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CASTAWAYS_MARI NA PLOT_
FINAL EIR RESPONSES
THE IRVINE COMPANY
CASTAWAYS MARINA
PROJECT SUMMARYf'-
APPENDIX D
June 2,1993
n
LJ
TABLE OF CONTENTS
APPENDIX D
1. "Castaways Marina Final Environmental Impact Report - Response to
Comments Addendum" prepared by Michael Brandman and Associates,
State Clearinghouse #88081016, November, 1991
2. "Report of Geotechnical Exploration - Proposed Castaways Marina -
Newport Beach, California" prepared by Converse Consultants
Orange County, Project No. 90-32155-01, July 19, 1990
3. "Test Excavation of a Portion of CA-Ora-84, Newport Beach, Orange
County, California" prepared by RMN Paleo Associates, Project
No. 89'-11801 May 9, 1990
4. "Castaways Marina, Engineering Study and Feasibility Report"
prepared by Cash & Associates Engineers, Project No. 2492.01,
August 26, 1987
• 5. "Castaways Marina Qualitative Analysis of Hydrodynamics and Sedi-
mentation" prepared by Rivertech Inc., July 16, 1987
6. Memorandum and Pacific Bell Plan regarding "Location and Status
of Submarine Cable in Newport Say", November, 1992
i
CASTAWAYS MARINA
FINAL ENVIRONMENTAL IMPACT REPORT RESPONSES TO
COMMENTS ADDENDUM
11
is
I•
Castaways Marina
a I E a 10a0o
Final
Environmental Impact Report
Responses to Comments Addendum
CITY OF NEWPORT BEACH
RECEIVED
• NOV 2 0 1991
CASH & ASSOCIATES
CASTAWAYS MARINA
FINAL
ENVIRONMENTAL IMPACT REPORT
RESPONSE TO COMMENTS ADDENDUM
State Clearinghouse #88081016
Prepared for:
City of Newport Beach
Planning Department
3300 Newport Boulevard
P.O. Box 1768
Newport Beach, California 92659-1768
(714) 644-3225
Contact: Patricia L. Temple
Prepared by:
L
Michael Brandman Associates
Carnegie Centre
2530 Red Hill Avenue
Santa Ana, California 92705
(714) 250-5555
Contact: Beverly Bruesch, AICP
0
November 1991
TABLE OF CONTENTS
• Section Page
1 INTRODUCTION ...................................... 1-1
•
2 LIST OF COMMENTORS, COMMENTS, AND
RESPONSES TO COMMENTS ............................. 2-1
3 ATTACHMENTS ....................................... 3-1
A. Comment Letters
B. Conceptual Biological Mitigation Plan for
Loss of Mudflat and Shallow Subtidal Habitat
C. Additional References Cited
D. County of Orange Ordinance No. 2200
J=0064001 I.TC 1
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SECTION 1
INTRODUCTION
In accordance with Section 15088 of the State CEQA Guidelines, the City of Newport Beach, as the
lead agency, has evaluated the comments received on the Draft Environmental Impact Report (EIR)
for the proposed Castaways Marina, and has prepared written responses to said comments. The
"Response to Comments Addendum" becomes a part of the Final EIR for the subject project, in
accordance with Section 15132 of the State CEQA Guidelines.
Section 2 of this document includes a list of those persons, organizations, and public agencies
commenting of the Draft EIR. The list is followed by restatement of the written comments received
on the Draft EIR, and the City's responses to the major environmental points raised by the written
comments. Where revisions to the Draft EIR text are required, the responses indicate this by
presenting the revised text (deleted material is shown with an overstrike [
and new material is underlined fas shown by this examolel). Also note that many comments are
related to the project and do not raise environmental issues or request additional information. These
comments are responded to with, "The comment is noted; no response is required."
Section 3 includes attachments or supporting material referenced in the responses to comments,
including (A) copies of the comment letters, (B) a copy of the conceptual mitigation plan for the loss
of mudflat and shallow subtidal habitat, (C) a list of additional references cited in this addendum, and
(D) a copy of the County of Orange Ordinance 2200.
tB21ooe40ott.I. 1-1
SECTION 2
• LIST OF COMMENTORS, COMMENTS, AND RESPONSES TO COMMENTS
•
11
Following a list of commentors, this section includes responses to all written comments on the Draft
EIR received during the Draft EIR review period. Each comment from each letter is restated in full,
then is followed by a response. Copies of the comment letters are provided for reference in
Section 3.A.
JB2/00640011.2a 2-1
LIST OF COMMENTORS
I. FEDERAL AGENCIES
Comment
and Response
Page No,
I.A. U.S. Department of the Interior,
Fish and Wildlife Service ............................... I-1
I.B. U.S. Department of Commerce,
National Marine Fisheries Service .......................... I-2
LL IL STATE OF CALIFORNIA AGENCIES
II.A. Governor's Office of Planning and Research ................... II-1
H.B. State Lands Commission ............................... II-2
II.C. California Department of Transportation (Caltrans),
District 12........................................ II-7
H.D. California Department of Fish and Game ..................... II-8
II.E. California Regional Water Quality Control Board,
Santa Ana Region .................................... II-9
M. LOCAL AGENCIES
M.A.
County of Orange,
Environmental Management Agency ........................
III-1
M.B.
City of Costa Mesa,
Transportation Services Manager ..........................
III-2
IV. INTERESTED PARTIES
N.A.
Terrell Watt, AICP..................................
N-1
N.B.
Friends of Newport Bay ...............................
N-9
N.C.
Sea & Sage Audubon ................................
N-12
N.D.
Jan D. Vandersloot, M.D..............................
IV-14
N.E.
Cliff Haven Community Association .......................
IV-19
N.F.
James Kociuba....................................
IV-22
N.G.
City of Newport Beach,
Environmental Quality Affairs Committee ...................
N-24
N.H.
Bayshores Community Association ........................
N-25
•
JB2\00640011.RTC
2-2
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I.A. UNITED STATES DEPARTMENT OF THE INTERIOR
Fish and Wildlife Service (October 10, 1991)
Comment I.A-1. Intertidal mudflats and shallow subtidal areas are among the highest habitat
value and most scarce habitat types in southern California. They can provide
food for very large numbers and many types of shorebirds, waterfowl, wading
birds, and diving birds. The state and federal endangered California least tern
breeds at Upper Newport Bay and relies on this "shallow water" habitat for
food. The proposed marina expansion would destroy or degrade these
important habitat types. Were a federal permit action pending, the Service
would likely recommend denial of the permit application for the proposed
project. On the other hand, we would have little objection to a project which
included excavation of the new marina basin, little dredge or fill and few slips
in the channel area.
Response I.A-1. Comments are noted for the record. These comments do not address the
Draft EIR; nor do they raise environmental issues not already addressed
in the Draft EDi (i.e., habitat loss). Please note that alternatives to the
proposed project have been evaluated in the Draft EIR which would
reduce the amount of dredging compared to the proposed project (the 121-
boat, 84-boat, and 50-boat alternatives are addressed in Section 6 of the
Draft EIR). Also, see response to comment I.B-1 which evaluates a 60-
boat alternative that includes a new marina basin but no pier.
JB2J00640011.RTC
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I.B. UNITED STATES DEPARTMENT OF COMMERCE,
NationaU Marine Fisheries Service (October 7, 1991)
Comment I.B-1. We believe that avoidance or minimization of impacts to high value habitats
should be vigorously pursued. As a consequence, we are concerned over the
loss of mudflat and shallow water habitat that would occur with
implementation of the proposed project and all of the alternatives described,
with the exception of the no project alternative. In order to reduce these
impacts, we believe consideration should be given to an alternative which
includes excavation of the marina basin in the Lower Castaways area but
eliminates all slips in the channel area. Dredging requirements, and
subsequent impacts to high value intertidal and shallow subtidal habitat, would
be minimal with this alternative.
Response I.B-1. N an alternative were considered which would eliminate the pier structure
altogether, it would have impacts similar to those of the 121-boat
alternative with the exception of impacts associated with in -bay dredging.
Such an alternative would reduce the amount of in -bay excavation but
would not substantially alter impacts to the mudflat and halibut nursery
habitats since these habitats are located primarily at the mouth of the
proposed new marina and would be dredged under any of the marina
alternatives at this site.
IWJW640011.RTC
The following table presents data for a new marina basin (such as that in
the 121-boat alternative, but without the pier structure (as conceptualized,
it would include approximately 60 boat slips).
New Marina Basin Without 121-Boat Slip
Pier Structure Alternative Alternative
Estimated amount of dredging
Dry material (cu. yds) 56,000 56,000
Wet material (cu. yds) 6,450 11.000
Total (cu. yds)
62,450
67,000
Halibut NOY Nursery)
Removed (acres)
-0.24
-0.24
Created (acres)
+0.03
+0.03
Net Loss (acres)
-0.21
-0.21
Halibut (Juvenile)
Removed (acres)
0.00
0.0
Created (acres)
+2.50
+2.50
Net Gain (acres)
2.50
+2.50
I-2
•
•
•
Mudflat
Removed (acres) -0.29 -0.34
Created (acres) 0_00 0_00
Net Loss (acres) -0.29 -0.34
As shown from the above table, this alternative would result in less
dredging than the 121-boat alternative (approximately 4,550 cubic yards
less). It would result in the same amount of halibut habitat alteration as
the 121-boat alternative, but less (approximately 0.05 acre) mudflat loss.
This alternative would be environmentally superior to the 84-boat, 121-
boat, and 125-boat alternatives but would not be economically feasible due
to the costs of developing and maintaining the marina.
Comment I.B-2. PagQ 5.4-1 . It is stated that the additional boats introduced by the project
will increase the incidence of oil and fuel spills and, therefore, contribute to
cumulatively significant water quality degradation in Newport Bay. The
mitigation measures described on page 5.5-21, while reducing the potential
impact, will not eliminate those effects. Additional mitigation to offset any
remaining impacts should be proposed.
Response I.B-2. No additional mitigation measures beyond those identified on pages 5.4-15
and 5.4-16 of the Draft EIR are available which can be implemented by
the project applicant or City of Newport. The City will grant full
consideration to any measures identified through the hearing process. The
proposed Castaways Marina would involve minimal risk of a spill, because
no fueling station would be located at the proposed marina, and the lease
agreement would prohibit major boat cleaning (boat painting, scraping)
and maintenance. These regulations will be enforced on a daily basis.
Thus, the risk of a discharge of pollutants associated with the marina
would be minimal, and the mitigation measures as proposed in the Draft
EIR are considered adequate.
Comment I.B-3. Paze 5.5-20. It is assumed that the new marina basin will be utilized by
California halibut in a manner similar to the existing habitat proposed for
dredging. Evidence from similar projects to support this statement should be
provided.
Response I.B-3. Preface: The data supporting the information presented on page 5.5-20
under "Halibut Nursery Loss" was reanalyzed during the preparation of
the Draft EIR, and incorporated into Table 6-1 (Alternatives), page 64
but not updated in Table 5.5.4 and the text on page 5.5-20. The text on
page 5.5-20 regarding Halibut Nursery Loss is hereby revised as follows
(please see Attachment C in Section 3 of this document for additional
references cited):
]B2/006WI t.RTC
"A permanent deepening of the subtidal halibut nursery habitat will
result from channel dredging. A total of 140,970 square feet
(3.2 acres) of halibut nursery habitat at depths between -1.5 and
-10 feet MLLW will be deepened to approximately -8 to
-10 feet MLLW. The deepening of this habitat will reduce the
available habitat are& quality, espeeially for newly settled young-of-
I-3
the -year (YOY) less than EO nun in length whieh. These individuals
• prefer depths less than 1 meter 0.21 feet . The net amount of
affected area associated with YOY habitat loss is 12,175 square feet
(0.28 acre). Juvenile and subadult halibut (greater than 50 mm in
lenzth prefer water depths between 3.2 and 10 feet MLLW
(Kramer and Hunter 1988). A total of 2.89 acres of this habitat in
the main channel will be recontoured to a maximum channel depth
of -8 to -10 feet MLLW, at —the e tPem- lower depth range
preferenee within the depth ranges for juveniles and subadults. The
-- The reduction of the shallow subtidal YOY halibut nursery habitat
(0.28 acre) is a significant local impact but is not expected to be a
significant regional impact. This impact is mitigable to below a level
of significance by the in -kind mitigation of shallow subtidal YOY
nursery habitat (depths between -3.21 and -1.5 feet MLLW) at
Shellmaker Island in Upper Newport Bay and with maintenance of
water quality and sediment quality in the Castaways Marina Basin
that provides suitable nursery area for halibut.
Habitat for larzer-Iuv_enRes and subadults in the deeper habitats in
the channel will be temporarily affected by channel dredging.
However, the depths to which the channel will be recontoured will
remain within the ranee reported for iuvenile and subadult halibut
in Upper and Lower Newport Bay (Allen 49891988 Hom and Allen
1981 Marine Bioloeical Consultants and Southern California
Coastal Water Research Project (1980). Allen (1976). and Posejpal
_ (1969) and other bays and harbors in Southern California (MBC
Applied Environmental Sciences 1984). MEC Analytical Systems
1988) Kramer (1990) Ngr- t(12S. and Ford (1986). Therefore,
no lone -term reduction or loss of juvenile and subadult halibut
habitat is expected to occur in the main channel at depths between
-3.21 and -10 feet MLLW and mitieation measures to replace this,
habitat are not required The addition (creation) of the marina
basin is a Rptentialiy beneficial impact because it increases juvenile
and subadult halibut habitat in the Upper Bay by 2.96 acres if water
_ and sediment quality are adequate to support and maintain fish
Ropulations This beneficial impact however is not intended as
mitigation measure for the loss of halibut nursery habitat.
In addition, project design alternatives which could reduce halibut
nursery impacts are discussed in Section 6.0."
In summaa
is acknowledged in the Draft EIR and provided for in the
• restoration of shallow subtidal habitat (depths -3.21 to -1.5 feet
MLLW) on Shellmaker Island, as described in the Draft Conceptual
MV00640011.RTC 1-4
•
Mitigation Plan for the Loss of Mudflat and Subtidal Habitats (EIP
Associates 1991).
Recontoured bottom depths in the main channel will still be within
halibut nursery habitat would result, no long-term impacts to
halibut populations are net expected and thus no mitigation is
r uired•
The addition of the subtidal habitat in the new marina basin is a
used as a mitigation measure for YOY halibut nursery loss.
The marina basin will potentially provide additional habitat for juvenile
and subadult %shes if water quality and sediment quality are maintained.
The use of the marina basin however, is not assumed to be as important
channel again on a frequent if not regular basis This is likely to occur
for two reasons: (1) the depths in the marina basin will be within the
nth range of iuvenile and subadult halibut that occur in the main
channels and side marina channels of both Newport Harbor and the
wetland channels of Upper Newport Bay. and (2) based upon tidal
circulation modeling performed for the Castaways project by Noble
Consultants tidal exchange is expected to be adequate to maintain
acceptable levels of dissolved oxygen needed to support marine life. A
benefit of the project location is that the marina be situated within an area
of the bay that is of relatively Food water quality and well flushed by tidal
action.
Previous studies support the hvpothesis that marina basins (and dredged
boattharbor channels and dredged wetland channels) are capable of
guppgrting California halibut when water quality and sediment quality are
maintained These studies include marina basin studies for the Sunroad
Marina Project in San Diego Bay, San Diego County (Ford 1986) and
Huntington Harbour in Orange County MC MS 1972 personal
observations) and Allen 4989 (1988).
Ford (1986) conducted marine resource surveys in the West Basin (a
developed marina basin) and East Basin (an existing site to be dredged for
a new marina) of Harbor Island in San Diego Bay. The study compared
marine habitats and biota found in the two areas, assessed the value of
habitats that would be disturbed or modified by dredging for the Sunroad
Marina Project and assessed the value of new substances and habitats
that would result from the project.
Fish sampling was conducted using beach seines, other trawls, and
minnow seines Although eelgrass was found in the West Basin. sampling
• was limited to areas of the Marina basin beneath and among the south
shore marina boat slips where eelgrass (Zostera marina) was absent.
764I00640011.RTC
I-5
Eelgrass was present within the sampling area in the East Basin Results
• of both fish and invertebrate studies "indicate very clearly that both the
East Basin and West Basin support assemblages of fish species t}pical of
central and outer San Diego Bay. Particularly important is the fact that
small and largeiuvenile fishes of nearly all species were found in both the
East and West Basins These include Yung -of -the -year juveniles of the
conditions exist in both the East and West Basins to support the
development of these ygung stages" and "All of these results suggest
very strongly that the West Basin with its large and very active marina
supports an assemblage of fishes very similar to that of the East Basin, in
terms of species composition abundance of individual specim and size
characteristics of the individuals" (Ford 1986. pp A-1 to A-13).
Huntington Harbour channels and marina basins were dredged between
channels and basins at various stages of completion A total of 41 species
the dredged marina basins and channels In 1972 water quality and
biological conditions including fish and invertebrate catches were poor in
cul-de-sac areas located on the eastern side of the harbor where circulation
was limited More recently, iuvenile halibut were observed by divers in
marina channels adjacent to the main channel. Halibut were present in
• the Sunset Aquatic Park Access Channel during 1983 and 1988• in Bolsa
Channel durine 1988 and Trinidad Cove in 1986 (personal observations:
MBC Applied Environmental Sciences 1985. 1986. and 1988). Recent
area (Allen and Herbinson 1990).
Allen (1988) conducted fish studies in the Upper Newport Bay Ecological
located above the dike Results of icthyofauna and adult fish sampling
conducted in dredged material indicated that the waters between
Shelimaker Island and the dike are halibut nursery areas. Halibut.
however, occurred as far inland as the newly created habitat near
Jamboree bridge. The distribution of halibut was correlated to the
deeper, cooler higher salinity waters of the Upper By. These
environmental conditions occur in the channel next to the proposed
Castaways marina site. and enhance the likelihood for recovery of the
dredged channel bottom.
Lastly. Allen (1976) conducted fish studies in both Newport Harbor and
U per Newport Bay. Iris findings indicated that the percent of the total
number of halibut captured was slightly greater in Newport Harbor than
Upper Newport Bay. The areas most important to halibut measured on
the basis of the Index of Relative Importance (IRA were the north and
south sides of Lido Isle, and south of Balboa Island. These areas are
JM/00640011.RTC 1-6
characterized by numerous boat moorings docks high levels of boat
traffic, and harbor related business and homes lining the waterfront.
• These studies indicate that Juvenile halibut are found in marina basins,
harbor channels and artificially deepened wetland channels in Orange
and San Diezo counties Young -of -the -year individuals are found in the
shallower habitats less than 1 meter (3.21 feet) deep. whereas juveniles
the main channel of Uoner Newport Bay and use the Castaways marina
basin habitat as well.
Comment I.B-4. Identification of the specific location of the proposed mitigation sites(s) should
be included in the final document.
