shall be used to
integrate the man-made and natural environments, to screen and soften the visual
impact of development- and to- provide privacy within existing adjacent
development. Landscape materials shall also provide diversity within the
developed areas. The City's "Plant Selection Guide"' shall be used in -considering
the appropriate plant materials. Temporary orpermanent irrigation systems will
be required only where necessary to sustain the plant materials selected.
3E. Landscape and irrigation plans shall be submitted for approval in accordance
with the provisions of the Hillside Development Overlay District.
4A. Areas adjacent to creeks and natural drainage swales shall- be kept as much as
practical in their natural state, consistent with the need to minimize flood and
erosion hazards. Adequate setbacks for development area, preferred alternative
to stream channelization in hillside areas. Open greenbelt swales are a preferred
alternative to undergrounding or open concrete lined channels.
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4B. Where channelization projects are found necessary., they should be part.of a larger
open space system, be landscaped to blend with the surroundings, and .include
trails. and linear parks along their banks as part of the overall open space -system.
SA. Access to special, endangered, rare or fragile plant -and animal habitats shall be
limited, with public access carefully managed. to prevent disruption of the area's
natural -values.
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APPENDIX G-III
EUCALYPTUS WINDROW PRESERVATION POLICY
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CITY COUNCIL RESOLUTION NO. 81-7'
A RESOLtTION OF THE CITY COUNCIL OF THE CITY OF IRVINE
RESCINDING AND SUPERSED= RESOLUTION 1036 ADO&`S1NG A
E[K'ALYPTUS WIMROW PRESERVATION POLICY.
MOMS,, the City of Irvine has- deemed trees to be an integral
part of the-City's fabric; and
WHEREAS,- soon after incorporation ordinances governing tree
removal were adopted; and .
WHEREAS, the City has recognized the significance of eucalyptus
windrows as cctmxmity design assets, and
WHEREAS, the City has required detailed eucalyptus tree reports
prior to development in areas containing windrows; and ,
WHEREAS, the City Council of the City of Irvine has appointed a
Eucalyptus Windrow Preservation C=mittee; and
WFUMAS, the Planning Commission has. requested staff to, examine .
the possibility of a more definitive policy on eucalyptus tree pre-
servation and removal in the City; and
WE LAMAS, staff has made such analysis; and
WHEREAS, staff recommends that a new eucalyptus windrow policy
designated as Exhibit A and attached hereto as a part of this -
Resolution be adopted; and
WHEREAS, -the Eucalyptus Windrow Preservation Committee has re-
viewed the staff -analysis and reccmrendations.
NOW, THEREFORE, THE CITY COUNCIL OF THE CITY OF IRVINE DOES HEREBY
RESOLVE AS FOLLOWS:
1. Resolution 1036 is hereby rescinded and superseded by this
Resolution 81-7.
2. That the City Council of the City of Irvine hereby does adopt
the eucalyptus windrow preservation policy designated as
Exhibit A.
Resolution No. 81-7
EXHIBIT A
EUCALYPTUS WINDROW POLICY
I. PURPOSE AND IN=
A. Eucalyptus windrows are a -unique -inheritance. It has been the
objective of the City to maintain eucalyptus windrows'as an integral
part of co mnuv ty design in Irvine. This intent has been carried
'out through. the policies. and standards established for existing
eucalyptus tree maintenance, preservationv re oval and replacement.
The maintenance of eucalyptus trees shall be in conformance with
accepted arborical standards and in accordance with budgetary
authorization.
B. Maintenance techniques for eucalyptus windrows in agricultural
operations are exempt from the provisions of the adopted City Council
policy due to the unique nature and function of the windrows in the
protection of agricultural crops., However, the removal, of these trees
shall -be in conformance -with Ordinance No. 67, which provides policies
for the preservation of trees on private and public property.
II. PRESERVATION AND RE4=1, PROCEDURE
A-. All existing eucalyptus trees shall be accurately surveyed and plotted
on subdivision maps and/or site plans.
B.. All applications for tree removal permits shall include the filing
-of an envircr w*al application and environmental•clearance prior to
permit approval in accordance with the City's CEUA procedures: -
C. If the developer proposes to remove any -eucalyptus trees within the
area of his development, an analysis of their.preservation or re-
moval including environmental clearance shall be determined at the'
subdivision map and/or site plan review, process. The Director of
Ccmrmnunity Development shall request the Tree Cmmittee to examine
eucalyptus trees and make re=mnendations regarding preservation
or -removal. These reccan*mdations shall be taken into consideration,
by the staff and be incorporated in the staff- analysis.. These
analyses shall be referred. to the Planning_Commission for their
approval Variance regarding preservation. or. re oval mayybe granted
by the Planning -Commission for the following cases:
1. That removal of eucalyptus trees will significantly improve
the utilization of the property and the developer has provided
satisfactory alternate landscaping.
2. That removal of eucalyptus trees will be for public benefits
such as but not limited to traffic or pedestrian safety,
utilities, drainage, walkways, recreation and other visual
amenities.
3. That "dead, dying and/or beyond repair" or infestation by pests,
infection by fungi and/or bacterial disease are given as
reason(s)-for the need to remove a eucalyptus tree, documentation
Resolution No. 81-7
•
of such conditions shall be provided to the Tree Cotmittee for review..
and verification prior to permit approval. In addition, evidence must
be provided that the condition of a tree is incurable.
D. All approved tree removals, trenching, pruning, and other maintenance
functions, shall be completed prior to grading. in a windrow easement.
E. Tree removal shall include the entire tree unless the Tree;Comtittee's
evaluation shows a reason to leave the stump.
F.. Eucalyptus tress that are approved for preservation at the subdiv-
ision arxi/or site plan review stage will require 'a tree reoval
permit for any individual tree removals. Such permit shall. be issued
.by the Director of Cam=dty Development upon receipt of recammendation
by the Tree Ccmmmittee.
III. MAINTENANCE.PROCURE
A. Eucalyptus windrows shall be maintained in a manner that is L cammpatible
with motor vehicles, pedestrians, bicycles and adjacent structures pro-
vided initial planning was in line with principles of tree preservation..
B. All. property owners shall be required to ,properly irrigate eucalyptus
windrows on a continuous basis with particular attention being paid
to the transition period.of•land develcpnent,between agricultural use
and development for nonagricultural purposes'. .Property owners. shall
insure that the trees stay in a good biological and aesthetic condition.
The irrigation system shall be compatible with the surrounding area.
The permanent irrigation systems shall be in accordance with the city Is
landscaping design policies.
C. All trees shall be selectively pruned to improve shape, and health.
Hazardous branches, weak limbs and questionable double trunks shall
be removed. The pruning shall be carried out with consideration
given to the potential for future growth.
D. Developers shall be required to irrigate, prune, treat, and maintain
existing trees and plant new ones .in such a way that -when the eucalyptus
windrows becamme City, association, 'or private' property the eucalyptus
trees will be in good biological condition upon acceptance. If
necessary* as determined by the -City Arborist,, trees must be treated
by surgery and/or with fertilizers, and other,chemicals. Such treatments
shall be carried out by the developers with inspections by the City
Arborist prior to final acceptance.
E. Prior to the start of pruning, a sample selection of trees
shall be pruned by the developer. These sample trees shall
be subject to inspection by the City Arborist to insure
adherence to recommended arboriculture practices.
Resolution No. 8L-7
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F. Pruning, prior to transfer of windrows to the City,'must be
done by developers -under specifications and inspection by the
City Arborist.
1. Remove dead or dying trees, stumps, and limbs or
multiple trunks.
2. Remove unsightly or poorly crotched limbs.
3. Thin out unsightly or interlacing growth.
4. Cut back out -of -scale limbs to bring tree into balance.
5. Cut back heavily. (pollard) where necessary to avoid
hazard.
6. Remove heavily leaning branches.
7. All cuts are to be made flush aria/or.in line with
proper arboricultural practices.
8. Remove sucker growth to a height of 101.
G. Soil preparation for replanting prior to transfer of -the
trees to City, association, or private owner must be done
by developers under specifications of and inspection' by
-_the City Arborist.
H. Prior to final acceptance of any windrow by the City", the Tree .
Committee shall" conduct a finial examination of the eucalyptus
trees to evaluate the developer's compliance with the City's
maintenance, pruning and trimming policies.
I. Prior to any site development, the developer shall be responsible
for fencing the eucalyptus windrow maintenance easement (20 feet "
on each side of the centerline of the windrow) to insure that the
easement is not utilized for storage and/or dumping purposes and,
also to protect the tree roots from damage due to construction.
J. -Whenever development results. in eucalyptus tree roots being .
exposed, the developer will be required to take corrective
measures under supervision and inspection by City Arborist.
K. Pruning and all other maintenance of trees shall .be -under the
supervision and approval of the City Arborist upon the.Tree.
Comittee's recommendation. The City Arborist shall require
the developer to submit the names of those who perform the
task and proof of their qualification.
L. At the earliest possible stage of the development review process,
i.e., zone change, subdivision maps and/or site plans, approvals
for those areas including eucalyptus windrows designated for
preservation shall be conditioned with a note requiring irrigation
of eucalyptus trees on "a continuous basis during the review process
and development. Developers shall install and maintain these
irrigation systems, subject to City supervision and -inspection.
Resolution No. 81-7
G-IIL 4
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Iv: DESIGbT/KUNTMQV= STANDARDS
A. Trees shall be topped to the following guidelines unless
alternate requirements are approved by the City Arborist
upon the Tree Cannittee's recommendation. Where the height
.of a tree exceeds the distance between the tree trunk and
an adjacent structure, such tree shall be -topped to a height
no greater than the distance to the closest structure or 40'
whichever is greater. In no instance -may a tree exceed 70'
in height unless alternate requirements are approved by the
City Arborist.
B. Trees which, with the approval of the City Arborist, will
remain over 70' shall require'selectivepruning of excessive
growth to reasonably insure health, safety and welfare of
the trees and the public.
C. Trees .pruned to approximately 40' will require close monitor-
ing and removal of excessive side growth. Pruning thereafter
shall be as necessary -to insure .the health, -safety and welfare
of the trees and the public.
D. In all locations, a mini.man area of 20' on each side of the
centerline of the windrows shall be left as an easement for
.maintenance unless adequate easement has been provided subject
to the approval of the Planning Catmission. This open area -
can serve the following purposes:
J.. Safety, i.e. prevent branches fran falling on adjacent
structures or people.
2. Access for maintenance crews which will remove hazardous
branches and keep the trees,in good health and aesthetic'
form.
3. Local park land dedication, if approved by.the Planning
Caimi:ssion, to accannodate passive recreation activities
or serve as a linear connection for bike and -pedestrian
paths linking the residential neighborhoods,to larger parks.
E. The -location of the eucalyptus windrow maintenance easement
and the identification of those responsible for maintenance
of same shall be designated on the subdivision map and it
shall be checked and verified for ccmpliance at the time of
site plan review.
F. The curb -cut access to the maintenance easements shall be
shown on subdivision maps, and cross sections shall, be'
provided to show acceptable.finished grade relationships
between the maintenance easement and access entry points to
insure accessibility to windrows during maintenance. These
maps shall be reviewed by the C=munIty Development Department
to assure a proper grading plan prior to the issuance of a
grading permit.
Resolution No. 81-7
G-III-5
G. In all eucalptus windrow maintenance easements-, disruption of the
root system will not be permitted within 8' from the centerline
of the windrow. In no case shall trenching other than for windrow
irrigation systems be permitted within this 8" area. Digging of
trenches -and other operations which may damage eucalyptus tree roots
in the windrow maintenance easement will require an encroachment
permit and wi.11'be under:City supervision and inspection.
H. In all eucaiyptus-windrow maintenance -easements, no paving other
than pedestrian'and bicycle trails shall be closer than 15' fram
the centerline of the windrow. Where grading is necessary, dis-
ruption shall not be closer than 8-' from the .centerline of the
windrow and such grading will require the -prior approval of the
Director of Cam unity Development upon receipt of rec^crtmendata on.
by the Tree Committee.
I. Root pruning may be allowed only if the need for it has been clearly
demonstrated. Should it be necessary, root pruning will -be carried
-out at a_ distance between 8'_ and 15' fram the centerline of the
windrow and at a depth of 4' to 5'. Reduction of foliage area must
precede root pruning.
J. All replacement trees are to be of a desirable species from a list,
Of selected eucalyptus trees (see Page 7 of this Resolution). Any
further amendments shall be approved by the Director of C mmnity
Development. As a guideline, replanting. shall be on approximately
20' centers and replacement trees shall. be no greater than one gallon
-container size.- The.planting holes shall not be dug with an auger..`
Earth basins must 'be constructed around replacement trees and shall
be irrigated as necessary untiY they -have became campetitive with
adjoiningplants (the property owners will be, responsible up to a
period of one year).
K. As a guideline, the distance between remaining trees in the
windrows shall be 15' to,20-'. However, tin no case should
healthy trees be removed merely to insure -such spacing.. if
the distance between -trees in a windrow exceed 30', new trees
of a desirable species shall be planted by-develcper-in accordance
with the guidelines to fill the voids.-_
L. Staking of any eucalyptus trees, replacement trees or off-
shoots is not recommended.
M. Any proposed ground cover or shrub planting under eucalyptus
trees shall be reviewed by the City Arborist to insure
carpatibility with the eucalyptus trees.
N. Eucalyptus trees standing upon private -property or property
held in common by an association shall'be-maintained by the
owner in conformance with the standards and policies for
City trees. Modification may be allowed'by the Tree Committee
only where it *is shown that it is, not physically or econcmi-
cally practical to comply with said policies.
Resolution No. 81-7
G-III-6
V. ADMIIVIST'RATION
A. The Superintendent
designee shall act
responsibility for
maintenance: -
of Park Maintenance or a qualified
as City Arborist and will have
supervision and inspection for tree
B.. Eucalyptus tree- removal permits, environmental documents
and design/maintenance standards shall be reviewed and
approved ' by the Director of Camimmiarmi:ty Development .
C. The -Tree Commmittee will .review all proposed removals and
pruning of windrow trees at the subdivision and/or site
plan review process and shall. make-rec=memdations regarding
tree preservation or removal, and pruning.
D. Persons or organization who prepare environmental docu-
ments. or deal with the tree removal,_ pruning, treatment, or
maintenance shall be required,to present evidence of
expertise and experience in working with trees.* This
shall include educational background related to ecology,
horticulture, arboriculture, biology, agriculture and
landscaping and experience in the area of tree maintenance
and trinming. In cases where persons may have experience
only, they must prove to the satisfaction of the City
Arborist that their experience is acceptable.
W. ENMRCEMENT
The provision of Chapter 19,.Section II.-M-1905 of the Code
-of Ordinances, City of Irvine, shall apply to all cases of
willful or unintentional disregard of the adopted. city policies
and standards pertaining to tree maintenance, removal and
replacements.
Resolution No. 81-7
G-M-7
ELr.AL=S WINDROWS
TREE REPL-ACEMENr LIST
Tree Species
Heights
.Eucalyptus maculata
Max. 150'
in Australia
-(spotted gun)-
50' = 60'
in Irvine
-Eucalyptus sideroxylon
Max. 40'
in Australia
Rosea (Red iron bark)
Max. 40'
in Irvine
Eucalyptus rudis
Max. 100'
in Australia
(Desert gum)
50' - 60'
in Irvine
Eucalyptus polyanthemos
Max. 150"
in Australia
(red box) (silver dollar
50' - 60'
in Irvine
gLm)
a
is
Resolution No. 51-7
Characteristics
The bark is
deciduous in patches.
The bark is persistent
and flowers are rose
color.
Rough gray, persistent
bark.
-The hark is persistent
leaves are green and
round (different than
others).
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PASSED AMID ADOPTED by the City Council of the City of.Irvine at
a regular meting held on the 27th day of Jamo y, 1981• , '
IN L.G
MAYOR OF THE CITY OF MOE
ATTEST:
CITY ffl;ERK OF THE CITY OF IRVINE
STATE OF CALSFORNIA) _
CtiLaTTY OF ORANGE ) SS
CITY OF IRVINE - )
I, NA= C.- FMAND, City Clerk of the City of Irvine, HERESY
Y. DO CERMthat the foregoing Resolution was duly adopted at a
regular meet; M of the City Council of the City of Irvine, held on.
the 27th day of January, 1981, by the following vote:
AYES:. 5 : Agran, GaI Sills. Vardoulis, ar4 Anti=fty
NOW: 0 : None
ABSENT: 0 CO : None
Resolution Db. 81.-7
G-III-9
•
APPENDIX H
GLOSSARY
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GLOSSARY
Association - A group of species occurring in the same place.
Biota - Fauna and flora together-.
Carrying Capacity - Number of individuals that the.resources of a habitat can support.
Community - An association of interacting. populations, usually delimited by their
interactions or by spatial occurrence.
Competition - Use or defense of a resource by one individual that reduces the availability
of that resource to other individuals.
Dispersal - Movement of organisms away from the place of birth or from centers of
population density.
Dispersion = Pattern of spacing of individuals in a population.
Diversity - A measure of the variety of species in a community that takes into account the
relative abundance of each species.
Ecotone -- A habitat created by the juxtaposition of distinctly different- habitats;_ an edge
habitat.
Environment - Surroundings of an organism, including the plants and animals with
which it interacts.
Food chain - An abstract representation .of the passage of energy through populations in
the community.
Gene flow - Exchange of genetic traits between populations by movement of individuals,
gametes, or spores. :
Habitat - Place where an animal or plant. normally lives, often characterized by a
dominant plant form or physical characteristic (i.e., the stream habitat, the forest
habitat).
Habitat selection - Preference for certain habitats. _
Heterogeneity - The variety of qualities found in an environment (habitat patches) or
population (genotypic variation).
Life form -Characteristic structure of a plant or animal.
H - 1
Microhabitat - The particular parts of the habitat that an individual encounters in the
course of its activities.
Niche - All the components of the environment with which the organism or population
interacts.
Productivity - Rate at which energy or nutrients are assimilated by an organism, a -
population, or an entire community.
Range - An area, from which, intruders may or, may not be excluded, to which an
individual restricts most of its normal activities (see territory).
-Relative abundance - Proportional representation of a species in a. sample or a
community.
Riparian = Along the bank of a river or lake.
Specialization - Restriction of an organism's .or a,population's activities to a portion -of,
the environment; a-, trait that enables an organism (or -one of tis organs) to modify (or
differentiate) in order to adapt to a particular function or environment.
Stability.- Inherent capacity of any system to resist change.
Subspecies - Subpopulations within a species that are' distinguishable by morphological
characteristics and, sometimes, by physiological or behavioral characteristics.
Territory - Any area defended by one or more individuals against intrusion by others of
the same or different species.
H-2
A
ARCHAEOLOGICAL RESOURCES
S
ELEMENT
0 Technical Supplement 3
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ARCHAEOLOGICAL RESOURCE INVENTORY
CITY OF IRVINE
AND
ITS SPHERE OF INFLUENCE
PREPARED FOR
COMMUNITY PLANNING SERVICES
AS A TECHNICAL COMPONENT OF
THE IRVINE MASTER ENVIRONMENTAL ASSESSMENT.
PREPARED BY
BETK PADON
PRINCIPAL INVESTIGATOR
BILL BREECE
FIELD DIRECTOR.
CULTURAL RESOURCE DIVISION
LSA
610 NEWPORT CENTER DRIVE, SUITE 555
NEWPORT BEACH, CA 92660
(714).640=6363
0 DUNE 1985
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TABLE OF CONTENTS
INTRODUCTION.............................................................. 1
PERSONNEL.....:........................................................... 1
DESCRIPTION OF THE PROJECT ...............: ........................ *so ...... 3
ARCHAEOLOGICAL OVERVIEW` .................................................... 5
Regional Cultural History ................ ...... :.................. 0... 5
Ethnographic Background .... ............................................ 9
METHODOLOGY...................................:.......................0...... 10
Archival' Research ...........:......................................... 10
Background......................................................... . 26
Previous Surveys and Reports ...................:...................... 27
Field Methods .............
Special Problems ...:.... ..... .... .................................... 28
FIELD.SURVEY RESULTS........................................................ 29
CA-Ora-1069.................... :.... .................................. 0 29
CA-Ora-1070........................................................... 30
CA-Ora-1071............................................ :.............. 30
Isolated Artifacts .......................................:....:...... 30
Previously Recorded Archaeological Sites ............................. 32
CONCLUSIONS AND RECOMMENDATIONS ..: ........................................ 35
REFERENCES ............................................................... 37
APPENDICES
Appendix A - Applicable Federal and State Laws for Archaeological
Resources
Appendix B - Resumes
Appendix C - Index to Base Map of Surveyed Areas
9
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LIST OF FIGURES AND TABLES
FIGURES
Im
Figure 1 - Regional Location ...................... .......... ....... .., 2
__ TABLES
Table A - Archaeological Sites Within the Ci-ty of Irvine and Its
Sphere of Influence ......... .... ......... ............. ... 11
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ARCHAEOLOGICAL RESOURCE INVENTORY
CITY OF IRVINE AN
ITS SPHERE OF INFLUENCE
INTRODUCTION
The following report presents the findings and results .of an archaeolog-
ical resource survey and records check of the previously unsurveyed portions
of. the City of Irvine and its sphere of influence (.Figure 1). The_ project
lies within central Orange County and extends from the central ridge of the
San Joaquin Hills inland to the central ridge of the Lomas de Santia-go. The
study, area included the entire area, under the jursidiction of _ the City of
Irvine and its sphere of influence, while the surveyed area included those
portions not previously systemati'call;y, surveyed.- This study provides an
inventory of the known archaeological resources and surveys conducted within
the City and -its sphere of influence. This report provides an important plan-
ning tool for the City of Irvine•, providing the City with a comprehensive data
base of existing, archaeological resources to assist in future development
plans for the city.
This report follows guidelines established by the California State His-
toric Preservation Office, the Society for California Archaeology (Ki-ng,
Moratto, and Leonard 1973), the Society for American Archaeology (McGimsey and
Davis 1977), and the City's Environmental' Review Matrix: Guidelines for
Archaeological Reports.
The body of this study follows a brief physical description of the pro-
ject area. It contains four sections: Archaeological Overview, Methodology,
Summary of Results and Findings, and Recommendations. Due to their .size,
index maps complied during the archival and field -work phase of this project
are provided under separate cover. The Archaeological Overview section serves
to provide the context for discussing, archaeological resources_ encountered.
The Methodology section describes how these resources were identi feed and how
the field reconnaissance was conducted. Data summaries and descriptions of
the archaeological sites newly recorded characterize the section Results and
Findings. Recommendations for continued research.to complement this inventory
make up the final section. The applicable Federal and State laws for archaeo-
logical.resources are contained in Appendix A.
PERSONNEL
Beth Padon, a certified Orange County Archaeologist and member of The
Society of Professional Archaeologists (SOPA), served as Principal Investiga-
tor for this study. Ms. Padon has served as principal investigator for a
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2
Regional Location. Lsa
Los Angeles Co.
91
m
AnaheN.c
Garde
San Bernardino Co:
Yorba
Linda
Riverside Co.
S
Cleveland
National
Forest
18
4
,/ San Diego Co.
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number of archaeological. surveys throughout Southern California. Mr.. Bill
Breece, also a certified Orange County Archaeologist and SOPA member, served
as Project Archaeologist. Cole Parker and Tony, Sawyer served as the primary
field assistants, while Wayne Bonner and Jody Neal -Post assisted in the final
days of the survey. Marian Parks served as 'research assistant for the proj-
ect. Resumes are -provided in Appendix B.
DESCRIPTION OF THE PROJECT AREA
The project area includes three prominent Orange County geographical fea-
tures: the Tustin Plain, the San Joaquin Hills, and the Lomas de Santiago. It
lies w-ithin the coastal and foothill zone of Central Orange County.- The Lomas
de Santiago, which form the northern portion of the project area, contain a
series of moderately -steep canyons and narrow ridges. From northwest to
southeast, these canyons are the Little Joaquin, Rattlesnake, Hicks,, Bee,
Round,''and Agua Chinon. The flat, open Tustin Plain covers about two-thirds
of the study area. The San. Joaquin Hills mark the southern portion - of the
study area. These hills slope moderately and feature open, broad valleys such
as Sand, Bommer, Shady, Bonita, and Coyote Canyons. San Diego Creek, which
flows east/west through- the -study area along the. inland side of the .San
Joaquin Hills, remains the major stream in the study area...