Response I.B-4. A draft conceptual mitigation plan for the loss of mudflat and shallow
subtidal habitat was prepared by EIP Associates and is included
Attachment B in Section 3 of this document. Shellmaker Island is
proposed as the mitigation area. Its proposal as the mitigation site for the
project was made in consultation with, and conceptually approved by,
California Department of Msh and Game biologists and the Region 5
Manager. The project will involve the removal of dredge material from
the island, and lowering the existing contours to mudflat and shallow
subtidal elevations. The specific mitigation site is located immediately
north of an existing channel cut that bisects Shellmaker Island. Selection
of the site conforms to the goals of the Department's Management Plan
• for the Upper Newport Bay Ecological Reserve to improve the fishery
resources of the reserve by increasing nursery, foraging, and spawning
grounds. There will be no net loss of sensitive wetland habitat as a result
of this mitigation project.
Comment I.B-5. ire 5.5-23. The proposed monitoring program should include sampling in
the marina basin to ensure that the new habitat created in this area is in fact
utilized by California halibut. If habitat equivalency between the new marina
basin habitat and the former channel habitat does not exit by the end of the
monitoring program (i.e., after five years) then additional mitigation should
be proposed.
Response I.B-5. As discussed in the response to comment I.B-39 the new marina is not
proposed to be used as mitigation for loss of shallow subtidal halibut
habitat and there is no net loss of juvenile and subadult halibut habitat in
the main charnel. Therefore, sampling in the marina or the dredged
habitat in the main channel is not required.
JB2100640011.RTC
The draft conceptual mitigation plan currently identifies a mitigation
monitoring program that will involve sampling young -of -the -year and
older age class halibut populations prior to and following habitat
restoration at Shellmaker Island and comparing the results over a 5-year
period with sampling conducted at another location in the bay that has
been identified as a halibut nursery area. The selection of this site will be
made with the assistance of the California Department of Fish and Game,
National Marine F7sheries Service, and U.S. Fish and Wildlife Service.
I-7
One option would be to locate a station in the main channel in the vicinity
. of the proposed marina. Another would he to locate the sampling station
nearer to the Shellmaker Island mitigation site. If habitat equivalency
between the two sites cannot he demonstrated after 5 years of monitoring,
additional mitigation measures will be proposed.
1]
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JBV0064001 LRTC 1-8
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H.A. GOVERNOR'S OFFICE OF PLANNING AND RESEARCH (October 79 1991)
Comment MA-1. The State Clearinghouse submitted the above named environmental document
to selected state agencies for review. The review period is closed and none
of the state agencies have comments. This letter acknowledges that you have
complied with the State Clearinghouse review requirements for draft
anvtrnnmentn1 dncumentq_ pursuant to the California Environmental Oualitv
H.B. STATE LANDS COMMSSION (October 3, 1991)
• Comment II.B-1. There appears to be a general lack of significance criteria. Without these
criteria the document resorts to conclusionary statements of impacts which are
unsupported by evidence in the record. Furthermore, without significance
criteria there is no way to measure the effectiveness of the proposed mitigation
measures and the residual impacts.
Response U.B-1. Although significance criteria are not formally delineated in the Draft
MR, the impact analysis discussion for each issue includes explanations as
to why identified impacts are considered significant or not significant.
Therefore, the significance criteria for each issue evaluated are implicit in
the impact analyses.
Comment II.B-2. The project description should include a clear discussion of liveaboards, public
access, waste disposal and drainage provisions. It should also show past,
present, and future (proposed project) bulkhead and pierlines. The impacts of
any channel width reduction must then be analyzed for impacts to access and
navigation.
Response II.B-2. See response to Comment IV.A-14 regarding liveaboards, public access,
_ waste disposal, and drainage. Bulkhead and pierhead lines are shown on
Exhibit 3-3 of the Draft EEL Exhibit 3 3 also shows that the proposed
pier would not reduce the width of the main and alternate navigation
channels (each of which is 100 feet wide). The established lines are
PJ
considered acceptable by the City of Newport Beach and County of
Orange.
Comment II.B-3. We appreciate the fact that the no -project alternative is being considered by the
City of Newport Beach. However, the EIR should, pursuant to CEQA
Guidelines Section 15126(d)2, identify which of the remaining project
alternatives is environmentally superior.
Response H.B-3. 121-boat-slips alternative - As stated in the first paragraph on page 6-5 of
the Draft EIR, this alternative would be environmentally superior to the
proposed project, and would be economically feasible according to the
project applicant.
84-boat-slipN alternative - As stated in the third paragraph on page 6-6 of
the Draft EIR, this alternative would be considered environmentally
superior to the proposed project; however, it is not economically feasible
according to the project applicant.
50-boat-slips alternative - As stated in the last paragraph on page 6-7 of
the Draft EM, this alternative is considered environmentally superior to
the proposed project; however, it is not economically feasible according to
the project applicant.
]B2100640011.RTC II-2
Alternative project site location - As stated in the last paragraph on page
• 6-8 of the Draft EIR, no site -spec comparison of an alternative project
site within Orange County to the proposed project site is possible due to
the unavailability of feasible site alternatives.
Alternative haul road/lone-term site access design - As stated in the
paragraph on page 6-11 of the Draft EIR, this alternative haul
route/access design is considered environmentally superior to the proposed
temporary haul road and access design.
Comment II.B-4. The DEIR does not include a mitigation plan for the loss of 0.69 acres of
mudflat or for the loss of 0.28 acres of habitat for "young -of -the -year" halibut.
It is, therefore, not possible to determine if mitigation is feasible. The loss of
mudflat and nursery area must be considered a significant adverse impact until
y such time as the mitigation plan is approved by the appropriate agencies. The
mitigation plan must include both monitoring and the remediation measures to
be taken if restoration is not successful.
0
Response II.B-4. The Draft EEk concludes that loss of mudflat and halibut nursery habitats
would represent a significant adverse effect until the mitigation program
is successfully implemented (see page 5.5-19, 5.15-20, and 5.5-22 of the
Draft EIR). If the mitigation program were unsuccessful, the impact
would remain significant. Pages 5.5-22 and 5.5-23 of the Draft EIR
identify basic elements of the mitigation plan to offset impacts to mudflat
and subtidal halibut habitats. A draft of the conceptual mitigation plan
is provided as Attachment B in Section 3 of this document, and includes
further detail on remediation measures and monitoring requirements
which are subject to further modification by California Department of
Fish and Game, U.S. Fish and Wildlife Service, and National Marine
Fisheries Service, and approval by the U.S. Army Corps of Engineers
during the federal permits process. Since these agencies have purview
over the mitigation plan, and since the successful implementation of the
plan is to be monitored over a number of years, the Draft EIR is revised
as follows:
Page 5.5-20, new sentence at end of second paragraph:
"Due to the sensitivity of this habitat, the loss of mudflat is
considered significant until the mitigation plan can be approved by
the responsible agencies."
Page 5.5-20, new sentence at end of last paragraph:
"Due to the sensitivity of this habitat, the loss of halibut nursery is
considered significant until the mitigation plan can be aooroved by
the responsible agencies."
JB21006WI l.RTC II-3
Page 5.5 24, new sentence at end of first full paragraph; page 8-1, new
sentence at the end of fifth paragraph:
"Due to the sensitivity of the mudflat and halibut habitats, the loss
of these resources is considered significant until the mitigation
plan(s) can be aooroved by the responsible agencies."
Page 1-24, third column, second item; and page 1-25 third column, first
item are hereby revised as follows:
Not Potentially significant. a€tef mitigation
Comment H.B-5. The enforcement of current regulations does not constitute a mitigation under
CEQA. How is this cumulatively significant impact going to be reduced?
Response U.B-5. The cumulatively poor water quality conditions of Newport Bay are
primarily a result of urban and agricultural stormwater runoff, and illegal
and accidental discharges of contaminants. The project applicant would
reduce the incremental water quality effects associated with the project by
regularly maintaining its marina facility, including the sewage pumpout
station, and by notifying its tenants regarding the laws and regulations
regarding vessel discharges of wastes, antifouling paint use, and refuse
management as part of its lease terms. Cumulative water quality
problems are controlled by the local agencies through the enforcement of
such laws and regulations, and through the issuance of NPDES permits for
point sources by the Santa Ana Regional Water Quality Control Board
and, more recently, stormwater runoff, by local municipalities.
Comment II.13-6. The estimate of annual sediment delivery is critical for both the economic
viability and the environmental impact of this project. How does the estimated
rate of 0.1 foot per year and the 5-year interval for maintenance dredging
compare to the rates in nearby marinas? What is the basis for assuring that
80 percent of fluvial sediment is retained in upper Newport Bay. Does the
estimated sedimentation rate take into account that sediment will not pass by
the marina once, but will recycle to some degree with the ebb and flow of the
tide?
Response U.B-6. The rates of sedimentation and maintenance dredging requirements at
marinas near the project site are expected to be different than the rate at
the project site due to the different conditions at each site. The Newport
Dunes Marina was recently dredged in conjunction with modification of
the marina. Prior this dredging, it had been approximately six years since
the marina had been dredged (E. Power, California Recreation Company,
pers. comm., 11/7/91).
The rate and characteristics of the sedimentation are based on studies
which were prepared as part of the San Diego Creek sedimentation
monitoring program (County of Orange 1988; and Boyle Engineering
Corporation, 1982). The sedimentation rate assumes that most of the
material that will be deposited beyond the project site will not be
resuspended and be "recycled" passed the project site.
JWJ00640011.RTC H 4
Comment 11.13-7. Total threshold limit concentrations (MC) for hazardous wastes are used to
determine the potential for impacts to human health. Water quality criteria for
the protection of aquatic organisms are orders of magnitude lower than the
TILC. The TTLC cannot be used to predict effects of dredging or disposal
_ on aquatic organisms. The results of the sea urchin sperm tests and the tests
using the marine worm (Nephtys caecoides) as well as the results of the
bioaccumulation tests suggest the dredged sediment may not be suitable for
ocean disposal.
Response H.B-7. The first three statements of the comment are correct. However, this
review comment is inappropriate because the statement made in the EIR
did not compare TTLC and predicted effects. Rather the statement made
in the EIR was that the trace metals present in the project area sediments
were substantially below TTLC values. This statement is correct. The
fact that the reviewer put the TTLC together with a prediction of toxicity
to aquatic organisms is inappropriate. See further discussion in responses
to Comments H.B-9, H.B-11, and HX 4.
Comment II.B-8. What methods would be used to treat the discharged water if it does not meet
U.S. Environmental Protection Agency (EPA) standards? What will be done
if the water cannot be sufficiently treated to meet the standards?
Response H.B-8. Water quality studies were conducted by MEC Analytical Systems, Inc.
during the spring of 1990 in the main channel near the proposed
Castaways Marina project site. The tests conducted utilized standardized
methodology approved by the EPA and the Army Corps of Engineers.
The purpose of the testing was to determine the suitability of project
dredged spoils for ocean disposal at the EPA LA-3 dredge disposal site
offshore from Newport Harbor. Please see section 5.4 and Appendix F of
the DEIR for a detailed analysis of the results of this study. The findings
of the study indicated that the level of contaminants in the project area
sediments are below the applicable standards for hazardous wastes. Thus,
it is anticipated that the discharged water from dewatering of dredged
material would meet all applicable standards. However, one potential
problem could be the turbidity of the discharge water. Treatment for
turbidity involves running the discharge into a desilting basin to allow the
suspended sediment to settle out. In the event that the discharge does not
meet EPA standards for toxic contaminants, the type of treatment would
be dependent upon the contaminant which exceeds the standards. For
example, one form of treatment would involve running the discharge
through carbon filters (M. Adacakapara, Regional Water Quality Control
Board —Santa Ana Region, pers. comm., 11/7/91). In the majority of
cases, the discharged water can be treated to meet all applicable
standards.
Comment II.13-9. As noted above, the available data does not support the conclusion that
disposal of sediments from the project has a low potential to degrade water
quality and/or water quality at the disposal site.
Response H.B-9. Data are presented in Appendix F of the Draft EIR, including both
elutriate toxicity test results and sediment bioassay results, which support
the conclusion in the Draft EIR.
J32/00640011ATC 11-5
The conclusion was based on the interpretation of the data by
• professionals in the field, and does not represent the regulatory agency's
final conclusion. The U.S. EPA and Army Corps of Engineers will make
the final decision on significance.
Comment II.13-10. Woody debris from construction should be picked up, not allowed to float out
in the harbor.
Response ILB-10. Please see Mitigation Measure No. 5.45 on page 5.416 of the Draft EIR.
Comment II.B-11. The levels of toxicants must be compared to EPA water quality criteria for the
protection of saltwater organisms, not TTLC.
Response H.B-11. The results of the bioassays indicated some minor acute toxicity in the sea
urchin bioassay, and solid phase toxicity in the mysid bioassay at one site
and the polychaete bioassay at one site. The liquid phase bioassay results
are compared to a limited permissible concentration as stated on page 5.4-
7 of the Draft EIR and were found to not exceed the LPC and were
therefore suitable for disposal.
Solid phase toxicity was observed in the mysid and polychaetes at one site.
The interpretation of these results in the bioassay were based upon
professional experience and not on regulatory interpretation. The
significance of these results are determined by the U.S. EPA and the U.S.
Corps of Engineers and is placed in a regulatory response. To date, the
agency's response has not been finalized.
Comment II.B-12. How will maintenance dredging affect the quality of habitat for juvenile
halibut?
Response H.B-12. Maintenance dredging is expected to occur approximately every five years
(see Section 5.3 of Draft EIR). During these short-term episodes, the
quality of the halibut habitat in the immediate vicinity of dredging will be
degraded. juvenile halibut will move away from the immediate area until
the operations are completed if turbidity, noise, and vibration from the
operation of the dredge equipment is intolerable. Dredging, however,
could also expose potential •benthic invertebrate prey items (such as
amphipods, ostracods, polychaetes, gastropods, pelecypods, and ghost
shrimp) and gobies that might attract bottom=foraging juvenile halibut and
other bottom foragers to the dredge area. In the long term, maintenance
dredging is likely to keep sediment loads of organics and potential
contaminants to a minimum. Clean, coarser sediments will be exposed
every five years. This will help maintain the quality of the juvenile
habitat in the long term.
JWJ006"11.RTC
If the commentor is referring to initial dredging required to attain channel
depths, young -of -the -year halibut habitat (the shallow shoreline habitat)
less than 1 meter (3.21 feet) will be deepened and replaced with habitat
more commonly preferred by older juveniles and subadults. This
reference to habitat "quality" should be more clearly referenced as habitat
"loss" (0.28 acre).
1 r.
Comment ]LB-13. If Southern tarplant is located on the site, it should be protected if at all
possible.
• Response ILB-13. Comment is noted; most recent site surveys found no southern tarplant on
either the upper or lower parts of the Castaways site.
Comment II.B-14. In Mitigation Measure 5.6-2 - change "should" to "shall."
Response II.B-14. Comment is noted. Mitigation Measure No. 5.6-2 is hereby revised to
read:
n
•
"Dredging and construction activity should will be terminated
between April 1 and September 30, the breeding season of
California least terns, to minimize adverse impacts on their foraging
habitat due to increased turbidity."
JB2100640011ATC 11-7
H.C. CALIFORNIA DEPARTMENT OF TRANSPORTATION (CALTRANS),
• DISTRICT 12 (October 8, 1991)
Comment II.C-1. Due to recent widening projects on Pacific Coast Highway (PCH), Caltrans
is concerned with any project which has the potential to adversely impact a
State Facility or worsen local and regional traffic/circulation. It is necessary
to reduce the traffic impact of the proposed project during construction and
after construction on PCH to a level of no significance. Ibis can be achieved
by implementing mitigation measures that would counterbalance the adverse
traffic impacts of this project.
Response H.C-1. The comment is noted; no response is required.
Comment II.C-2. Caltrans favors the Alternative 1.3.5 on page 1-8 from a safety stand point.
The benefits that would be achieved in using this alternative are more
substantial than the other Alternatives presented.
Response H.C-2. The comment is noted; no response is required
Comment II.C-3. In addition, an Encroachment Permit is required for any work within Caltrans
Right of Way. Consideration should be given to release of the surface runoff
from the project directly towards the existing channel without reaching State
Right of Way. The proposed project will have a negative impact on the
Pacific Coast Highway Bridge mitigation measures. Offsets to these impacts
should be addressed in the Final Document.
• Response ILC-3. The proposed project would not be located within Ca►traw right-of-way.
Therefore, no encroachment permits are required. While the proposed
project is located upstream of Coast Highway, the project would not direct
water flow onto Coast Highway during storms. The project would have
a minimal amount of impervious surfaces and would utilize an existing 33-
inch storm drain which discharges into Newport Bay under the Coast
Highway Bridge.
•
As shown in Table 5.8-1 of the Draft EIR, the proposed project is
projected to generate a total of 13 vehicle trips during the AM peak 2.5
hour period, and 20 trips during the PM peak 2.5 hour period. The ADT
for the project is estimated to be 183. The trip distribution for the project
along the Coast Highway Bridge is anticipated to be 25 percent of the total
trips generated by the project (please see Exhibit 5.8-1 in the Draft EIR).
Thus, during the AM peak 2.5 hour period the project would generate a
total of 3 trips along the bridge. During the PM peak 2.5 hour period, a
total of five trips would be generated along the bridge. Due to the
relatively small number of trips generated by the project, and the minimal
amount of project -generated trips on the Coast Highway Bridge, no
significant adverse impacts are anticipated. Thus, no mitigation measures,
other than those needed during the construction period, are required to
handle project -related traffic.
JB2/00640011.RTC 11-8
H.D. CAIHORNIA DEPARTMENT OF FISH AND GAME (October 15, 1991)
40 Comment II.D-1. The proposed project will result in a loss of 0.28 acre of what has been
identified as "halibut young -of -year nursery habitat" (shallow subtidal habitat
between -1.5 to -3.2 feet mean lower low water RdLLW] and 0.69 acre of
mudflat habitat between -1.5 to +2.5 feet MLLW. These habitat losses have
been identified as significant and mitigation for their losses would be required.
The applicant has indicated that mitigation will be provided at a 1.5 to 1 ratio.
However, no specific mitigation proposal, including monitoring, has been
prepared and included in the EIR. The applicant has initiated discussions with
the Department and other resources agencies regarding potential mitigation
sites within Upper Newport Bay, however; no site -specific plan has been
developed.
Response H.D-1. A more detailed mitigation plan has been prepared and is included in
Attachment B of Section 3 of the document. Copies of this document have
also been distributed to the responsible local, state, and federal agencies
for their review.
Comment II.D-2. An area of concern, which has not been addressed in the Draft EIR, is the
potential exclusion of sport fishermen from existing shoreline areas within the
project area. This issue should be addressed in the Final EIR.
Response H.D-2. The proposed project would not preclude fishing along the shoreline north
of the new marina basin (below the bluffs of the Upper Castaways site).
. Pedestrian access to this shoreline would be available via steps from the
new parking lot down to the shore immediately north of the basin. Also,
boats could also access this part of the shoreline by maneuvering behind
the proposed pier structure.