The Irvine Company continues. to farm the majority of the study area,
however, residential and commercial developments dot the project area. The
University of California at Irvine covers several hundred acres in the proj-
ect's southwest corner. Both the I-405 and I-5 freeways .cross the project
site -from northwest to southeast. The majority of the study area is situated
on the E1 Toro and.Tustin USGS 7.5' quadrangles with small portions located on
Orange, Black Star Canyon, and Laguna Beach USGS 7..5" quadrangles.
Open grasslands characterize rural areas of the San Joaquin Hills. Vege
tation here varies from introduced grasses and grains to isolated areas of
native chapparal and oak woodland. Crop cultivation dominates the. Tustin
Plain. Rows of eucalyptus trees mark the boundaries of several fields.
Even though' areas of dense chaparral exist within the Lomas de Santiago,
orchards, reservoirs, and sand -and -gravel operations have reduced native vege-
tation within this area.
In its natural state, the majority of the study area would have consisted
of three major biotic communities: riparian/oak woodland, chaparral/coastal
sage scrub, and southern (valley) grassland. A fresh -water marsh and a salt-
water marsh community lies within the project area. These types of biotic
communities offered several potential food and raw material resources for the
prehistoric population of the area: K. Dixon ha.s classified six basic
L]
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biological habitats for the general area of Orange County -which ai.d in deter-
mining available natural resources for an area (Dixon 1974). His model
suggests several resources for these. habitats, as described in the following -
paragraphs.
Coastal sage scrub is found on steep, dry, rocky or gravelly slopes and
in narrow canyons, generally below 1,500, feet. It is less dense'than-chapar-
ral habitat. It consists of dry -type vegetation such as white sage (Salvia
apia�na), sagebrush (Artemisia californi.ca), cactus (0 unta occidenta is ,
wheat (Erin onum ascciculatum),and sumac -(Rhus laurina) z and Keck
1959). Native Americans uti ized many of these plants. For example, the
leaves of California sagebrush were used for medicinal purposes. The ground
seeds of white sage were used -to make meal; the leaves were used as a food, as.
a purification agent, as a hair dye, and as a deodorant. The leaves of buck-
wheat were brewed for a medicinal drink while the flowers, when steeped, were
used as an eyewash (Curtis 1959'; Bean and Saubel 1972).
Riparian habitat, found along drainages with a year-round water source,
consists of trees and shrubs. This habitat includes coast live oak (Quercus
a rifolia), western sycamore (Platanus racemosa), mulefat (Baccharis lutino=
sa), and willow (Salix spp.) (Munz anT Keck 195The aboriginal popu ations
extensively used tTe- several species of oak -- coast live oak, scrub oak
(Quercus dumosa), and interior live oak (Quercus wislizenii) -- as sources of-
acornsfor food (Bean and Saubel 1972; Spar man 908).
Southern rassland habitat was previously located on dry hills, on lower
mountain slopes, and in inland valleys. The various. bunch grasses (Stipa
spp.) originally grew as the dominant plant of this community. E1de.rberry
(Sambucus mexicana) and prickly pear (Opunta littoralis) also occasionally
occur in this habitat. However, since European contact, introduced grasses
and annual species prevail. Today, wild oat Uvena spp.), filaree (Erodium
sp.p.), and mustard (Brassica spp.) commonly grow as part of this habitat. The
native populations- found the grass seeds edible by grinding them into meal,
and the berries of the elderberry also edible when dried and cooked as a sauce
(Curtis 1959:142).
Freshwater marsh, found in river -bottom lagoons and bays along the coast
and behind salty areas (Munz and Keck 1959) is abundant' in small animals and
birds. It is filled with plants that are useful to prehistoric populations,
including cattails (Typha spp.), rushes (Heleocharis palustris), sedges, and
willows (Salix hinasiana) that could be used to manufacture baskets and mats,
construct ewe l ings, and as a food source (Dixon 1974).
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Saltwater marsh is'located mainly in the tidal environments or sand flats
that range up to ten feet in elevation (Munz and. -Keck. 1959). Dominated by
plants and adapted to high soil salinity, the saltwater marsh/estuary also
offers a rich source of protein in the form of shellfish, especially scallops
(Pecten), clams (Chione), and oysters. Seasonal migration of waterfowl would
have provided a temporary abundance of food in the form of marsh -dwelling
birds and bird eggs. Rodents, reptiles, sharks and rays, and bay fish would
also have been available year-round.
Although it may be assumed that the remaining natural vegetation within
the study 'area generally represents the prehistoric flora of the region,
intensive livestock grazing, dry -farm disking, cultivation, diminishing water
table levels, residential development, and the suppression -of wildfires over
the last 150 years have significantly altered the biological environment. The
Irvine Company maintains hundreds of acres of orchards (citrus and avocados)
within the study area. Much- of the study area southeast of the Lomas de San-
tiago ridge is within these Irvine Company orchards. Livestock activities,
sand and gravel operations, commercial nurseries, and roadways.dot the study
area north of the E1 Toro and Mission Viejo communities.
ARCHAEOLOGICAL OVERVIEW
Regional.Cultural History
The following cultural history outline briefly describes known pre -Euro-
pean cultural development in the Southern California coastal region. I-n gen-
eral, this region is represented by cultural developments that persist over a
long period of time and exhibit notable stability when compared to other * cul-
tures in North America. This stability makes it difficult to accurately
define cultural changes through time. Without distinct cultural changes, only
a general cultural history can be used to provide a chronological framework
for the Southern California coastal cultures. Effective exploitation of
coastal and foothill environs is viewed as one explanation for the persistence
of this cultural pattern, which is reflected in the archaeological record as
an increase im local population size and a more sedentary form of settlement.
Most archaeologists divide the general prehistory of this region into a
four -stage chronology based upon changes in artifact assemblages and ecologi-
cal adaptation. The two most widely referenced cultural frameworks are those
proposed by 14. Wallace (1955) and C. Warren (1968),. With both of these broad
chronologies, the authors cover the non -desert areas of Santa Barbara, Ven-
tura, Los Angeles, and San Diego Counties.
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W. Wallace (1955) defines four cultural horizons for the coastal area:
Horizon
I
Early Man
Prior to 5500 B.C.
Horizon
II
Millingstone
5500 to 1000 B.C.
Horizon
III
Intermediate cultures
1000 B.C. to 1000 A.D.
Horizon
IV
Late Prehistoric cultures
1000 A.D. to 1800 A.D.
C. Warren in 1968 outlined a different regional synthesis which utilizes.
the concepts of cultural ecology to explain cultural changes. He defined his
traditions as:
San Dieguito Prior to 6000 B.C.
Encinitas 5500 B.C. to 1 A.D.
Campbell 1 A.D. to 500 A.D. (for San Diego County)
Chumash, Shoshonean, Yuman 500 A.D. to European contact
The Early Man Horizon covers the Late Pleistocene to post -glacial period.
This period remains best documented in San Diego County; ,however, the skeleton
known as the Laguna Woman, found in Orange County on the coast, falls within
this horizon. The Laguna Woman dates by- radiocarbon calibration- to 16,670
B.C. or at least older than 12,850 B.C: (UCLA-1233A: 17,150 + 1,470 B.P.;
UCLA-1233B: 14,800 B.P. [Schroth 19791). In Los Angeles County, the human
bones found at the La Brea tar pits and the Los Angeles -Man bones found along
Ballona Creek also represent this period. The UCLA radiocarbon lab dated -the
Los Angeles Man to 23,600 years ago .and the La Brea skeleton to 9,000 + 80
years ago (Stickel 1978).. In San Diego County, three sites have yi-el.ded skel-
etal as well as artifactual material which dates to this early period. These
sites are the"Texas Street Site (Carter 1957), the Del Mar skeleton (Rogers
1974), and the Harris Site (Rogers 1929; Warren et al. 1961). Diagnostic
artifacts from San Diego sites of the period include numerous large projectile
points, scrapers, crescentics, and hammerstones. Groundstone implements are
lacking for this period. Archaeologists interpret this absence of groundstone
to imply that the Early Man people emphasized hunting in their subsistence
strategy rather than the gathering and processing of plant materials.
Warren's San Dieguito Tradition parallels Wallace's Early Man Horizon.
However, Warren focused his description of this period on the San Diego sites.
He noted several different scraper tools, leaf -shaped knives, some hammer -
stones, and a few crescentics for this period. He also infers that the San
Di egui,to Tradition was a hunting, culture, since he found no manos or metate-s
at these sites.
• In Orange County, the crescentics found at the Upper Newort Bay site (CA-
Ora-64) suggest some tie to the San Diequito Tradition (ARI 1977). This
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site also dates to 6500 B.C., which falls within Warren's time frame for this
period. However, the excavation also yielded evidence that even- the early
native populations at the site exploited the marine resources of the bay.
This subsistence strategy differs from the identified hunting strategy of the
San Dieguito period. Further research is needed in order to document whether
the San Dieguito Tradition exists in Orange County.
By 5500 B.C., several prehistoric groups occupied both the coastal plains
and foothills and the .interior valleys of the Southern California region.
These early inhabitants represented the Millingstone Horizon for Wallace.
Wallace lists the following diagnostic artifacts for this period: cogstones,_
stone di-scoidals, metates, manos, some soapstone objects, and a few bone awls.
The people of the Millingstone Horizon were primarily plant food and shellfish
collectors, as evidenced by the large number -of manos and metates. Few pro-
jectile -points are found at these sites; however, some hunting and trapping of
animals continued and is implied by the faunal remains of jack rabbits, pocket
gophers; California ground squirrels, and deer mice. The Oak Grove culture in
the Santa Barbara region (D. Rogers 1929) provided Wallace with his basic
definition of this horizon. Wallace (1954) also identified this horizon - at
the Little'Sycamore Site in Ventura County.. Other sites which contain this
horizon include the Topanga Tank Site (Treganza and Malamud 1950), Malaga
Cove, Level 2 (Walker 1951), and the La Jolla Sites in San Diego.
C. Warren defines the -Encinitas Tradition, his next cultural development,
as an ecological adaptation to littoral and coastal foothill environments.
Like Wallace's Millingstone Horizon, the native populations relied on gather-
ing of wild plants and on shellfish collecting rather than only on hunting
wild game. Warren, however, describes this tradi�tion,as persisting for a long
time in San Diego and suggests that this same pattern existed for the -entire
Southern California region. Crude chopping and scraping tools, manos,.meta-
tes, and large projectile points characterized this tradition. The mano and
metate allowed these hunters and gatherers to render previously non -digestible
plant foods into edible food. This new technology,- grinding hard seeds and
other plant foods, gradually replaced projectile points as the primary subsis-
tence tools.
In Orange County, sites CA-0 ra-83, -85, -188 (Huntington Beach area), and
-99A (Newport Beach area) tentatively represent this period (ARI 1977). Most
of these sites are dense shell middens which contain few diagnostic artifacts.
The absence of diagnostic artifacts of late periods places these sites within
the Millingstone Horizon or the Encinitas Tradition. The lowest stratum of
CA-Ora-119, Locus A (in Irvine), also represents this period. Here, the
approximate date of 3500 B.C. and the large leaf -shaped projectile points,
manos, and metates support the placement of this site within the Millingstone
Horizon.
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Wallace also uses subsistence -related artifacts to define the Interme-
diate Horizon. He notes the introduction of the mortar and pestle and an
increase in the number of small projectile points as indications of the Inter-
mediate Horizon. As grinding tools, the mortar and pestle are usually identi-
fied with acorn .processing (Leonard 1966) . The mortar and pestle technology
implies that the native populations knew how to leach the poisonous tannic
acid from acorns and make an edible food. Little archaeological evidence
exists to support this Intermediate Horizon for the entire region., This.
horizon remains defined for only a few sites: CA-Ora-196 in Irvine (Cottrell
1979), CA-Ora=507, and CA-Ora-486 in E1 Toro area (Van Horn 1980).
1
C. Warren instead defines a transitional tradition, the Campbell Tradi-
tion, for only the Santa Barbara area. He. maintains that the silt -filled bays
and estuaries of the northern counties demanded a new subsistence strategy for
the coastal settlements. Here, an ocean-going technology developed to exploit
deep-sea fishing and sea mammal hunting._
The native populations in Orange and San Diego Counties, according to
Warren; maintained a mixed subsistence strategy of primarily gathering wild
plants and collecting shellfish. However, certain traits of the Campbell Tra-
dition, do appear in Orange County sites around 2000 B.C." Rice (1976) refers,
to this period as the Encinitas II Tradition. These traits include the
increase of stemmed, side -notched; and lanceolate -shaped projectile points and
an increase in the number and styles of shell ornaments.
The Late Prehistoric Horizon .begins approximately 1.000 A.D. . Wallace
views this period as an elaboration of the number and kinds of artifacts from
the previous horizon. Small, triangular projectile points which indicate the
use of the bow and arrow characterize this horizon. The number of steatite
vessels, bone tools, and other ceremonial and personal ornaments also
increases in occurrence.
Warren identifies three separate traditions for the region which develop-
ed independently approximately 2,000 years ago. The Yuman Tradition developed
in southern San Diego. The people of this tradition shared distinct cultural
traits with the people of the Colorado/Gila River drainage (Moriarty 1966).
The Chumash Tradition developed in the Santa Barbara area and possessed a com-'
plex social'organization which included village chiefs, shamans, craft guilds,
and commoners.. The Chumash became noted for their elaborate ornamental items
and shell money. The Shoshonean Tradition covers a large geographical area
which includes northern San Diego, Orange, and most of Los Angeles Counties.
Warren (1968) leaves this tradition loosely defined. Generally, it is an
elaboration of the previous characteristics of the Encinitas Tradition in
Orange County. Archaeological evidence based on available linguistic evidence
•
E7
Lsa
suggests that several groups entered this region from the Southern Great
Basin. These groups are believed to have been Shoshonean -speakers .who, in
moving to the coast, separated the indigenous Hokan-speaking groups. The
appearance of cremations, small triangular points, bone tools, and use of
asphalt marks this cultural period. By 1000 A.D. this period is also identi-
fied by ceramic smoking pipes and brownware pottery.
This latest prehistoric period ended rather abruptly with 'the Spanish
expeditions and establishment of missions and outposts during, the 18th centu=
ry. With the founding. -of Mission San Gabriel Archangel in 1771 and Mission
San Juan Capistrano in 1776, the prehistoric life was gradually abandoned as
more and more Indians - became neophytes of the missions. The post -contact
native populations of Southern California were divided into groups by the
Spanish, based on the similarity of their spoken language and their proximity
to lands controlled by the missions.
Ethnographic Background
According to A. L. Kroeber (1925:6211, L. J. Bean and C. R. Smith (1978:
538), and B. E. Johnston (1962:37), the geographic location of the City of
Irvine study area falls within the traditional Gabrielino territory during the
protohistoric period. At the time of European contact, the Southern Gabrie-
lino occupied most of present-day Los Angeles County south of the Santa Monica
Mountains, half of present-day Orange County, part of Riverside County, and
Santa Catalina and San Clemente Islands (Kroeber 1925:620):
The name Gabrielino is an Americanization of a Spanish word referring to
Native Californians living on lands controlled- by Mission San Gabriel. The
Gabrielino may have called themselves Town a-va.- A. L. K.roeber recorded the
Luiseno name for Gabrielino as Tumangama u-1 m,-"northerners," and C. H. Merriam
recorded the Buena Vista Lake Yokut name for Gabrielino as -miyah-hik-tchal-
lop, "long arms." The Ventura Chumash who lived north of the Gabrielino
called them Ataplilish (Heiner 1968).
The Gabrielino language was one of the Cupan languages of the Takic fami-
ly of the greater Uto-Aztecan linguistic stock. The Takic family is further
divided into six languages: Gabri-el-ino-Fernandeno, Luiseno-Juaneno, Serrano,
Kitanemuk, Cahuilla, and Cupeno.
These Takic-speaking people moved into. southwestern California by at
least 500 A.D.- and displaced the earlier Hokan-speaking people related to the
Chumash in the Santa Barbara area and_ the Yumans in San Diego County. Ethno-
graphic accounts and archaeological evidence from -the Gabrielino territory
•
10
Lsa
indicate that the Gabrielino occupied a number of permanent villages along the
coast and in the inland valley regions. Although the Gabrielino maintained a
complex socio-political organization, wild food foraging and limited hunting
in the. interior areas.and intensive shellfish gathe-ri.ng and sea mammal hunting
along the.coast characterized their subsistence.
The Gabrielino were organized in patrilineal lineages- and' clans. Larger
villages were politically affiliated with'satellite villages, bound to them by
socio-economic and religious ties. Leadership was inherited, and was legiti-
mized by possession of =a "sacred bundle" which provided a tangible link with
the sacred past. Chiefs shared administrative duties with shamans, and with
other officials of -the group who distributed food after communal hunts and
organized the annual mourning ceremonies (Bean and Smith 1978: 543-544).
'METHODOLOGY
The research effort for -this project consisted of . two phases:. archival
research- and field reconnaissance. Modern topographic: maps link these two
phases.by providing the basis for data organization.
Archival Research
The. archival search checks for any previously recorded materials of
.archaeological significance concerning ,the project area. This information.
gai-ned beforehand reduces duplication of effort as well as provides up-to-date
archaeological information on the immediate area for field reconnaissance.
This records search included the following sources: files, site records,
and maps housed. at the University of Cal i fornta, Los Angeles (UCLA) Archaeo-
logical Survey -(the State -recognized clearinghouse for archaeological records
for Orange County), and files and records housed at the.Orange County Environ-
mental Management Agency under the supervision of Rob Selway.-
The site maps at UCLA indicate that 129 archaeological sites have been
previously identified within or adjacent to the boundaries of the .study- area.
Table A lists these recorded archaeological sites and includes the site num-
ber; site description, date the site was recorded, and condition and archaeo-
logical status of the site (e.g., -whether the site has been tested or salvaged
and whether a report exists). The condition of a site (preserved, disturbed,
or destroyed) can be determined only by an in -field visit, a task which was
not included in the scope of work for this study except for those sites newly
recorded or sites immediately adjacent to the surveyed portions. However,
IDattempts were made to determine the condition of sites within the study area:
based upon available documentation. Under the condition column in Table A, SR
stands for site record.
TABLE A 11
ARCHAEOLOGICAL SITES WITHIN THE CITY
OF IR INE AND ITS SPHERE OF INFLUENCE
Site No./
Artifactual
Date/
Planning
CA -Ora-
Description
Material
Size
Update
Condition Area.
106/219-
shell midden
asphaltum,
350 x 160 ft.
1-938
WPA: tested I 25A
with lithic
burials,
1950
SR: impacted
artifacts
points, stone
.1981
Douglas-: re-
tool & grinding
located (1)
implements,
540 x 840 ft.
1966
SR impacted
chipping waste
1979
Cottrell: tested
107
shell midden
points,
125 x 250 ft.
1938
WPA: tested I 25A
with lithic
asphaltum,
1950
SR: impacted
artifacts,
stone -grinding
1967
PCAS: tested
cemetery
implements
1981
Weil.: relocated
3 Toc i :
1) mound,, 11
burials --
2) Sepulveda -
structure
3) shell mid -
den with
lithic
arti facts
115a&b shell-midden
with stone -
grinding
implements
116a&b shell midden
with lithic
artifacts
0
grave goods 240 x 70 ft. 1938 WPA: salvaged- I 19B
burials
historic glass
and metal,
ceramics,
wood
bowl fragments,
pestle fragment,
manos
stone -grinding
implements,
charcoal, manos,
metates, and his-
toric items
300 x.200 ft. 1975 Westec: tested
700 x 900 ft.
650 x 400 ft.
200 x 200 ft.
1976 .Rice and Cot-
trell: tested
1976 Mitchell: nomi
nation
1963
1963
1980
n. d.
SR: impacted
SR: intact
Hurd: tested
Hurd: marine
I 37
I 37
TABLE A (continued)
ARCHAEOLOGICAL SITES WITHIN THE CITY
OF IRVINE AND ITS SPHERE OF INFLUENCE
12
Site No./
Artifactual
Date/
Planning
CA Ora-
Description
Material-
Size
Update
Condition. Area
119 a,b,
shell midden,
stone tools,
420 x 540 ft.'.
'140
1963-
SR: disturbed I 24
&"c
3
shell ornaments,
x 180 yrds.
1966
Lytton: tested.,
,burials,
lithic arti-
stone bowl,
30 x 30 m.
1981
Allen: salvage
facts
pestle, steatite
(Locus B)-
pendant-& beads,
1981
Koerper (.Ph.D.
points
Dissertation)
(Locus A)
1976
Rice: tested
120
shell midden
pestle fragment,
255-x 255 ft.
1963
SR: intact
I 19B
with lithic
bowl fragment,
1975
ARI:-salvaged
artifacts,
stone tools,
Post-
Gill: 1M.A.
2-burials
chipping waste,
1975
Thesis)
shell instrument.,
cogstones
12-1
shell midden
stone -grinding
3000 x 1000 ft.
1963
SR: impacted
I 368
with lithic
implements,
2000 z 100 ft.
1966.
SR: impacted
artifacts
points, chip-
1973
Ellis: tested/
ping waste.
one area
-
1978
Cottrell:
tested/one
area
1979
Westec: sal-
vaged
portion
124/134
shell midden
stone -grind-
200 x 50 ft.
1963
SR: impacted
I 25A
with lithic
ing imple-
1965
SR: impacted
artifacts
ments, points,
1.967
Chace:— tested
stone & bone
tools, chip-
ing waste,
shell beads,
125
rock shelter
6 x 24 yds.
1963
SR: intact
I 25A
with shell
1965
PCAS.: tested
midden
1981
Weil: relocated
78
lithic scat-
chipping waste,
500 x 90 ft.
1966
1972-3
SR: impacted
ARI:-suevey
I 21
ter with shell
mano fragment,
granite chopper
1979•
Cooley: tested
0 1
TABLE A (continued) 13
ARCHAEOLOGICAL SITES WITHIN THE CITY
OF IRVINE AND'ITS SPHERE OF INFLUENCE
Site No./.
Artifactual
Date/
Planning .
CA -Ora-.
Description
Material
Size Update
Condition- Area
195
shell midden
manos, debitage,
300 x 1000 ft. 1967
SR: impacted I 36B
with lithic
hammerstones,
500 x 320 ft. 1967
Desautels and
artifacts
points, his:-
Fenenga: par-
15 prehis-
torical evi-
tial salvage
toric burials
dence, bone
tools, shell
implements
196
1) shell mid-
stone -grinding
1000 x 100 ft.' 1967
SR: impacted I 19A
den with
tool implements,
1969
PCAS: survey
Ti thi c
bone awl., shell
'1969
Hayes and Long:
artifacts,
ornaments
surface col --
burials
lection
1976
Cottrell: tested
2) historic
historic ceram-
1979-
Cottrell: partial
locus
ics, and glass
salvage
197
shell scatter
projectile
50
x 150
ft.
1967
SR: impacted I
19B
with lithic
point, shell
1976
Cottrell: tested
artifacts
ornaments and
1977
Craib-: sal -
implements,
vaged
mano, metate
206
shell midden
none noted
1200
ft.
1966
SR: impacted I
25A,
1981
Weil: site
destroyed
207
shell scatter
none noted
50
x 10
ft.
1966
SR: intact I
25A
1981
Douglas: site .
destroyed
208
shell scatter
none noted
80
x 25
ft.
1966
SR:.intact I
25A
1975
Drover: tested
and mitigated
209
shell midden
80
x 40
ft.
1966
SR: impacted. I
25A
1981
Douglas: re-
located
10
rock shelter
none noted
10
x 5
ft.
1966
1981
SR.: th tact I
Douglas-: re-
25A
with shell
midden
located •
TABLE A (continued) 14
ARCHAEOLOGICAL SITES WITHIN THE CITY
OF IRVINE AND ITS SRHERE OF INFLUENCE
Site No./
Artifactual
'Date/ .
Planning
CA -Ora-
Description
Material
Si-ze.
Update
Condition
Area
211
shell midden
hammerstone
40
ft.
1966
SR: impacted
I 25A
1981
Douglas: did,
not relocate
216
shell scatter
debitage
40 x 40
ft.
1966
SR: impacted
I 25A
1981
Douglas: de-
-
stroyed
220
shell midden
chipping waste,
210 x 155
ft.
i965
SR: impacted
I 25A
with lithic
mano, scraper
1981
'Douglas: re -
artifacts
located
221
shell midden
scraper; debitage
60 x 30
m.