Comment II.D-3. The 121 boat marina would reduce loss of mudflat from 0.69 acre to 0.34
acre, and halibut young -of -year habitat from 0.28 acre to 0.21 acre. In
addition, there would be a reduction in the gain of halibut juvenile habitat
from 2.96 acres to 2.50 acres. The project has been altered to include the
realignment of bayside boat docks and elimination of four boat slips of side
ties, reduction of dredging within Newport Bay, and the construction of rock
slopes (breakwaters) at the upper and lower boundary of the boat basin. This
alternative has been identified as the environmentally superior alternative,
however; we would recommend a further reduction of in bay dredging to
reduce impacts to mudflats by the elimination of boat slips from that portion
of the marina in the area of existing mudflats.
Response H.D-3. The comment is noted. Removal of the pier structure would somewhat
reduce mudflat impacts. However, as noted in response to comment I.B-
1, most of the mudflat habitat loss is associated with the creation of the
marina basin. Therefore, any alternative which would include a marina
basin such as the one proposed would have a similar effect on the mudflat
habitat in the study area. It should also be noted that the applicant does
not consider the alternatives with the smaller number of boats as
• economically viable due to the estimated costs associated with developing
and maintaining the new marina.
JB2I00640011.RTC II-9
H.E. CALWORNIA REGIONAL WATER QUALITY CONTROL BOARD, SANTA ANA
• REGION (OCTOBER 24, 1991)
Comment ME-1 The proposed marina, including the parking lot and structures, will increase
the impervious surfaces and the amount of surface runoff. In accordance with
the new stormwater regulations published by the EPA in the Federal Register
(40 CFR Parts 122, 123, and 124), stormwater discharges from the facility
must comply with the NPDES permit requirements. The DEIR has recognized
these regulations, and we urge you to work closely with the City of Newport
Beach and the Orange County Environmental Management Agency to
m4geninimize the impact on water quality due to the increased stormwater
runoff from the project site.
Response ILE-1 The comment is noted; no response is required
Comment II.E-2 The DEIR has identified the potential increase in the turbidity and suspended
sediments from dredging and excavation activities associated with the project.
A permit will be required from this Regional Board for dredging activities.
The permit will incorporate requirements for the protection of the beneficial
uses in accordance with the Basin Plan, the California Enclosed Bays and
Estuaries Plan (EBEP), and other State and Federal regulations.
Response ILE-2 The comment i noted; no response is required.
. Comment II.E-3 The discharge of any dewatering wastes will also require a permit from this
Regional Board. Again, the discharge of wastes to Newport Bay shall be in
accordance with the EBEP and other applicable regulations.
Response ILE-3 The comment is noted; no response is required.
Comment II.E-4 The toxicity tests with sediments from one of the test sites indicated acute
toxicity (page 5.4-7). The DEIR also states that significant bioaccumulation
of chemical constituents was found for both the marine worm and clam at all
three test sites (page 5.4.9). It does not appear that these findings have been
fully addressed in the DEIR.
Response HXA The results of the bioassays were addressed in the Draft EIR. The acute
toxicity to sea urchins was described and appropriately discounted using
the least permissible concentration (LPC) analysis (see page 5.4-7 of the
Draft EIR). The solid phase and bioaccumulation results are also
discussed on page 5.4-7. The results of the toxicity studies do not appear
to be significant based upon professional experience. however, regulatory
review of these results may interpret them differently. The significance
of the bioaccumulation analysis is often subjectively interpreted and the
statements made in the bioassay report (see Appendix F of the Draft EIR)
are based upon professional judgment and are not regulatory
interpretations.
Comment II.E-5 We note that specific facilities and policies to address the potential for illegal
• vessel discharges are proposed by the project applicant. We commend the
applicant for these proposals, which are described on page 5.4-13. These
JBV00640011.RTC II-10
i
include installation and routine maintenance of a vessel sewage pumpout
station and certain conditions for use of the marina to be included in lease
Isagreements (prohibition of waste discharges; requirement for holding tanks,
etc.). We suggest that these proposals be added to the list of mitigation
measures specified on pages 5.4-15 and -16 of the DEIR.
Response H.E-5 The EIR hereby incorporates the following additional mitigation measure:
115.4-12 For the life of the project the project applicant shall include in
•
•
holding_tanks desiened to retain all contents until they can be
Comment I1.E-6 We commend the applicants' proposal to specifically prohibit painting,
scraping and other boat maintenance activities at the marina and to provide
routine compliance oversight. Again, we suggest that these measures be added
to the list of mitigation measures on pages 5.4-15 and -16.
Response 11.E-6 Please see the response to comment II.E-5.
JBV00640011.RTC 11-11
M. COUNTY OF ORANGE
• Environmental Management Agency (October 99 1991)
Comment M.A-1. The Master Plan of Countywide Bikeways (MPCB) identifies Route 55, a
Class I (paved, off -road) trail in the project vicinity. The EIR should address
subject trail and linkage with Route 25, a Class I trail along Pacific Coast
Highway.
Response MA-1. The Master Plan of Countywide Bikeways identifies Route 55 for future
construction as a -Class I bike trail (paved, off -road) that would run along
the western border of Upper Newport Bay (across Upper Castaways and
a portion of Lower Castaways). Route 55 is slated to connect at Coast
Highway with Route 25, another Class I bike trail along Coast Highway.
County officials indicate that the County is willing to work with the
project applicant to reroute the Route 55 bike trail around the perimeter
of the proposed project (Sherri Miller, County of Orange Environmental
Management Agency, pers. comm.10/29/91).. Route 25 on Coast Highway
would not be impacted by the proposed project.
Comment III.A-2. The proposed project will create a positive increase in regional recreational
opportunities within Orange County by providing new boat slips in Newport
Beach and public access to coastal areas through the construction of a public
viewing area.
• Response III.A 2. The comment is noted; no response is required.
7B2100640011.RTC 111-1
•
M.B. CITY OF COSTA MESA, TRANSPORTATION SERVICES MANAGER
(October 10, 1991)
Comment III.B-1. The City of Costa Mesa has no comments regarding the traffic/circulation
impacts of the Castaways Marina project.
Response M.11-1. Comment so noted; no response is required.
JB2100640011.RTC III-2
s
IV, TERRELL WATT, AICP (October 3, 1991)
• Comment IV.A-1. At the foundation of an adequate analysis of environmental impacts is a
thorough description of the environmental setting. In this case, an crucial
piece of setting information has been omitted from the DEIR; the extent of
public trust lands and the permissible uses under the grant of these lands and
resources -to the County of Orange. This information is relevant for a number
of reasons:
1. While the lands may have been granted to the County of Orange, such
granted lands are monitored by the State Lands Commission to ensure
compliance with the terms of the grant. The land grant may be highly
restrictive of the permissible uses, and the extent of those uses, and of
the lands and resources. Absent this information, it is not possible to
determine whether the use proposed is consistent with the public trust
restrictions governing those lands and resources.
2. Where competing public trust uses are under consideration (e.g., a
marina vs. fishing and shoreline recreation), the least environmentally
damaging alternative should be approved. No public trust use should
be approved which precludes an existing public trust use, such as
fishing or habitat. Without adequate setting information, this choice
cannot be properly made.
• 3. Finally, the DEIR should contain a map which shows the extent of the
public trust lands and the upland area affected by development of those
lands. All existing public trust uses should be described.
Response 1V.A-1. 1. Pursuant to the 1975 amendment to the original 1919 tidelands
grant to the County of Orange which included the project area
(Section 1 of Chapter 415, Statutes of 1975), the portion of the
project area within the tidelands grant can be utilized "for the
establishment, improvement and conduct of a public harbor, and for
the construction, maintenance and operation thereon of wharves,
docks, piers, slips, quays, ways and streets, and other utilities,
structures and appliances necessary or convenient for the promotion
or accommodation of commerce and navigation ...". Therefore, the
proposed marina development is consistent with the permissible uses
in the tidelands grant.
2. The public tidelands grant does not include any direction to the
effect that the least environmentally damaging alternative must be
approved, or that no public trust use should be approved which
precludes an existing public trust use.
3. A map of the area within the tidelands grant is available from the
City of Newport Beach, Marina Department, Tidelands
Administrator.
• Comment IV.A-2. The State Lands Commission, a trustee agency, was missing from the list of
agencies contacted during the preparation of the DEIR. This agency should
1B2/00640011.RTC IV-1
be contacted immediately and included in the dialogue about the appropriate
• uses for the property consistent with the public trust. Also, the grant to
Orange County should be described in the DEIR and the complete grant
included in the DEIR appendix.
Response IV.A 2. The Draft M was sent to the State Lands Commission for review during
the public review period for the document, and the Commission submitted
a comment letter (see Comment Letter II.B.).
As discussed in Response MA-1 above, the tidelands grant to Orange
County which includes the project area, specified pier construction as a
permissible use in the project area.
The original tidelands grant of 1919, and all subsequent amendments, are
part of the public record and can be accessed by interested parties. These
documents are not included in the appendix to the Draft EIR.
Comment IV.A-3. Absent this information, the City cannot make a determination of what are the
uses permitted on the property. Even if a marina use is permitted, if the
impacts of that use on other public trust resources or uses would be
significant, the marina use should be scaled back so impacts will be
insignificant or the project denied.
Response MA-3. Although potentially significant cumulative impacts to water quality,
marine biological resources, and air quality are identified, all project -
specific impacts can be mitigated to below a level of significance.
Comment IV.A-4. What is the justification for a DEIR rather than a joint EIRMIS? The DEIR
identifies significant impacts of the project that are related to the actions
required of a number of federal agencies. For this reason SPON believes that
the document should be a joint MIMS.
Response IV.A4. While the proposed marina development does require permits from the
U.S. Coast Guard, U.S. Army Corps of Engineers, and the U.S.
Environmental Protection Agency (see Section 3.5 in the Draft EIR); the
project does not involve federal funds or development on federal property;
therefore, an EIS is not required.
Comment IV.A-5 If no EIS is being prepared, what environmental review process will be
completed for the federal permits and what is the timing of that process?
Response MA-5. Upon certification of the EIR, it will be utilized by all responsible agencies
as supporting information for permit decisions. Each federal permit
required for the project has an established review process. It is the intent
of the applicant to apply for all federal permits upon certification of the
EIR. These permits must be approved prior to Coastal Commission
approval or the receipt of any grading or building permits from the City
of Newport Beach.
Comment IV.A-6. If a "Finding of No Significant Impacts" (FONSI) is being prepared for the
• Federal actions, what is the rationale for this given the significant impacts
identified in the DEIR?
J=00640011.RTC IV-2
Response IV.A-6. As discussed in Response IV.A4, a federal environmental document is not
41 required for this project; therefore, no FONSI will be prepared.
Comment IV.A-7. The impact analysis does not provide adequate information from which
decision makers may choose between the proposed project alternatives.
Specifically, the DEIR does not analyze the ability of the Upper Newport
Bay/Newport Bay to accommodate additional marina development without
significant negative impact on human, ecological or water quality benefits
associated with the Bay; or in other words, is the Bay's carrying capacity
adequate for this type and intensity of use?
Response IV.A 7. The Draft EIR acknowledges that the proposed marina development would
represent an increase in boats in Newport Bay of approximately
1.5 percent. It is acknowledged in the Draft EIR, that the new marina
would add incrementally to water quality problems in the bay which are
considered cumulatively significant and not altogether avoidable, and that
it would have adverse biological impacts which could be mitigated with an
appropriate mitigation program which is under the purview of state and
federal resource agencies. The need for a "carrying capacity" study for
Newport Bay was not considered appropriate given the relatively small size
of the proposed marina and because this marina would most likely
represent the last new marina development in Upper Newport Bay.
Comment IV.A-8. While the discussion of water quality is a good start, the discussion lacks
adequate information to establish whether or not (1) the Bay (Upper and
Lower) is already at capacity for this type of use and (2) this use would exceed
the Bay's carrying capacity. Attached is a Carrying Capacity Analysis
completed for the Sacramento River Marina by the State Lands Commission.
SPON submits this study into the record as an example of the type of analysis
required for the DEIR to be considered adequate.
Response IV.A-8. The analysis in the Draft EIR is considered adequate to identify existing
and potential water quality concerns associated with the proposed marina.
The Draft EIR acknowledges that significant cumulative water quality
problems occur in parts of Newport Bay, and that the proposed marina
would contribute incrementally to these problems. Therefore, a need for
a carrying capacity analysis is not considered necessary for this project.
Comment IV.A-9. In addition, the conclusions reached in the DEIR that virtually all rp_oject_
related impacts are insignificant or reduced to a level of insignificance after
mitigation are not supported by evidence in the record. Specifically, how are
the water quality and biological impacts found to be less than significant? For
example, loss of any mudflat habitat, even if replaced, is significant. In this
case, the efficacy of the mitigation measure is completely unknown since the
"replacement plan" has not yet been developed and there is no known site that
will suffice for "replacing" or creating new habitat of this kind.
Response IV.A-9. Cumulative water quality impacts are not found to be "insignificant" in
the Draft EIR (see page 5.4-17 of the Draft EIR). Also see response to
Comment II.B-4.
IBV00640011.RTC IV-3
r�
U
In consultation with the California Department of Fish and Game, a site
on Shellmaker Island in Upper Newport Bay has been identified as a
possible mitigation site. See Attachment B in Section 3 of this document
for the conceptual mitigation plan for mudflat loss.
Comment IV.A-10. The lands proposed for this development belong to the public. As such,
SPON believes that if the project will result in significant effects or contribute
to cumulatively significant effects, the project as proposed should be denied.
Response 1V.A-10. The land portion of the project site proposed for the marina development
is in private ownership (The Irvine Company). The water portion of the
project site is administered by the County as part of the public trust. The
County would lease the area to The Irvine Company for the purpose of
developing a marina on the site.
Comment MA-11. This property is part of the public trust. As such, other public trust uses
should be evaluated for the area. Such uses could include other types of
public recreational uses including fishing and swimming. SPON believes that
the alternative use of a swimming and fishing beach with associated support
facilities upland should be evaluated for comparative impacts to the proposed
project. Such a use would not require dredging and other disturbance
associated with the project.
Response IV.A 11. Development of a marina on the project site is a permissible public trust
use under the tidelands grant of the area to the County.
Comment IV.A-12. The analysis of the alternatives is cursory and should be expanded pursuant to
the carrying capacity analysis called for above. In addition, SPON could find
no evidence in the record to support the applicant's contention that the
alternative marina's with fewer boat slips were infeasible. In the absence of
financial information which demonstrates such reduced projects are in fact
infeasible, CEQA provides that the environmentally superior project that meets
most project objectives must be adopted. This is inherent in the action -forcing
provisions of CEQA. SPON looks forward to reviewing the applicant's data
related to project feasibility.
Response IV.A 12. See responses to Comment IV.A-7 and MA-8 regarding carrying capacity
study.
An analysis of the economic feasibility of the project alternatives is on rile
at the City of Newport Beach Planning Department. The analysis
evaluated, among other parameters, the estimated costs of developing and
maintaining the new marina, potential revenues from slip rental fees, and
the estimated residual value of the property. It demonstrates that the 121-
boat alternative would result in a rate of investment return of
approximately 12 percent in 10 years, the 84-boat alternative would result
in a 3.6 percent rate of return, and the 50•boat alternative would result
in a negative rate of return. Thus, a 121-boat alternative would represent
a reasonable, although relatively small, rate of return, and the smaller
alternatives represent unacceptable economic returns.
IB2i00640011.RTC IV-4
Comment IV.A-13. The analysis of off -site alternatives is inadequate. It is not sufficient to
provide bare conclusions about the suitability of alternative sites. In the
absence of even a map of these sites, the public cannot review the sufficiency
of the statements at page 1-8 regarding the alternative sites. The DEIR must
include comparative information about the specific sites purportedly analyzed
so that the public can review this information. In light of the significant
effects of the project and the severity of this deficiency, the DEIR should be
recirculated once the information has been provided.
Response IV.A-13. Page 1-8 of the Draft EIR is a part of the summary section. Section 6.3
on page 6-8 of the Draft EIR presents the more complete analysis, and
Exhibit 6-6 presents a map showing the locations of the alternative sites
considered in the analysis.
Comment IV.A-14. Absent from the project description are the following items:
1. The number of liveaboards or the deed restriction that will preclude
such use; (note: liveaboards may not be a permissible use)
2. Provisions for public access to the area;
3. Provisions for recycling;
4. Provisions for waste disposal;
5. Details of the drainage plan;
SPON assumes that each of these aspects of the project will require
environmental analysis at some point in the future if not presented in the DEIR
at this time.
Response IV.A-14. 1. Live-aboards (defined as people staying aboard a vessel at its birth
for a period in excess of 48 hours) are not permitted under the
California Recreation Company's Vessel Mooring Agreement.
2. As shown in Exhibit 3-3 in the Draft E1R, public access to the
proposed project would be via the proposed entrance to the parldng
lot. A public viewing area is provided at the northeast corner of the
proposed parking lot. In addition, access to the shoreline north of
the project would be provided via steps from the northeast corner
of the parking lot.
3. The City of Newport Beach has developed a series of goals and
objectives designed to meet the mandate of the Integrated Waste
Management Act of 1989. The overall goal is to provide an
integrated management system that emphasizes source reduction,
recycling, and disposal of remaining waste such that the potential
adverse impacts to the environment and public health are minimized
(City of Newport Beach, Source Reduction and Recycling Element
1991). The City of Newport Beach has plans to require new
projects to provide containers for the separation of recyclable
JBV00640011.RTC IV-5
0
material onsite. Therefore, the Castaways project may be required
to provide such facilities prior to approval of the building permits.
4. Trash containers will be located at opposing ends of the proposed
project near the bathroom and shower buildings. The receptacles
are accessible from both the sidewalk and parking lots. Solid waste
generated by the project would be hauled by private refuse haulers
to the County of Orange Bee Canyon Landfill.
5. A detailed master plan of drainage must be developed for, and
approved by, the City of Newport Beach, prior to the issuance of a
grading permit. The master plan of drainage will be based on a
detailed hydrology study prepared specifically for the Castaways
Marina project, and will result in a drainage system which can
handle storm flows as indicated in the hydrology study.
Comment IV.A-15. The study area for the cumulative impact analysis is inadequate and therefore
the list of cumulative projects fails to include projects that are likely to
contribute to cumulative impacts. This in turn resulted in an inadequate
discussion of cumulative impacts with respect to water quality, among other
impacts.
Response MA-15. As stated in Section 5.4.5 on page 5.4-16 of the DEIR, the cumulative
impacts study area for water quality is the entire Newport Bay Watershed.
By definition, this study area takes into account all projects and activities
that contribute to the water quality of the bay. A watershed is a kind of
catchment basin. It is an area bounded peripherally by a water parting
feature which provides drainage into a body of water or watercourse. All
potential and actual contributors to the water quality of the bay are
_ located within this watershed. Therefore,the study area is adequate for
the analysis of cumulative water quality impacts.
0
Comment IV.A-16. Specifically, the project study area appears to include only those projects
directly adjacent to the Bay in Newport Beach. Projects outside of Newport
generate runoff into the Bay. Such projects include but are not limited to the
San Joaquin Hills Transportation Corridor, projects in Irvine and Santa Ana
within the watershed of the Bay. Runoff from development in these areas will
also contribute to the degradation of water quality in the Bay and must be
considered in the cumulative analysis.
Response IV.A 16. Although not specifically identified, the Draft EIR acknowledges that
cumulative water quality impacts are a result of urban and agricultural
runoff throughout the Newport Bay watershed. This would include
projects such as the San Joaquin Hills Transportation Corridor, and other
development projects in the watershed (see page 5.4.16 of the Draft EIR).
Comment IV.A-17. The DER should be revised to include a study area for water quality impacts
that includes the area of runoff into the Bay at a minimum. The cumulative
analysis should be based on this study area.
IBV00640011.RTC
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Response MA-17. The Draft EIR recognizes the cumulative study area is the entire Newport
Bay watershed (see Section 5.4.5 on page 5.4-16 of the Draft EIR). Please
see the response to comment MA-15.
Comment IV.A-18. A number of key mitigation measures, relied on to reduce significant impacts
to a level of insignificance are not true mitigation measures, but simply future
plans or studies. These include the following:
1. A detailed conceptual mitigation plan for the loss of the .69 acres of
mudflat habitat. (It is unknown whether there are any sites where true
new habitat can even be created).
2. A detailed conceptual mitigation plan to replace the halibut nursery
habitat. See above comment.
3. A landscape and irrigation plan. (This plan should be part of the
project description and its impacts analyzed as part of the project since
runoff from the site could impact the public trust resources. Also, why
are grease traps not required as mitigation pursuant to the new EPA
NPDES regulations? This issue must be analyzed in the DEIR and is
not.)
4. Grading plan and soil engineering reports.
These plans will not be subject to public scrutiny contrary to CEQA. They
should be completed and evaluated in a recirculated DEIR.
Response IV.A 18. 1. See Attachment B in Section 3 for a copy of the draft conceptual
mitigation plan for the loss of mudflat and shallow subddal habitats.
2. See Attachment B in Section 3 for a copy of the draft conceptual
mitigation plan for the loss of mudflat and shallow subtidal habitats.
3. The preliminary landscape plan is a part of the proposed project
description (see Exhibit 34 of the Draft EIR. While it is anticipated
that drainage from the site would continue to drain into Newport
Bay (see page 5.3-7 of the Draft EIR); a detailed irrigation and
drainage plan is required prior to the approval of the grading
permit by the City of Newport Beach and will also be subject to the
requirements of the municipal stormwater NPDES permit.
4. A description of the proposed grading and dredging activities are
presented in Section 3 of the Draft EIR and evaluated in
Section 5.2. A more detailed grading plan will be required prior to
the City's issuance of a grading permit for the project. Soil
engineering reports are presented in Appendix D of the Draft EIR,
and are also discussed in Section 5.2 of the Draft EIR.
As noted above, a draft of the conceptual mitigation plan is now available
for review by the public as a part of this Responses to Comments
Addendum, and is therefore a part of the Final EIR. Also, the
preliminary landscape plan and soil reports have been available for review
JBV0064MI IATC IV-7
as part of the Draft EEL The more detailed grading and drainage plans
• have not been provided to date. However, the concepts associated with
both the grading and drainage elements of the proposed marina have been
discussed and evaluated in the Draft EIR (see sections 5.2 and 5.3 of the
Draft EIR). These plans will be reviewed and approved by the City of
Newport Beach Public Works Department prior to issuance of the grading
permit. This is a standard practice of the City.
Comment IV.A-19. Also, it is not apparent how the effect of an accidental spill can be reduced to
a level of insignificance. If a spill happens, the impacts will be significant.
n
U
•
Response IV.A-19. The Draft EIR identifies accidental spills or leaks as having the potential
to significantly impact local water quality. As stated on page 5.412 of the
Draft EIR, spills or leaks associated with construction activities could lead
to a potentially significant effect on the local water quality and marine
life. In addition, on page 5.4-15, the Draft EIR identifies the spillage of
hazardous materials such as lubricating oil, organic solvents, etc.,
associated with the operation of the marina as contributing to a
cumulatively significant water quality degradation in Newport Bay.
JBV00640011.RTC IV-8
IV.B. FRIENDS OF NEWPORT BAY (October 4, 1991)
Comment IV.B-1. The proposed marina has a land frontage of approximately 450'. However, -
the piers proposed for the marina extend approximately 1,000' along the
waterway, approximately 550' more than the amount permitted by city policy.
Most of the proposed piers are well out in the public water away from the
marina property.
We believe that the marina proposed by California Recreation Company
should be limited to the 450' width of their property in keeping with public
policy so that the remaining tidelands can be managed in the spirit of the
tidelands trust for the purposes of commerce, fishing, navigation, access and
recreation. A larger marina to increase the income of the California
Recreation Company hardly qualifies as a compelling public benefit.
Response IV.B-1. The additional land frontage to the north of the approximate 450-foot land
frontage along the Lower Castaways Marina site extends along the Upper
Castaways properly, which is also owned by The Irvine Company.
Therefore, the entire proposed pier construction is within the land
frontage of the same owner and is within the area permitted by City policy
for pier construction.
Comment IV.B-2. Exhibit 3-3 showing the locations of the U.S. bulkhead and U.S. pierhead
lines is in error. These lines do not exist.
• Many years ago the Orange County Board of Supervisors adopted bulkhead
and pierhead lines in anticipation of a land trade proposed by The Irvine
Company. The lines never were adopted by the U.S. Corps of Engineers.
When the proposed land trade was abandoned, the lines were removed by a
Minute Order of the Board of Supervisors.
is
If this project is to be considered, bulkhead and pierhead lines must be adopted
by the county and be approved by the U.S. Corps of Engineers. Any new
harbor lines in this area must meet the U.S. Corps of Engineers requirements.
Response IV.B-2. The bulkhead and pierhead lines shown on Exhibit 3-3 are those adopted
and recognized by the County of Orange (see Orange County Ordinance
No. 2200 in Attachment D in Section 3 of this. document). No evidence
that these lines are not in force has been presented.
Comment IV.B-3. Without the approved bulkhead and pierhead lines, it is unclear to me whether
or not this project can proceed through the review process.
Response IV.B-3. Please see response to comment IV.B-2. Review of the proposed project
can proceed.
Comment IV.B-4. In addition, this project fronts on and is in the tideland grant to the County of
Orange. Therefore, does the city of Newport Beach have the authority to
approve or disapprove the pier system of this project?
JB2/00640011.RTC
Ii=
Response IV.B4. The land portion of the project site is under The Irvine Company
ownership and is subject to the zoning regulations of the City of Newport
Beach. The Irvine Company maintains an existing lease with the County
for the tidelands portion of the project site. This lease was originally
formulated in conjunction with the old marina that previously occupied
the site. A new lease has been drafted in conjunction with the currently
proposed marina development, which has tentatively been approved by the
County and The Irvine Company, but has not yet been signed. Both
leases allow development of a marina on the site. The marina will also be
subject to the City's harbor permits.
Comment IV.B-5. It is clear from the bulkhead lines, originally proposed by the county, that a
wider channel was preferred. This project reduces theeffectivewidth of the
channel to approximately one-half of the proposed channel width.
Response IV.B-5. The U.S. bulkhead line is intended to be the farthest point into the
channel that fill is allowed. The U.S. pierhead line is intended to be the
farthest point into the channel that a floating pier extension is allowed.
No fill is proposed as part of this project. Also, as shown on Figure 3-3 of
the EIR (Proposed Marina Concept Layout), no floating extension of the
proposed pier development would extend beyond the U.S. pierhead line.
Therefore, the project design is not in conflict with the U.S. bulkhead and
U.S. pierhead lines delineated in the site area. The original width of the
channel was proposed when a small craft harbor was considered for
Upper Newport Bay.
. Comment IV.B-6. The piers would impact severely 600' of the 1800' now available for shoreline
fishing. Since the tideland trust protects the public's right to fish, the marina
should not extend beyond the land property line of the marina.
•
Response IV.B-6. Pedestrian access to the shoreline north of the proposed new marina basin
would be provided through provision of steps from the northeast corner
of the new parking lot down to the shore. Fishing along the shoreline
from boats would not be precluded by the project since boats could
maneuver behind the pier.
Comment IV.B-7. Dredging at the marina site in the channel will remove significant amounts of
mud flats. The EIR suggests that the lost mud flats be replaced by dredging
in UNB. Some parts of Shellmaker island in the ecological reserve are being
considered. I do not think that any part of the ecological reserve or any other
part of UNB should be considered for this purpose.
Response IV.B-7. Comments are noted. See Attachment B in Section 3 of the document for
further description of the conceptual mitigation plan which includes
Shellmaker Island. Use of this site requires the approval of the California
Department of Fish and Game as manager of the Upper Newport Bay
Ecological Reserve.
JWJ00640011.RTC
IV-10
Comment IV.B-8. In the past, conventional wisdom held that the best use of wetlands and open
water was the conversion of these resources to boat related activities. As a
result, Newport bay is now the world's largest small boat harbor with 10,500
boats. When is enough enough?
Response IV.B-8. The proposed marina project most likely represents the last major new
commercial marina facility which can be built in Newport Bay given the
lack of available shoreline in Upper and Lower Newport Bay, and the
limitations on use of the ecological reserve in Upper Newport Bay.
Comment IV.B-9. The EIR includes the marina basin dredged area (6.99 acres) as compensation
for the loss of open water foraging for birds and bottom foraging for fish.
This area should not be considered since the area principally is to be covered
by boats and docks bringing pollutants such as the poison from bottom paints
and other chemicals. It also is likely there will be a siltation problem similar
to that in Dover Shores.
The proposal in no way compares to an open channel, flushed and cleaned by
tidal currents.
Response IV.B-9. Please refer to response to Comment B-3. The size of the marina dredge
basin is erroneously given by the commentor. The correct value is
2.96 acres. The EIR text has been revised to state that the marina is not
being used as compensation area for young -of -the -year halibut habitat
loss. The same can be stated for benthic foraging fishes. The basin will
• provide additional habitat (2.96) acres more than the required amount of
habitat to be mitigated for the loss of bottom habitat (0.28 acre). Water
column foraging birds, including endangered species, commonly forage
among boats and docks in Newport Harbor charnels and marinas and
they are likely to do so in the new marina basin without significant
impacts imposed upon them.
•
In regard to siltation issues, bedload sediments will be trapped at the
juncture of the marina basin and the main channel, and will be removed
during maintenance dredging operations approximately every 5 years. It
is unlikely that the marina will experience serious sedimentation problems
if the mitigation measures to remove accumulated sediments are carried
out. Sedimentation impacts are addressed in the EIR in Section 5.3
(Hydrology/Sedimentation), Section 5.4 (Water Quality), and Section 5.5
(Marine Resources). Also, see results of hydraulic model prepared in
conjunction with the EIR (Section 53 and Appendix E of the Draft EIR).
Comment IV.B-10. We recommend that a modification of the 84 boat marina be built instead of
the 125 boat marina, the modification consisting of limiting the pier to the
frontage between the property lines (450'). This marina configuration will
have a minimum impact on the ecology and public fishing rights in UNB.
Response IV.B-10. Comment so noted; no response is required.
7B2I00640011.RTC IV-1I
IV.C. SEA & SAGE AUDUBON (October 6, 1991)
Comment IV.C-1. The long pier planned for the main channel would have significant potential
to increase pollution in the upper bay. While waste discharges are not
permitted in the harbor, it is well known that they do occur, and enforcement
of the law has been difficult. Coupled with this is the chance for accidental
discharge of fuel and oil. Because this pier borders the main channel a flood
tide could easily distribute wastes and hydrocarbons over the entire ecological
reserve in just a few hours, well before any containment response could be
organized. This is a highly dangerous situation which dictates removal of this
long pier from any project plan.
Response IV.C-1. The Draft EIR acknowledges that the project would contribute to potential
cumulative water quality effects. Restrictions on boat maintenance
activities allowed at the new marina will reduce these potential effects.
Also, no fueling facility will be provided at the marina. Based on the
hydraulic model prepared for the project (Noble 1989a), flow patterns
within the bay would not be substantially altered by the proposed pier
structure.
Comment IV.C-2. All alternatives listed for this project are clearly described as having less short
term and long term environmental impacts than the proposed plan. The 84-
Boat Marina alternative has the smallest pier and therefore the least impact on
the chances for disastrous pollution of the upper bay. Why is there no
• alternative described using only the Lower Castaways basin, with no
protrusion into the main channel?
Response IV.C-2. See response to comment I.B-1.
Comment IV.C-3. The only mitigation measures offered for the dredging activity period seem to
be that proper permits will be obtained from the Army Corps of Engineers,
the Environmental Protection Agency, etc. Except for screening to reduce
turbidity (as feasible the mere approval of these agencies does not give
confidence that the effects of dredging will be insignificant.
11
Response IV.C-3. Best Management Practices (BMPs) are likely to result in insignificant
impacts related to dredging. Employing a dredge screen is one practice
that greatly reduces turbidity impacts; other BMPs include: using
appropriate equipment or machinery when dredging and transporting
dredge materials; employing proper maintenance and operation on
equipment or machinery, including adequate training, staffing, and
working procedures; and lastly, restricting dredging operations to the
period of September 15 to April 1 to avoid the California least tern
Sterna albifrons brownii breeding season. Relative to impacts on
halibut, dredging within the time period of September through February
is likely to limit potential dredging impacts to young -of -the -year
individuals, as they typically settle in embayments between March and
July (Kramer 1990).
J132100640011.RTC
IV-12
The Santa Ana Regional Water Quality Control Board (SARWQCB) will
determine permit conditions to maintain water quality during dredging.
For example, waste discharge requirements imposed for the Sunset
Bay/Huntington Harbour Maintenance Dredging Project, administered by
the Orange County Environmental Management Agency, included a
specification that stated, "dredging in the channels and harbors... shall not
cause the turbidity of the dredged harbors to be increased by more than
twenty (20) percent." The SARWQCB will identify these measures.
Turbidity monitoring during construction for the Castaways Marina may
be included as a mitigation measure to ensure compliance with standards
set by the Regional Board.
Comment IV.C-4. At several points mitigation for mudflat and halibut habitat removal is offered,
suggesting that this will, or may, occur within the upper bay. This plan
contains the possibility of further heavy activity in the Ecological Reserve, and
while not impossible, should be approached with extreme caution and approval
of the California Department of Fish and Game.
Response IV.C4. Comment so noted. See Attachment B in Section 3 of this document for
a draft of the conceptual mitigation plan. This plan shall be reviewed and
approved by the California Department of Fish and Game prior to
issuance of any federal permits.
We feel the disposal activity of dredged materials would be least damaging if
the ocean disposal were to be used exclusively, removing the impacts on the
local
• Response IV.C-5. Conn
•
Comment IV.C-5.
JBV00640011.RTC
IV.D. JAN D. VANDERSLOOT, M.D. (Oetober 7, 1991)
• Comment IV.D-I. A traffic signal, temporary or permanent, should be considered for the
entrance into the project site, without connecting to Cliff Drive. Ibis signal
would be 3-way, would not require a cut into the bluff facing Dover Drive,
would obviate the need for the destructive temporary road across the Upper
Castaways, and would allow the trucks hauling material away from the site
easy access to PCH. Therefore, there would be no adverse impacts to Cliff
Haven or Newport Heights.
Response IV.D-I. North and south bound lanes on Dover Drive are separated by a divider
at the current entrance to the Lower Castaways site. Thus, current access
to and from the site is from northbound Dover Drive only. The suggested
traffic signal is considered unacceptable by the City of Newport Beach
because it would require the removal of a portion of the divider to create
access to southbound Dover Drive, thus interrupting the left turn lanes on
southbound Dover Drive. In addition, according to the City of Newport
Beach, the current location of the access point to the site presents safety
concerns associated with the proximity to the intersection of Coast
highway and Dover Drive (approximately 200 feet). The proximity of the
entrance to this intersection could result in conflicts between vehicles
exiting the site and cars turning right or left from Coast highway onto
Northbound Dover Drive (Webb, pers. comm. 8/8/91).
Comment IV.D-2. Ways to remove the "temporary" road across the Upper Castaways should be
. more thoroughly considered. An alternative is to haul the material up Irvine
Ave. to the Coyote Canyon Land Fill, thus not requiring the trucks to make
a U-turn on Dover or circle above on the temporary road to get back down to
PCH.
Response IV.D-2. This alternative is not considered appropriate, because the alignment
would route trucks through a greater number of residential areas along
Irvine Avenue. Also, this route would add a substantial amount of
mileage to the haul trips along primarily smaller residential roads which
were not designed to handle large-scale truck traffic.
Please see discussion of alternative access route in Section 6.4 (page 6-9)
of the Draft EIR.
Comment IV.D-3. A "Minimum Grading Alternative" should be discussed in the EIR. The less
grading, the fewer trucks are needed to haul the material away. Such a plan
would mean no temporary road, no cuts into the bluff, no high retaining walls
along Dover, minimum dredging of the bay.
Response IV.D-3. The Draft EIR evaluates a 50-boat slip alternative that would reduce the
amount of dredging activity by 79 percent over the proposed project (see
Section 6.2.3 [page 6-6] of the Draft EIR). This alternative would
substantially reduce the number of truck haul trips required to dispose of
the material. The alternative has been evaluated and is under
• consideration by the City of Newport Beach.
JBV00640011.RTC IV-14
Comment IV.D-4. - • A 60 space marina with no floating docks protruding into the bay should be
. analyzed. The floating docks appear to disturb current flow into and out of
the bay north of the bridge (see Hydrology Study, Appendix E, Figures 5,
6, 7, 8): An alternative without docks protruding into the bay is not present
in the EIR.
Response IV.D4. See response to comment I.B.I. In addition, see Section 5.3 of the Draft
EIR which addressed results of the hydraulic model study for the project
(Noble Consultants 1989a). The pier.structure was not found to have
significant effects on the flow into the bay north of the Coast Highway
Bridge.
Comment IV.D-5. An analysis of shoreline erosion of the bay below the Castaways bluffs should
be in the EIR. Flood current (high tide) and ebb current (low tide) both will
1 act to scour the shoreline, increasing erosion of the shore (again, see
Appendix E, Hydrology Study, Figures 7 and 8, Noble Consultants).
Response IV.D-5. The analysis in Appendix E of the Draft EIR addresses existing and
projected flow velocities and shoreline erosion. No significant effect on
currents or shoreline erosion are expected due the proposed project.
Comment MD-6. Exactly where the temporary road will go on the Upper Castaways, as well as
where the dredge spoils will be dried out on the Upper Castaways should be
in the EIR.
. Response 1V.D-6. Please see Exhibit 3-8 in the Draft EIR for a graphic representation of the
temporary haul road. Dredged material would not be dried on the Upper
Castaways site; it would only occur on the Lower Castaways site (see
pages 3-3 to 3-4 of the Draft EIR).
Comment IV.D-7. The plans of the Irvine Company to dedicate the "nose" of the Castaways for
open space as part of its Open Space and Circulation Development Agreement
should be in the EIR. Portions of the "nose" appear to be negatively impacted
by this project, including grading of the bluffs, the temporary road, the drying
out site for dredged material. The EIR lacks assessment of the cumulative
impacts of this project on the Upper Castaways and its ecologic resources.