'1965
SR:'i'ntact
I 25B
with lithic
manos
1981
Weil: -relocated
222
223
224
225
226
1027
artifacts
shell midden
with lithic
artifacts
shell midden
with 1 i th-i c
artifacts
scraper, mano,
pestle
manos, chipping.
waste, hammer -
stone, steatite
bowl
burnt rock,
mano
projectile
points, asphal-
tum, mano, chop-
per, chi-pping
waste
shell midden chipping waste,
with lithic points, pendant
artifacts
lithic scat- scraper, mano,
ter with shell chipping waste,
hearths
shell midden
with lithic
artifacts
shell midden
and historic
debris
75 x 40 m. 1965
1981
225 x 130 ft. 1965
1981
12 x 20 ft.. 1966
270 x 200 ft. 1966
766 x 175 ft. 1966
135 x 80 ft. 1966
1977
1979
SR: impacted. , I 258
Weil: relocated
SR: impacted I 25A
Douglas: re-
located
SR: destroyed I 25B
SR: intact I 25B
SR: impacted I 25B
SR: impacted I 25B
Van Horn-: tested
Douglas: sal-
vaged
TABLE A (continued) 15
ARCHAEOLOGICAL SITES WITHIN THE CITY
OFIRV'INE AND ITS SPHERE OF INFLUENCE.
Site No./ Artifactual Date/ Planning
CA -Ora- Description Material Size Update Condition Area
228 shell midden mano, burnt rock, 1/2 acre 1967 SR: impacted I 21
and possible stone tools 280 sq.. m: 1978. Mabry: tested
ceremonial
center
231. rock shelter
with shell
scatter
cooking stones,
charred human
bone, points,"
beads, stone -
grinding imple-
ments, hammerstones
20 x 15 ft. 1967 SR: impacted I 26
1967 PCAS: tested
1981 " Weil: ,relocated
sj3 2 shell midden points, beads, 150" x 200 ft. 1968 SR: i"mp4cted
With lithic faunal implements, 60'x 55. m. 1977 SR: impacted
artifacts burnt rock, chip-
ping waste, many,
pestle, scraper,
metate .
233
lithic scatter
chipping waste,
150 x 250 ft.
1968
with shell
hammerstone,
1981
mano, choppers-
234
shell midden
none noted:
50 x 75 ft:"
1968
historic ceramics
1981
and glass noted
235
shell midden
chipping waste,"
300 x 50 ft.
A 967
with lithic
mano, bedrock
1981
artifacts
mortar
236
rock shelter,
cooking rock,
50 x 20 m.
1968
and shell
projectile
19'68'
midden
points, shell
1975
beads, bone tools"
1981
244
shell midden
points, manos,
over 40 acres
1965
with numerous
metates, scrapers,
-
1981
lithic "arti-
chipping waste
facts
,C 4
SR: intact . C 4
Weil; relocated
SR: intact
Weil: did not
relocate
SR: intact
Weil: did not
relocate
SR: impacted
PCAS:. tested
Hines: M.A.
"thes-i s
Weill relocated
SR: impacted
Cottrel'l:,par-
tial excava-
tion
I' 25B
I 26
-I 4-5
TABLE A (continued) 16
ARCHAEOLOGICAL SITES WITHIN THE CITY
OF IRVINE AND ITS SPHERE OF INFLUENCE
Site No./
Artifac.tual
Date/
Plann.ing
CA -Ora-
Description
Material
Size
Update
Condition
Area
269
rock shelter
petroglyph
10
x
40
ft.
1969
SR:
intact
126
with shell
midden
270
rock shelter
petroglyph
30
x
- 30
ft.
1-969
SR:
impacted
I
26
with shell
midden
271
rock shelter
none noted
50
x
30
ft.
1969
SR:
i-ntact
I
26
with shell
scatter
rock shelter
none noted
8
x
15
ft.
1969
SR:
intact
I
26-
6272
with shell
1981
Weil,:
relocated
midden
273-
rock shelter
none noted
15
x
25
ft.
1969
SR:
in -tact
I
26
with shell
scatter
275
shell scatter
mano, debitage
200
x
400
ft.
1977
SR:
impacted
125E
with lithics '
1984
ARM:
did not
284
shell midden
none noted
336
rock shelter
petroglyph
with lithic
scatter
341
lithic scatter
hammerstone,
manos, chop-
pers
343
rock shelter
chipping waste,
with shell
flakes, cores
scatter
344
lithic scatter
manos, hammer-
0
stone, -chopper
100 x 200 ft. 1970
6 x 3 x 1-1/2 m. 1971
200 x 300 ft. 1972
1983
30 x 30 m. 1972
1979
20 x 40 m. 1972
1979
relocate
SR; impacted' I 36B.
SR': intact 'I 22
SR: intact I 13B
Padon: relo-
cated
SR: intact I 21
Mabry: relocated
SR: impacted I 16
Mabry: relo=
Gated
TABLE A (continued). 17
ARCHAEOLOGICAL SITES WITHIN THE CITY
OF IRV-INE AND ITS SPHERE OF INFLUENCE
Site No./ Artifactual Date/ Planning
CA -Ora- Description Material Size Update Condition Area
'34.9 lithic scatter hammerstones, 75 x 25 yds. 1972 SR: impacted I 16
milling stone 1979 Mabry: relo-
fragments sated
350
rock shelter
chipping waste,
15
x
15
m.
1972
SR: intact - - I
21
with shell
stone tools,
10
m.
(exclu-
1980
Cottrell: tested
midden
shell instru-
sive
of shel-
ments and
ter)
jewel ry, stone -
grinding imple-
ments, points
361
lithic arti-
manos, metate
20
x
80
m.
1972
SR: impacted I
2A
facts
fragments-, cores,
1982
B-reece: relo-
hammerstones
cated
373
lithic scatter,
manos,-core,
600
x
600
ft.
1972
SR: impacted I
10A-
3 burials
chipping, debris,
1973
Ellis: tested
-
metate fragment
1979
Howard: salvaged
376
lithic arti-
chipping waste;
not
given
.1972
SR: impacted I
21
facts with
point, pestle,
1976
ARI: salvaged
shell scatter
manos
317
lithic arti-
chipping waste,
200
x
50-ft.
1972
SR: impacted I'
21
facts with
metate fragment,
1976
ARI: salvaged*
shell scatter
mano
378
shell midden
chipping waste,
300
x
300
ft.
1972
SR: intact I
21
with lithic
manos, metates,
artifacts
cores, flakes
379
2 rock shel-
cooking stone,
15
x
10-
ft..
1972
SR: intact
ters with
mano, bedrock
10_x
10
ft.
1979
Mabry: tested
mortar, flakes
1980
Douglas: sal-
vaged
382
shell scatter
debitage, burnt
100
x
50
ft.
1972
SR: intact I
21
with lithic
rock
1979
Mabry: rel-ocated
artifacts
9
TABLE A _(continued') 18
ARCHAEOLOGICAL SITES ,WITHIN THE CITY
OF IRVINE AND ITS SPHERE OF INFLUENCE
Site No./
CA -Ora-
Description
Artifactual
Material Size
Date/
Update
Planning
Condition Area
383
rock shelter
with shell
manos, metates,, 50 x 50
chipping waste,
ft. 1972
1979
SR: intact I 16
Mabry: intact,
midden
burnt rocks,
hammerstones
384
lithic scatter
metate fragments, 125 x 75
manos,-chipping
ft. 1972
1979 -
SR: intact I 16
Mabry: relocated
waste, hammerstone
386 shell midden pestle, manos,
with lithic cores,.metate
artifacts
87 lithic scatter manos, metate
fragment
391 lithic scatter .chipping waste,
manos, hammer
.stones, choppers_
478 lithic scatter manos, bowl frag-
ment, chipping
waste, hammerstone
480 shell scatter chipping waste,
with lithic worked shell
scatter
481 shell midden burnt rock, chip-
- ping waste
482 shell midden worked stone,
chipping waste,
burnt rock
483 shell midden burnt rock,
mano fragment,
scraper
250
x
100
-ft.
1973
SR: intact
I 16
1980
Douglas: tested
50
x
200
ft..
1973
SR: i°n.tact
I 16
1979
Mabry: relocated
500
x
500
ft.
1973
SR: impacted
'I 13B
1984
Padon: tested
50-x
100
M.
-1974-
SR: impacted
I 4-5
10
x
30
m.
1974
SR: impacted
I 25A
1975
Drover: tested
40
x
15
m.
1974
SR: impacted.-.
I 25A
50
x
20
m.
1974
SR: impacted
I 25A
1981
Douglas: re-
located
100 x' 20 m. 1974
1979
1981
SR: ilnpacted I 25A
Cottrell': tested
Douglas: re-
located
TABLL A (continued) 19
ARCHAEOLOGICAL SITES WITHIN THE CITY
OF IRVINE AND ITS SPHERE OF INFLUENCE
Site No,./ Artifactual Date/ Planning
'CA -Ora- Description Material Size Update Condition_ Area
494 rock shelter ceramics, chip- 3 x 11:.5 .m. 1974 SR: intact I 17
with shell ping waste,
midden hearth
495'
lithic scatter,
hammerstones,
954 x 370•m.
- 1974
SR: impacted. •I
13B
rock cairns.
manos, chipping
195 x• 90
M.
1978
SR: impacted,
waste, piled
1979
Westec: re -
rock
(1980
located
report)
1982
CSRI: tested-
496
'shell *scatter
manos, cores,
231 x 154
m.
1974
SR: impacted I
17
with lithic
debitage
(indicated
in
1978
Dodge: relocated
scatter
1980 drawings.)
1979
Bean & Vane:
rel-ocated
1980
Westec: impacted
1982
.CSRI: tested
499
lithic scatter
manos, metates,
100 x 50
m.
1974
SR: impacted I
13.B'
chopper, core,
1978
Dodge; relocated
-
debitage
1979
Bean & Vane:
relocated -
1980
Westec: relocated
1982
CSRI: tested-
508
shell scatter
manor, metate
'30 acres
1975
SR: impacted 114
with lithic
fragments,
1979
Westec: portion
artifacts
hammerstones,
salvage,-rec.
cores, flakes
no further
pursuit
511
lithic scatter
chipping waste,,
24,000 sq.
ft.
1975
SR: impacted- 14-5
cores, flakes
513
special activ-
chert cores and
5,000 sq.
ft.
1976
SR: impacted I
2B
ity area
some shell
1978
SRS: destroyed
520
lithic scatter
chipping waste,
10 sq.
m.
1976
SR:. intact I
4-5
flakes, core
1979
SRS: tested
0 -
TABLE A (continued) 20
ARCHAEOLOGICAL SITES WITHIN THE CITY
OF I'RVINE AND ITS SPHERE OF INFLUENCE
Site No./
Artifactual
-Date/
Planning
CA -Ora-
Description
Material Size
Update
-C.ondition
Area
521
lithic scatter
bedrock mortar, 100 x 40-1m.
1976
SR:
intact
I 4-5
with burial
chipping waste,
1978
SRS:
tested
knife, burnt rock,
stone tools, bone
tools, points,
shell implements -
522
lithic scatter
worked stone, 15 x 25 m.
1976
'SR:
intact
I 4-5
stone tool
1978
SRS:
tested
implements
523
1 i thi c. scatter
flakes, cores,
30
x-
-30 m.
1976
SR: intact
I 4-5
hammerstone
1978
SRS: tested -
&24
lithic scatter
manor chipping
10
x
5 m.
1976
SR: intact
I 4-5
waste
543
lithic scatter
hamm_erstone,
unknown
1976
SR: impacted
I 12B
=
debitage,
1977
Cottrell: tested
scrapers
545
lithic scatter
manos, metate
180
x
125 m.
1976
SR: impacted
I 4-5
fragments, ham-
1982
Breece: relo-
merstones, chop-
cated, dis-
p er
to rbed
575
shell midden
flakes, cores,
360
x
160 ft.
1975
SR: intact
UCI
with lithic
chipping waste,
1976-
ARI/Recon:
scatter:
burnt rock
tested
historic
portion
invalid
601
lithic scatter
chipping waste,
60
x
80 ft.
1974
SR: impacted
I 4-5
flakes
1982
Breece: relo-
cated, impacted
602
lithic scatter
bowl fragment,
50
x
50 yds.
1976
SR: impacted
I 35B
manos, cores,
•
metate fragment
TABLE A_(continued) 21
ARCHAEOLOGICAL SITES WITHIN THE CITY
OF IRVINE AND ITS SPHERE OF INFLUENCE
Site No./ Artifattual Date/ Planning.
CA Ora Description Material Size Update Condition Area
617 shell scatter chipping waste, 20 x 30 ft. 1977 SR: intact I 26
with lithic flakes 1981 Weil: site
scatter- destroyed
618 lithic scatter 2 metates 1977 SR: intact I 25B
with some shell 1981 Weil: site
destroyed
619 shell scatter stone tool, 500 x 300 ft. 1977 SR: impacted I 25B
chipping waste 1977 Van Horn: tested
1981 Weil: did not
relocate
20 lithic scatter scrapers, core; 300 x 200. ft. 1977 SR: intact .-I 25B
burnt rock, 100 x 50 ft. 1977 Van Horn: tested
metate fragments, 1-981 Weil: did not
flakes relocate
649 lithic scatter chipping waste 75 x 75 m. 1977 SR: intact I 4-5
1981 LSA: surface
collection
1982 Breece: relo-
cated, dis-
turbed,
650 lithic scatter chipping waste, 75 x 75 m. 1977 SR: impacted I 4-5
manos, metate 1981 Cottrell-: de -
fragment, hammer- stroyed
stones
651 lithic scatter hammerstones, 75 x 75 m. 1977
manos, scrapers 1-981
652'
lithic scatter
scraper, cores,
manos, metates
689
rock shelter
faunal imple-
with shell
ment, chipping
midden
waste
717
lithic scatter
hammerstones,
manos, metate
75 x 75 m. 1977
7.6 x 8.1 m. 1977
(i'nc. talus)
SR: impacted
Cottrell: de-
stroyed
SR: impacted
SR: impacted
100 x 30 m. 1977 SR: i.ntact
I 4-5
I 4-5
I 26
I 4-5
TABLE A (continued) 22
ARCHAEOLOG.ICAL SITES WITHIN THE .CITY
OF IRVINE AND ITS SPHERE OF -INFLUENCE
Site No./
Artifactual
Date/
Planning
CA -Ora-
Description
Material
Size
Update
Condition'
Area
718
lithic
scatter
metate, _manos,
100
x
50
m.
1977
SR:
:intact
I
4-5
hammerstones
719
lithic
scatter
choppers, cores,
30
x
25
m.
1978
SR:
intact
I
2A
scrapers
720
lithic
scatter
metate, scraper,
''400-
x
100
m.
'1978
SR:
intact
I
4-5
cores, manos
721
lithic
scatter
-choppers,
30.
x
25
m.
1978
SR:
intact
I
4-5
729
lithic
scatter
hammerstone;
100
x
20
m...
1978
SR:
intact
I
25B
core, manor,,
1979
Mabry: tested-
1 metate frag-
ment, chipping
waste
730
rock shelter
mano fragments,
=
with shell
chipping waste
midden
731
lithic scatter
chipping waste
732
rock shelter
chipping waste,
with shell
flakes
scatter -
733
rock shelter
chipping waste,
with shell
flakes
scatter
734
rock shelter
none observed
with shell
scatter
735
rock shelter
mano
with shell
scatter
06
rock shelter
core, flakes,
with shell
hammerstone
midden
100 x 100 m. 1978 SR: intact_ I 22
1982 Padon: relo-
cated
20 x 20 M. 1978 SR: intact 122
10 x 10 m. 1978 SR: 'intact I 22
1982* Pa.don: relocated
20 x 30 m. 1978 SR: intact I 22
1982 Padon: relocated
10 x 8 m. 19.7,8 SR: i ntact I 22
1982 Padon: relocated
20 x 30 m. 1978 SR-: intact I 22
1982 Padon': relo-
cated, intact
30 x 28 m. 1978 SR': intact I 22
(inside & out)
TABLE A (continued) 23'
ARCHAEOLOGICAL SITES WITHIN THE. CITY
OF IRVINE AND ITS SPHERE OF INFLUENCE
Site, No./,
Artifactual
Date/
Planning
CA -Ora- Description
Material
Size Update
Condition Area
7.61 lithic
scatter
manos, metates,
undetermined 1978'
SR: impacted 14-5
cores, scrapers
1984
P-adon: did not
relocate
762 lithic
scatter
metates, manos',
1978'
SR: intact I 4-5
cores, discoidal,
1982
Breece: relo-
hammerstone
cated, d-is-
turbed
1984
Padon: relocated
767a&b lithic
scatter
metate fragments,
40 x 40 M. 1978
SR:*intact - I 22
manos, hammer -
stones
&769 lithic scatter manos, cores,
hammerstones
797 lithic scatter chipping waste,
with shell mano, flakes
scatter
.798 special bedrock slick.
Activity
20 x 20 m. 1978 SR-: -intact
50 x 100 m. 1979
1979
1982
799
special
bedrock slick
1979
activity
1982
800
special
bedrock mortar
1979
activity
1982
801
special
bedrock mortar
1979'
activity
1982
03
lithic scatter
chipping waste
30 x 40 m. 1979
04
lithic scatter
chipping waste
40 x 60 m. 1979
805
lithic scatter
chipping waste
100 m. 1979
SR: impacted
SR,: intact
,Padon: not
relocated
SR: intact
Padon-: not
relocated
SR:. intact
Padon: not
relocated
SR: intact
Padon: not
relocated
SR: impacted
SR: intact
SR: intact
I 18
I 25B
I 22
I 22
I 22
I 22
I 22
I 22
I 22
TABLE A (continued) 24.
ARCHAEOLOGICAL SITES WITHIN THE CITY
OF IRVINE AND ITS SPHERE OF INFLUENCE
Site No./
A'rtifactual
- Date/
Planning
CA -Ora-
Description.
Material
Size -Update
Condition Area
806
shell scatter
burnt rock, pro-
350 x 250 m. 1979
SR: -impacted I 16
jectile point
1979
:Mabry: relocated
807
rock shelter
burnt rock,
25. x 30 M. .1979
SR: intact 117
with shell
chipping waste
'1979
Mabry: relocated
scatter
808
rock shelter
burnt rock,
30 x 40 m. -1979
SR: intact I 16
with shell
chipping waste
1979
Mabry: relocated,
scatter
809
rock -shelter
chipping waste
with lithic
s
41810
scatter
lithic scatter
hearth? stone -
grinding and tool
implements, chi-p-
pi n.g waste
811
rock shelter
hearths, flakes
with shell
midden
815
rock shelter
1 cobble mano
with lithic
scatter
822
1) lithic
manos, cores,
scatter
flakes
2) shell
scatter
904
lithic scatter
flakes, cores,
hammerstones
1011
lithic scatter
flakes, mano,
with historic
hammerstone
farm equipment
•
onsite
5 x 10 m. 1979
1979
20 x .20 m. 1979
1979
40 x 40 m. 19:79
SR: intact I 16
Mabry: relocated
SR! impacted I 16/
Mabry.:. relocated 17
SR: impacted I 12A
172 x
105 m.
1979'
SR: impacted. 121
1983
Padon: diA not
relocate
180 x
60 m.
1979
SR: intact I 16
60 x
30 m.
100 x
200 m.
1980'
SR: intact I 13B
12 x 15 m. 1982
SR: impacted I 13B
TABLE A (continued) 25
ARCHAEOLOGICAL SITES WITHIN THE CITY
OF IRVINE AND ITS SPHERE OF INFLUENCE
Site No./ Artifactual. Date/ Planning
CA -Ora- Description Material Size Update Condition Area
1029 rock shelter none noted 10 x 4 x 3 M. 1-982 SR: impac.te_d I 22
- with 'shell
scatter
1 Relocated = found again.
6
•
•
26
Wa
The archival search also revealed that additional archaeological work has
been conducted at several of these sites-.. Previous systematic. -surveys have
also included major portions of the project,area. These areas -we -re- outlined
on the appropriate USGS topographic maps in order to defi-ne the remaining
unsurveyed areas. From the compiled data, two indexed base -maps have been
prepared. One base map consists of 'recorded archaeological sites. indexed by
the trinomial site number designated by the State C1 eari.nghouse.. For refer-
ence, the base maps include those archaeological sites, located within the Uni-
versity of California at Irvine campus; however, these -sites, were not listed
in Table A since they lie outside the direct project area.
The second base map consists of recorded field surveys indexed according
to the area covered, the company conducting the .survey; and the date the
report was submitted.. Only those surveys for which! reports have.b.een prepared
and submitted to the two resource agencies referenced- above were included ,on
the map and accompanying index.
Background
Prior to passage of the California Environmental Quality Act -,of 1970
(CEQA), most local agencies did not require systematic surveys of private
_properties for archaeological resources, Early surveys .were -conducted by
interested archaeologists, both avocational and professional, whenever volun-
teers were available and landowner permission could be obtained. As a result-,.
the Pacific Coast Archaeological Society (PCAS.),, an avocational group, and
Archaeological Research, Inc. (ARI)., a non -.profit corporation, conducted most
of the pre-1974 archaeological surveys. Surveys conducted .by PCAS.were on a
vol u'nteer basis.. However, The I rvi ne Company funded many, of the surveys con-
ducted by ARI in the late 1960s and early.1970s (Schroth 1979):
Since 1970, most local agencies have required systematic surveys of pri-
vate properties as part of the Environmental Impact Report process., In 1973,
the C.ity of Irvine adopted a General Plan that outlined goals., obj.ectives,,
action policies, and standards for community development. The Historical and
Archaeological Sites Element of the General Plan provided a. -broad policy
guidance for the disposition. of hi`stori cal and archaeol ogi-cal sites,, and 'for
development of the historic context of the Irvine area. - With implementation
of the California Environmental Quality Act came the ,need for more definitive
policies. In February of 1975, discussions on the proper role of archaeology,
history, and paleontology in the overall planning policies of the City began.
This discussion culminated in the adoption of a Historical, Archaeological,
and Paleontological Policy and Program. The policy -package and -action pro-
gram:
•
27
Ua
1. Establish historical, archaeological and. paleontological plan-
ning programs as a priority item in the City;
2. Allocate staff time and City funds to the pursuit of the pol. i cy;
3. Establish an "Historical., Archaeological, and Paleontological
Committee" as an advisory committee to the City._
Previous Surveys and Reports
There are two major problems or concerns regarding archaeological field
surveys and resulting reports. The first and greatest problem: applies
primarily to the earliest surveys, while the second and. 'lesser concern applies
to reports submitted since 1976.
Since surveys done prior to passage and implementation of CEQA were
undertaken by archaeol.gists primarily for specific areal or research interest,
reports may not have been prepared. 'If reports were prepared, they may' be
lost, consist only of a brief letter, or contain only vague or ambiguous
descriptions of the methods used and areas covered. Such reports fail to meet
CEQA Guidelines.
Generally, reports have 'been prepared on' surveys done since 1976,
although there may be a lag time of a few days to several months between com-
pletion of a report and submission of that report to the State Clearinghouse.
As local agencies have become more specific in their guidelines for imp.lemen-
tation of CEQA., the surveys and resulting reports have become more consistent,
accurate, and complete.
Even high -quality surveys and reports undertaken to implement CEQA guide-
lines -may not be adequate if field conditions are ,poor. Thick vegetation,
particularly after a winter of heavy rainfall.,. may obscure the ground -surface,
and require that further surveys 'b& conducted after surface vegetation is cut
back or removed.
For purposes of this study, vague. location information or no desc.ription
of the survey methods used flagged a survey as inadequate. Any areas suppos-
edly covered by such studies were then included in the present systematic
survey. However, if an area was noted as sensitive for archaeological re-
sources or as unsurveyed because of dense vegetation cover, and if the survey
report over that area was judged adequate, then that area was excluded from
this present study. These areas were excluded because the survey_ reports
• recommended that additional walk -over investigations be conducted when visi-
bility is better and prior to approval 'of the -Tentative Tract Map.
WE
Field Methods
Lsa
The topographic diversity of the study area required the use of several
different survey techniques in order to conduct an adequate yet economical
reconnaissance. - The degree of ground visibility, the ruggedness of the
terrain, and the potential for cultural resource, areas demanded flexibility.
The field crew made standard transects, with the surveyors spaced at 15 to 20-
meter intervals, over approximately two thirds of the surveyed area. This was
most effective in citrus ,groves, open valleys, broad knolls, and flat
terraces. In standard, transects; the individual surveyor followed a zigzag
path covering all of the .sector while creating minimum overlap. At narrow
ridges, the survey team split into individual teams to inspect the individual.
erosional fingers and isolated knolls.