Response IV.D-7. Page 5.1-5 of the Draft EIR addresses the proposed Circulation
Improvement and Open Space Agreement between the City of Newport
Beach and The Irvine Company; and the preliminary land use plans for
the Upper Castaways site. It acknowledges that park and open space uses
would be placed along the bluffs of the upper site. The potential
secondary effects on Upper Castaways' biological resources are addressed
in Section 5.6 of the Draft EIR. On page 5.6-9, it is acknowledged that
the proposed marina and temporary road construction may further
degrade the condition of the resources on the upper site. In addition,
under the discussion of cumulative impacts to biological resources (Section
5.6.5 on page 5.6-13), it is acknowledged that the proposed project would
further diminish the quality of the habitat on the Upper Castaways site
due to the increased human activity in these areas. Any future
development on the Upper Castaways site would add to the cumulative
impacts to onsite resources.
JWJ00640011.RTC Iv-15
Comment IV.D-8. The project EIR lacks a cumulative impacts assessment on the communities of
Cliff Haven and Newport Heights. Specifically, if a signal is placed at Dover
•
and Cliff, through traffic may increase on Cliff Drive, especially as traffic
increases on PCH as a result of the other large projects planned in the general
area, including the Hoag Hospital expansion, and the West Newport Oil -
project at the Santa Ana River mouth.
Response IV.D-8. A cumulative impact analysis of the project in conjunction with the City
of Newport Beach approved and committed projects list was conducted for
this Draft EIR (please see Section 5.8 of the Draft EIR and the traffic
study in Appendix j). The analysis was conducted in accordance with the
City of Newport Beach Traffic Phasing Ordinance (TPO) 1 percent
analysis and included traffic assumptions for all approved and committed
projects (mown at the time of this analysis (see Table 4-2 in the Draft
EIR). This constituted the cumulative impacts analysis, and was
conducted for the proposed access route in Section 5.8 of the Draft EIR,
and for the alternative access route in Section 6.4. Five intersections were
chosen for analysis and approved by the City of Newport Beach. The
study indicated that the projected peak 2.5 hour traffic volume generated
by the proposed project would be less than 1 percent of the projected peak
2.5 hour volumes (including approved projects) on any approach of any
intersection analyzed, including the Dover Drive/Cliff Drive intersection.
Thus, neither the proposed access route or the alternative access plan
would have a significant impact on traffic flow at this intersection.
. Comment IV.D-9. The Water Quality section does not appear to address the question of long
term pollution of the bay, especially the Upper Newport Bay ecological
reserve, because of oil, grease, and gasoline discharged into the bay as a result
of operating motor boats. These pollutants will be directly swept into the
Upper Bay because of the floating dock protruding into the flood current at
high tide. This question was asked by the City's CEQAC's Subcommittee on
EIRS, 26 March 1990, as well as other questions by CEQAC, but which were
not answered in the EIR.
0
Response IV.D-9. Page 5.4-12 of the Draft EIR addresses the potential of the project to
contribute to the degradation of water quality in Newport Bay. As stated
on page 5.4.14 of the Draft EIR, project -related water quality impacts are
identified as locally significant, but mitigable to a level of less than
significant with the implementation of the proposed mitigation measures
on page 5.4.15. In addition, the proposed marina would not contain
fueling facilities, and the lease agreement would prohibit boat painting,
scraping, and engine maintenance. These regulations would be enforced
on a daily basis. Therefore, the potential for discharge of pollutants into
Upper Newport Bay which could result from boating activities occurring
at the marina is considered minimal.
Comment IV.D-10. A coastal bluff along Dover exists. The EIR does not appear to recognize the
City's coastal bluff protections in the General Plan or LCP. Applicability of
the Coastal Bluff ordinances to this project should be in the EIR.
=00640011ATC IV-16
Response IVM-10. The Local Coastal Program for the City of Newport Beach (1990) defines
a coastal bluff as any natural landform having an average slope of 26.6
degrees or greater, with a vertical rise of 25 feet or greater. When there
is confusion as to the applicability of this section to a specific landform,
a determination as to whether or not the specific landform constitutes a
bluff shall be made by the Planning Commission, consistent with the
purposes of this regulation. The coastal bluff along Dover Drive has been
modified by previous construction of Dover Drive, Pacific Coast Highway,
and by commercial activities on the site in the late 1800's. Because this
bluff is not a natural bluff, it is not subject to the coastal bluff policies of
the City of Newport Beach.
Comment IV.D-11. Two wetlands appear to be impacted by this project: the wetlands containing
halibut nurseries in the Bay, and wetlands along Dover which may be
impacted by the temporary road. Because of the significance of Upper
Newport Bay to the regional environment, the US Fish and Wildlife Service
should have been notified and comments solicited. There is no evidence that
USFWS was notified in the EIR.
Response IV.D-11. Please note that the U.S. Fish and Wildlife Service was contacted during
preparation of the Draft EIR and draft Conceptual Biological Mitigation
Plan for the Loss of Mudflat and Shallow Subtidal Habitat, and received
a copy of the Draft EIR and Conceptual Plan for review and input; please
refer to comment letter I.A.
Comment IV.D-12. Because of the potential current changes induced by this project, the US Army
• Corps of Engineers should be more completely informed of the scope of this
project. A modelling study of shoreline erosion, and possible changes in the
tidal prism entering the Upper Bay north of the Coast Highway bridge, should
be done by the Corps before this project is considered by the City. This
project affects navigable waters and may affect navigation into and out of the
Bay, affecting Dover Shores and the Dunes Aquatic Park.
Response IV.D-12. See Section 5.3 and Appendix E of the Draft EIR for a discussion of
potential current flow pattern effects associated with the proposed project.
The primary currents are not expected to change; thus shoreline erosion
characteristics are not expected to be significantly altered by the project.
Comment IV.D-13. There should be a discussion of the permitting agencies involved in the
approval of this project, including applicable sections of the Coastal Act and
Section 404 of the Clean Water Act.
Response IV.D-13. Section 3.5 on page 3-6 of the Draft EIR presents a list of the local, state
and federal permits required prior to construction of the project.
Comment IV.D-14. The project may be a violation of the Tidelands Public Trust administered by
the State. It appears to turn public tidelands into a private venture. A
discussion of the tidelands ramifications should be in the EIR. The position
of the State Lands Commission should be more thoroughly researched than
what is stated in the EIR.
0 Response IV.D-14. Please refer to Responses IV.A-1 and IV.A-2.
JBV006"11.RTC IV-17
Comment IV.D-15. Halibut habitat for juveniles appears to be mitigated under the boats in the
• marina. Is this mitigation acceptable to the resource agencies? It would
appear that pollution from the boats, oil, gas, paint, and the frequent dredging
of this area due to acknowledged siltation of the marina, would not make this
area an acceptable mitigation site for juvenile halibut.
Response IV.D-15. Please refer to the responses to Comments I.B-3, I.B-5, II.11-12, and
IV.B-9.
Comment IV.D-16. A desire to mitigate the halibut nursery somewhere in Upper Newport Bay is
expressed in the EIR. Exactly where it is intended to be mitigated should be
in the EIR, since the rest of Upper Newport Bay is itself sensitive habitat.
Mitigating into an already high value wetland would result in the "net loss of
wetlands" which is contrary to state policies and law.
Response IV.D-16. Comments are noted. Please refer to Attachment B in Section 3 of this
document which includes the draft of the conceptual mitigation plan for
mudflat and halibut nursery habitats. A map of the proposed mitigation
site—Shelbnaker Island —is included in the plan.
Comment IV.D-17. An alternative showing a publicly useful marina, such as a ramp for trailers
for small boats, should be in the EIR, since the land is public tidelands and
should have public access. Such an alternative would require the least amount
of dredging and would cause the least amount of environmental damage, yet
be consistent with the City's desire for a marina there.
• Response IV.D-17. It should be noted that the land portion of the project site is not with the
public tidelands; it is in private ownership. The parking lot and view area
of the marina will be available to the public.
Comment IV.D-18. An effort to identify possible ways to transfer the site to public ownership
should be in the EIR. Such a transfer would be most consistent with the effort
to transfer the whole of the Castaways to public ownership, and would be the
most consistent with keeping the nose of Castaways as natural open space.
Response IV.D-18. The City is not considering acquisition of the Lower Castaways site; nor
is it considering acquisition of the entire Upper Castaways site. The
proposed land use is consistent with the City's General Plan land uses for
the study area.
0
JBV0064001 IATC IV-18
•
•
•
IV.E. CLIFF HAVEN COMMpNPPY ASSOCIATION
Comment ME-1. The timing of the left -turn signal should be infrequent enough that traffic is
discouraged from making left turns onto Cliff from northbound Dover, thereby
negating any time saving that this "shortcut" might otherwise provide. We do
not want Cliff Drive to pick up PCH traffic.
Response IV.E-1. M'digation measure 5.8.4 on page 5.8-9 in the Draft EIR is hereby
amended as follows:
"......to form a 4-way, signalized intersection. This signal shall be
the extent possible."
Comment ME-2. The signal should default to a green light in each direction for Dover Drive
traffic — this should be the signal's normal position. Only when significant
traffic accrues should the light change to stop traffic from freely flowing on
Dover. This no only helps with a, above, but also will eliminate any potential
backup of cars on Dover, at the Cliff/Dover intersection (we are especially
concerned about backed up traffic on southbound Dover).
Response IV.E-2. Please see the response to comment 1V.E-1.
Comment ME-3. Speed bumps should be installed along Kings Place and Signal Road, between
Cliff Drive and 15th Street. This will not only discourage people trying to
make a shortcut from PCH to the Newport Heights area (Newport Beach and
Costa Mesa), but will also help to reduce the existing problem Kings Place and
Signal Road residents are experiencing with speeders. Further, "SLOW -
Children at Play" signs should be posted on these streets. We welcome your
suggestion of designing signs that are of more architectural interest (and thus
more likely to be read) than the standard yellow diamond signs.
Response IV.E-3. The proposed project is projected to have an ADT of 183. As shown in
Exhibit 5.8-1 of the Draft EIR, seventy percent of project generated traffic
will flow to and from the project site along Coast highway between
Newport Boulevard and Dover Drive. Forty five percent of project traffic
is anticipated to travel along Newport Boulevard to and from the Costa
Mesa Freeway (SR-55). Only 5 percent of project generated traffic is
projected to use Dover Drive north of the project site. Thus, the majority
of project generated traffic would avoid the area in question by
predominantly using Coast Highway and Newport Boulevard. Therefore,
no significant adverse impacts are anticipated as a result of this project
and no mitigation measures are required for the area specified.
JWJ00640011.RTC
However, City of Newport Beach policy L-13 indicates that the City will
IV-19
consider the placement of speed bumps in the area indicated. The Cliff
Haven Community Association should 'submit an application for the
placement of speed bumps through the Traffic Affairs Committee. In
addition, City policy does not provide for the placement of non-standard
warning signs along street right-of-way. Such non-standard signs can be
placed on private property (Don Webb pers. comm. 10/28/91).
Comment IV.E-4. A sign indicating "PCH - that -a -way" should be installed at the intersection of
16th Street and Irvine Avenue, so that PCH-bound vehicles do not proceed all
the way to Cliff Drive.
Response IV.E4. No adverse traffic impacts are anticipated at the intersection of 16th Street
and Irvine Avenue (Please see response to comment IVX-5). Thus, no
mitigation measures are required as part of the proposed project. If the
Cliff Haven Community Association feels such a sign is necessary, the City
will consider such a request. An application for the request should be
submitted to the City of Newport Beach Traffic Affairs Committee.
Comment IV.E-5. Crosswalks should be incorporated into the signal design for the Cliff/Dover
intersection. Ideally, crosswalks should be located across all four comers of
the intersection. If only three crosswalks are designed, the crosswalk across
Dover should be located on the north end (i.e., connecting the medical offices
to the access to Upper Castaways).
Response IV.E-5. The City of Newport Beach provides for crosswalks as part of traffic
signal instillation. The initial design of the traffic signal will provide for
three crosswalks as described. A fourth crosswalk would be added if
necessary.
Comment IV.E-6. The requisite bluff retaining wall for the extension of Cliff Drive must be
constructed in such a way as to minimize the `block' effect of such a massive
structure. Ideally we would like to see a series of gradual setbacks, each
landscaped in harmony with the proposed landscape plan for the marina/
P B & R's plans for the view park on Upper Castaways. Additionally,
pedestrian areas to the Upper Castaways should be incorporated into the
overall design. Our community should be involved in this architectural
process as it develops.
Response IV.E-6. The comment is noted. The City will include conditions on the parcel map
to provide pedestrian and bicycle access to Upper Castaways from Lower
Castaways.
Comment IV.E-7. Finally, the existing public walkway appearing on the Cliff Haven tract map
that I pointed out to you during our meeting should be developed to provide
access to the Castaways site for Cliff Haven residents. A significant number
of our residents would have much greater access to both Lower and Upper
Castaways were this existing public land to be used for the purpose intended.
Obviously, given the heavily treed, rustic flavor of the area, the public
walkway should respect the existing landscape and conform as much as
possible. Jerry King informed me today that he has already begun exploratory
• discussions with the City and The Irvine Company regarding development of
this walkway.
JBV00640011.RTC IV-20
'Response IV.E-7. The proposed walkway •is potentially controversial. Implementing the
• walkway would impact the backyards of several homes in the surrounding
area. The walkway is not part of the Castaways project, and therefore
should not be included within the scope of the Draft EIR. However, if the
Cliff Haven Community Association is interested in pursuing this
walkway, the - City of Newport Beach is willing to work with the
Association outside of the environmental process for the Castaways
project.
r 1
►- J
0
W.F. JAMES KOCIUBA (October 4, 19.01
• Comment IV.F-1. The draft calls for a temporary road that extends from Dover Drive and
Sixteenth Street to the marina area. This road was deemed necessary to allow
Coyote Landfill bound dirt hauling trucks leaving the marina development site
to access PCH without making a U-turn on Dover Drive. Alternately, the
trucks could leave the development site's primary entrance headed north on
Dover Drive, turn left on Westcliff Drive, turn right on Irvine Ave., turn right
on Bristol, then proceed to the Coyote Landfill. This scheme eliminates the
U-turn in question, thereby eliminating the need for the temporary road. This
dirt hauling option needs to be examined.
Response IV.F-1. This is not considered a reasonable option by the City of Newport Beach.
Please see the response to comment IV.D-2.
Comment IV.F-2. Why does the Upper Castaways development concept have a permanent access
to the temporary road? Since the Castaways marina site is to be developed
long before the Upper Castaways site, the Upper Castaways site does not need
permanent access to the temporary road. Does the Upper Castaways
permanent access to the temporary road mean the temporary road in the
Castaways Marina draft EIR is not temporary?
Response IV.F 2. The proposed Castaways Marina project does not contain proposals for
the Upper Castaways site with the exception of the temporary haul road.
Therefore, no permanent connection to the temporary road would be
provided as a part of this project.
Comment IV.17-3. If the temporary road is built, when will the temporary road be permanently
closed?
Response IV.F 3. The proposed temporary haul road on the Upper Castaways site would
close at the end of the marina's construction.
Comment IV.F-4. When the temporary road is closed, what will it be permanently replace with
and when?
Response IV.F4. Upon the closure of the temporary haul road, the road would be
hydroseeded with compatible plant material. The plant material would be
selected by a licensed landscape architect and approved by the City of
Newport Beach.
Comment IV.F-5. The Irvine Ave. and Westcliff Drive intersection, along with the Irvine Ave.
and Sixteenth Street intersection, will be impacted by the Castaways Marine
development. This impact needs to contained in the EIR.
Response IV.F-5. As shown in Table 5.8-1 of the Draft EIR, the proposed project is
projected to generate a total of 13 vehicle trips during the AM peak 2.5
hour period, and 20 trips during the PM peak 2.5 hour period. The
average daily trips for the project is estimated to be 183. Coast Highway
is anticipated to be the primary travel route for the proposed project. As
shown in Exhibit 5.8-1 of the Draft EIR, 70 percent of project -generated
JBV00640011.RTC IV-22
4)
trips would flow to and from the project site along -Pacific Coast Highway
between Newport Boulevard and Dover Drive. Forty five percent of
project traffic is anticipated to travel along Newport Boulevard to and
from the Costa Mesa Freeway (SR-55). Only 5 percent of project
generated traffic is projected to use Dover Drive, which provides access to
the project site from Sixteenth Street and Westcliff Drive. During the AM
peak 2.5 hour period, an additional .65 trip would be generated along
Dover Drive, and during the PM peak 2.5 hour period, only 1 trip along
Dover Drive would be generated by the proposed project. The majority
of project -generated traffic would avoid traveling along Sixteenth Street
and Irvine Avenue by using Coast Highway and Newport Boulevard.
Thus, no significant impacts to Sixteenth Street and Irvine Boulevard are
anticipated, and no further traffic analysis is required.
Comment IV.17-6. Finally, the traffic impact needs to be analyzed on Costa Mesa's East Sixteenth
Street between Newport Blvd. to Irvine ave. This is a residential street
segment that is not on the county's master plan of highways, and whose
residents are sensitive to traffic increases due to this marina development.
Response IV.F-6. Please see response to comment IV.F-5.
JB2100640011.RTC IV-23
MG. CITY OF NEWPORT BEACH
. Environmental Quality Affairs•Committee (September 2% 1991)
Comment MG -I. The 121-boat alternative significantly reduces concern regarding wetlands
destruction, primarily due to the reduced dredging. -(1.3.2, 6-3)
Response IV.G-1. Comment is noted. This alternative is under consideration by the City
and is considered economically feasible by the project applicant.
1]
Comment IV.G-2. Traffic safety requires signalization of the project entrance at Dover
Drive/Cliff Drive intersection. (6-9)
Response IV.G-2. Comment is noted. As a part of the alternative access design, a traffic
signal would be provided at the intersection of Dover and Cliff drives.
Comment IV.G-3. Timing of the construction should be carefully planned to cause least
disruption to the reproductive cycle of the birds and fish.
Response IV.G-3. Comment is noted. XMigation measures 5.6-2 and 5.6-3 in the Draft EIR
would reduce potential effects on sensitive bird species' nesting seasons.
Comment MG-4. Attention should be given to changing "could" to "should" in the last
paragraph regarding aesthetic impact of the Alternative Site Access Design.
(6-9)
Response IV.G4. Comment is noted. H this alternative access design is selected as part of
the proposed project, the following mitigation measure will be
implemented:
IBV00640011.RTC
"A_2. The landscape plan for the project will be modified to
incorporate landscaping alone the cribwall and will be
reviewed and approved by the City of Newport Beach
prior to issuance of the grading permit."
IV-24
•
1]
IV.H. BAYSHORES COMMUNITY ASSOCIATION (September 25, 1991)•
Comment IV.H-1. The Board has voted to approve the project with the condition that the
alternate access -plan as detailed in Section 6.4 of•the EIR be incorporated into --
the overall project. This requires the entrance of the marina to be located at
the Cliff Drive extension to Dover Drive with the development of a new
access road.