The survey team also did spot- check.ing.. Occasionally, a- bedrock cl-aster
or overhang may be noted on the side, of a hi-11 or just outside a study
boundary. In such instances a surveyor would visit these areas to search for
mortars, caches, caves, or other site indicators.
Throughout the survey the crew examined for subsurface remains by
inspecting any available rodent burrow backdirt, various strata cuts, and
exposed drainage banks.
Special Problems
Eight portions within the previously unsurveyed study area coul d not be
inspected due to a vari.ety of circumstances. The most extensive unsurveyed
portion is the nursery and . adj-acent agri c.ul.tural fields located between
Jeffrey Road and Sand Canyon Road, south of Siphon Reservoir and Hicks Canyon
Wash; where crops and the nursery prevented: the crew from surveyi=ng. The
second area not inspected was a small knoll located just south of Lambert
Reservoir, where several .grazing bulls prevented a systematic survey. The
third area is the Orange County Industrial Farm property .and the agricultural
fields immediately adjacent to this property. New plants and densely -growing
crops in the fields and restricted entry onto the County Farm property pre-
vented an adequate survey of this area. The fourth area not -inspected con-
sisted of the Lion County Safari property, deleted because of the zoo. _The E1
Toro USGS 7.5' quadrangle contains these four unsurveyed areas. The remaining
areas not inspected include four small portions on the Tustin USGS 7.5' quad-
rangle. The southwest corner of the intersection of the Laguna Freeway and
I-405, covered by a strawberry crop, was the fifth unsurveyed area. The'last
three unsurveyed portions are agricultural fields located within the area
bounded by. Bryan Road, Myford Road, Little San Joaquin Val l,ey, and Culver
Boulevard. New plants and strawberries in these fields limited crew entry.
•
29
Wa
The total area not surveyed measures approximately. 1,.400 acres. These areas
not surveyed are indicated on the topographic base map.
William H. Breece and:a two or three -person field crew conducted this
systematic survey of- the study area between November 12 and December 11,, 1984.
The crew spent a total of 363 person -hours in the field. The total area sur-
veyed measures approximately 10,500 acres.
FIELD SURVEY RESULTS
The systematic; on -foot survey of the study area' documented three pre-
viously unrecorded prehistoric sites., -and seven previously unrecorded prehis-
toric isolated finds. In addition, the survey crew found a sandstone cave
with a possible prehistoric etching on the wall, designated as an archaeo-
logically .sensitive area until further research documents its prehistoric
value. The following provides a description of these new cultural resources.
CA-Ora-1069
This site is located' southwest of. the intersection of the Laguna Freeway
and I-405. The site encompasses a north/south.trending ridge, a low knoll,
and a slope that leads down from the ridge. The site overlooks *an unnamed
drainage to the east. Site CA-Ora-904 lies approximately 300 meters north of
this site at the northern end of the ridge. On the low knoll located imme-
diately adjacent to the drainage. at 310 feet above sea level,' the crew noted
three oval granitic mano fragments, one granitic metate fragment, one chert
core, one metavolcanic core, and five Pecten shell fragments-. The ridge por-
tion of the site, located at 460 feet above sea level, yielded one
metavolcanic core, one obsidian. flake, two chert flakes, tw.o, metavoicanic
flakes, three granitic metate fragments and a single- Chione shell fragment.
The site material continued from the ridge area to the knoll located south-
west. On the gentle slope leading to this knoll, the crew -recorded one quart-
zite core tool, one granitic hammerstone, one granitic metate fragment, two
broken, oval granitic manos and one piece of chert debitage. The site area
measures approximately 200 meters east/west and 60 meters north/south. The
slope between the ridge and the low knoll rises. steeply, however, the crew
noted three metate fragments and mano fragments on this slope: The types of
artifacts at the site indicate stone tool manufacturing and, extensive milling
and grinding activities. Shellfish fragments i_n the rodent back dirt on the
low knoll indicate the possiblfty of subsurface material also at this site.
Broken pieces of wood and metal, remnants of farm equipment, are found on the
ridge top and a dirt access road passes through the site area at the ridge to
• the southwest.
0
30
CA-0 ra-1070
Lsa
This site lies above Agua Chinon Wash, east and north of the E1 Toro
Marine Base. The site is located on ,three adjacent knolls, connected by -a
saddle- to the southwest and -separated. by a small drainage to the -northeast. A
dirt access road bisects the main knoll of the site area. The crew recorded
on the central knoll ten granitic, oval whole manos-, twelve granitic mano
fragments', four granitic metate fragments, six cores, 30 flakes-, and one meta -
volcanic scraper. Chert,'jasper, and metavolcanic flakes were noted with the
majority consisting of :chert. None of the flakes showed retouching or 'use.
0-n the southwest knoll the crew noted two granitic 'mano fragments-, one whole
granitic mano, and seven pieces of a single metate. The knoll located at the
northeast yielded one whole granitic, basin metate, one granitic mano,, and -one
mano fragment.- The whole metate basin 1-ies approximately '120 meters from the
central knoll, with the other artifacts' found between this metate and the
central knoll. Disturbance to the site area includes the dirt access road and
discing along the edge of the southwest knoll, but most of the site remains
undisturbed. The site measures approximately 170 meters northeast to south-
west-, and 40 meters northwest to southeast.
CA-Ora-1071
This prehistoric' site is located above and on the west side of Agua
Chinon Wash. It lies one and a half miles northeast of Lambert Reservoir.
The entire site consists of a concentrated area of lithic flakes, estimated at
more than 200 flakes. This count included'.cortical, primary; secondary, and
retouched flakes as - well as chipped debris. One chert core. and an unused
Cheri chunk was also found. Also 95 percent of the material is the brown -
yellow chert, with the remainder consisting of 'gray -banded, red, and black
chert. The site area includes a rather steep -sided ridge, with the flake -
concentration on top, 800 feet above sea. level. -The site area measures
approximately-50 meters southeast/northwest, and 22 meters northeast/ south-
west. The crew noted no disturbance to this site except for minimal soil
erosion. Inspection of the rodent burrows indicated no -midden soil. -
Archaeological survey forms have been filled out and submitted to the
UCLA Archaeological Survey to document these newly -recorded sites. Due to
confidentiality, these forms are not included with this report, but are avail-
able for review at the State Clearinghouse.
Isolated Artifacts
Isolate #1. The first isolated find consisted of one shallow - basin
metate fragment. It was located in a saddle southeast of- Sand Canyon Creek
•
31
Lsa
and north of Shady' Canyon. Careful i-nspection- of the surrounding area failed
to reveal any additional cultural material. Photographs are. on file at LSA.
. Isolate #2. This isolate was a granitic bowl fragment found .200
meters northeast of CA-Ora-807. No other cultural material was observed with
this artifact. It lies on a small knoll across,from a south -trending drain-
age. Photographs are on file at LSA.
Isolate #3. This isolated artifact was :located in a road -cut adja-
cent to the citrus grove above the channelized Peters Canyon Creek, approxi-
mately 60 meters northeast of Bryan Road. It consisted of a whole chest pro-
jectile point. A careful inspection of the area yielded no additional arti-
factural remains. Photographs are on file• at'LSA.
Iso-late A. The crew found this granitic shallow basin metate -frag-
ment within the far northwest corner of the project area. It lies within a
citrus grove 35 meters south of a dirt access road and about 300 meters• east
of the future extension of Myford Road. The surface survey did not yield any
other artifacts within the vicinity of this metate fragment. Photographs are
on *file at LSA.
Isolate #5. This isolate artifact consisted of one granitic, whole
pestle. It was located on the southern slope of a low knoll, and 400 meters
northeast of CA-Ora-1070. Sparse sage and cactus permitted a c-areful inspec-
V on of the area for additional artifacts or midden soil; however, none were
noted. Photographs are on file at LSA.
Isolate #6. Near the far -eastern border of .the project area, the
crew found a w ole, granitic mano. It was located on.a knoll overlooking
Borrego Canyon Wash. Sparse vegetation surrounding this isolate gave the crew
good ground visibility. No other indications of prehistoric use of the area
were noted. Photographs are on file at LSA.
Isolate V . Within a 20 by 15 meter area, the crew found three chert
chunks. These, were located in a plowed field north of Irvi-ne Boulevard and
far away from a natural outcropping, of chert material. ,However, these speci-
mens showed no flake scars, the evidence of prehistoric use. No other arti=
facts or midden soil was noted for this area.
Isolate artifact forms have been prepared and submitted to the UCLA Arch-
aeological Survey to document these finds. By definition,. isolated archaeo-
logical finds are not focused areas of past human activity and therefore are
not considered archaeological sites. Their distribution, however, may be
indicative of exploitation of the area .and procurement activities. 'Because
LJ
32
LEM
the, research potential of isolated finds' is low and the, :artifacts themselves
do, not constitute significant cultural- resources, the included .description and
filed' locational information are considered -'adequate mitigation for these
finds.
Previously Recorded Archaeological Sites
The following sites were recorded during previous surveys and -were rein-
vestigated. These sites lie within or immediately' adjacent to the present
surveyed portions of the study area. These' previously recorded sites were
updated as follows.
CA-Ora-161. Originally, this site was recorded in 1966 and is.
located near the intersection of Laguna Freeway and I-405.. The survey, crew
relocated this site in the pasture south of the existing ranch house. They
noted one flat granitic metate, one basin granitic metate, three complete
granitic �manos, one metavolcanic hammerstone- and core, and a chert flake.
Subsurface material is likely to be, found at this site.
CA-Ora-349. This site was recorded on 'a- knoll overlooking - Sand -Can-
yon Creek and consisted of manos, milling -stone fragments, and' hammerstones
with a few shellfish fragments. The- survey crew relocated this site and noted
oneChione shell fragment, one whole granitic mano, .and two metavolcanic cores
on_ the surface.
CA=0ra-361. T. C. Elliott and John Houser recorded this site, in.•1972
and noted metates, hammers"tones, manos, and cores at the site.• The crew noted
two granitic, whole manos, one granitic mano fragment, and one granitic ham-
mers.tone. Photographs of this site are on file at LSA.
CA-Ora-383-. The survey crew relocated this site :approximately 175
meters northwest of the Sand Canyon powerline which- overlooks the Sand Canyon
Reservoir. The survey crew recorded 1: granitic bowl fragment, two ground -
stone fragments, fire -cracked rocks,' three pieces of burnt :bone, seven meta -
volcanic flakes, three chert flakes, and two granitic flakes. Pecten. Chione,
and Ostrea- shell fragments were also found at this 'site.. The site extends
along an east/west dirt road for approximately 150 meters.
CA-Ora-478. T. Cooley
et al.
recorded this site in 1974 i•n
Hicks
Canyon and noted that a dirt
road had
been graded across the east side
of the
site area. After careful
inspection
.it appears that continued use
of the
access, road disturbed this site
area.
The current survey crew did not
observe
any artifactural remains at
this location.
•
091
Lsa
'CA-Ora-494. This rock shelter is located on a. _steep slope,. overbook-
ing an east west drainage. The survey crew relocated this shelter_ and noted
midden soil with Pecten shellfish fragments, one possible metate fragment, and .
a possible rock wall. Photographs are on, file at LSA.
CA-Ora-495. Previously, CA=0ra-495- has been recorded as a possible
rock cairn site which covers an extensive area.- The current survey crew, -how-
ever, only observed at this site one bowl fragment, two granitic mano frag-
ments, and four non -utilized flakes. While this definitely is indicative of
the site, it reflects the additional investigation conducted by -CSRI (1982) at
this site. They partially surface collected this site in order to mitigate
any adverse impacts to -the site area from use- of the Southern Ca-lifornia
Edison access road.
CA-Ora.496. The- crew relocated this site on a disturbed knoll where
a transmission tower and access road intersect. They found one granite -bowl
fragment, two whole granitic manos, two granitic mano fragments, one metavol-
canic flake, and one metavolcanic core.. Photographs are on file at LSA.
CA-Ora-499. This site is situated west of Laguna Canyon Road and
overlooks I-40 . It also falls within the Southern California Edison trans-
mission -line boundaries. The crew observed only one whole granitic mano and
one whol-e granitic hammerstone at this location.. Cultural Systems Research,
Inc. (CSRI) also surface -collected at this site in 1982. No subsurface
investigation was -conducted at that'ti'me. -Photographs are on file at LSA.
CA-0ra-545-. This site is situated within the citrus grove north and
east of Lambert Reservoir. T. Cool.ey in 1776 had noted on the surf -ace manos,
metate fragments, hammerstones, choppers, -and -flake tools; however, our sur-
vey failed to relocate this site. The agricultural operations have disturbed
and possibly reburied this site.
CA-Ora-601. This site is situated on a low knoll* southeast of Siphon
Reservoir. The field crew noted eleven chert .flakes, one whole granitic mano,
one granitic mano fragment, three metavolcanic flakes,.and I one, -red, jasper
flake. The site lies immediately adjacent to a citrus grove.
CA-Ora-734. This rock shelter is situated in Bommer. Canyon and con-
tained a shellfish midden eroding out of the cave. The current crew relocated
the shelter and noted in addition to the midden, one metavolcanic flake.
Photographs are on. file at LSA.
CA-Ora-735. This rock shelter is also located in Bommer Canyon,
approximately 100 meters 'northwest of CA-Ora-734. The crew observed only
L J
34
Lsa,
mi dden soi 1 wi th 'shel 1 fi sh fragments ' around , the outsi de of the shel ter.
Photographs are on file at LSA.
CA-Ora-767 a and b. Recorded i,n 1978, the site - is situated on a low
knoll and extends ..into the pasture area to the -northeast. The survey crew
relocated this site and found eight grani ti-c manos; four granitic mano frag-
ments, six granitic metate fragments, one .schist metate fragment., three fe1-
site. cores, two metavolcanic flakes, and a few shell fragments. The si'te area
remains in good condition.
CA-Ora-803. The site consisted of a few lithic flakes and was
located along a ridge slope in Shady -'Canyon. W.L: and J. Tadlock recorded
this site- in 1976. Even with good ground visibility, the survey crew found no
evidence of this site.
CA-Ora-804. This site also was located in Shady Canyon along the
ridge face and of a sparse .scatter of flakes. W.L. and J. Tadlock-
.recorded this site in 1976. A careful check of the suspected location, how-
ever, yielded no indication of a site.'
CA-Ora-805. This, site was recorded fn Shady Canyon at the confluence
of two drainages. The survey crew observed only one chert'flake in the rodent
back dirt. It appears that more artifactual material may be buried at this
location.
CA-Ora7806. This site was recorded at the confluence of the Shady
Canyon and Sand Canyon drainages. The survey crew relocated and noted a dense
shell midden of Pecten, Chione, and O.strea,, and one chert-flake, four metavol-
canic flakes, and one chert core fragment. 'Photographs are on file at LSA.
CA-Ora-807. The- small rock shelter is located along the proposed
Sand Canyon Road extension. The crew noted a possible midden deposit. Pecten
and Chione shellfish framents were observed and one chest flake. Photographs
are on fie at LSA.
CA-Ora-808. This rock -shelter is also located along the Sand Canyon
Road extension. The crew noted a shell midden deposit inside and in front of
the shelter. They also noted one quartzite flake and one metavolcanic flake.
The shelter opens to the northeast and is partially hidden by vegetation.
CA-Ora-809. This rock shelter was locate-d above Sand Canyon Creek
and contained chert flakes and a few shell fragments. The survey crew relo-
cated the rock shelter; however, found no artifactual, or ecological material
associated with it.
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CA-Ora-810.- This open site is located on the terrace that overlooks
Sand Canyon Creek. It is located at the intersections of two power lines.
The crew noted in the rodent back dirt 12 metavdlcanic flakes, eight chert
flakes, three quartz flakes, and one Ostrea shell fragment. The rock ring
feature noted previously -was not relocated.
CA4ra-811. This rock shelter was located west of Rattlesnake Reser-
voir. T. Cooley recorded this site in 1979 and noted the area had been graded
for flood control purposes. The crew relocated the rock shelter, however,
found no evidence of prehistoric use. No midden was observed or artifacts
noted on the surface.
CA-Ora-904. L. McCoy originally recorded this site on a ridge, finger
and described the site as a thin lithic scatter. The current survey relocated
the site and found one whole metate, two granitic.manos, two, granitic mano
fragments, one granitic metate fragment, and one felsite flake. Photographs
are on file at LSA.
CA-Ora-1011. This site lies on top of a knoll that overlooks I405
and was described as a temporary -campsite. Observed artifactual material
included three chert flakes, one granitic..mano, and one chert core. The
shellfish fragments noted before were not found by the survey crew.. Photo-
graphs are on file at LSA.
In addition to the reinvestigated sites and the newly -recorded sites, the
survey crew located in Shady Canyon a possible prehistoric petroglyph in a
small cave. No other indications of prehistoric use exists inside or outside
of the cave. The suspected petroglyph design has been scratched into the sur-
face of the south wall of the cave. Presently, comparative research suggests
similarity to those pictographs located at Vasquez Rocks in the Upper Santa
Clara River (Los Angeles County) (King 1981) or to rock -art designs in Baja
California. To clarify whether this etched design is prehistoric or not, fur-
ther research has been initiated with the Rock Art Research Lab at UCLA.. This
location then is archaeologically sensitive, however, an official State number
will not be assigned until the prehistoric nature of the design has been veri-
fied.
CONCLUSIONS AND RECOMMENDATIONS
This inventory identified a total of 132 archaeological sites in the City
of Irvine and its sphere of influence. The archival research reviewed more
than 75 archaeological reports. The field reconnaissance covered more than
12,000 acres. It resulted in the discovery of three previously unrecorded
sites, a possible petroglyph site, and numerous isolated finds. In addition,
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25 previously recorded sites lying within or immediately adjacent to -the sur-
vey areas were reinvestigated for site report updating.' The archival and
field research are indexed by three USGS topographic base maps and a survey
base chart (Appendix C).
However, the potential for discovering additional archaeological.
resources cannot be dismissed. Approximately 1,400 acres .remain .unsurveyed
for cultural resources, where dense ground cover and fragil-e agricultural
activities prevented inspection. Furthermore, investigation from a walk -over
survey cannot always reveal subsurface remains. Known sites prove that the
project area was long used by prehistoric inhabitants, and -there undoubtedly
remain important, undetected archaeological sites. It is recommended that the
remaining unsurveyed portions be systematically surveyed as soon as field con-
ditions permit. Crop rotation begins in March and April, and would allow sur-
vey of several of these areas.
The archival and field investigations of this inventory indicate that
there are important archaeological resource-s in the study area. However, the
inventory does not address significance and cannot be used to determine eligi-
bility under CEQA or the National Register nomination process under the
National Historic Preservation Act of 1974. - Further research and study by
qualified archaeologists under review of the HAP Committee, remains a require-
ment for any development project which may. ffsturb archaeological resources.
Although this i.nventory provides the basis -for organizing future i-nvesti-
gati.ons, site -specific studies cannot- address some of the= important questions
about our prehistoric past, questions which requ ire .intersite eomparisions.
This i nventory ' serves as a source for deriving i ni ti al intersite Simi l.ari ti es
and differences, and for initiati-ng re.giona.l hypotheses about prehistoric
life-styles and conditions, which can .then be pursued in site -specific
studies. It can. also provide a geographical and archaeological reference for
coordinating the concurrent investigations at two -or .more separate sites. It
establishes the local framework for recording of future surveys and excava-
tions, and for identifying areas set aside in preservation. It also identi-
fies for the City of Irvine the archaeological resources which may be impacted
by future development plans. The data provided on the maps and in the, accom-
panying report are intended to inform specific project planning teams and
qualified archaeologists so necessary steps can be taken to ensure the protec-
tion and preservation of the irreplaceable data rel ati n.g to the prehistory of
Orange County.
It is further recommended that the site -specific information, the maps in
particular, should be considered highly confidential,, since dissemination of
this information could be detrimental to the scientific/cultural value of
these resources. Site -specific data should not be made -available as a public
document.
37
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0
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Dixon, Keith
1974 Archaeological Resources and Policy Recommendations of Long Beach.
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Dodge, William
1978 An Archaeological Assessment of Eight Cultural Localit.fes Along the
San Onofre - Santiago,220-KY Transmission Line. Submitted to South-
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Douglas, . Ronal d and Theo Mabry ( Archaeological Planning Collaborative)
1979 Excavations at CA-Ora-227, a Late Prehistoric Site in the San
Joaquin Hills Region of Orange County, California. County of
Orange, Santa Ana, CA.
Douglas, Ronald
1980 Archaeological Investigation of a Late • Prehistoric -Horizon Site, CA-
Ora-379, City -of Irvine, California. Archaeological Planning Col-
laborative (LSA). Newport Beach, CA.
1980 Excavation at CA-Ora-386, A Millingstone Assemblage Site Overlooking
Sand Canyon Wash, Orange County, California. LSA, Newport Beach,
CA.
Douglas, Ronald (Larry Seeman and Associates)
1981 Archaeological Resource Survey Northern'Coastal Hills Planning Area,
Orange County, -California, Newport Beach, CA.
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Drover., Christopher E. (Archaeological Research, Inc.)
1975 Test Excavations ,of Lower .Bonita Creek. Pacific Telephone, Newport
Beach, CA.
Ellis, Robert R. (Archaeological Research, Inc.)
1973 Report, Archaeological Test Excavations. at Site Ora-121, Orange
County, California., Beckman Instruments Company, Newport Beach,
CA.
1913 Archaeological - Report of Test Excavations at Site Ora-373, Orange
County, California. The Irvine Company, Newport Beach, CA.
Gill, Pamela M. (Master's Thesis)
n.d. A Report of the Excavation at CA-Ora-120. California State
University, Fullerton. Prepared for The Irvine Company by -
Archaeological Resource Management Corporation.
He.izer, R. F.
1968 - The Indians of Los Angeles County: Hugo Reid' s Letters of 1852.
Southwest Museum Papers 21, Los Angeles.
Howard, Jerry Brian
1979 Archaeological Investigations Conducted at CA-Ora-373, An Encinitas
Tradition Site in Orange County, California. Archaeological
Research, Inc., Goleta, California and Archaeological Planning Col-
laborative, Newport Beach, CA.
Hines, Phillip
1975 Faunal Analysis of Site, CA-Ora-236:. On file at the PCAS Research
Library.
Hurd,. Gary Si.
1980 Test Excavation for CA-Ora-116. University of California, Irvine,
CA.
n.d. Statistical Analysis of Marine Mollusea recovered from CA-Ora-116.
On file at the PCAS Research Library.
Johnston, B. E.
1962 California's Gabrielino Indians. Southwest Museum, Los Angeles.
Kaldenburg, Russell H., an,d Charles S. Bull
1976 Archaeological Investigations at the World Medical Foundati-on Site,
. Orange County; California. Prepared for The Iry the Company, Newport
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King, Linda
1981 The Incised Petroglyph Sites at Aqua Dulce, Los Angeles County Cali-
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King, T. F., Michael J. Moratto, and N..Nelson Leonard III
1973 Recommended Procedures for Archaeological Impact Evaluation. Joint
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Koerper, Henry C.
1981 Prehistoric Subsistence and Settlement in the Newport Bay Area and
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Kroeber, A. L.
1925 Handbook of the Indians of California. Bureau of American Ethnology
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1966 Ven-70 and Its Place in the Late Period' in the Western Santa Monica
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1978 Test -Level. Investigations Conducted at CA-Ora-228,' Turtle Rock,
Irvine, California. Broadmoor Homes, Irvine, CA.
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• 1979 A Test -Level Investigation of CA-Ora-729, Bonita Canyon Creek, City
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1979 Assessment of Ora-373, Home Improvement Center; Ir.vi.ne, California.
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of -Ways, Irvine, California. On file at'UCLA Archaeological Survey.
McGimsey,'Charles R. III and Hester A. Davis (Eds.)
1977 The Management of Archaeological Resources in The Airlie House
Report, a special publication for the Society for American Archaeol-
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Mitchell, Laura L.
1976 National Register Application for Rancho San. Joaquin Headquarters
and House (CA-Ora-111.) On file at the PCAS Research Library.
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APPENDIX A
APPLICABLE FEDERAL AND STATE LAWS
FOR ARCHAEOLOGICA RESOURCES
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RELEVANT STATE AND FEDERAL REGULATIONS
Relevant State and Federal laws which pertain to archaeological resources
located on public lands are summarized as follows:
California Environmental Quality Act. of. 1970 (P.R.C. Section 21001)
Requires that cultural resources be 'considered in assessing the
environmental impact of proposed projects within the State and that
examples of the major periods of California- history will be pre-
served.
California Publi-c Resources Code-= Ghapter 1.7, Section-5097.5
Prohibits the knowing destruction of objects of antiquity with-
out a permit (expressed permission) on public lands, and provides
for criminal sanctions.
California Penal Code, Title 14, Part 1, Section 622-1/2
Provides that any person,'not the owner thereof, who willingly
destroys or injures objects of archaeological or historical value;.
whether on public or private land, is guilty of a misdemeanor.
California Administrative Code, Title 14, Secti,on 4307
States- that, no person shall remove, injure,, disfigure, deface
or destroy any object,of paleontological, archaeological or histori-
cal � interest or value: Section 4309 provi-des that, if thought to
be fn. the best interest of the State Park System, ,the director may
grant permission to remove, disturb, etc. objects of antiquity.
California Public Resources Code - Ghap_ter 1332, Section 5091.9
Establishes the California Native American Heritage Commission
to. make recommendations to encourage private property owners to .pro=
tect and preserve sacred places in a natural state and to allow
app.roproi ate access to Native Americans for ceremonial' or spi ri tua-1
activities. The Commission is authorized to as-sist Native Americans
in obtaining appropriate access to sacred places on public land-s,.
and to aid State agencies in any negotiations with Federal agencies,
for the protection of Native American sacred places on Federally -
administered lands in California.
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The Antiquity Act of-1906 as Amended
This act sets forth the Federal Government's basic principle
of protection, preservation, and public -availability of archaeo.logi-
ca-1 resources. The act provides for Federal control of all
archaeological resources on Federally -owned or controlled land.
The Historic Sites Act of 1935
This act declares a national policy to preserve historic
(including prehistoric) sites, buildings, and objects of national
significance for the public.
The Reservoir Salvage Act of 1935
This act provides for the survey and necessary research of
archaeological sites affected by. the construction of dams and
resultant reservoir areas. This act may affect .treatment plants,
storage plants, and rights -of -way as well as dam and reservoir
areas.
The Historic Preservation Act of 1966 as Amended
This act provides for an expanded National Register of dis-
tricts, sites, buildings, structures, and objects significant in
American history, architecture, archaeology, and culture- and makes
provisions for matching funds to help acquire and/or preserve them.
This act also affects properties eligible for listing.
The National Environmental Policy Act .(NEPA).
Provides for the protection or enhancement of the cultural
environment. "An act for the preservation of American Antiquities."
The National Archaeological/Historical
Preservation Act of 1974mended
This act provides Federal agencies with methods of mitigati-ng.
impacts of their undertakings upon those his.tori.c properties that
contain scientific, prehistoric, or archaeological data.
Public Law 95-341; .92 Stat. 469; 42 U.S.C. 1996
• This law provides for American Indian religious freedom and
access to traditional Native American sacred sites.
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APPENDIX B
RESUMES
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Natural Resource Management
Transportation Engineering
Environmental AssessmentLsa. .
Community Planning
E.LIZABET_H F.. PADON
PRINCIPAL INVESTIGATOR
SUMMARY OF QUALIFICATIONS -AND EXPERIENCE
EDUCATION.
University of Wisconsin -Milwaukee, Master of Science in Anthropology,
summa cum .laude, Milwaukee, WI, 1.977.
Beloit College, Bachelor of Arts 'in International Relations, -cum laude,
Beloit, WI, 1970.
ARCHAEOLOGICAL -FIELD TRAINING
University of Wisconsin -Milwaukee, WI (Crawfish River Archaeological Field
School), 1976, Lynne Goldstein, Director.
PROFESSIONAL EXPERIENCE
Principal Investigator, LSA, Inc.,- environmental planning consultants,
Newport Beach, CA, 1981-present.
Research Collaborator, UCLA Institute of Archaeology, Los Angeles County,
1980=present.
Consulting Archaeologist, Los Angeles, Ventura, and Riverside Counties,
1979-1981.
District Archaeologist, CalTrans District 7, Los Angeles, CA, 1980-1981.
Survey Archaeologist, UCLA State Historic Preservation Regional Office,
Los Angeles, CA, 1980.
Archaeologist, U.S. Army Corps 'of Engineers- - Los Angel -es District, Los
Angeles, CA, 1979-1980.
Research Ass.istant, Museo Nacional de Costa Rica, San Jose, Costa Rica,
1979.
Archaeological Research Assistant, UCLA Archaeological Survey, Los
Angeles, CA, 1977-1978.
• Numerous field crew member and supervisory positions on professional
archaeological projects throughout Southern California, Wisconsin, and
Costa Rica, 1976-present.
❑ 610 Newport Center Drive, Suite 555 • Newport Beach, California 92660 • (714) 640-6363
0 2606 Eighth Street 9 Berkeley, California 94710 • (415)' 841-6840 .
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Elizabeth F. Padon
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PRINCIPAL PROFESSIONAL RESPONSIBILITIES
-Conducting archaeological research,projects with pri nc"i.p"al .responsi bi 1 i ty
as follows:
Administer the Cultural Resources Division.(CRM) of LSA, and oversee/
coordinate all of its archaeological, historical, and paleontological
activities and services.
. Prepare CRM research designs, literature reviews, and background syn-
theses.
. Conduct archaeological field surveys, "excavations, and laboratory anal-
yses.
. Prepare National Register nominations, Historic Property,. Survey
"reports, final- re ports-on"archaeological investigations, and CRM sec"
tions of EIRs and EISs.
Develop,. execute, and monitor preservation strategies or mitigation
programs for known cultural resources.
. Provide technical and legal CRM consulting services at the, planning
stages of development programs.
. Coordinate CRM public outreach and service activi-ti-es.
. Provide expert testimony in public"hearings and legal proceedings.
PUBLICATIONS
Archaeological Reports and Manuscri-pts on File at UCLA: Los -Angeles,
Ventura, and Orange Counties. Occasional- Paper 10, .Institute of Archaeo-
logy, University of.California, Los Angeles, 1982.
Author or co-author of numerous professional archaeological site survey
and excavation reports (examples available upon request).
Cultural Resource Management Track Coordinator and Chairperson at the
State Historic Preservation Conference, May 1983, Orange; CA.
SELECTED REPORTS
Cultural Resource Assessment of Forster Ranch, San Clemente -,,California,
LSA, Inc., October 1984.
•
Elizabeth F. Padon
Page 3 LCM
Archaeological Testing at CA-Ora-660, Cameo del Mar, Orange County, Cali-
fornia, co-authored with Bill Breece, LSA, Inc., August 1984
Historical Review of The Irvine Company Agricultural Headquarters,
Irvine, California, LSA, Inc., July 1 .
Archaeological Resource Assessment, Ridgway/Ahmanson Project, Riverside
County, California, LSA, Inc., July .
Cultural. Resource.. Assessment, Planning Area 34B, Orange County, Cali-
fornia, LSA, Inc., June 1984.
Assessment of Archaeological Resources, Diamond Bar Project, Los Angeles -
County, California, LSA, .Inc., May 1984.
Historic Property Survey Report for the Proposed Sand_ Canyon/I--405
'Interchange, City of -Irvine,. LSA, Inc., April 1984.
Archaeological Field Review, Villa a 19A .Project, City of Irvine, Cali-
fornia, LSA, Inc., March 19b4.
Archaeological Reconnaissance, Carmel Valley Ranch Area F, Carmel, Cali-
fornia, LSA, Inc., March 1 .
Cultural Resource Assessment, Bressi Ranch, San Diego County, California,
LSA*, Inc., February 1984.
Su l-emental Archaeological. Assessment, Oak Tree West Project, Riverside
County, California, LSA, Inc., January 1984.
Historic Property Report, Proposed Yale Avenue/I-5 Overcrossin ,,Irvi-ne,
California, LSA, Inc., December 1983.
Archaeological and Paleontological Assessment, Salt Creek Disposal Site,
Orange County, California, LSA, Inc., October 198.3.
Archaeological Data Recovery at Locus B, CA-SDi-7197, San Diego County,
California, LSA, Inc., September 1983.
Cultural Resource Overview, La Quinta Redevelopment Project, Riverside
County, Ca i ornia;"LSA, Inc., August 1983.
Research Design for: the Data Recovery Program at CA-Ora-166, Newport
'LSA, Inc., June
Beach, California, co-authored with. E. Jane Rosenthal,
1983.
•
Elizabeth F. Padon
Page 4
Lsa
Archaeological Assessment, Proposed Upper Newport, Bay Bicycle/Equestrian
Trail, Newport Beach, California, LSA, Inc., June 1983.
Archaeolo ical Assessment of a- Portion. of Rancho' -San Clemente, San
Clemente, California, LSA, Inc., May 198U.
An Initial Survey of Historic Resources With tn'the City of Irvine and Its
Sphere of Influence,-, LSA, Inc., Fe ruary .
Archaeolo ical Testing at CA-Riv-1801-,, Green. River Meadow Project,
Riverside County, California, co-authoredFo-auth6red with Bi I I Breece, LSA, Inc.,
October 1982.
Cultural Resources Survey, Archaeological' -Resources, Foothill' Transporta-
tion Corridor, Phase II, LSA, Inc., October 19 2� .
Archaeological Assessment of Woodlake Villa aGeneral', Plan Amendment,
LSA, Inc., June ME
Cultural Resource Survey for General ,P-lan Amendment, Bonner and, Shady
Canyons, Orange County, California, LSA, I.nc., June 1982.
PROFESSIONAL AFFILIATIONS AND ACCREDITATION -
Society of Professional -Archaeologists ('SOPA)
Society for American Archaeology (SAA)
Pacific Coast Archaeol'ogical.Society (PCAS)
Society for California Archaeology (SCA)
UCLA Friends of Archaeology
Southwest Anthropological Association
National Trust for Historic Preservation
Los Angeles Conservancy
Environmental Management Agency., Orange County
•
Natural Resource Management
Transportation Engineering
Environmental Assessment
Lsa Community Planning
WILLIAM H.'BREECE
FIELD DIRECTOR
SUMMARY OF QUALIFICATIONS AND EXPERIENCE
EDUCATION
University of 'Cal i forni a, Los Angeles, Master of Arts in Archaeology, _Los
Angeles, CA, 1977."=
California State University, Long Beach, Bachelor of Arts in Anthropology,
Long Beach, CA, 1973.
. PROFESS.IONAL EXPERIENCE
Principal Investigator, Environmental' Science Associates, Environmental
Planning Consultants, San Francisco, CA, 1981.
Principal Investigator and Project Archaeologist, Westec Services, Inc.,
Tustin, CA, 1978-1981.
Consultant, G.rabhorn Engineering.; San Diego, CA, 1978 "
Section Chief, University of Bordeaux, Anquitaine Region, France, 1976-
1977.
Field Foreman, UCLA in Solvieux, France, 1973-1974.
Laboratory Technician, UCLA in Solvieux, France, 1973-1974..
Field crew member, UCLA Archaeological Survey, Los Angeles, CA, 1972.
PRINCIPAL PROFESSIONAL RESPONSIBILITIES
Conducting archaeological research projects with principal responsibility
for:
Data analysis and write-up
Directing field and laboratory operations (survey and excavation)
Personnel management and supervision
Feasibility studies and cost analyses for cultural .resource manage-
ment
❑ 610 Newport Center Drive, Suite 555 - Newport Beach, Califomia 92660 - (714) 640-6363
0 2606 Eighth Street - Berkeley, California 94710 - (415) 841-6846
William H. Breece
Page 2
UM
PUBLICATIONS
Author or co-author of numerous professional. archaeological site survey
and excavation reports (examples avail -able upon request).
PROFESSIONAL AFFILIATIONS AND ACCREDITATION
Society of Professional Archaeologists.
San Luis Obispo County Archaeologica-1 Society
Society for California Archaeology (SCA).
Society for American Archaeology '(SAA)
Phi Kappa Phi - National Honor Society
p; 500-Newport Center Drive, Suite 600
Newport Beach, California 92660
phone- (714) 640-6363
L mca ❑ 2606 Eighth Street
Berkeley, California 94710
phone (415) 841-6840
Community Planning n Natural Resource Management C Environmental Assessment
WAYNE HOWARD BONNER
FIELD ARCHAEOLOGIST
SUMMARY'OF QUALIFICA-TIONS AND EXPERIENCE
EDUCATION
California State, University, Long Beach, Master of Arts in Anthropology,
specializing in Archaeology, Long Beach, CA (in' progress).
California State College, Long Beach, Bachelor of Arts in Anthropology,
Long Beach, CA, 1970.
E1 Camino Community College, Associate of Arts, Torrance, CA, 1969.
PROFESSIONAL EXPERIENCE
Laboratory director, Puvunga Village test excavation project, Los
Angeles, CA, 1982.
Research assistant under Dr. Jane Rosenthal,. Los Angeles, CA-, 1982.
Director of Rock Art Archives, Institute of Archaeology, UCLA, Los
Angeles, CA, 1980.
Site Director, Southern Illinois University, Carbondale, IL, 1979.
Laboratory assistant, Los Angeles County 'Museum of Natural History, Los
Angeles, CA, 1978.
Field crew member, various site excavations, under direction of Dr.
Clement Meighan, Los Angeles County and Ventura County, CA, 1975-78.
PRINCIPAL PROFESSIONAL RESPONSIBILITIES
Assistant field director
Laboratory technician
Field cartography
Artifact analysis
Archaeological site form preparation
•
❑ 500 Newport Center Drive, Suite 525
Newport Beach, California 92660
phone (714) 640-6363
Lsa❑ 2927 Newbury Street, Suite C
Berkeley, California 94703
phone (415)841-6840
Community Planning , ❑ - Natural Resource Management ❑ Environmental Assessment
COL-E J. PARKER
FIELD RCHAEOL G ST
SUMMARY OF EXPERIENCE
EDUCATION.
California State University, Long Beach, Master of Arts in Archaeology,
Long Beach, CA (in progress),,
California State University, Long Beach, Bachelor of Arts in Anthropology,
Long Beach, CA, 1976.
Goldenwest College, Associate of Arts, Huntington Beach., CA; 1973'.
PROFESSIONAL EXPERIENCE
41 Field crew member, Recon, Regional, EnVironmental Consultants, San Diego-,
CA, 1980-1981.
Research assistant, California State University, Long Beach., CA, 1980-
1981.
Field crew member, Archaeological Resource Management Corporation, Garden
Grove, CA, 1979-1980.
Field crew. member, Pacific Coast Archaeologi-cal'Society, Santa Ana, CA,
1979.-
PRINCIPAL PROFESSIONAL RESPONSIBILITIES
Field cartography
.Artifact analysis
Archaeological site form preparation
❑ S00 Newport Center Drive, Suite S2S
Newport Beach, California 92660
phone (714) G.40-6363
0 2927 Newbury Street, Suite
Berkeley, California 94703
phone (41S) 841-G840
Community Planning C Natural Resource Management C Environmental Assessment
JODY NEAL-POST
FIELD ARCHAEULOGIST
SUMMARY OF QUALIFICATIONS AND -EXPERIENCE
EDUCATION
California State University, Dominguez Hills, Certification in Cultural
Resource Management, Carson,. -CA, 1980.
California State University, Dominguez Hills,. Bachelor of Arts in Human
Studies/Ethnography, Carson, CA, 1979.
PROFESSIONAL EXPERIENCE
Field Crew Member, excavation at site CA-Sh-a-782, California State Uni-
versity, Chino, 1982.
Staff Archaeologist, U.S.- Department of Agriculture,. Shasta -Trinity
National Forest, -CA, Summer 1982.
Assistant District Archaeologist, Bureau -of Land Management, Redding, CA,
Spring 1982.
Field Photographer and Ethnographer, Anthro-Graphics, New York, India,
Nepal, Spain, Portugal, -and Morocco, 1981=82.
Field Crew Member, Mojave Desert survey, Applied Conservation Technology,
Fullerton, CA, 1979.
Ethnographer, project in Goa, India, January -July 1978.
PRINCIPAL PROFESSIONAL RESPONSIBILITIES
Field photographer
Topographic map interpretations
Preparation of archaeological site record forms
r�
❑ 500 Newport Center Drive, Suite 525
Newport Beach, California. 92660
phone (7.14) 640-6363
❑ 2927 Newbury Street, Suite C
Lsa
Berkeley, California 94703
phone (415)841-6840
Community Planning ❑ Natural Resource Management ❑ Environmental Assessment
WILLIAM A. SAWYER
FIELD ARCH EOLOGI-T
SUMMARY OF QUALI I ATIONS AND EXPERIENCE
EDUCATION
California State University, Long Beach, Bachelor of Arts in Anthropol-
ogy, Long Beach, CA,'1980.
Associate of Arts Degree, Santa Ana College., Santa.Ana, CA, 1976.
PROFESSIONAL EXPERIENCE
Crew Member, San Clemente Island survey, Chambers Consultants and -Plan-
ners, Stanton, CA, 1980.
Crew Chief, Harper. Dry Lake survey, California State University, Long
Beach, 1980.
Crew Member; excavation and surface collection at sites CA-SDi-4276, CA-
SDi-5593, CA-SDi-5594, and CA-SDi-5595 i.n San Diego, CA, 197.9.
Crew Member, survey of Prado Dam Regional Park, California State Univer-
sity, Long Beach, CA, 1979.
Crew Member, excavation at site CA-Ora-119, California State University-,
Long Beach, 1978.
PRINCIPAL PROFESSIONAL RESPONSIBILITIES
Preparation of archaeological site record forms
Artifact analysis
Field photographer
PROFESSIONAL AFFILIATIONS
Society for American Archaeology
Society for -California Archaeology
Pacific Coast Archaeological Society
Malki Museum Association
Southwest Museum Association
Natural History Museum Associate
MARIAN PARKS
233 MORNING CANYON
CORONA DEL MAR, CA 92625
(714) 760-07-98
RESUME
F,ducation
B.A., University of Southern California
California Teacher's Credential, University of California, Los Angeles
M.A., American History, Claremont'Graduate School, Claremont, California
Courses- in history and archaeology, University of California, Los Angeles,
Irvine, and California State University, Long Beach
Archaeological field class, California State University, Long Beach, under
Dr,. Maroaret- (Weide) Lyneis
Archaeological and Historical Experience -
Research
National Archives in. Seattle, Laguna Niguel, Washington, D.C.
County records in California, Illinois, Ohio, Washington:
Tax assessments, Recorder's Of+ice (deeds, births, deaths,
trusts), labor rolls, mining claims, probates, directories,
court cases, etc.
Archival collections and newspapers in
Chicago: Newbery Library, Historical Society, Public Library
Canada: British Columbia Provincial Archives
Cincinnati: Historical Society, Public Library
Mother Lode: Mariposa, Sonora, Stockton
Philadelphia:1-averford.College Quaker Collection
Sacramento: State Library and Archives
San Francisco: Bancroft, Sutro, California Historical Society
Seattle: The Libraries of the'University of.Jashino on-,
Collections at Port To:msend and Port Angeles
Southern California: Honnold, Claremont; University -of
California, Irvine and Los Angeles;'University of
Southern California; Los Angeles County -Natural
History Museum (History Division); Sherman Library,
Corona Del Mar
Archaeolo~ical Excavations
Middle East and England, artifacts cataloguing
San Buenaventura Fission Project, Ventura, California: Greenwood
and Associates, lab technician
New Melones Reservoir Prcjecty Sonora, California: 111 OTEC, Dr. idichael
J. Foratto, Principal Invest irZator, Department o:' Interior contract.
. Mother Lode historical research and historical artifacts, under
o seasons
Greenwood & Associates, t:•r
Included two weeks' research in Salt bake City at the Mormon
archives for Mormon sites in the project area. The writing.
will appear in the Interior final. report.
Shasta/I-5 Project, Lakehead, California. "INF=C, Dr. Christopher
Raven, Principal Investigator-, Caltrans contract, testing phase.
Historical artifacts cataloguing. Development of the historical
computer code for the prehaistoric test phase of the project.
Work under Raven.
Preservation Efforts
Newport Beach, California. City Environmental Committee representative
for history and archaeology
Orange County, California. Preservation of historical and archaeological
data along the Aliso Water Management Agency pipeline project. .
Affiliations
Society for California'.Archaeology, Society for American Archaeology,
Pacific Coast Archaeological Society (board), American Historical
Association/Pacific Coast Branch, Western Historical Society, Historical
Society of Southern California (board).,- Historical Society of .Orange County
(ex board), Chinese Historical Society of Southern California
Literature
.41 In 1979 presented a paper at the Society for California Archaeology on
the preservation efforts indicated above.
In 1980 prepared a paper for the Department of Parks and Recreation,
California, under John McAleer, historian, on the Japanese. use of state park
area, the newly acquired Crystal Cove State Park, Orange*Zounty. The
research included local and Irvine Company records and oral interviews.
In 1984 an article to appear in the Historical Society of Southern
California Quarterly, Spring 1984 on the one -hundred -year history of
the society. .
The Department of Interior work is cited above.
•
APPENDIX C
INDEX TO THE BASE MAP
OF SURVEYED AREAS
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•
Lsa
il
•
Lsa
INDEX TO THE BASE MAP OF -SURVEYED AREAS
No. Area
Survey Reports Included Within the Numbered Area
1
Padon, Beth and Bill Breece, Archaeological Resource Inven-
tory, 1984, City of Irvine and Its Sphere of I-nfluence.
2
Scientific Resource Surveys, Inc., 1978, Archaeological and
Historical Report on the Proposed Bee & Round Canyons Landfill
Disposal Station.
Steve E. Colegrove, 1972, Village of Valley View .(letter
report).
Public Antiquities Salvage Team, California State University
'Tentative
at Fullerton, 1976, Archaeological Resources of the
Coyote Canyon Landfill Replacement Site in Central Orange
County..
Scientific Resource Surveys, Inc., 1978, Cultural Resources
Report - Preliminary Assessment on the San Diego, Creek Water-
shed in Hicks Canyon, Rattlesnake Creek Wash, San Diego Creek,
and the San Joaquin Marsh.
Bill Breece and Beth Padon, 1982, Cultural Resource Survey of
Archaeological Resources, 'Foothi.11 Transportation Corridor,
Phase II.
E. Gary Stickel, 1979, Evaluation of Cultural Resources at the
City of Los Angeles Hyperion Water Faci-l-i ti es and the-, County
of Los Angeles, and Orange -County Sanitation District Proposed
Round Canyon. Site.
3
(El Toro Marine Base)
4
N. Nelson Leonard III, 1975 Archaeological Impact Evaluation:
Park Place.'
Scientific Resource Surveys, Inc., 1976, Archaeological- Survey
Report on Tentative Tract No. 9379, Lots'A-G and A-5 of Tract
No. 282 in the City of Irvine.
C7
2
LCM
No. Area Survey Reports Included Wi-thi.n the Numbered Area
Scientific Resource Surveys, Inc., 1976, Archaeological Survey
Report on a Four Acre P-a�rcel of Land Located in Irvine Indus-
trial Area, Irvine, California.
Scientific Resource Surveys, Inc., 1976, Archaeological Survey
Report on The North Irvine Assessment District Located in the
"Frances" Area of the City of Irvine.
Scientific Resource Surveys, Inc., 1977 Archaeological Survey
Report on Tentative Tract 9623 Located in the City of Irvine..
Archaeological Planni-ng, Collaborati"ve, 1980, Archaeological
Records Search and FJ el-d Survey, Northwood Project Sites No. 1
and 2, City of Irvine.
Scientific Resource Surveys, Inc.,.1976, Archaeological Report
on the Survey of Meadow Mobile Homes Proposed'Development "The
Groves" Located i-n the Frances Area, North Irvine.
Archaeological Planning Collaborative, 1979, Archaeological
Records Search and Reconnaissance Survey, Orangetree Park
20-Acre Initial Study, Irvine.
Michael L. Ahlering, A Discussion of Scientific Cultural
Resources in Relation to the North Irvine Precise Land Use
Plan.
LSA, Inc.; 1981, Cultural Resources Records Search and Field
Survey, Northwood Project Sites 3 and 4, City of Irvine.,
LSA, Inc., 1982, Historic Property Survey for Proposed
Improvements to Jeff rey.Road and I-5, Irvine.
5 Marie G. Cottrell, 1976, Archaeological Record Search and
Field Survey of Sites_ No. 1, 2, .and 5, ,North Irvine (letter
report).
Marie 'G. Cottrell, 1977, Village 10 - Records Search (letter
report).
Steve E. Colegrove, 1972, Village of Valley View (letter
0 report).