Response IV.11-1. Comment so noted; no response is required.
JB2/00640011.RTC IV-25
•
•
•
SECTION 3
ATTACHMENTS
A. Comment Letters
B. Conceptual Biological Mitigation Plan for Loss of Mudflat and Shallow Subtidal Habitat
C. Additional References Cited
D. County of Orange Ordinance No. 2200
IB2100640011.RTC
3-1
A. • COMMENT LETTERS
•
ited States Department of the Interior
ry pp pgyVPORT BEACH
OCT 111991
17SII AND WILDLIFE SERVICE
FISH AND WILDLIFE ENHANCEMENT
SOUTHERN CALIFORNIA FIELD STATION
Laguna Niguel Office
24000 Avila Road
TAXI M—�-.pff
AMMQ=Mmz ■�
mom —
•—' :
Federal Building,
Am P97�8)e(1��11 t1t2(3t4►�18 1.3TVA tg1VUg1.. California 92656
October 10, 1991
Ms. Patricia Temple
Planning Department
City of Newport Beach
3300 Newport Blvd.
Newport Beach, California
92659-1768
Re: Draft Environmental Impact Report, Castaways Marina
Dear Ms. Temple:
The Fish and Wildlife Service (Service) received the referenced draft on
August 29, 1991. Unfortunately, due to a staff shortage at this time we are
unable to properly review the document. However, due to our prior effort£awo
coordinate with the Proponents and the likelihood of a Federal per
remarks seem warranted.
are
bighoRt
Intertidal moflflats and shadow subt eouthe�in Calif
rnia.ng a They can provide
value and most scarce habitat types of shorebirds, waterfowl, wading
food for very large numbers and many types endangered California least
birds, and diving birds. The andte relies on theral shallow water" habitat
tern broads at Upper NewportY
for food. The Proposed marina expansion would destroy or digrade Service
important habitat types. Were a federal Permit action pending,
would likely recommend denial of the permit application for the proposed
included excavation of the new Marina basin, little dredgeject
morofillrand fewhich
slips in the channel area.
We regret that we are unable to respond further at this time. It is expected
that we would respond to notices of pending California Coastal Act or Corps of
�EngineersPermit may be ked atapplications- our
Ostaff representative remains He. Rim Gould
ice Supervisor
•
1. A-1
I.A
RECGiDEPAR'MEW
PLAN%% EWPORS 30CI4 Q UNITED STATES DEPARTMENT OF COMMERCE
CRY OF % National Ocpa�nnnic and Atmospheric Administration
}991 \ WJ NSOQUJA*W6StN Reglon SERVICE
• Q�i� i 0 " 300 South Ferry Street
$`9I% d2jJI2I%9t516 Terminal island, CA 90731
li
It October 7, 1991 F/SWRI3:RSH
Ms. Patricia Temple
City of Newport Beach
Planning Department
3300 Newport Blvd.
Newport Beach, California 92659-1768
Dear No. Temple:
We have reviewed the Draft Environmental Impact Report for the
Castaways Marina, Newport Bay. We offer the.following comments
for your consideration.
General comments
We believe that avoidance or minimization of impacts to high
value habitats should be vigorously pursued. As a consequence,
ss of mudflat and shallow water
we are Concerned over the lo
habitat that would occur with implementation of the proposed
project and all of the alternatives described, with the exception of the no project alternative. in order to reduce these impacts, I. B-1
we believe consideration should be given to an alternative which
includes excavation of the marina basin in the Lower Castaways
area but eliminates all slips in the channel area. Dredging
requirements, and subsequent impacts to high value intertidal and
shallow subtidal habitat, would be minimal with this alternative.
8neo *{o Comments •
Pace 5 4-15. It is stated that the additional boats introduced
by the project will increase the incidence of oil and fuel spills
and, therefore, contribute to cumulatively significant water
quality degradation in Newport Bay. The mitigation measures I. B-2
described on page 5.5-21, while•reducing the potential impact,
will not eliminate those effects. Additional mitigation to
offset any remaining impacts should be.proposed.
n��o a-5-2o. It is assumed that the new marina basin will be
utilized by California halibut in a manner similar to the I. B-3
existing habitat proposed for dredging- Evidence from similar
'projects to support this statement•should be provided.
Identification of the specific 1•ocation of the proposed I. B-4
mitigation sites) should be included in the final document.
p&ae 5.5-23_ The proposed monitoring program should include I B-5
sampling in the marina basin to ensure that the new habitat
• �
.qyR,i)
I.B
• created in this area is in fact utilized by California halibut.
If habitat equivalency between the new marina basin habitat and I B-5
the former channel habitat does not exit by the end of the
monitoring program (i.e., after five years) then additional
mitigation should be proposed.
We hope our comments are helpful to you as you continue the
planning process for this project. Should you need any
additional information regarding our position on this project,
please contact Robert Hoffman of my staff at (213) 514-6663.
Sincerely,
-E.C. Fullerton
Regional Director
cc:
USFWS
CDFG
•
0
MATE OF CAUFORNIA
WERNOR'S OFFICE OF PLANNING AND RESEARCH
1400 TENTH STREET
ACRAMENTO, CA 95814
Oct 07, 1991
PATRICIA TEMPLE
NEWPORT BEACH CITY
3300 NEWPORT BLVD
NEWPORT BEACH, CA 92658-8915
Subject: CASTAWAYS MARINA, NEWPORT BEACH
SCH # 88081016
Dear PATRICIA TEMPLE:
PETE WILSON, Gdvemor
RECEIVED BY
PLANNING DEPARTMENT
r.ITY OF NEVdPORT BEACH
0CT 9 1991 FM
AM 123456
gl$1911UIU11''1 11 1 1 1
The State Clearinghouse submitted the above named environmental
document to selected state agencies for review. The review period is
closed and none of the state agencies have comments. This letter
acknowledges that you have complied with the State Clearinghouse review
requirements for draft environmental documents, pursuant to the
California Environmental Quality Act.
• Please call Tom Loftus
any questions regarding the
contacting the Clearinghouse
State Clearinghouse number
•
at (916) 445-0613 if you have
environmental review process.,
in this matter, please use th
so that we may respond promptly.
Sincerely,
e
When
eight -digit
David C. Nunenkamp
Deputy Director, Permit Assistance
II. A-1
ILA
Notice oi.Compietion Appendix F
/(mbum:S=C7aunghoW-1400TathS=cfoSa=MCodn.G95814 9161445-0613 SCH+1 98081016
project Tltist-
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Cit=of Newoo=t Beach— 92663 cc-syP-
3300 Newport boulevard Phone:
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Premsnt Land Ume(fadngmenerd plan Use Zoning: Planned Community
Existin Land Use: Open Space
Genera Pt an Ilse_.- Recreational 8 Marine Commercial
---------------
project DOsadpllen 125-boat commercial marina located at site of an historical -wring (since removed). New
wring to be developed by dredging appriximately 80,000 cubic yards of material from land and bay to provide
adpuate channel depth. Support facilities to include: 106 parking spaces, rsstroums, shown, sewage pump -out
station. storage anas, fin hydrants, and utilities.
CLEARINGHOUSE CONTACTS Tom Lotus
STATE REVIEW BSGAN:
DEPT REV TO AGENCYt
AGENCY REV TO SCH t
SCH COMPLIANCE :
LEASE NOTE SCE NUMBER ON ALL COMMENTS
CHT SKY
•
X
t
PLEASE FORWARD LATE COi MTS DIRECTLY
TO THE LEAD AGENCY ONLY
AQMDIAPCD: (Resources:
Off SNT
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Lands Cc=
STATE
CItJFaRNIA
l E LANDS COMMISSION
AL! oCARTMY. Lieutanant Governor
PRAY DAVIS. Controller
1 WAS W. HAVES, DbeetorarFinenca
October 31 1991
Ms. Carol Whiteside
State Projects Coordinator
The Resources Agency
1416 Ninth Street, Room #449
Sacramento, CA 95814
Ms. Patricia L Temple
City of Newport Beach
3300 Newport Boulevard
• Newport Beach, CA 92661
Dear Mesdames:
S8 Mmmto. CA 3eE
Searem
CNARLE9 WARREN
Esecuiiw OHIu►
Staff of the State Lands Commission (SLC) bas reviewed the Draft Environmental
Impact Report (DEIR) for the Castaways Marina Project (SCH 88081016). Based on this
review, we offer the following comments.
SLC Jurisdiction
An Seueral background, the SLC has jurisdiction and authority over all ungranted
tidelands, submerged lands, and the beds of navigable rivers, sloughs, lakes, etc. The SLC
has an oversight responsibility for tide and submerged lands legislatively granted in trust to
local jurisdictions (Public Resources Code Section 6301). All tide and submerged lands,
grunted or ungranted, as well as navigable rivers, sloughs, etc. are impressed with the
Common Law Public Trust.
The Public Trust is a sovereign public property right held by the State or its
delegated trustee for the benefit of all the people. This right limits the uses of these lands
to waterborne co u ncrac, navigation, fisheries, open space, recreation, or other recognized
Public Trust purposes. A lease from the Commission is required for any portion of a project
extending onto State-owned lands which are under its exclusive jurisdiction and the SLC
would be a Responsible Agency under the California Environmental Quality Act (CEQA).
Additionally, if development indirectly affects lands or resources under the jurisdiction of
40 the SLC, the Commission would be a Trustee Agency under the (CBQA).
II.B
• The proposed project is located on lands that have, been granted in trust by the
LZOIAture to the CIty of Newport Beach, with minerals reserved to the state. Therefore,
as indicated on page 3-6, the project is subject to authorization of the Commission.
GENERAL COMMENTS
There appears to be a general lack of significance criteria Without these criteria the
document resorts to conclusionary statements of impacts which are unsupported by evidence I I . B-1
in the record. Furthermore, without significance criteria there is no way to measure the
effectiveness of the proposed mitigation measures and the residual impacts.
The project description should include a clear discussion of liveaboards, public access,
waste disposal and drainage provisions. it should also show past, present and future II B-2
(proposed project) bulkhead and plorlines. The impacts of any channel width reduction
must then be analyzed for impacts to access and navigation.
We appreciate the fact that the nu -project alternative is being considered by the City
of Newport Beach. However, the EIR should, pursuant to CEQA Guidelines Section H. B-3
15126(d)2, identify which of the remaining project alternatives is environmentally superior.
The DEIR dues not include a mitigation plan for the loss of 0.69 acres of mudflat
or for the loss of 0.28 acres of habitat for "young -of -the -year" halibut. It is, therefore, not
possible to determine if mitigation is feasible. The loss of mudflat and nursery area must I I B-4
be considered a significant adverse impact until such time us the mi tigatiou plazt is approved
by the appropriate agencies. The mitigation plan must include both monitoring and the
remediation measures to be taken if restoration is not successfuL
SPECIFIC COMMENTS
Page 1-19, paragraph 3 -
The enfurcutucut of current regulations does not constitute a mitigation under II. B-5
CEQA. How is this cumulatively significant impact going to be reduced?
Page 53-8 -
The estimate of annual sediment delivery Is critical for both the economic viability
and the environmental impact of this project. How does the estimated rate of 0.1 foot per
year and the 5-year interval for maintenance dredging compare to the rates in nearby
marinas? What is the basis for assuring that 80% of fluvial sediment is retained in upper I I . B-6
Newport Bay. Does the estimated sedimentation rate take Into account that sediment will
not pass by the marina once, but will recycle to some degree with the ebb and flow of the
tide?
0 -2-
. Page 5.4-6 -
Total threshold limit concentrations (rrLC) for hazardous wastes are used to
determine the potential for impacts to human health- Water quality criteria for the
protection of aquatic organisms are orders of magnitude lower than the TTLC. The TTLC
Cannot be used to predict effects of dredging or disposal on aquatic organisms- The results I I B-7
of the sea urchin sperm tests and the tests using the marine worm (Nephtys caccoides) as
well as the results of the bioaccumulation tests suggest the dredged sediment may not be
suitable for nccan disposal.
Page 5.4-11-
What methods would be used to treat the discharged water if it does not meet U. S.
Eaviromnental Protection Agency (EPA) standards? What will be done if the water cannot I
I I . B-8
be sufficiently treated to meet the standards?
Page 5.4-11 and 5.5-13
As noted above, the available data does not iuppw t Ilig 4011 1010 that disposal Of I
I I B-9
sediments from the project has a low potential to degrade water qualityand/or water quality
at the disposal site.
Page 5.4-11, bottom -
Woody debris from construction should be picked up, not allowed to float out in the I I I . B-10
harbor.
Page 5.5-13 -
The levels of toxicants must be compared to EPA water quality criteria for the] II. B-11
protection of saltwater organisms, not TTLC.
Page 5.5-20 -
How will maintmtlauce dredging affect the quality of habitat for juvenile halibut? :1 I1- B-12
Page 5.6-11 -
If Southern tarplant is located on the site, it should be protected if at all possible.] I I . B-13
Page 5.6-11 -
In Mitigation Measure 5.6-2 - change "sh9vid" to "shall'. ] I I. B-14
-3-
cc:
0
0
You for the opportunity to comment. .If you have any
of the environmental document, please contact Dr. Mary Berge
MIAN
rz .CEIVED BY
KING DEPARTMENT
AND
,.pEPARTMENT OF TRANSPORTATION CT , 111991
� Tz pll
S01 ►UWAAN STAIS Am 2 $ 4 5 6
SAWA ANA, CA TnQ5 _ 70191101U112111 I I 1 I
A
0
E
Patricia L. Temple
City of Newport Beach
Planning Department
P.O. Box 1768
Newport Beach, CA 92659-1769
Dear Ms. Temple:
October 8, 1991
File: IGR/CEQA
DER
SCH #88081016
Castaways Marina
Thank you for the opportunity to comment on the Draft.Bnvironmental Impact Report
for the Castaways Marina. The proposed Castaways Marina site is located in the City
of Newport Beach north of the Coast Highway Bridge at the intersection a f Dover
Drive and Coast Highway. The proposed marina will consist of floating, p upported,
and land -base facilities. The- facilities will include restrooms, showers, trash and storage
containers, utilities, and two on -site fire hydrants. Caltrans District 12 has the
following comments:
Due to recent widening projects on Pacific Coast Highway (PCH); Calirans is concerned
with any project which has the potential to adversely impact a State Facility or worsen
local and regional traffic/circulation. It is necessary to reduce the traffic irnpact of the
proposed project during constructibn and after eoustructian on PCH to a level of no
significance. This can be achieved by implementing mitigation measures that would
counterbalance the adverse traffic impacts of this project.
Caltrans favors the Alternative 1.35 on page 1-8 from a safety stand point. The l benefits that would be achieved in using this alternative are more substantial than the H. C-2
J
other Alternatives presented.
In addition, an Encroachment Permit is required for any work within Caltraus Might of
Way. Consideration should be given to rclease'of the surface runoff from the project
directly towards the existing channel without reaching State Right 'of Way. ..The II. C-3
proposed project wiil'have. a negative impact on the Pacific Coast High y Bridge
mitigation measures. Offsets to these impacts should be addressed in the Final
Document.
116C
Patricia L. Temple
October 10, 1992
Page Two
We appreciate the opportunity to comment on this NOR If you should have any
questions concerning these comments, please contact Aileen Kennedy of my staff at
(714) 724-2239.
Sincerely,
Robert F. J , Ch f
Advance Planning Branch
cc: Howard Lee, Hydraulics
Jane Warren, Traffic Operations
Tom Loftus, OPR
Ron Helgeson, HDQTRS Planning
r
0
RECEIVED BY
STATE OF CAUFORMA-THE 730URCFS AGENCY PLANNINr, DFP-ApMAg PFE �+' =K G+—�
DEPARTMENT OF FISH AND GAME -COY OF NEWPORT BEACH
. P.o box NINs 2? OCT 2 11991
SACRAMENTO, CA 942442M AM PM
(•916) 653-7664 718191IDIu(12311218141516
October 15, 1991
Ms. Patricia L. Temple
City of Newport Beach
Planning Department
3300 Newport Boulevard
Newport Beach, California 92663
Dear Ms. Temples
scu ee091016 - Draft Environmental Impact.Report (EIR) for
the Castaways Marina, Newport Bay, Orange County
Department of Fish and Game personnel have reviewed the
subject EIR for the construction of a 125 slip marina in Newport
Bay. The project consists of the removal of an existing bulkhead
and construction of a new bulkhead wall, dredging of about
56,000 cubic yards of material behind existing bulkheads and
24,000 cubic yards from the bay, and the construction of a
floating dock system within the created marina basin and existing
• bay. Landside improvements consist of restrooms, showers, storage
facilities, parking area, and landscaping. Dredging will occur
after bulkhead construction and will be accomplished by hydraulic
dredge for in bay dredging and land based equipment for marina
dredging. Dredge material will be disposed of at either Coyote
Canyon Landfill or an approved ocean disposal site or a
combination of both sites.
•
The document provides an adequate description of the proposed
project and impacts to marine and terrestrial habitats and
resources. The proposed project will result in a loss of
0.28 acre of what has been identified as "halibut young -of -year
nursery habitat" (shallow subtidal habitat between -1.5 to
-3.2 feet mean lower low water (MLLW)) and 0.69 acre of mudflat
habitat between -1.5 to +2.5 feet MLLW. These habitat losses have
been identified as significant and mitigation for their loss would
be required. The applicant has indicated that mitigation will be II. D-1
provided at a 1.5 to 1 ratio. However, no specific mitigation
proposal, including monitoring, has been prepared and included in
the EIR. The applicant has initiated discussions with the
Department and other resources agencies regarding potential
mitigation sites within Upper Newport Bay, however; no site -
specific plan has been developed.
An area of concern, which has not been addressed in the Draft
EIR, is the potential exclusion of sport fishermen from existing II. D-2
shoreline areas within the project area. This issue should be
addressed in the Final EIR.
ILD
Ms. Patricia L. Temple
October'I5, 1991
Page Two
• In addition to the proposed project, the EIR provides an
analysis of various project alternatives including the no -project
alternative. Alternatives analyzed are:
1. 121 Boat Marina
2. 84 Boat Marina
3. 50 Boat Marina
4. Alternative project site locations within Upper and Lower
Newport Bay, West Newport/Newport Shores, Dana Point and
Huntington/Sunset Harbor
The applicant rejected all alternatives except the 121 Boat
Marina because they are either economically not feasible or
unavailable.
The-121 boat marina would reduce loss of mudflat from
0.69 acre to 0.34 acre, and halibut'young-of-year habitat from
0:28 acre to 0.21 acre. In addition, there would be a reduction
in the gain of halibut juvenile habitat from 2.96 acres to
2.50 acres. The project has been altered to include the
realignment of bayside boat docks and elimination of four boat
slips or side ties, reduction of dredging within Newport Bay, and
the construction of rock slopes (breakwaters) at the upper and
lower boundary of the boat basin. This alternative has been
identified as the environmentally superior alternative, however;
we would recommend a further -reduction of in bay dredging to
reduce impacts to mudflats by the elimination of boat slips from
that portion of the marina in the area of existing mudflats.