•
3
Wa
No. Area Survey Reports Included Within the Numbered -Area
Michael L. Ahlering, A Discussion of Scientific Cultural
Resources in Relation to the North Irvine Precise Land Use
Plan.
6 Marie G. Cottrell, 1978, Archaeological Resources Located in
Village 14, Irvine (fetter report).
Laura Lee Mitchell, 1976 Woodbei-ge Observer'Survey Project.
Steve E. Colegrove, 1973, Central Village "A" East Irvine
Business and Industrial Center and Regional Commercial Tri-
angle Scientific Resources Survey (letter report).
Theo N. Mabry, 1979, Culver/I-405 and Harvard./I=405 Area
Archaeological Report Inventory"(letter report).
Theo N. Mabry, 1979, Archaeological Record Search, and Recon-
naissance, Yale Avenue Rights -of -Ways, Irvine, CA.
Marie G. Cottrell, 1978, Culver Drive/I-405 Interchange
Improvements (letter report).
Marie G. Cottrell, 1976, Walk -Over Survey Central Village "A"
(letter report).
Beth Padon, 1984, Archaeological Resource Assessment Irvine
Industrial Complex -East, Phase IV, Irvine.
N. Nelson Leonard III, 1975, Archaeol-ogical Resources of
Rancho San Joaquin.
7 Beth Padon, 1983, Assessment of Archaeological Resources, RV
Storage Project, Irvine.
Marie Cottrell; 1980, Walk -Over Survey of 25 Acres, Southwest
Corner of Sand Canyon and AT&SF Railroad',in- City, of Irvine..
8 Theo N. Mabry, 1979, Archaeological Records 'Search and Recon-
naissance Survey, Orange Tree Park 20=Acre Initial Study,
Irvine.
•
n
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0
4
No Area Survey Reports Included Within the Numbered Area
0
LSA, Inc., 1981, Cultural Resource Assessment Village 12
Development Site.
Marie G. Cottrell,- 1976, Walk -Over, Survey Central Village. "A"
(letter report).
Steve E. Colegrove, 1973, Proposed Orange tree Acres Planned
Community-0 etter report).
Marie G. Cottrell, 1976, Archaeological Survey on San Diego
Creek Flood Control Channel (letter report).
Marie G. Cottrell, 1977, Archaeological Survey Report on Vil-
lage 12 and Village 14.
Beth Padon, 1984, Cultural Resource. Assessment, Irvine Center
Project, Irvine.
Marie G. Cottrell, 1978,, Alton/Santa Ana -Freeway Interchange
Construction and Irvine Center Drive San Diego Freeway Inter-
change Expansion: Archaeological Resources Review (letter
report).
LSA, Inc., 1981, Historic Property Survey, Alton Parkway/1-5
.Interchange and Irvine Center Drive/I-405 Interchange, Irvine.
Theo Mabry, 1979, Archaeological Survey, Alton and Irvine
Center D-rive Interchange Improvements (letter report).
Steve E. Colegrove, 1973; Central Village "A" East Irvine
Business and Industrial Center and Regional Commercial Tri-
angle (letter report).
Jill Weisbord, 1981 Cultural Resource Survey of the Irvine
Center D.A. Village 13.
Beth Padon, 1983, Assessment of Archaeological and Paleonto-
logical Resources, Irvine Medical Complex, Irvine.
Beth Padon, 1983, Assessment of Archaeological and Paleonto-
logical Medical Center, Irvine, CA.
•
Ll
0
�i
Lsa-
No: Area
Survey Reports Included Within the Numbered Area
10
Theo N. Mabry, 1978, Archaeological Records Search and Recon-
naissance Survey, Irvine Industrial Complex -East, Phase 2 and
3 Areas, Irvine..
Beth Padon, 1984, Cultural Resource Assessment., Planning Area
34B.
Scientific Resource Surveys, Inc., 1977, Archaeological Survey
Report on a 34-Acre Parcel- in the E1 Toro Area.
11
LSA, Inc., 1981 Cultural Resource Assessment Irvine Meadows
Amphitheatre Development.Site, Irvine.
Marie G. Cottrell, 1978, Report- of Archaeological Resources
Survey on Laguna and Peters Canyons.
Charles N. Irwin, 1974, Laguna Canyon Survey:
John Romani, 1984, Archaeological Survey -Report for the -Widen-
ing of Route Ora-133, Between Canyon Acres Drive and I-405 PM.
12
Theo N. Mabry, 1979, Updated Archaeological Records Search and
Reconnaissance with Mitigation Recommendations, Quail Hill
Planning Area, Irvi.ne.
Archaeological Planning Collaborative, 1979, Archaeological
Records Search and Reconnaissance Survey, Turtle -Rock Enclaves
6 and 7.
Steve E. Colegrove, 1-973, Turtle Rock 'Pla-nning Area (letter
report).
LSA, Inc., 1981 Archaeological and Paleon.tol'ogical Resource
Assessment Turtle Rock Enclave 8, Irvine.
Steve E. Colegrove, 1913, Scientific Resources Survey on
Turtle Rock Planning Area,'Irvine (letter report).
Raymond L. Bernor,.1977, Paleontological Resource Survey and .
Impact Evaluation for Turtle Rock Enclaves 3 and 5, 'Irvine.
a
•
N
Lsa
No Area Survey Reports Included Within -the Numbered -Area
Theodore Cooley, 1974-, Archaeological Site Survey Records for
Bonita Canyon Extension (letter report).
Marie G. Cottrell, 1976, Archaeological Survey on Turtle Rock
Enclave 4 (letter report).
13 Archaeological Resource Management Corporation, 1978,.Report
of Archaeological Resources .Assessment conducted for the
Irvine Industrial Complex -West.
Beth Padon,-1984, Archaeological Field Review, Vill-age 19A
Project, Irvine.
PBR and LSA, Inc., 1979, Wastewater Management and Action Pro-
gram Draft Env-ironmental' & Action Program'.
Theo N. Mabry,.1.979, Archaeological Records Search and Recon-
naissance, Upper Newport Bay, Newport Beach.
14 E. Gary Stickel and Jerry B. Howard, 1976, Cultural Resource
Survey of the University of California, .Irvine.
Thomas F. King, 1973, Archaeological Reconnaissance of the
Irvine Town Center Project.
Glen Rice, 1976, Systematic Surface Inspection in Town Center
Area (letter report).
15 Theo N. Mabry, 1979, Archaeological Reconnaissance of 11-Acre
Bonita Canyon Baptist Church.Site.
Ultrasystems, 1976, .Archaeological, Historical, and Paleonto-
logical Resources Western World Medical Foundation Project,
Irvine.
Archaeological Research, Inc., 1975,- Preliminary Report -
Bonita Canyon.
Robert H. Crabtree, 1973, Harborview Hills Development Section
3 and 4, Sites 11, 13, and 14 (letter report).
•
0
7
Ua-
No. Area Survey Reports Included Within the Numbered -Area
Archaeological Research, Inc., 1977, Archaeological Resources
of the Coyote Canyon Disposal Station.
Marie G. Cottrell, 1978, Preliminary Archaeological Survey
Conducted for the San Joaquin Hills Transportation Corridor.
Marie G. Cottrell, 1983, Archaeological Resource_ Assessment,
Coyote Canyon Sanitary Landfill.
Edward B. Weil, 1981, Cultural Resource Survey ---of Proposed
Pel.ican Hill Road.
Jean & L. W-. Lewis TadTock, 1979, San J oaqu-i n Hi 1-1 s Transpor-
tation Corridor Cultural Resources Study.
David Van Horn, 1983, A Cultural/Scfentffic Resources In'ves-ti-
gation of the Planned San Joaquin Hills Transportation Corri-
dor (Phase II).
Beth Padon, 1982, Cultural Resources Survey for General Plan
Amendment, Bommer and Shady Canyons.
16 Theodore G. Cooley, 1974,.Scientific Resources Survey of Field
514 in Irvine Center (letter -report).
17 Theo'N. Mabry, 1978, Archaeological Records Search and Recon-
naissance Investigation; Agua Chinon Flood Control Improvement
Project.
18 Theodore. Cooley and Adella Schroth, 1979, Archaeological
Resources Assessment, Irvine Ranch Water District Pipeline
Ri ght-of-Ways.
19 Marie Cottrell, 1977,: Santiago Aqueduct Parallel Reaches 2-6
(letter report).
20 Beth Padon, 1983, Historic Property Survey Report for Irvine
Center Drive Widening.
21 Theodore Cooley, 1974, Letter Report on Proposed Haul Road.
•
NO
Lsa
No. Area Survey Reports Included Within the-Numbered,Area
22 Cottrell, 'Marie, 1978, Letter Report on Addendum to Previous
Report on Reach 4, Santiago Canyon Parallel Aqueduct.
23- Pat Sperry, 1972, Site Survey Report, U.S. Marine Helicopter
Base: Tustin, CA.
24 Beth Padon, 1,983, Historic Property Survey Report Proposed
Yale Avenue/I-5 Overcro.ssing.
25 LSA, Inc., 1982, Historic Property Survey, for Proposed
Improvements to Jeffrey Road and I-5.
26 SRS,'Inc., 1978, Cultural Resources Report, San Diego Creek
Watershed in Hicks Canyon, Hicks Canyon, Wash, Rattlesnake
Canyon Wash, San Diego Creek, and San Joaquin Marsh.
27 Marie Cottrell, 1976, Walk -Over Survey of Irvine Boulevard
Between Sand Canyon and Jeffrey Road.
28 Archaeol-ogical Planning Collaborative, 1979, Historic Property
Survey, Moulton Parkway/Irvine Center Drive.
29 SRS, 1982, Cultural Resource Property Survey, Orange County
Rapid Transit Concept Design located in the Central Portion of
Orange County.
30 Pacific Coast Archaeological Society, Inc., 1,973, Walk=Over
Survey of Five Miles Along North Side of San Diego Freeway
(letter report). On file at the PCAS Research Li-brary.
31 Theodore Cooley, 1974, Field Survey, of the Proposed Right -of -
Way for the Extension of Michelson D rive (letter report).
32. Ron Douglas, 1981, Historic Perspective Survey, Harvard
Avenue/I-405 Overcrossing.
33 Theo Mabry, 1979, Records Search and Reconnaissance, Harvard
Avenue Extension.
34 William A. Dodge, 1978, An Archaeological Assessment of Eight
Cultural Localities Along the San Onofre/Santiago 220-KV
Transmission Line.
a
Q
Lsa
No. Area Survey Reports Included Within the Numbered Area
Lowell Bean and S. Vane, 1979, Cultural Resources and the -
High -Voltage Transmission Line From San Onofre to Santiago
Substation and Black Star Canyon.
Westec, Inc., 1980, National. Register Assessment Program of
Cultural Resources of the 230=KV Transmission Line Right -of -
Way From San Onofre Nuclear Generating Substa,ti-on to Black
Star Canyon and Santiago Substation and to Encina and Mission
Valley.
CSRI, Inc., 1982, Cultural Resource Data Recovery Program for
the 230-KV Transmission Line Right-of=Way From San Onofre
Nuclear Generating Station to Black Star Canyon and Santiago
Substation and to Encina and Mission Valley Substation,
Volumes 1 and 2.
0
PALEONTOLOGICAL RESOURCES
41 ELEMENT
0 Technical Supplement 4
•
PALEONTOLOGICAL R-ESOURCES INVENTORY
FOR
CITY OF IRVINE MASTER ENV'IRONMENTAL ASSESSMENT
prepared for
Community Planning Services
E1 Toro,, California
As a technical component of Phase I of the
Irvine Master Environmental Assessment
prepared by
Rod Raschke
Certified Paleontologist
RMW Paleo. Associates
Mission Viejo, California
April 19-85
•
•
a
�J
INTRODUCTIO'N
This paleontological inventory is a techanical component of
the Phase I Irvine Master Environmental Assessment. Th,e following
report represents the first comprehensive inventory of th-e
paleontological resources within the City of Irvine and it's
sphere of influence. The purpose of this report is threefold:
first to establish baseline data o.n the paleontological resources
of the study area, secondly to develop sensitivity zones to
assist in the evaluatio-n of the impacts of proposed projects on
the resource, and finally to determine the signific-ance of the
resource. A Phase II effort suggesting specific mitigation
measures will be submitted under a seperat.e cover later.
The study area consists of the City of Irvine an-d it's
sphere of influence (Figure 1). The study area includes portions
of th-e Santa Ana Mountains in the north,_ the Tustin Plain, and
the San Joaquin Hills in th.e south.
This project is an outgrowth of the concern by the City of
Irvine for paleontological resources. It is the City's desire to
determine the extent of this resource so that it may be
adequately evaluated during future environmental analysis.
The legislative background for the protection of
paleontological resources in-cludes Federal,-State,,County,.and
local measures. Although not specifically described in the
earlier Federal and State legislation this resource is commonly
considered to be covered by implication as a "pre -historic"
resource. Later State and Federal law.s specifically deal with the
protection of paleontological resour.ces on both public and
private lands. The County of Orange has established what may be
the most comprehensive set of guidelines for the -evaluation and
protection of paleontological remains. The City of Irvine has
established a broad set of guidelines for evaluation of the
resource. The respective laws are listed in the bibliography
(Appendix A).
0
SUMMARY
The Paleontological -Resources Inventory for the Phase I
Irvine Master Environmental Assessment was prepared with three
main tasks defined as goals; 1) to inventory known
paleontological resources in the City of Irvine and its' sphere
of influence, 2) to determine the potential for the discovery of
additional paleontological resources and define zones of similar
potential or sensitivity, axed 3-) to determine the extent and
adequacy of previous EIR related,paleontological assessments. The
accompanying report pre.sents the detailed finding-s of these
efforts. Measures to mitigate the potential impacts of
development on the paleontological resources of the Irvine MEA
study area will be presented in the Phase II report:
During this study known fossil occurrences were, identified
and plotted on the accompanying maps. The locality information
and .past fossil production,in adjacent areas was used to develop
zones of similar paleontological potential or sensitivity. These
zon-es are also shown on the accompanying ma.ps.-
Exposed within the study are fifteen :stratigrap-hic units
ranging in age from less than 10,000 years old to more than '63
million years old. The majority .of these units were deposited in
and along the margins of a sea that occupied the region during
most of this time. Fossils have been located in each of the rock
units at'localities in Orange County. The wide variety organisms
represented by these fossils -include; plants, numerous marine
invertebrates, whales, sea lions, fishes, sharks, birds, a=nd
occassionally terrestrial verte-brates.
Four paleontological sensitivity zones were developed -to
group rocks with similar pal-eontological potential. Th-e four
zones are "No", "Low", "Moderate", and "High". The accuracy of
the assignment of an area to a particular zone depe-nds on our
knowledge of the paleontological resources of the rock unit(s)
present. In general the more common fossils are within a 'rock
unit the higher the paleontological sensitivity of the area where
that unit is exposed. The only exception is the "-Mode-rate"
sensitivity zone, which includes some areas underlain by rocks
for which little is known about the paleontological resources of
the rock units in the study area, but -have produced significant
fossils in other areas. The Moderate and High Sensitivity Zon-es
are -concentrated in the San Joaquin Hills and Sa-nta Ana Mountains
were older rock unit-s are exposed. The alluvium exposed in the
Tustin Plain has a low sensitivity because of its geologic youth.
There is a small area of volcanic rock exposed i.n th.e San Joaquin
Hills, t.h,at has no sensitivity d,ue to their igneous origin.
One task in this effort was to identify the previous studies
that were of prepared by currently acceptable standards. These
efforts revealed that most of the early EIR related studies did
not meet current acceptable standards. There are several reports
that, do contain adequate information, these are presented in
Appendix B. Included in these reports are survey information that
indicates that although large areas o.f the study area have been
surveyed there are still large areas that need to b.e surveyed.
The Irvine MEA study area contains rock units that span some
60+ million years of geologic history. It.is highly proba-ble.that
t=hese rocks contain fossils that will, be- of great s-ignifi.cance to
paleontologists or geologists studying the geologic and
evolutionary history of the region. There are indications from
localities within the study area and immediately south of it that"
fossil of intra- or intercontine-ntal significance may be present
in these rocks. Fossils from the area -have already, added
important new information on the evolution of two g.roups of
fossil marine mammals and a-dd-i-tional new information is expected
by scientists familiar'with t-he area.
•
is
METHODS
The information contained in this-re.port was obtained
through a review of a variety of published and unpublished
geological and paleontological reports and documents. There was
no field work conducted during this study, however information
gathered by the author and others during field work in the study
area was used to aid in the compilation of baseline data and
establishment of the sensitivity zones.
Locality records of the following institutions were -utilized.
during the course of this study.
Natural Hist-ory-'Muse-um of Los Angeles County (LA.CM)
University of C-alifornia; Los Angeles (UCLA)
University of California, Riverside (UCR)
Museum of Paleontology, University of California,
Berkeley (UCMP)
California Institute of Technology (CIT) records now at
LACM
Natural History Foundation of Orange County (NH'FOC)
United States Geological. Survey (U'SGS)
California State University Fullerton-(CSF)
Fossil locality information was also obtained from EIR reports,
published documents, and the personal field notes of
paleontologists who have worked in the study, area. These sources
are listed in the bibliography (Appen-dix A). Fossil localities
are shown on Maps 1 thru 6, and listed in Ap-pendix D.
STRATIGRAPHY
Exposed within the Irvine MEA stu-dy area are fifteen
stratigraphic units. Table 1 lists these rock units a -long with
their age and stratigraphic position. The discussion, below
briefly describes each rock unit and the paleontological
resources known from it.
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TABLE 1
GEOLOGIC TIME PERIODS AND ROCK UNITS
Epoch Age (yea-rs) Rock Unit
Quaternary Period
Recent less than 10,000 alluvium
Pleistocene 10',000 to 2 million
Tertiary Period
Pliocene ' 2 to 5 million_
Early Pliocene to 4 to 9'million
Late Miocene
Late to MiAdle 9 to 16 million
Miocene
Early Miocene
16
to
24
mill -ion
Early Miocene to
22
to
30
million
Oligocene
Oligocene
24
to
37
million
Eocene
37
to
55
million
Paleocene
55
to
63
million
Cretaceous Period
Upper Cretaceous 63+ million
older alluvium
terrace deposits
Marine terrace de -posits
Fernando.F'ormation
Niguel Formati:o.n
Capistrano Formation
Pu.e.nte Formation'
(Soquel Member)
Puente Formation ,
(-t.a Vida Member)
.Monterey Formatio-n
Topa.nga Formation
Vaqueros Formation
Vaqu_eros-Sespe
Formations
Sespe- Formation
Santiago Formation
Silverado Formation
Williams Formation
•
marine invertebrates and vertebrates. In the Irvine MEA area the
remains of a land mammal were found intermixed with these marine
fossils.
Capistrano Formation
This formation consists of two members, the Oso Sand Member
and the' i nforma 1 "s i ltstone member". These. sa-nds- and s i 1 st.on.es
were deposited in a deep sea that covered southern. Orange County.
One of the largest assemblages of marine vertebrates in the world
has been collected from the Capistrano Formation, as a result -.of -
the cooperation between developers and scientists.
Puente -Formation
S
The Puente Formation is represented by t.wo of its four
members -the Soquel and La -Vida Members. The Soquel Member is a
sand -and conglomerate unit of.marine origin. This member has
produced the remains of sharks, fishes, and marine„ma.mmals in the
eastern Puente Hills. The La -Vida.Member is represented by
siltstones an.d diatomaceous shales, at present little. is knew-n
about the paleontological resourc-es of this unit other than a few
leaf impressions, fish skeletons, isolated marine mammal -bones
and a skeleton of a baleen whale from this -unit in the Anaheim
Hills. area.
Monterey Formation
This marine formation consists of int.erbe,dded sands,
silstones, and diatomaceous shales. Although t-his, rock unit is
the most wide spread formation in California it is.restricted to
the Agua Chinon area of th-e Irvine MEA study area. This unit has
been the most consistent producer of fossil marine verte-brates in
California. The fossils of fishes, whales, sea lions, birds,
other marine vertebrates and numerous inv-ertebrates have been
-found in every district where this unit is exposed.
5
•
Topanga Formation
The Topanga Formation is a nearshore marine deposit composed
almost entirely of sandstone. In the Irvine MEA area it forms,
some of the steep cliffs in the Bee and Round C-anyon areas. This
unit has recently begun to reveal the presence of a very large
and diverse assemblage of marine vertebrates and invertebrates.
To the south of the study area several hundred vertebrate fossils
were removed from the first- tw-o major grading operations into
this rock unit.
Vaqueros Formation
This marine to marginal.marine unit is represented in th-e
st.udy.area by tan sandstones and green siltstones. Fossil
invertebrates have long been kn-own form this unit. Only recently
have large numbers of fossil vertebrates been discovered in the
unit. These vertebrates include terrestrial and marine mamma -Is,
sharks, birds, reptiles, and fishes.
undifferentiated Vaqueros-Sespe Formation
This formation was est-ablished to include the rocks that
represent the complex interfingering between the marine Vaqueros
Formation and the non -marine Sespe Formation. The rock types
represe-nted-include the sands and silst-ones of the Vaqueros
Formation and the reddish to yellow sands, clays, a.nd
conglomerates of the Sespe Formation. Numerous invertebrate
fossils are known from this unit in the Santa Ana Mountains.
Early work in the Bolero Lookout area revealed the presence of
potentially significant fossils in the u.nit. More recent work by
students from San Diego State and Saddleback College staff have
supported this conclusion. The ve-rtebrate_f,ossils reported from
this unit include marine fishes and mammals in association with
terrestrial mammals.
A
•
S,espe Formation
Of all the rock units in the study area the paleontological
resources of the Sespe are the least known. This unit co-nsists of
the red to yellow sandstones, claystones, and conglomerates
deposited in and along deltas a-nd-flood plains of rivers flowing
across the area. There are old reports of vertebrate fossils from
this unit in Orange County, however, none can -be confirmed. The
best known record of fossils from the Se-spe Formation is in th-e
Simi Valley where a very large and diverse -assemblage -of fossil
land animals have been collected over the past fifty years.
Santiago Formation
The Santiago Formation is represented by sands.to.nes and
conglomerates deposited on beachs a.nd in shallow coastal lagoons.
The fossil resources of this unit are poorly known, at present
only poorly preserved inverte-brates are known from the study
area. Vertebrate fossils are known from this unit in the
Oceanside -Carlsbad area of San Diego County and from Camp
Pendleton.
Silverado Formation
As with the two proceeding formations very little i.s known
about the paleontological resources of the sandstones and low .
grade coal that make up this marginal marine unit. There are
reports of plant fossils from the coals and associated rocks.
Recent grading at Robinson Ranch revealed a large plant
assemblage at that location.
Williams Formation
The sandstones, siltstones, and shales of the Williams
Formation are -known to contain abundant invertebrate fossils. In
addition the only record of a dinosaur from southern California
may be from this formation just east of the study area.
7
J
000,
x�.
Y'
MPAL
kQ0
ASSOCIATES
a
41 LLS
CITY OF IRVINE
SOUTHERN AREA
-SPHERE OF
INFLUENCE
ACRES 9 R
0 4000 8000 12000
�-�FEET
�
Figure 1. Location Map
-City Of Irvine MEA, Study Area
Paleontological Assessment
P
SENSITIVITY ZONES AND MAPS
The zones shown on maps 1 thru 6-are designed to delineate
areas of similar paleontological sensitivity. Paleontological
sensitivity could better be termed the."paleontological
potential", which means the probability for the discovery of
significant fossils during development of a property within a
given zone. The limits 'of a zone are determined by the
distribution of rock units of similar potential. The potential of
a given rock unit is based on the past production of fossils an.d
th.e significance of the fossils located within that rock unit.
This approach is strictly qualitative and based.on field
observations during grading inspections, field surveys, a:nd
reviews of geological and paleontological, documents.
Maps 1 thru 6 also show the.fossi'l localities within the
study area for which information about the s,pec.i:mens present was
available. The locality information is listed in Appendix D.
The accuracy of the predicted potential varies directly with
the distance from recorded fossil occurrences...The acc:u.ra-cy of
the zones also varies directly with the level of knowled-ge of the
paleontological resources of the various rock units within a
zone. In areas that have been subject to exte-nsive grading
observations and field surveys. the palegntological sensitivity
can be more accurately determined than in unstudied or little -
studied areas or rock units. Grading observation is one of
the best methods f'o.r gath-ering paleontological data .as it
provides the paleontologist with large expanses of exposed rock
units that are otherwise not available. Howe.-v-er, grading also
rapidly destroys the fossils present. Therefore, the
paleontological sensitivity zones assigned to little studied
areas may over estimate the potential resource. This is done to
prevent the destruction of significant fossils.
Within the Irvine MEA'st.udy area there have been several
surveys but little gradin:g observation. Therefore, information
used to establish the sensitivity zones has been derived from the
limited local data and by inference from the more thoroughly -
:
studied Laguna Hills -El Toro district where many of the rock
units in the current study area have been subject to grading
observations for over ten years.. For those rock units that have
not been subject to extensive grading o-bservation,s (discussed in
the following section) data from other portions of Orange County
and finally the remainder of southern California is utilized.
This approach has worked in th-e evaluation o.f praperties i.n San
Clemente and was employed in the development of the sensitivity
zones for the County of Orange MEA.
Each zone reflects the potential for the discovery of
significant fossil resources during development of a site. The
proposed use of the site does not greatly affect paleontologic
resources, it is the mass grading of sedimentary rocks, associated
With development that affects the fossils. The four pro.posed
sensitivity zones are:
No Sensitivity;
This is for areas with exposed volcanic rocks.
Low Sensitivity;
Areas in this zone typically_haVe altered or
geologically young rocks exposed at the surface.
Moderate Sensitivity;
Areas within this zone contain sedimentary rocks
with limited histories of producing .sighAficant
fossils. The limited histories may reflect the
lack of -fossils or lack -of systematic exploration
of exposures of these rock units.
High Sensitivity;
This zon-e contains sedimentary rocks with w.ell
established histories of containing.,significant
fossils.
In areas where rock units of a lower se-nsitivity form a thin
cover over rocks of a higher sensitivity the. higher value is
indicated on the map. This is done because the variability of
4
geologic conditions may result in grading operations penetrating
the lower sensitivity units into.the high sensitivity units and
destroying significant fossils. If at the specific design lev-el
information indicates that the higher sensitivity rock unit will
not be.impacted; mitigation can be scaled down to that,of the,
lower zone.
The following section lists the various rock units exposed
in the study area -by sensitivity zone, included are brief
discussions of the unique features of each zone.
No Sensitivity
Tertiary Volca►iics
These rocks by their igneous n.a.ture do not co.nta-in fossils.
In the Irvine MEA study area, particularly in the Sa-.n Joaquin
Hills, the volcanic rocks are complexly intermixed with the
surrounding potentially fossil.iferous rocks. In -areas were
exposures of volcanic rocks -are small or the relationship with
surrounding rocks is complex the volcanic rocks are included
within the sensitivity zone of th.e potentially fossilifero.us
rocks.
Low Sensitivity
Quaternary alluvium
Quaternary terrace deposits (locally moderate)
Quaternary Marine terrace deposits (locally moderate to high)
These rock units have a low potential for the discovery of
significant fossils because eith'e=r_the environment .in which they
formed was not conducive to t-he accumulation of fossils or as in
the case of the Quaternary alluvium are not old enough, to contain
fossils. The Quaternary terrace deposits are considered locally
to have a Moderate sensitivity becaus-e several significant
accumulations of vertebrate fossils 'ha-ve been located in them in
Laguna Hills. We can not now predicat where these accumulations
will occur, however, the past fossil occurrences near a proje-ct
10
suggests others may exist. Developers should be.a-wa.re that the
potential exists for the dis-covery of these accumulation.
Quaternary marine terrace deposits exposed adjacent to MacArthur
Boulevard between University Drive -and the Bonita Canyon area
have an extensive history of prod-ucing significant- fossils a-nd
should be considered- to have a high potential for the discovery
of significant fossils. East of UCI. and south of San Joaquin
Hills Reservoir these rocks do not have a history of,fossil
producti,on but should be carefully. -watched.. These areas are sh-own
to have a HIGH Sensitivity on the accompaning maps because of
their known and potential fossil -producing hist-ory.
Moderate Sens-itivity
Sesp.e Formation
Fernando Formation
Niguel Formation (locally high)
Santiago Formati-on.
Silverado Formation
The Moderate sensitivity zone inclu-des rock units that have
been studied to varying degrees of completeness. -This is why rock
units of such varying age an-d types are includedhere.
The Niguel Formation has been extensively studied in the
Laguna Hills district and is known to contain localized
concentrations of signifi.ca-nt fossils. Unfort,u.nately we cannot
predict where these concentrations are with a=ny certainty. The
develope-r and planner should be aware that there is a potential
for these concentrations and develop flexi,bl,e grading sche-dvles,
to -allow for salvage if one is encountered.
The Silverado and Santiago Formations are t.ypi.cal of the
'ro.ck units assigned to this sensitivity zone. Both formations
have not been extensively st-udied and only -scattered natural
occurrences of fossils are known,fr-om them. However, recent,
grading activity in the Silverado Formation has reve.aled a large
and significant fossil plant assemblage. Earlier grading in
0
northern San Diego County revealed local accumulations of
abundant vertebrate fossils in the Santiago Formation. Thia-is a
strong indication that as develop.ment ex-pands into areas
underlain by these rock units additional paleontological
resources will be -discovered.
The-Sespe Formation is largely unstudied in Orang-e County.
In the Simi Valley northwest of Los Angeles a large an-d dive -rse
assemblage of Oligocene and Eocene age vertebrates has been
discovered. If a similar assemblage is found in Orange County it
.would add greatly to our understanding of the geologic history of
the entire southern California regio-n.. The close association of
the Sespe Formation with the highly fossiliferous Vaqueros
Formation and the undifferentiated V,aqu.eros-Sesp, Formation
implies that fossils may be prese-nt in this unit.. More study is
necessary in areas where this unit is expos-ed before the
paleontological sensitivity can be accurately determined.
The Fernando Formation is exposed- only at the corner of
MacArthur Boulevard and University Drive, but is thought to
underlie. the area w-est of UCI. This small e.xposure has produced a
several important vertebrate and invertebrate fossils. The
limited exposure prevents full evaluation of the entire
formation, but the fossils present d,o suggest at least a Moderate
potential for additional materials.
High Sensitivity
Topanga Formation. (locally very .hig:h)
Monterey Formation (-locally very high)
Capistrano Formation (especially the Oso Sand Member)
Williams Formation
Puente Formation
Vaqueros Formation
undifferentiated -Vaqueros-Sespe Form-atiobs
This sensitivity zone contains those rock units which have
produced significant vertebrate or invertebrate fossils at
several localities. Typically there are fossils exposed at the
12
surface in areas underlain by these rocks. It is these areas
where pre -construction salvage and special mitigation is most
likely to be necessary. Grading operations in these rocks
typically produce numerous fossils.
The Williams Formation contains numerous fossil localities
within a limited area of exposure at the mouth of Bee Canyon.
This dense accumulation of fossils in a small area strongly
suggests that significant fossils are present and additio-nal
fossils will be found during development of the area.
The Vaqueros Formation contains the second most recorded
localities within the study area. Recent discoveries in -the
Vaqueros within the Irvine MEA area, which are the result of EIR
related studies, have lead to the recovery of vertebrate fossils,
with international significance. Thus it is easily understood why
it is considered to have a high sensitivity.
The Topanga Formation contains many of the other recorded
localities and has produced significant fossils in all- areas of
exposure where it has been carefully examined. Its high
sensitivity is also obvious.
Although exposed only in the Agua Chinon area a-nd-with only
one possible locality in the study area the Monterey Formation is
considered to have a high sensitivity based on
the -well -established history of producing significant fossils in. Laguna
Hills -El Toro, Newport Beach, and most other areas of exposure
throughout California. The Monterey is perhaps the most prolific
producer of fossil marine vertebrates in California.
The Capistrano Formation, Oso Sa-nd Member, is a rock unit
that is restricted to the east side of the Saddleb-ack Valley of
Orange County. This limited area of exposure has not limited its
importance to vertebrate paleontologists. In the Mission Viejo
area this unit has produced the remains of hundreds of marine
vertebrates many of which are new t-o science. At two localities
within the Irvine MEA area several significant fossils have been
collected. Grading in this rock unit commonly reveal.s fossils.
• "The siltstone member" of the Capistranq Formation has -also
13
produced significant marine vertebrate fossils in most exposures.
The siltstone member is exposed along MacArthur 'Bouleva.rd in the
Bonita Canyon area. This well established history of fossil
.production justifies the High Sensitivity rating.
In the study area there has been little research into the
paleontological resources of the Puente Formation. In Ana.heim,
Hills, Puente Hills, and to the sout-heast of the Irvine MEA area
indications are that significant deposits of fossils are present
within -this formation and more wi-1.1 be l.o�cated as additional
development takes place- Thus as with the, other units already
discussed past fossil producing history in adjacent areas
indicates a HIGH paleont.ol-.ogical. sensitivity.
In the Orange County MEA-the undifferentiated-.Vaqueros-Sespe
Formations were considered to be of Moderate paleontological
sensitivity. However, recent paleontological work in this
rock combined with additional discoveries of significant fos-,sils
during gra.ding observations in the Vaqueros.Formation su-ggests a
higher potential for the discovery of significant fossils. This
formation is included in the High Sensiti-vity based on these
discoveries, the high number of invertebrate localities wit-hin
the present study area, and the inability to separate the
moderately sensitive Sespe Formation from the highly sensitive
Vaqueros Formation. This is an excellent example of how the
environmental analysis process can lead to the discovery and
collection of important spec-im-ens and yet not adversely affect
development.
PREVIOUS STUDIES
The paleontological reso.ur"ces of the Irvine MEA study area
have been included in several pale-onto,logical studies. EIR
related st-udies date_from the 1970's, with scientific.studies-
dating from the 1920's. For the purposes of this discussion only
those reports prepared for environmental -impact analysis will be
• considered. The quality and detail of these early studies and
14
accompanying surveys varies greatly. Most of these early studies
lack the detail to adequately determine if the known and
potential paleontological resources were adequately evaluated.
Typically there is no indication of the rock unit(s) present, if
a s-urvey was -conducted or -if done, who did it. Due to this lack
of adequate information these reports cannot be considered to
adequately evaluate the paleontological resources.,Guidelines for
reports are discussed in the Orange County,R-eport on
Cultural/Scientific Resources.
Those reports that were reviewed and found to contain
ade.quate information are listed in Appendix B. Included are three
reports; Cooper (1982), Cooper and Sundberg (1976), and RMW
(1983) which discuss significant paleontological resources in
areas adjacent to the Irvine MEA study area.
There are five reports included in Appendix B that are broad
scale reports covering all or portions of the Irvine MEA study
area. Cooper (1982) and Roeder (198.0) provide a review of the
,paleontological resources of the Senta Ana Mountains (Loma Ridge)
area. Gruen (1978) and Archaeological Associates, Ltd. (1983)
reviewed the paleontological resources of the Stan Joaquin Hills.
PBR in the IRWD MEA provided the only overall review of the
resource for the entire study area. -
Maps of the study areas from those reports which included
field surveys are included in Appendix C.
SIGNIFICANCE OF PALEONTOLOGICAL RESOURCES
Paleontology is a diverse science that encompasses a wide
variety of areas of study ranging from the evolutionary history
of a single organism to the history of life on Earth. Also the
past traces of life (i.e. fossils.) are used to interpret the past
climates and environments of areas. The rocks within the Irvine
MEA study area contain information that will be useful in many of
these studies. Below are presented a few examples of the type of
studies that can and will be aided by fossils from the Irvine
. area.
15
13
The rock units exposed in th,e-Irvine MEA study area
represent a nearly continuous span of time dating from 60 million
years ago. During this time the organisms living on the earth
have undergone several major changes or radiations. Base-d on.
information obtained from adjacent areas the rock units within
the Irvine MEA study area probably contain fossils that would
contribute to the scientific communities' understanding of at
least two of these radiations. The first is the m-ajor radiation
that took place some 50 to 60 million years ago when mammals
first began to expand their numbers and diversity. Most of the
living orders of mammals appeared during this time period. This
time period is represented.by the Silverado an-d Santiago
Formations in the study area. The discovery of fo.ssils-in these,
units will add to our understanding of the development of later
mammalian groups. The second is the major radiation in the marine
mammals that took place between 12 and 20 million years ago. It
was at this time that many of the modern forms appeared in the
seas. This time period is very well represented in the study area
by the Vaqueros, Topang.a, Monterey; and La Vida Member of the
Puente Formation.
In addition to understanding changes in the wo.rldwide
character of the world's animal life the fossils from the various
rock units will contribute to our unde-rstanding of the variations
-within single groups. New species of fossil vertebr-ate.s have been
located in the Vaqueros, Topanga, Monterey, and 'Capistra.no
Formations within ten miles of the study area. The continued
exploration of these -units will certainly add new specimens and
aid in the understanding. of the relationships of these new
species to known forms. The completeness of the sequence'of rocks
increases the potential for the understanding- of evolutionary
lin..ages within various groups.
. The fossils and rocks within the Irvine'MEA study area
Accumulated during a period of rapid change in the landscape .of
.southern California. The study of these resources by earth
scientists will provide information about development of the
16
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southeastern margins of the. Los Angeles basin, the timing, of
basin development, the position of ancient shorelines, and the
environment of the region. The s.tud'y of continuous_ sequences,
like that within Irvine, allow scientist to develop a better
understan-ding of the earth's process, which is of use in studing
less continuous sequences.
In conclusion the rocks -within the Irvine MEA study area
contain a great wealth of information on the paleontological and
geological history of southern California. This information is a
non-renewable resource that once altered or destoryed by
development can never be reconstructed. The past cooperation of
scientist, developer, and regulator has resulted i.n the
collection and preservation of a large volume of data from
-adjacent areas. Similar cooperation within the Irvine MEA study
area will add to this information.
17
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APPENDIX A
BIBLIOGRAPHY
Co-unty of Orange, - 1977. Resolution -of :Board of Supervisors (Nos.
77-866 and 77-9911, En-vironm�ental Management Agency.
-----, 1977. A report on cultural./scientific resources for the
County -of Orange. Cultural/Scientific Resources Policy Task
Force.
Environmental Impact Profiles, 1976. Results of the field survey
of paleontologic resources of the Coyote C'anyo.n Landfill
replacement sites. by R. Ras-chke for County of Orange, EMA.,
Federal Law, 1906. The Antiquity Act of 1906,'(Public Law 59-209,
34 stat. 225; 16 U.S.C. 431-433)
-----, 1935, The Historic Sites Act of 1935, (Public Law 74-292,
'49 stat. 666; 16 U.S.C. 4461-467)-.
-----, 1960. The Reservoir Salvage Act of 1960., (Public Law 86-
523, 74 stat. 220; 16 U.S.C. 469-469c).
-----, 1966. The Historic Preservation Act of 1966, (Public Law
89-665, 80 stat. 915; 16 U.S.C. 470).
-----, 1969. The National Environmental Policy.Act of 1969,
Executive Order 11593 (Public Law 209)
Fife, D.. L., 1973. Lower Tertiary Silverado and Santiago
Formations of the Santa -Ana Mountains region, -Orange -County,
California: NAGT, SCGS Field Trip guidebook -to the northern
Peninsular ranges
-----, 1974, Geology of the south half of the E1 Toro Quadrangle,
Orange County., California: Calif. Div-. of Mines and Geology,
Special Report 110, 27 p. map 1:12000
Golz, D. J., 1976. Eocene artiodactyla of-southe-rn California.
Natural History Museum of Los An-geles County, Science
Bulletin 26, 85 p.
-----, and Lillegraven, J. A., 1977. Summary of known occurrences
of terrestrial vertebrates from Eocene strata of southern -
California. Contribs. to Ge-ology Univ. Wyoming 15 (1):43-65.
Ingle, J. C., Jr., 1979, Biostratigraphy a.nd paleoecology of
Early Miocene through Early Pleisto-cene benthic and
planktonic foraminifera, San Joaquin Hills -Newport ,Bay -Dana
Point area, Orange County, California: in Stuart, C. J.,
ed., A guidebook to Miocene lithofacies and depositio-nal
environments, coastal southern California -and, northwest Baja
California. Pacific Section, Soc. Econ. Mineralogists and
Paleontologists, pp. 53=79.
,
Irvine, City of, 198.3 Environmental Review Matrix, by Community
Planning Services.
Kanakoff, G. P., and Emerson, W. K., 1959. Late Pleistocene.
invertebrates if the Newport Bay area, California. Natural
History Museum of Los Angeles County Contributio-ns in Sci.
No. 31, 47p.
'Leighton and Associates, 1978. Paleontologic _resources of the
Coythe projectoarea. forltheeCountysoflOrange,aassessment
GSA/SolidWaste
the
Management...
1978. Phase II, Pre-construction'paleontol.ogic salvage -
operations at Coyote Canyon La'nd.fill site. for County of
Orange GSA/Solid Waste'Mana-gement.
Loel, W:, and Corey, W. H., 1932, The Vaqueros Formation, lower
Miocene of California: Cptl I, paleontology: Calif. Univ.
Dept. Geol. Sci. Bull., 22(3):31-410.
Merriam, C. W., 1941, Fossil turritellas from -the Pacific Coast
.region of*North America: Univ.-Calif. Publ. Bull. Dept.
Geol. Sci.,26(1)1-214.
Miller, W. E., 1971. Pleist.ocehe vertebrates of the Los Angeles
basin and. vicinity (exclusive of Ranch-o La Brea). Natural
History Museum.of Los Angeles County, Scien.ce_Bull. 10,
1,24p.
Morton, P. K., Miller, R. V., and Fife, D. L., 1973, Preliminary
geo-environmental maps of Orange County, California: Calif.
Divison of Mines and Geology, Preliminary Report 151 4
Plates. 1:48000
Phillips Brandt Reddick/Larry Seeman Associate. Irvine Ranch
Water District Master Environmental Assessment.
Popenoe,, W. P., 1937. Upper Cretaceous mollusca from southern
California. Jour. Paleo. 11(5):,45-49.
1942. Upper Cretaceous formations a,n-d faun -as of southern
California. Amer. Assoc. Petroleum Geologists Bull. 26
(2):162-187.
----, 1954. Mesozoic formations and fa.u.nas,, southern California.
Chapter III, Historical Geology, Calif. Division of Mines
and Geology Bull. 170:15-21.
Raschke, R., 1979. Final report on paleontologic salvage
operations at the Coyote -Canyon -Landfill. prepared, for the
County of Orange, GSA/Solid Waste Management
----, 1980. Paleontological assessment of the proposed SCE HVTL
for Village 12. for Archaeological Planning Collaborative.
1981. Paleontological evaluation of Irvine Center DA,
Village 13. for Larry Seeman.Associates
-_---, 1982. Phase II, Orange County Master Environmental
Assessment. for Larry Seeman Associates.
RMW Paleo. Associates, 1982. Preliminary paleontologic evaluat'ion,,
of Irvine Planning Area 17. for Larry Seeman Associates.
-----, 1982. Paleontological evaluation of �Bommer Canyon -Shady
Canyon. for Larry Seeman Associates.-
1982. Preliminary paleontologic evaluation of Irvine
Center DA. for Larry seeman Associat-es
-----, 1983. Phase III Orange County Master.Environmental
Assessment, Paleontological Resources. for Larry Seeman
A-ssociates
-----, 1983. Paleontological evaluation of proposed improvements
to Laguna Canyon Road (Route 133). for State -of California-,
Department of Transportation.
-----, 1983. East Tustin EIR, Arc'haeology'and paleontology. for
Michael Brandman and Associates
-----, 1983. Proposed,SCE H.VTL alignment, Village 12 Irvi.ne,_
California; review. for Larry Seeman Associ-ates
-----, 1983. Paleontological assessment of IIC-East, Phase III.
for Larry Seeman Associates.
-------1983. Paleontological resources a,ssess-ment "of the Irvine
Medical Complex. for Larry Seeman Associates.
-----, 1984. Final report University Town Center Commercial Core
area. for Larry Seeman Associates.
-----, 1984.. Paleontological resources assessment of' Route 133,,
Laguna Freeway project. for Larry Seeman Associates.
---=-, 1984. Paleontological resources of Planning Area 34 B,
.Irvine Ranch, Irvine, California. for Larry Seeman
Associates.
-----, 1984. Final report paleontological monitoring activities
at Irvine Industrial Complex -East, Phase III._ for Larry,
Seeman Associates.
-----, 1984. Paleo-ntological assessment of the Irvine Center
Study area, Irvine, California.. for Larry S-eeman Associates.
-----, 19,84. Paleontological assessment of Village 19,A, Irvine,
California. for Larry Seeman Associates.
---=-, 1984. Paleontological resource assessment of the proposed
widening of Irvine Center Drive. for Larry Seeman
Associates.
Roeder, M. A., 1980. Paleontologic assessment of the proposed
Foothill/Portola Parkway study corridor. for Phillips Brandt
Reddick.
Schoellhamer, J. E., Kinney, D. M., Yerkes, R. F., and Vedder,,J.
G., 1954, Geologic map of the northern Santa Aria Mountains,
Orange and Riverside Counties, California: U. S. Geol.
Survey Oil and Gas Inventory Map OM-154, 1:24,000
-----; Vedder, J. G., Yerkes, R. F., and Kinney, D. M.., 1981,
Geology of the northe.rn'Sant.a Ana Mountains, California.
Geology of the easterrT Los Angeles basin, southern
California: U. S. Geol. 'Survey -Prof. Paper 420-D, 109 p..
Sundberg, F. A., and Cooper, J. D., 1978. Late Cretaceous
depositional environments, northern Santa Ana Mountains;
southern California. in Mesozoic Paleogeogra-phy of the
Western United States -Pacific. -Section. Soc. Economic
Paleontologists and Mineralogists; Paleogeog'raphy
Symposium II, pp 535-546.
Tan, S. S., and Edgington, W. J., 1976. Geology a,nd-enginee-ring
geologic aspect of the Laguna Beach Quadrangle, Orange
County, California. Cal-ifo�rnia Divison of Mines and Geology,
.Special Report 127 32p. 1 map 1:12000.
Vedde-r, J. G.., 1972. Review of stratigraphic names and megafaunal
correlation of Pliocene rock along the southeast margin of
'Los Angeles basin, California. in Proceedings of ;;the Pacific
Coast Miocene Biostratigraphic Symposium: Society of -
Economic Paleontologists and Mineralogists, Pacific Section,
Bakersfield, California, pp. 158-172.
-----, 1979, The Topanga Formatio-n of the San Joaquin Hills,
Orange County California: in Stuart,,',C. J., ed., Miocene
lithofacies and depositionar environments, coastal Southern
California anal northwester-n Baja California: Pacific
-
Section, Soc. Econ. Paleontologists and Mi-neralogists,'pp.
19-24.
-----, Yerkes, R: F., and Sc-hoellhame'r, J. E., 1957, Geologic map
of the San Joaquin Hills -San Juan Capistrano area, Orange
County, California: U. S. Gedl. Survey Oil and Ga-s Inventory
Map OM-193. 1:24,000
Yerkes, R. F., McCulloh, T. H., Schoellhamer, J. E., and Vedd-er',
J. G., 1965, Geology of the Los Angeles Basin, California -An
introduction: U. S. Geol. Survey Prof. Paper 42,0-A, 57 p.
0
APPENDIX B
ACCEPTABLE SURVEYS AND REP-ORTS
0
Archaeological Associates, Ltd., 1983. A, Cultural/Scientific
Resources Investigation of the Planned'San Joaquin
Transport-ation Corridor. for EMA County of Orange,
Environmental analysis
Barnes, L. G., 1980. Phase I,,Orange County Master Environmen-tal
'Assessment, Paleontological Resources. for EDAW, Inc.
Coo.per., J. D., 1978. Archaeological, Pa-leontological, and -
Historical -Report on the propo-sed Bee,and Round Canyons
Landfill Disposal Station, 0-range County, California. by
SRS, Inc. for Lockman and Associates/Toups Corp.
-----, 1978. Paleontologic assessment of the Hicks Canyon are -a.
for SRS, Inc.
-----, 1982. County of'Orange Foothill Transportation Corridor
study phase II, paleontological assessment;. for Larry Seeman
Associates.
----- and Sundberg, F. A., 1976. Paleontological assessment of
Peters Canyon Reservoir Regional Park study area. for County
of Orange EMA Advance Planning.
Environmental Impact Profiles, 1976. Results of the field survey
of paleontologic.resource.s of the Coyote Canyon Landfill
replacement sites. by R. Raschke for County of Orange, EMA.
Gruen Associates, Inc., 1978. Environmental Impact Report 2,67 and
Study Report Phase I San Joaquin Hills Transportation
Corridor Route Location Study. for EMA-County of Orange
Leighton and Associates, 1978. Paleontologic re,s,ou.rces of the
Coyote Canyon Landfill area, Phase I, initial assessment of
the project area. for the County of Orange, GSA/Solid Waste
Management.