• Based on our analysis, the Draft EIR is deficient in its
discussion of mitigation to offset identified iiapacts, its
potential impacts to sport fishing within the project area, and
inasmuch as it fails to explore potentially feasible, less
environmentally damaging alternatives which would eliminate most
impacts to existing mudflats.
For the foregoing reasons, we recommend against certification
of the Draft EIR.
Should you -have any questions please contact Mr. Richard
Nitsos, Environmental Services Division, Department of Fish and
Game, 330 Golden Shore, suite 50, Long Beach, California 90802,
telephone (213) 590-5174.
cc: Mr. Richard Nitsos
Department of Fish and Game
Long Beach, California
0
Sincerely,
4,,,,J A Sc
Pete Bontadelli
Director
II. 0-3
.,,ATECFCAUFONNIA - RECEIVEL isY PETE WILSON. Gorornor
CALIFORNIA REGIONAL WATER QUALITY CONTROL BOARD CITY OF NEWPORT BEACH
SANTA ANA REGION
2010 IOWA AVENUE, SUITE 100 OCT 2 1991
ERSIDE, CALIFORNIA 92507-2409 P� �i
NE: (IER: 714) 7 0 718191101nI)2111213141M
TELECOPIER: (714) 781-6288
October 24, 1991 1
Ms. Patricia L. Temple
City of Newport Beach
3300 Newport Boulevard
Newport Beach, CA 92663
DRAFT ENVIRONMENTAL IMPACT REPORT (DEIR) FOR CASTAWAYS MARINA,
NEWPORT BEACH, ORANGE COUNTY, SCH # 88081016
Dear Ms. Temple:
We have reviewed the above -referenced report and note that the DEIR
addresses the principal area of concern to us, i.e., impacts to
surface water quality in Newport Bay associated with 'the
construction and operation of the facility including dredging and
dewatering. However, please note the following:
1. The proposed marina, including the parking lot and structures,
will" increase the impervious surfaces and the amount of
surface runoff. In accordance with the new stormwater
regulations published by the EPA in the Federal Register (40
• CPR Parts 122, 123, and 124), stormwater discharges from the II.•E-1
facility must comply with the NPDES permit requirements. The
DEIR has recognized these regulations, and we urge you to work
closely with the City of Newport Beach and the Orange County
Environmental Management Agency to minimize the impact on
water quality due to the increased stormwater runoff from the
project site.
2. The DEIR has identified the potential increase in the
turbidity and suspended sediments from dredging and excavation
activities associated with the project. A permit will be
required from this Regional Board for dredging activities. II. E-2
The permit will incorporate requirements for the protection
of the beneficial uses in accordance with the Basin Plan, the
California Enclosed Bays and Estuaries Plan (EBEP), and other
State and Federal regulations.
3. The discharge of any dewatering wastes will also require a
permit from this Regional Board. Again, the discharge of II. E-3
wastes to Newport Bay shall be in accordance with the EBEP
and other applicable regulations.
4. The toxicity tests with sediments from one of the test sites
indicated acute toxicity (page 5.4-7). The DEIR also states
that significant bieaccumulation of chemical constituents was II. E-4
found for both the marine worm and clam at all three test
• sites (page 5.4.9). It does not appear that these findings
have been fully addressed in the DEIR.
ILE
n
lJ
0
•
Patricia Temple
-2-
October 24, 1991
5. We note that specific facilities and policies to address the
potential for illegal vessel discharges are proposed by the
project .applicant. We commend the applicant for these
proposals, which are described on page: 5.4-11. These include
installation and routine maintenance of a vessel sewage H. E-5
pumpout station and certain conditions for use of the marina
to be included in lease agreements (prohibition of waste
discharges; requirement for holding tanks, etc.). We suggest
that these proposals be added to the list of mitigation
measures specified on pages 5.4-15 and -16 of the DEIR.
6. We commend the applicants' proposal to specifically prohibit
painting, scraping and other boat maintenance activities at H. E-6
the marina and to provide routine compliance oversight.
Again, we suggest that these measures be added to the list of
mitigation measures on pages 5.4-15 and -16.
We appreciate the opportunity to review this DEIR. If you have any
questions regarding these comments, please contact me at 714-782-
3238.
Sincerely,
Michael Adacakapara, Chief
Regulations Section
cc: Tom Loftus, State Clearinghouse
AEA17/4015nwpt.eir
RECEIVED BY
PLANNING DEPARTMENT
CITY OF NEWPORT BEACH
OF
OCT 15 1991 PM
G E 718191101i111E1 A3141 6
ENVIRONMENTAL MANAGEMENT AGENCY
OCT 0 9 1991
Patricia L. Temple
City of Newport Beach
3300 Newport Boulevard
Newport Beach, CA 92663
SUBJECT: DEIR for the Castaways Marina
MICHAEL M. RUANE
DIRECTOR, EMA
12 CIVIC CENTER PLAZA
SANTA ANA, CALIFORNIA
MAILING ADDRESS:
P.O. BOX 4048
SANTA ANA, CA 927n2-4048
TELEPHONE:
(714) 834-2306
FAX N 834-2395
mLE NCL 91-130
Dear Ms. Temple:
The above referenced item is a Draft Environmental Impact Report (DEIR) for the
City of Newport Beach. The project is located in the City of Newport Beach on
the Lower Castaways site. The site is immediately north of the Pacific Coast
Highway Bridge at the intersection of Dover Drive and Pacific Coast Highway.
The project will construct floating, pile -supported and land -based facilities,
which includes restrooms, showers, trash and storage containers, utilities and
two onsite fire hydrants, a public viewing area, 106 parking spaces and up to
125 slips of four different sizes. The County of Orange has reviewed the DEIR
resulting in the following comments:
BICYCLE TRAILS
The Master Plan of Countywide Bikeways (MPCB) identifies Route 55, a Class I
(paved, off -road) trail in the project vicinity. The EIR should address subject III. A-1
trail and linkage with Route 25, a Class I trail along Pacific Coast Highway.
OPEN SPACE/RECREATION
The proposed project will create a positive increase in regional recreational
opportunities within Orange County by providing new boat slips in Newport Beach III A-1
and public access to coastal areas through the construction of a public viewing
area.
Thank you for the opportunity to respond to the DEIR. If you have questions,
please call Rari Rigoni at (714)834-2109.
Very truly yours,
Joan Golding, Program Manager
Regional Coordination Office
By: c
isri A. Rigoni,.5r. P ner
CH:sp/vmPRCO2-27(1277)
1100409112570 I11,A
L"
CITY OF COSTA MESA
CALIFORNIA 9282&1200 P0. SOX 12°° RECEIVED BY
01 Am MINA DEPARTMENT
CITY OF NEWPORT BEACH
FROM THE OFFICE OF THE TRANSPORTATION SERVICES MANAGER
AM OCT 15 1991 PM
71819110,u,12111213141516
October 10, 1991
Ms. Patricia Temple
City of Newport Beach
3300 Newport Boulevard
Newport Beach, CA 92658-8915
SUBJECT: CASTAWAYS MARINA DRAFT EIR
Dear Ms. Temple:
The City of Costa Mesa has no comments regarding the ]III. B-1
traffic/circulation impacts of the Castaways Marina project.
Thank you for the opportunity to review the above -mentioned
document.
` Sincerely,
N
PETER NA VI
Transportation Services Manager
c
•
VSC:cv
III.B
77 FAIR DRIVE • (714) 754.5334
TERRELL WATT, AICP
PLANNING CONSULTANT
1757 UNION STREET
SAN FRANCISCO, CA 94123
(415) 563.0543
PAX (416) 463.8701
October 3, 1991
Patricia L. Temple
City of Newport Beach
Planning Department
3300 Newport Blvd.
Newport Beach, CA 92659-1768
RECEIVED BY
PLANNING DEPARTMENT
CITY OF NEWPORT BEACH
OCTAM 7 1991
1911DIll112111213141516
SUBJECT: Draft EIR for Castaways Marina
Dear Ms. Temple:
This letter is submitted on behalf of Stop Polluting Our Newport
(SPON) for the purpose of informing the City of SPON's concerns
related to the adequacy of the draft environmental impact report
(DEIR) for the proposed Castaways Marina project. The Draft EIR,
while a good initial attempt at exposing the issues relevant to
the proposed project, falls short of providing adequate
information to allow for an informed decision by the City in
numerous respects. Set forth below is a summary of the
deficiencies in the DEIR.
SPON, in submitting these comments incorporates by reference the
comments submitted by the Friends of Newport Bay.
INADEQUATE SETTING INFORMATION
The public trust is an affirmation of the duty of
the state to protect the people's common heritage
in streams, lakes, marshlands and tidelands,
surrendering that right to protection only in rare
cases when abandonment of that right is consistent
with the purposes of the trust." National Audubon
Society v. Superior Court 33 Cal.3d 419, 441 (1983)
At the foundation of an adequate analysis of environmental impacts
is a thorough description of the environmental setting. In this
case, an crucial piece of setting information has been omitted
from the DEIR; the extent of ,public trust lands and the
permissible uses under the grant of these lands and resources to
the county of Orange. This information is relevant for a number
of reasons:
1
MA
Patricia Temple
October 3, 1991
1. While the lands may have been granted to the County of
Orange, such granted lands are monitored by the State
Lands Commission to ensure compliance with the terms of
the grant. The land grant may be highly restrictive of
the permissible uses, and the extent of those uses, and
of the lands and resources. Absent this information,
it is not possible to determine whether the use proposed
is consistent with the public trust restrictions
governing those lands and resources.
2. Where competing public trust uses are- under
consideration (e.g. a marina vs. fishing and shoreline
recreation), the least environmentally damaging
alternative should be approved. No public trust use
should be approved which precludes an existing public
trust use, such as fishing or habitat. Without adequate
setting information, this choice cannot be properly
made.
3. Finally, the DEIR should contain a map which shows the
extent of the public trust lands and the upland area
affected by development of those lands. All existing
public trust uses should be described.
The State Lands Commission, a trustee agency, was missing from the
list of agencies contacted during the preparation of the DEIR.
This agency should be contacted immediately and included in the
dialogue about the appropriate uses for the property consistent
with the public trust. Also, the grant to orange County should
be described in the DEIR and the complete grant included in the
DEIR appendix.
IV. A-1
IV. A-2
Absent this information, the City cannot make a determination of
what are the uses permitted on the property. Even if a marina use
is permitted, if the impacts of that use on other public trust
resources or uses would be significant, the marina use should be IV
scaled back so impacts will be insignificant or the project
denied.
What is the justification for a DEIR rather than a joint EIR/EIS?
The DEIR identifies significant impacts of the project that are
related to the actions required of a number of federal agencies.
For this reason, SPON believes that the document should be a joint
EIR/EIS. If no EIS is being prepared, what environmental review
process will be completed for the federal permits and what is the
timing of that process? If a "Finding of No Significant Impacts"
A-3
�IV. A-4
IV. A-5
IV. A-6
0
Patricia Temple
October 3, 1991
("FONSI") is being prepared for the Federal actions, what is the
rationale for this given the significant impacts identified in the IIV. A-6
DEIR? JJJ
The impact analysis does not provide adequate information from
which decision makers may choose between the proposed project
alternatives. Specifically, the DEIR does not analyze the ability
of the Upper Newport Bay/Newport Bay to accommodate additional IV. A-7
marina development without significant negative impact on human,
ecological or water quality benefits associated with the.Bay; or
in other words, is the Bay's carrying capacity adequate for this
type and intensity of use?
While the discussion of water quality is a good start, the
discussion lacks adequate information to establish whether or not
(1) the Bay (Upper and Lower) is already at capacity for this
type of use and (2) this use would exceed the Bay"s carrying
capacity. Attached is a Carrying Capacity Analysis completed for
the Sacramento River Marina by the State Lands Commission. SPON
submits this study into the record as an example of the type of
analysis required for the DEIR to be considered adequate.
In addition, the conclusions reached in the DEIR that virtually'
all Aroiec =r fated impacts are insignificant or reduced to a
level of insignificance after mitigation are not supported by
evidence in the record. Specifically, how are the water quality
and biological impacts found to be less than significant? For
example, loss of any mudflat habitat, even if replaced, is
significant. In this case, the efficacy of the mitigation measure
is completely unknown since the "replacement plane has not yet
been developed and there is no known site that will suffice for
"replacing" or creating new habitat of this kind.
IV. A-8
IV. A-9
The lands proposed for this development belong to the public. As
such, SPON believes that if the project will result in significant
effects or contribute to cumulatively significant effects, the IV. A-10
project as proposed should be denied.
This property is part of the public trust. As such, other public
trust uses should be evaluated for the area. such uses could
include other types of public recreational uses including fishing
and swimming. SPON believes that the alternative use of a IV. A-11
swimming and fishing beach with associated support facilities
upland should be evaluated for comparative impacts to the proposed
project. Such a use would not require dredging and other
L
•
•
•
Patricia Temple
October 3, 1991
disturbance associated with the project.
The analysis of the alternatives is cursory and should be expanded
pursuant to the carrying capacity analysis called for above. In
addition, SPON could find no evidence in the record to support the
applicant's contention that the alternative marina's with fewer
boat slips were infeasible. In the absence of financial
information which demonstrates such reduced projects are in fact
infeasible, CEQA provides that the environmentally superior
project that meets most project objectives must be adopted. This
is inherent in the action -forcing provisions of CEQA. SPON looks
forward to reviewing the applicant's data related to project
feasibility.
The analysis of off -site alternatives is inadequate. It is not
sufficient to provide bare conclusions about the suitability of
alternative sites. In the absence of even a map of these sites,
the public cannot review the sufficiency of the statements at page
1-8 regarding the alternative sites. The DEIR must include
comparative information about the specific sites purportedly
analyzed so that the public can review this information. In light
of the significant effects of the project and the severity of this
deficiency, the DEIR should be recirculated once the information
has been provided.
Absent from the project description are the following items:
1.
The number
of
livaboards or the deed restriction that
will preclude such use; (note: livaboards may not be a
permissible
use)
2.
Provisions
for
public access to the area;
3.
Provisions
for
recycling;
4.
Provisions
for
waste disposal;
5.
Details of
the
drainage plan;
SPON assumes that each of these aspects of the project will
require environmental analysis at some point in the future if not
presented in the DEIR at this time.
J IV. A-11
IV. A-12
IV. A-13
IV. A-14
•Patricia Temple
October 3, 1991
r
•
MI SPISIMN 0 ZW616V0)
The study area for the cumulative impact analysis is inadequate
and therefore the list of cumulative projects fails to include
projects that are likely to contribute to cumulative impacts. I.V. A-15
This in turn resulted in an inadequate discussion of cumulative
impacts with respect to water quality, among other impacts.
Specifically, the project study area appears to include only those
projects directly adjacent to the Bay in Newport Beach. Projects
outside of Newport generate runoff into the Bay. Such projects
include but are not limited to the San Joaquin Hills
Transportation Corridor, projects in Irvine and Santa Ana within IV. A-16
the watershed of the Bay. Runoff from development in these areas
will also contribute to the degradation of water quality in the
Bay and must be considered in the cumulative analysis.
The DEIR should be revised to include a study area for water
quality impacts that includes the area of runoff into the Bay at IV. A-17
a minimum. The cumulative analysis should be based on this study
area.
A number of key mitigation measures, relied on to reduce
significant impacts to a level of insignificance are not true
mitigation measures, but simply future plans or studies. These
include the following:
1. A detailed conceptual mitigation plan for the loss of
the 69 acres of mudflat habitat. (It is unknown
whether there are any sites where true new habitat can
even be created).
2. A detailed conceptual mitigation plan to replace the
halibut nursery habitat. See above comment.
3. A landscape and irrigation plan. (This plan should be
part of the project description and its impacts analyzed
as part of the project since runoff from the site could
impact the public trust resources. Also, why are grease
traps not required as mitigation pursuant to the new EPA
NPDES regulations? This issue must be analyzed in the
DEIR and is not.)
4. Grading plan and soil engineering reports.
5
IV. A-18
•Patricia Temple
October 3, 1991
i
•
These plans will not be subject to public scrutiny contrary to
CEQA. They should be completed and evaluated in a recirculated IV. A-18
DEIR.
Also, it is not apparent how the effect of an accidental spill IV. A-19
can be reduced to a level of insignificance. If a spill happens,
the impacts will be significant.
We appreciate this opportunity to comment on the proposed marina.
Please keep this office informed of upcoming hearings on the
project.
L'
Very truly yours,
W&--
Terry Watt
FRIENDS OF NENPORT BAY
•P. 0. Box 2001
Newport Beach, CA 92663
LJ
Patricia L. Temple
City of Newport Beach
Planning Department
3300 Newport Boulevard
P. 0. Box 1768
Newport Beach, CA 92659-1768
RECEIVED BY
PLANNING DEPARTMENT
CITY OF NEWPORT BEACH
Aft OCT 41991
7i819i@iui12I1I2A41516
SUBJECT: Castaways Marina, Draft Environmental Impact Report.
The board of directors of Friends of Newport Bay (FONB) of which I am a member
has asked me to review the Draft Environmental Impact Report (EIR) of the pro-
posed Castaways Marina on their behalf. FONB was founded 24 years ago to pre-
serve and protect Upper Newport Bay. Since 1968, the Friends have presented
environmental tours as a free public service during the migratory season.
Thousands of people, of all ages, have attended these tours, the purpose of
which is to educate the citizenry regarding this critically important estu-
arine ecosystem, including how to enjoy it without ruining it. FONB has a
membership of approximately 1500 people, most of whom are local residents.
While we recognize that the EIR is directed toward the details of the pro-
posed marina, the project raises issues that involve the public policies of
the city of Newport Beach, the county of Orange, the California Department
of Fish and Game and other governmental agencies. Therefore, in the absence
of a more suitable forum, we will address these issues so that more informa-
tion will be available to everyone as this project moves through the reviewing
process.
THE CITY OF NE47PORT BEACH
AND THE COUNTY OF ORANGE
ARE REQUIRED TO MANAGE THE TIDELANDS
IN ACCORDANCE WITH THE STATE GRANTS
AND ARTICLE X OF THE STATE CONSTITUTIO
Early in this century the city of Newport Beach and the county of Orange re-
ceived tideland grants from the state legislature. The county of Orange was
authorized to develop a harbor in mm at no public expense. Both the county
and city agencies are required to conform to the common law tidelands trust
as stated in Article X of the state Constitution. This protects the public
rights in the tidelands for commerce, fishing, navigation and access. These
rights evolved from the Greek philosophers over 2,000 years ago.
In 1970, the Supreme Court of the state of California included ecology and
education as proper uses of the tideland trust. This ruling provided the
basis of a 1975 state law that established the Upper Newport Bay State Eco-
logical Reserve. Article X applies as well to all of the tidelands outside
the ecological reserve.
IV.B
2) Friends of Newport Bay - Castaways Marina, Draft EIR
THE PROPOSED MARINA
• DOES NOT CONFORM TO
THE PUBLIC POLICY
OF THE CITY OF NEWPORT BEACH
The city of Newport Beach permits waterfront home owners to build
piers in front of their property limited to the extention of the
property lines. This policy allows property owners to build piers
up to the width of their property.