Phillips Brandt Reddick/Larry Seeman Associate. Irvine Ran-ch
Water District Master Environmental Assessment.
Raschke, R., 1979. Final report on paleontologic salvage
operations at the Coyote Canyon Landfill. prepared for the
County of Orange, GSA/Solid Waste Management
-----, 1980. Paleontological assessment of the proposed SCE HVTL
for Village 12. for Archaeological Planning Collaborative.
-----, 1981. Paleontological e-valuation of Irvine Center DA,
Village 13. for Larry Seeman Associates
-----, 1982. Phase II, Orange County Master Environmental
• Assessment. for Larry Seeman Associates.
RMW Paleo. Associates, 1982. Preli-minary paleontologic evaluation
of Irvine Planning Area 17. for Larry Seeman Associates.
1982. Paleontological eof Bommer Canyon -Shady
Canyon. for Larry Seeman Associates
----- 1982. Preliminary paleontologic evaluation of Irvine
Center DA. for Larry Seeman Associates
----- 1.983. Phase III Orange County -.Master Environmental
Assessment, Paleontological Resources: for Larry Seeman,
Associates
-----, 1983. Paleontological evaluation of proposed imp.roveme.nts
to Laguna Canyon Road (Route 133). for State of California,
Department of Transportation.
-----, 1983. East Tustin EIR, Archaeology and paleontology. for
Michael Brandman and. Associates
1983. Proposed SCE HVTL alignment, Villa-g-e 12 Irvine,
California, review. for Larry Seeman Associates
1983. Paleontological assessment of IIC-East, Ph-ase III.
for Larry Seeman Associates.
1983. Paleontological resources assessment of. th•e Irvine
Medical Complex. for Larry Seeman Associates
-----, 1984. Final report University Town Center Commercial Core
area. for Larry Seeman Associat-es.
_---=, 1984. Paleontological resources assessment of Route 113,
Laguna Freeway project. for Larry Seeman Ass-ociates.
-----, 1984. Paleontological resources of Planning Area 34 B,
Irv-ine Ranch, Irvine, Cal-ifornia.- for Larry seeman
Associates.
-----, 1984. Paleontological assessment of the Irvine Center _
Study area, Irvine, California. for Larry Seeman Associates.
-----, 1984. Paleontological assessment of Village 19 A, Irvine,
California. for Larry Seeman Associates.
1984. Paleontological reso�.urce assessment of the proposed
widening of .Irvine Center Drive. for Larry S-eeman,
Associates.
Roeder, M. A., 1980. Paleontologic assessment of the proposed
Foothill/Portola Parkway study corridor. for Phillips Brandt
0
Reddick.
•
a
•
APPENDIX C
MAP .FROM SURVEYED AREAS,
El Tori
tarme SciY "�'.. I t\ r F' _': 60
. ♦ 1 1 { �.11 ate__.- \ .•e
It It I
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00
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,fir' • , • ,♦ ., �; 'y � ` � Y . r� � �<E" � 2R1?'QitSi.:7Y i �iy
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cp
T CORPS \•\�: ¢;' + �/\;` v'• r'a�. �.tr� �i .�/ �k
,j �i �i;�.. �,�^I•-'jig � �, � �� •/'-� J ` .
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S-CCI,� 1 _s
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Figure 1 Location Map
Ir•vine'Industrial Complex-
East- Phase IU Study Area
RMW Paleo. Assoc. 1984
• t• - .. ... - , is
rri-n�•
_ .. - ' .r a--:e•- � ��-...:..- •..• /Oc•_: •v It
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.56
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4
--� :Archaeological Site (taken from USGS Tustin, California IS" Quad.)
:Distroyed Archaeological Site T u rtt 1•e R o k III and V -
is.Tr.?sa.Ttlt, Gae : Lithological Units A r c h-a e o l o g i c a� Research Inc 19 7 7-
e
I
a�
a
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Figure 1. Location map -of study area showing paleontologic localities
S dv area
N 0 0•. O • � • Q .� o ' o o °� o o : o , c • o .•a . " '. . ' • • • ; • S
'*vaqueros- -Vaqueros.
c jesgg„
e O O p G7
O O,O p p O C •� •o C• 0 o O• O O
• • c o o ° o' . ° o , • 'e� Sespe
O - °•
o
Figure 2. Cross-section diagram depicting iaterfingering facies rela-
tionship between marine Vaqueros and non -marine Sespe.
•
Hicks Canyon Cooper 1978
1
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is
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�� � S-urveyed M W PAL�O Area
ASSOCIATC-S Fossil occurrer
RMW Paleo Associates 1982
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13
Figure 1. Stu-dy Area
Irvine Industrial Co.r.plex
Paleontological assessment
(El Toro 7.5 min. Ouad-)
RMW Paleo.. Assoc. 1983
� i i Ir1N,•YtAts •/ � .• a
• ~' � to � / ?` .
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m
N
Fossil Locality
ASSOCIATES i t i v i t z o-n e
High Sens Y .
RMW Paleo, Assoc. 1983
am 12/0
A. N J A G
MPALQO
NASSOCIATQS
1984
C1
2 1
19
Figure 1. Planning A.rea 34B'
Paleontological Resource
Evaluation
Fossil.Occurrence
'Project Boundary
Her
Q k
A.
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N.
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M -195
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Figure T. Irvine Ce-nte'r
Paleohtological Resources'
V-aqueros Formation
(High Sensitivity)
RMW 'Paleo. Assoc.-1984
0
APPENDIX 'D
FOSSIL LOCALITIES
•
•
The following are abbreviations. used in thA-s appendix and- on
the locality maps:
LA -CM = Natural Histo-ry Museum of Los Angeles County
UCLA = University of California, Los Angeles
UCRIVP = University of California, 'Riverside invertebrate
paleontology
UCMP = Museum of Paleo"ntology, University of California, Berkeley
LACM (CIT) = California Institute of Tech-nolog,y. (CIT) .records, now
at LACM
'UCLA (CIT) = California Institute of Technology (CIT) records now
at UCLA
NHF = Natural History Foundation of Orange County
USGS,= United States Geological Survey
JBC-HC- = John Cooper Hicks Canyon San Diego Creek study -'see
Cooper, 1978
JBC-BR- = John Cooper Bee and Round Canyons study see Cooper
1978b.
'RR = Personal field records of Rod-ney Ra.sc-h--ke
LC = published records of Loel,and Corey, 1932
Map Abbreviations
plotted location in institution records
O = approximate locality, exact location uncertain.
•
PALEONTOLOGICAL LOCALITIES DESCRIPTIONS
vine
to # _ Site Description
Planning Area 1
001 Locality Number LACM 6666 Quad. Tustin
Formation Vaqueros, or Santiago Fos.siIs vertebrates
Source of Information LACM locality Records
002
003
004
005
6006
Planning Ar-ea 1
Locali.ty Number U"SGS
Formation Santiago
Source of Information
Planning Area 1
Locality Number USGS
Formation Santiago
Source of Information
Planning, Area 1
Locality Number USGS
Formation Santiago
Source of Information
Planning Area 1
Locality Number USGS
Formation Santiago
Source of Information
106 Quad. Tustin
Fossils invertebrates
Schoellhamer et al. (1981)
107 Qu-ad. Orange
Fossils invertebrates
Schoellhamer et al. (1981)
ill Quad. E1 Toro
Fossils invertebrates
Scho-el lhamer. et al. ( 19,81 )
112 Quad. E1 Toro
Fossils invertebrates
Schoellhamer et al. (19B1).
Planning Area 1
Locality Number USGS 136 Q"ua,d._ E,1 Toro
Formation Vaqueros-Sespe Fossils invertebrate.s
Source of Information Schoellhamer et al. (1981)
007
Planning
Area 1
Locality
Number USGS 137
Quad. E1
Toro
Formation
Vaqueros-Sespe
Fos-sils
invertebrates
Source of
Information Schoel l'ha"me:r
et
aI I. ( 1981)
Planning
Area 2
008
Locality
Number USES 114b
Quad. E1
Toro
Formation
Santiago
Fossils
invertebrates
Source of
Information Schoellhamer
et
al. (19,81)
Planning
Area. 2
009
Locality
Number USGS 13.5
Quad. E1
Toro
Formation
Vaqueros-Sespe
Fossils
invertebrates
Source of
Information Schoellhamer
et
al. (1981)
Planning
Area 2
010
Locality
Number JDC-HC-6
Quad. El
Toro
Formation
Vaqueros-Sespe
Fossils
invertebrates, plants
•
Source of
Information Cooper
(1978b)
Planning
Area 3
.
Oil
Locality
Number JDC-HC-1
Quad. El
Toro
Formation
Vaqueros-Sespe
Fossils
invertebrates
Source of
Information Cooper
(1978b)
PALEONTOLOGICAL LOCALITIES DESCRIPTIONS (Cont.)
vine
te # Site Des-cription
012 Plannin-g Area 3
Locality Number JDC-HC-2 Quad. E1 Toro
Formation Vaqueros-Sespe Fossils invertebrates
Source, of Information Cooper (1978b)
013' P-lanning Area 3
Locality Number JDC'-HC-3 Quad. E1 Toro
Fo-rmation Vaqueros-Sespe Fossils-i.nverteb-rates, vertebrates
Source of Information Cooper (1978b)
014 Planning Area 3
Locality Number JDC-HC-4 Quad. E1 Toro
Formation Vaqueros-Sespe Fossils i,nvertebrates-
Sou.rc.e of Information Cooper (1978b)
015 Planning Area 3
Locality Number JDC-HC-5 Quad. El Toro
Formation Vaqueros-Sespe F6.ssi-Is plant
Source of Information Cooper (1978b)
016 Planning Area 4
Locality Number JDC-BR-1 Quad. E1 Toro
Formation Williams Fossils inve'rte.brates
Source of Information Cooper (1978a)
17 Planning Area 4
Locality Number JDC-BR-6 Q-ua-d. El Toro
Formation Topanga Fossils invertebrates
Source of Information Coo -per (1978a)
018 Planning Area 4
Locality Number JDC-BR-8 Quad, El Toro
Formation Puente, La Vida Fossils verteb.r.ates
Source of Information Cooper (1978a)
019 Planning Area 4
Locality Number JDC-BR-9 Quad. E1 Toro
Formation Puente, La Vida Fossils vertebrates
Source of Information Cooper (1978a)
020 Planning Area 4
Locality Number RR153'
Formation Puente
Source of Information
Planning
Area 4
021
Locality
Number R-R154
Formation
Puente, La
•
Source of
Planning
Information
Area 4
022
Locality
Number RR155
Formation
Puente, La
Source of
Information
Quad. El Toro
Fossils invertebrates
Environment-a.1 Impact.; Profiles (1976),
Quad. El Toro
Vida Fossils vertebrates
E.nviron-mental Impact Profiles (1976)
Quad-. El Toro
Vida Fossils vertebrates
Environmental Impact Profile.,
PALEONTOLOGICAL LOCALITIES DESCRIPTIONS (Cont.)
rvine
ite # Site Description_
023 Planning Area 4
Locality Number RR-156 Quad. E1 Toro
Formation Puente, La 'Vida Fossils vertebrates
Source of Information Envi-ro=entaj Impact Profiles (1976)
024 Planning Area 4
Locality Number USGS 44 Quad. E1 Toro
Formation Williams Fossils invertebrates
Source of Information Schoellhamer et al. (1981)
025 Planning Area 4
Locality Number UCLA 414 Quad. E1 Toro
Formation Williams Fossils in.vert,ebrates
Source of Information UCLA Locaity Records
026 Planning Area 4
Locality Number UCLA 415 Quad. E1 Toro
Formation Williams Fossils invertebrates
Source of Information UCLA locality records
027
Planning
Area 4
Locality
Number UC.RIVP 7898
Quad. E1
Toro
Formation
Williams
Fossils
invertebrates
Source of
Information UCR locality records-
2-8
Planning
Area ' 5
Locality
Number LC 6131
Quad. El
Toro
Formation
Vaqueros-Sespe
Fossils
invertebrates
Source of
Informatio-n Loel and- C-orey (1932)
029
Planning
Area 5
Locality
Number JOG-OR-2
Quad. E1
Toro
Formation
Vaqueros-Sespe
Fossils -invertebrates
Source of
Information Cooper
(1978a)
030
Planning
Area 5
Locality
Number JDC-BR-3
Quad. E1
Toro
Formation
Vaqueros-Sespe
Fossils"
nverteb=rate.s = =
Source of
Information Cooper
(1978a)
031
Planning
Area 5
1
Locality
Number JD-C-B.R-4
Quad., El
Toro
Formation
Vaque.ro.s-Sespe
Fossils.
invertebrates, vertebrates
Source of
Information Cooper
(1978a)
032
Planning
Area 5
Locality
Number JDC-BR-7
Quad. El
Toro
Formation
Topanga
Fossils
i.nvertebrate:s
0033
Source of
Information Cooper_(1978a)
Planning
Area 5
Locality
Number UCLA 282
Quad:- E1
Toro
Formation
Vaqueros-Sespe
Fossils
invertebrates
Source of
Information. UCLA .locality records
PALEONTOLOGICAL LOCALITIES DESCRIPTIONS (Cant.)
vine
ite # Site Description-
034 Planning Area 5
Locality Number UCLA 413 Quad'. E1 Toro
Formation -Vaqueros.-Sespe Fossils invertebrates
Source of Information UCLA locality records
035 Planning Area 5
Locality Number LACM 4171 Quad. El Toro
Formation Capistr-ano,Oso SandFo.ss.ils vertebrates
Source of Information LACM verte-b-rate pale -ontology
locality recordEl
036 Planning Area 5
Locality Number RR160 Quad. E1 Toro
Formation- Vaqueros=Sespe Fossils inyertebr-ates
Source of Information Environmental Impact P-rofiles (1,976)
037 Planning Area 5
Locality Number RR161 Quad. E1 Toro
Formation Vaqueros-Sespe Fossils invertebrates
Source of Information Environmental Impact Profiles ('1976)
038 Planning
Area 5
Locality
Number LC 2.337
Quad. E1
Toro
Formation
Vaqueros-Sespe
Fossils
'inverte,brate-s
Source -of
439
Information Loel
and Co-rey (1932)
Planning
Area. 5
Locality
Number USGS 138
Quad. E1
Toro
Formation
Vaqueros-Sespe
Fossils
invertebrates
Source of
Information Schoellhamer et
al. (19.81)
040 Planning
Area 5
Locality
Number USGS 192
Quad. E1
Toro
Formation
Topanga
Fossils
invertebrates
Source of
Information Sch.oell'h.amer et
al. (1981)
041 Planning Area 6
Locality Number USGS 1 Quad. El Toro
Formation Vaqueros-Sespe Fos.sils verteb-rates
Source of Information Schoellh-amer et al. (tHl ) also UCMP v6100
Planning
Area 6
042
Locality
Number USGS 193
Quad.
E1 Toro
Formation
Topanga
Fossils
invertebrates
Source of
Information Sc'hoellhamer et
al..-(1981)
Planning
Area 6
043
Locality
Number UCLA 1,534
Quad.
E1 Toro
Formation
Vaqueros-Sespe
Fos-sils
invertebrates
•
Source of
Information UCLA
locality
records
044
Planning
Area East of 6
Locality
Number LACM(CIT) 449 Quad.
E-1 Toro
Formation
Vaqueros-Sespe
Fossils
vertebrates
Source Source of
Information LACM
locality
records
PALEONTOLOGICAL LOCALITIES DESCRIPTIONS (Cont.)
vine
Oite # Site Description
045 Planning Area 16
Locality Number LC A537 Quad. Tustin
Formation. Vaqueros Fossils invertebrates
Source of Information Loel and Corey (1932)
046 Planning Area 17
Locality N-umberUSGS503 Quad. Tustin
Formation Vaqueros Fossils invertebrates
Source of Information Vedder et al. (19-57)
047 Planning Area 17
Locality- Number USGS 505 Quad. Tustin
Formation Vaqueros Fossils invertebra-tes
Source of Information Vedder et al: (1957)
048 Planning Area 17
Locality Number USGS 506 Quad. Tustin
Formation Vaqueros Fossils invertebrates
Source of Information Vedder et al. .(1957)
049 Planning Area 17
Locality Number USGS 507' Au,ad. Tustin
Formation Vaqueros Fossils invertebrates
Source of Information Vedder et al. (1957)
050 Planning Area 17
Locality Number USGS 508 Quad.. Tustin
Formation Vaqueros Fossils. invertebrates
Source of Information 'Vedder et al. (1'957)
051 Planning Area 17
Locality Number USGS 509 Quad. Tustin
Formation Vaqueros Fossils invertebrates
Source of Information Vedder et al. (1957)
052 Planning Area 17
Locality Number USGS 510 Quad., Tustin
Formation Vaqueros Fossils invertebrates
Source of Information Vedder et al. (1957)
053 Planning Area 17
Locality Number USGS 512 Quad. Tustin'
Formation Vaqueros Fossils invertebrates
Source of Information Vedder et al. (1957)-
Planning Area 17
054 Locality Number LC A535 Quad. Tustin
Formation Vaqueros Fo-ssils invertebrates
• Source of Information Loel and Corey (1932)
Planning Area 18-
055 Locality Number USGS 511 Quad. Tustin
Formation Vaqueros Fossils invertebrates
Source of Information Vedder et al. (1957)
PALEONTOLOGICAL LOCALITIES DESCRIPTIONS (Cont.)
vine
ite # Site Description.
056 Planning Area 21
Locality Number.NHF 54 Quad. -Tustin
Formation Vaqueros Fossils, invertebrates
Source of Information Natural History Foundation, Orange County
057
Planning Area 21
Locality Number NHF 55
Quad.
Tustin.
Formation Vaqueros
Fossils
invertebrates
Source of Information Natural History Foundation, Orange County
058
Planning Area 21
Locality Number NHF 121
Quad.
Tustin
Formation Vaqueros
Fossils invertebrates
Source of Information Natural History,Foundation, Orange County
059
Planning Area 21
Locality Number LC A538
Quad.
Tustin
Formation Vaqueros
Fossils invertebrates
Source of Information Loel,and
Corey (1932)
060
Planning Area 22
Locality Number UCLA(CIT) '374 Qua-d.
L.a,guna B.ea-ch
Fo_rmation Vaqueros
Fossils invertebrates
Source of Information UCLA
locality
records.'
061
Planning Area 25
Locality Number LACM- 1067
Q,uzd.
Tustin
Formation Fernando
Fossils vertebrates
Source of Information LACM
locality
records
062
Planning Area 25
Locality Number LACM 3407
Quad.
Tustin
Formation Marine to
'Fossils Fossils
Vertebrates an-d invertebrates
Source of 'Information LACM
locality
records
063
Planning Area 25
Locality Number LACM 3877
Quad.
T-ustin
Formation Marine Terrace
Fossils
vertebrates
Source of Information LACM
locality
records
064
Planning Area 25
Locality Number LACM 3980
Quad._
Tustin
Formation Fernando
Fossils.
vertebrates
Source of Information LACM
locality
records
065
Planning Area 32
Locality Number LACM 3866
Quad.
E1 Toro
Formation Capistrano/Monterey
Source of Information .LACM
Fossils
locality
vertebrates
records
66
Planning Area 34
:
Locality Number USGS 504
-Quad.
Tustin
Formation Vaqueros
Fossils
invertebrates
Source of Information Vedder
et.al.
(1957).
PALEONTOLOGICAL LOCALITIES DESCRIPTIONS (font.)
vine
Oite # Site Description
067 Planning Area 37
Locality Number LACM 1068 Qu.ad. Tustin
Formation Marine terrace Fossils vertebrates
Source of Information LACM' locality, records.
068
Planning Area 37
Locality Number LACM 1069
Qu-ad. Tustin
Formation ?
Fossils verte-brates'
Source of Information LACM
-locality records
069
Planning Area- 37
Locality Number LACM 3977
Quad. Tustin
Formation Fernando
Fossils vertebrates-
So,urce of Information LACM,
locality records
070
Planning.Area 37.
-
Locality Number LACM 3978
Quad. Tustin
Formation Fernando
Fossils vertebrates
Source of Infor.mation LACM
LocALITY records
071
Planning Area 37
Locality Number LACM 3986
Quad. Tustin
Formation Fernando
Fossils-.verteb-rates
Source of Information LACM
locality r.e-cords�
072
Planning Area 37
Locality Number.N-HF 96
Quad. Tustin
Formatio-n Topanga
Fossils vertebrates
Source of Information Natural
History Foundation, Orange County
073
Planning Area MCAS
Locality Number NHF 128
Quad. E1 Toro
Formation Topanga
Fossils inverte°b-rates
Source of Information Natural
History Found.ati.on, Orange Cou-nty
074
Planning Area MCAS
Locality Number USGS 534
Quad. E1 Toro
Formation Topan.ga
Fossils invertebrates
So-urce of Information Schoellhamer
et al. (1581)
075� Planning Area MCAS
Locality Number RR 622 Quad. -E1 Toro
'Formation Vaqueros - Fos-sils 've-rt:elb-rates a-nd invertebrate's
Source of Information Rod .Raschke personal field notes
0
6
6
•
APPENDIX E.
REPORT INDEX
PA Report Type Date Report # Project -Title
01 Survey 08/30/82 1-2 Foothill Trans. -Corridor Phase II
Ol Evaluation 12/05/80 1=1 Foothill Trans. Corridor Phase I
02 Survey 03/02/78 2-1 Hicks'Canyon.
02 Survey 08/30/82 1-2 Foothill.Trans. Corridor Phase II
02 Evaluation 12/05/80 1-1 Foothill Trans. Corridor Phase I.
03 Survey 09/30/82 1-2 Foothill Trans.. Corridor Phase I -I
03 Survey 03/02/78 2,1 Hicks Canyon
03 Survey 01/01/78 4-2 Bee and Round -Canyons
03 Evaluation 12/05/80 1-1 Foothill -Trans. Corridor Phase,I
04 Survey 09/30/82 1-2 Foothill Trans. Corridor Phase II
04 Survey 01/01/78 4-2 Bee and -Round Canyons
04 Survey 05/01/76 4-1 Coyote Canyon Landfill Replacement
04 Evaluation 12/06/80 1-1 Foothill Trans. Corridor Phase I
05 Survey 09/30/82 1-2 -Foothill Trans. Corridor Phase II
05 Survey 01/01/78 4-2 Bee and Round Canyons
05 Survey 05/01/76 4-1 Coyote Canyon Landfill Replacement
05 Evaluation 12/05/80 1-1 Foothill Trans. Corridor -Phase I
06 Survey 09/30/82 1-2 Foothill Trans. Corridor'Phase II
06 Evaluation 12/05/80 1-1 'Foothill Trans:- Corridor Phase I
12 Evaluation 11/24/80 12-1 SCE HVTL-,Realignment
13 Survey 11/04/81 13-1 Village 13 Assessment
•
l�
r�
u
13 Survey 05/03/83 13-2 Irvine Medical C6mplex-
13 Evaluation 08/31/84 13-3 Route 133-Overcrossings
17 Survey 08/19/83 17-2 Laguna Canyon Road,.Improvements
17 Survey 07/06/82 17-1 Planning Area 17
18 Survey 08/19/83 17.4 Laguna Canyon Road Improvements
19 Survey 03/23/84 19-1 Village 19A
21 Survey 02/24/77 21-1 Turtle Rock Enclaves III & V
22 Survey 05/25/82.22-1 Bommer/Shady Canyon
24 Grading 05/25/84 24-1 Town Center Commercial Core
25 Evaluation '01/01/83 25-2 San Joaquin Hills Trans. Corridor
33 Survey 11/06/84 33-2 Irvine Center
33 Evaluation 09/16/82 33=-1 Irvine Center Development -Agreement
33 Evaluation 68/31/84 13-3 Route .133 Overcrossings
34 Survey 09/19/83 17-2 Lag-una Canyon Road Improvements
34 Survey 06/11/84 34-2 Planning Area 34 B
34 Survey 06/08/84 34-1 Irvine Center Drive Widening
34 Evaluation 09'/16/82 33-1 Irvine Center Development Agreement
35 Survey 12/09/83 35-1 Irvine Industrial: Center Phase III
35 Evaluation 09/16/82 33-1 Irvine Center Development Agreement
99 Evaluation 06/.25/79 99-2 IRWD MEA
99 Evaluation 01/16/85 99-1 ,Irvine Mea
i