The proposed marina has a land frontage of approximately 450'
However, the piers proposed for the marina extend approximately
1,000' along the waterway, approximately 550' more than the amount
permitted by city policy. Most of the proposed piers are well out
in the public water away from the marina property.
We believe that the marina proposed by California Recreation Com- IV. B-1
pany should be limited to the 450' width of their property in
keeping with public policy so that the remaining tidelands can
be managed in the spirit of the tidelands trust for the purposes
of commerce, fishing, navigation, access and recreation. A larger
marina to increase the income of the California Recreation Company
hardly qualifies as a compelling public benefit.
THE U.S. BULKHEAD
AND PIERHEAD LINES
DO NOT EXIST
• Exhibit 3-3 showing the locations of the U.S. bulkhead and U.S.
pierhead lines is in error. These lines do not exist.
Many years ago the Orange County Board of Supervisors adopted
bulkhead and pierhead lines in anticipation of a land trade pro-
posed by The Irvine Company. The lines never were adopted by the
U.S. Corps of Engineers. When the proposed land trade was aban- IV. B-2
doned, the lines were removed by a Minute Order of the Board of
Supervisors.
If this project is to be considered, bulkhead and pierhead lines
must be adopted by the county and be approved by the U. S. Corps
of Engineers. Any new harbor lines in this area must meet the
U.S. Corps of Engineers requirements.
CHANNEL CONSTRICTION
NORTH OF THE BRIDGE
Condition Width
1) No marina (present condition) 450'
2) With proposed marina 300'
3) With the old proposed bulkhead 550'
lines (abandoned by the Board of
• Supervisors)
3) Friends of Newport Bay - Castaways Marina, Draft EIR
Without the approved bulkhead and pierhead lines, it is unclear
• to me whether or not this project can proceed through the re- IV. B-3
view process.
in addition, this project fronts on and is in the tideland grant
to the county of Orange. Therefore, does the city of Newport IV. B-4
Beach have the authority to approve or disapprove the pier sys-
tem of this project?
It is clear from the bulkhead lines, originally proposed by the
county, that a wider channel was preferred. This project re- IV. B-5
duces the effective width of the channel to approximately one-
half of the proposed channel width.
PUBLIC RECREATIONAL FISHING
WILL BE DEGRADED
There are approximately 31.5 miles (166,3001) of waterfront in
all of Newport bay. In the lower bay, there are 10 public piers
available for fishing. These piers represent less than 400'
available for fishing without a boat. The last significant
shoreline beaches are in UNB. One is located at North Star
Beach but was significantly impacted when the aquatic center
was built. The other location is below the Castaways next to
the site of the proposed marina pier extension. This beach is
one of the finest fishing beaches on the southern California
. coast because all fish entering or leaving UNB must pass this
area. It is known that over 70% of the ocean's fish must spend
part of their life cycle in an estuary such as UNB.
The piers would impact severely 600' of the 1800' now available
for shoreline fishing. Since the tideland trust protects the IV. B-6
public's right to fish, the marina should not extend beyond the
land property line of the marina.
MITIGATION
Dredging at the marina site in the channel will remove signif-
icant amounts of mud flats. The EIR suggests that the lost mud
flats be replaced by dredging in UNB. Some parts of Shellmaker IV B-7
island in the ecological reserve are being considered. I do not
think that any part of the ecological reserve or any other part
of UNB should be considered for this purpose. This rich, diverse
endangered environment became a state ecological reserve in 1975
as a result of the efforts of thousands of people nationwide, the
unanimous support of all members of the state assembly and state
senate, all governmental committees, the governor and an expend-
iture of $3.48 million. An additional $13,000,000 was appropri-
ated later for the restoration of the UNB.
The intent of the legislature is clear. The UNB shall remain a
• state ecological reserve in perpetuity. It shall not be destroyed
4) Friends of Newport Bay - Castaways Marina, Draft EIR
by being converted into a vehicle existing merely to provide
• handy mitigation. If this happens, the reserve will be digested
bite by bite and all of its interrelated flora and fauna will be
exterminated. The thousands of children and adults who now enjoy
it and love it will be the losers.
In the past, conventional wisdom held that the best use of wet-
lands and open water was the conversion of these resources to
boat related activities. As a result, Newport bay is now the IV. B-8
world's largest small boat harbor with 10,500 boats. When is
enough enough?
The EIR includes the marina basin dredged area (6.99 acres) as
compensation for the loss of open water foraging for birds and
bottom foraging for fish. This area should not be considered
since the area principally is to be covered by boats and docks
bringing pollutants such as the poison from bottom paints and
other chemicals. It also is likely there will be a siltation
problem similar to that in Dover Shores.
This proposal in no way compares to an open channel, flushed
and cleaned by tidal currents.
RECOMMENDATIONS
We recommend that a modification of the 84 boat
instead of the 125 boat marina, the modification
limiting the pier to the frontage between the pr
(450'). This marina configuration will have a
on the ecology and public fishing rights in UNB.
Respectfully,
Frank
Friends of Newport Bay
0
IV. B-9
marina be built
consisting of
operty lines IV. B-10
minimum impact
ea P.O. BOX 25 SANTA ANA. CA 92702
- - Audubon
RECEIVED BY
PLANNING DEPARTMENT
4age
CITY OF NEWPORT BEACH
•
•
October 6, 1991
Patricia L Temple
City of Newport Beach Planning Department
3300 Newport Boulevard
Newport Beach, CA 92659-1768
SUBJECT: Comments on Castaways Marina Draft EIR
Dear Ms. Temple;
After review of the subject EIR, we have several
major concerns are for the environmental health
Newport Bay Ecological Reserve. These are given
order or priority:
AM OCT 91991
718191100164112131415 6
A
comments. Our
of the Upper
in no particular
i. The long pier planned for the main channel would have
significant potential to increase pollution in the upper bay.
While waste discharges are not permitted in the harbor,.it is well
known that they do occur, and enforcement.of the law has been
difficult. Coupled with this is the chance for accidental
discharge of fuel -and oil. Because this pier borders the main
channel a flood tide could easily distribute wastes and IV. C-1
hydrocarbons.over the entire ecological reserve in just a few
hours, well before any containment response could be organized.
This is a highly dangerous situation which dictates removal of
this long pier from any project plan.
2. All alternatives listed for this project are clearly
described as having less short term and long tl?bm environmental
impacts than the proposed plan. The 84-Boat Marina alternative has
the smallest pier and therefore the least impact on the chances IV. C-2
for disastrous pollution of the upper bay. Why is there no
alternative described using only the Lower Castaways basin, with
no protrusion into the main channel?
3. The only mitigation measures offered for the dredging
activity period seem to be that proper permits will be obtained
from the Army Corps of Engineers, the Environmental Protection IV. C-3
Agency, etc. Except for screening to reduce turbidity (as
feasible) the mere approval of these agencies does not give
confidence that the effects of dredging will be insignifcant.
IV.0
t
n
0
4. At several points mitigation for mudflat and halibut
habitat removal is offered, suggesting that this will, or may,
occur within the upper bay. This plan contains the possibility of IV. C-4
further heavy activity in the Ecological Reserve, and while not
impossible, should be approached with extreme caution and approval
of the California Department of Fish and Game.
S. We feel the disposal activity of dredged'materials would
be least damaging if the ocean disposal were to be used IV. C-5
exclusively, removing the impacts on the local neighborhoods and
the Upper Castaways site.
Thank you for the opportunity to comment on this report, and your
review of our comments.
Sincerely,
'-f, hl�ok
Richard E. Kust
for the Conservation Committee
6101 NEWMAN, SUITE C
hvNTINGTON BEACH, CA 92647
0
JAN D.'VANDERSLOOT, M.D.
DIPLOMAT£ A"fAICAN DOAA00! DEAMATOLOOY
2221 East 16th Street
Newport Beach, CA 92663
October 7, 1991
Patricia Temple
Principal Planner
City of Newport Beach
P.O. Box 1768
3300 Newport Blvd.
Newport Beach, CA 92659-1768
Re: Castaways -Marina EIR
Dear Ms. Temple,
(7141848.0770
RECEIVED BY
PLANNING DEPARTMENT
PITY OF NEWPORT BEACH
AN OCT 10 1991 FM
7181911DIU112111213141516
Enclosed are my comments relative to the Draft EIR for the above project.
Further alternatives should be discussed in the EIR:
1. A%traffic signal, temporary or permanent, should be considered for the entrance
into the project site; without connecting to Cliff Drive. This signal would.be
3-way, would not require a cut into the bluff facing Dover Drive, would obviate IV. D-1
the need for the destructive temporary road across the Upper Castaways, and
would allow the trucks hauling material away from the site easy access to PCH.
Therefore,,there would be no adverse impacts to Cliffhaven or Newport Heights.
2. Ways to remove the "temporary" road'across the .Upper Castaways should be more
thoroughly considered. An alternative is to haul the material up Irvine Ave. to �IV.
D-2
the Coyote Canyon Land Fill, thus not requiring the trucks to make a U-turn on
Dover or cisc9't above on the temporary road to get back down to PCH.
3. A "Minimum Grading Alternative" should be discussed in the EIR. The less
grading, the fewer trucks are needed to haul the -..material away. Such a plan'
IV. D-3
would mean no:.temporary road, no cuts into the bluff, no high retaining walls
.along.Dover, minimum dredging of the bay.
4. A 60 space marina with no floating ducks protruding into the bay should be
I analyzed. The floating docks appear.:to:.disturb.;current flow into and out of the
bay north of the bridge (see Hydrology Study, Appendix E, Figures 5,6,7,8).
IV. D-4
An alternative without docks protruding into the bay is not present in the EIR.
5. An asialysis of shoreline erosion of the bay below the Castaways bluffs should
be in the EIR. Flood current (high tide) and ebb current (low tide) both will act
IV. D-5
to scour'the shoreline, increasing erosion of the shore (again, see Appendix E,
Hydrology Study, Figures 7 and 8, Noble Consultants).
r
6. Exactly where the temporary road will go on the Upper Castaways, as well as
where the dredge spoils will be dried out on the Upper Castaways should be in the IV. D-6
EIR.
. 7. The plans of the Irvine Company to dedicate .the "nose" of the Castaways for
open space as part of its Open Space and Circulation Development Agreement should
be in the EIR. Portions of the "nose" appear to be negatively impacted by this IV. D-7
project, including grading of the bluffs, the temporary road, the drying out
site for dredged material. The EIR lacks assessment of the cumulative impacts of 1V.^
JAN D. VANDERSLOOT, M.D.
. DIILOMATE AMCnICAN DOAnO Of OCDMATOLOGY
Pat Temple
6101 NEWMAN, SUITE C Castaways Marina EIR (7hj6t6•oT70
UNTINGTONBEACN,CA9t6+T October 7., 1991
page-2
this project on the Upper Castaways and its ecologic resources.
8. The project EIR.lacks a cumulative impacts assessment on.the communities
of Cliffhaven and Newport Heights. Specifically, if a signal is placed at Dover
and Cliff, through traffic may increase on Cliff Drive, especially as•traffic
IV. D-8
increases on PCH as a result of the other large projects planned in the general
area, including the Hoag Hospital expansion, and the West Newport Oil project
at the Santa Ana River Mouth.
9. The Water Quality section does not appear to address the question of long
term pollution of the bay, especially the Upper Newport Bay ecologic -reserve,
because of oil, grease, and gasoline discharged into the bay as a result of
operating motor boats. These pollutants will be directly swept into the Upper
at high tide.
IV. D-9
Bay because of the floating dock protruding into fhe flood current
26 March 1990,
- This question was ibkdd by the City's CEQAC's Subcommittee on EIRS,
as well as other questions by CEQAC, but which were not answered in the EIR.
10. A coastal bluff along Dover exists. The EIR does not appear to recognize
�(
the City's coastal bluff protections in the General Plan or LCP, Applicability
IIV. D-10
of the Coastal Bluff' ordinances to this project should be in the EIR.
J
11. Two wetlands appear to be impacted by this project: the wetlands containing
halibut nurseries in the Bay, and wetlands along Dover which may be impacted
the
IV. D-11
' by the temporary road, Because of the signifidance of Upper Newport Bay to
regional environment, the US Fish and Wildlife Service should have been notified
in the EIR.
and comments solicited. There is no evidence that USFWS was notified
12. Because of the potential current changes induced by Chid project, the US Army
this project.
Corps of Engineers should be more completely informed of the scope of
in the tidal" prism
A modelling study of shoreline erosion, and possible changes
bridge, should be'.doue by the
IV. D-12
entering the Upper Bay north'of the Coast Highway
Corps before this project is considered by the City. This project affects navigable
` waters::and may affect navigation into and out of the Bay, affecting Dover Shores
and'the Dunes -Aquatic Park.
13.•There should be a discussion of the permitting agencies involved in the
approval of this project, including applicable sections of the Coastal Act and
IV. D-13
Section 404 of the Clean Water Act:
14. The project Daiy.bxaviolation of the Tidelands Public Trust administered by
the State. It appears to turn public tidelands into a private venture. A discussion
the State
IV. D-14
of the tidelands ramifications should be in the EIR. The position of
in the EIR.
.be
Lands Commission should more thoioughly researched than what is stated
15. Halibut habitat' for juveniles appears to be mitigated under the boats in the
it appear that
marina. Is this mitigation acceptable to the resource agencies? would
thins
IV. D-15
pollution from the boats, oil, gas, paint, and the frequent dredging of
make this area an
area due to acknowledged siltation of the marina, would not
acceptable mitigation site for juvenile halibut.
1101 NEWMAN, SUITE C
WNTINGTON BEACH, CA 916/1
JAN D.'VANDERSLOOT, M.D.
D)PLOUA,[ AMCMCAM SOAAD O, D[nMAYOLOGY
Pat -.Temple
Castaways Marina EIR 1714184e•0770
October 7, 1991
page 3
16. A desire to mitigate the halibut nursery somewhere in Upper Newport Bay is
expressed in the EIR. Exactly where it is intended to be mitigated should be is
the EIR, since the'rest of Upper Newport Bay is itself sensitive habitat. Mitigating IV. D-16
into an already high value wetland would result in the net loss of wetlands
which is contrary to state policies and law.
` 17. An alternative showing a publicly useful marina-, such as a ramp for trailers
for small boats, should -be in the EIR, since the land is publically tidelands and
should have public access. Such an alternative would require the least amount of IV. D-17
dredging and would cause the least amount of environmental damage, yet be consistent
with the City's desire for a marina there.
18. An effort to identify possible ways to'transfer the site to.public ownership
should be in the•ETA. Such a transfer would be most consistent with the effort IV. D-18
to transfer the whole of the Castaways to public ownership, and would be
the most consistent with keeping the nose of Castaways as natural open space.
Sincerely-, /
Jan D. Vandersloot, MD
9
kEGt1YLU DI
L VNING DEPARTMENT
Ty OF NEWPORT BEACH
N #T . 8 1991 PM
I1201011111211121 A516
Octobel 7, 1991
Ms. Pat Temple
Advanced Planning Manager
CITY OF NEWPORT BEACH
3300 Newport Blvd.
Newport Beach, CA 92663
Dear Pat:
It was a pleasure to meet with you and Jerry King last week
regarding the proposed marina development at the Lower Castaways
site. As we discussed, the Cliff Haven community has a number of
concerns relative to the development of both the Upper and Lower
Castaways site. Our "position paper" regarding the Upper
Castaways site was drafted and circulated this spring; I will
forward a copy to you shortly. our concerns regarding development
of the Lower Castaways site are listed below.
It is our understanding that, as part of the development of Lower
astaways, a traffic signal will be installed at the intersection
f Cliff and Dover Drives, and Cliff Drive will be extended into
the proposed marina project. While we welcome the idea of
crosswalks across Dover to provide access to both Lower and Upper
Castaways, we also fear that a traffic signal will inevitably
create more traffic up Cliff Drive and the closest arterial
outlet streets (Kings Place and Signal Road).
Therefore, we request that the following mitigation measures be
incorporated concurrently with installation of the traffic signal
and extension of Cliff Drive:
a. The timing of the left -turn signal should be infrequent
enough that traffic is discouraged from making left
turns onto Cliff from northbound Dover, thereby IV. E-1
negating any time saving that this "shortcut" might
otherwise provide. We do not want Cliff Drive to pick
up PCH traffic.
b. The signal should default to a green light in each
direction for Dover Drive traffic -- this should be the
signal's normal position. Only when significant
traffic accrues should the light change to stop traffic IV. E-2
from freely flowing on Dover. This not only helps with
a. above, but also will eliminate any potential backup
of cars on Dover, at the Cliff/Dover intersection (we
are especially concerned about backed up traffic on
southbound Dover).
IV.E
Page two
C. Speed bumps should be installed along Kings Place and '
Signal Road, between Cliff Drive and 15th Street. This
will not only discourage people trying to make a
shortcut from PCH to the Newport Heights area (Newport
Beach and Costa Mesa), but will also help to reduce the
existing problem Kings Place and Signal Road residents
are experiencing with speeders. Further, "SLOW -
IV. E-3
Children at Play" signs should be posted on these
streets. We welcome your suggestion of designing signs
that are of more architectural interest (and thus more
likely to be read) than the standard yellow diamond
signs.
d. A sign indicating "PCH - that -a -way" should- be
installed at the intersection of 16th Street and Irvine
IV. E-4
Avenue, so that PCH-bound vehicles do not proceed all
the way to Cliff Drive.
e. Crosswalks should be incorporated into the signal
design for the Cliff/Dover intersection. Ideally,
crosswalks should be located across all four corners of
IV. E-5
the intersection. If only three crosswalks are
designed, the crosswalk across Dover should be located
on the north end (i.e., connecting the medical offices
to the access to Upper Castaways).
f. The requisite bluff retaining wall for the extension o
Cliff Drive must be constructed in such a way as to
minimize the block' effect of such a massive
structure. Ideally we would like to see a series of
gradual setbacks, each landscaped in harmony with the
IV. E-6
proposed landscape plan for the marina/P B & R's plans
for the view park on Upper Castaways. Additionally,
pedestrian areas to the Upper Castaways should be
incorporated into the overall design. our community
should be involved in this architectural process as it
develops.
g. Finally, the existing public walkway appearing on the
Cliff Haven tract map that I pointed out to you during
our meeting should be developed to provide access to
the Castaways site for Cliff Haven residents. A
significant number of our residents would have much
greater access to both Lower and Upper Castaways were
this existing public land to be used for the purpose
IV. E-7
intended. Obviously, given the heavily treed, rustic
flavor of the area, the public walkway should respect
the existing landscape and conform ac much ae poasible.
Jerry King informed me today that he has already begun
exploratory discussions with the City and The Irvine
Company regarding development of this walkway.
• Page three
Pat, we sincerely appreciate the time and energy you and your
staff have already invested in the proposed development of the
Castaways site. As we all know, a great deal of work lies ahead.
We are hopeful that through the participatory planning process
that has evolved in three invipient stages, the development of
Upper and Lower Castaways will become a model for future
processes and projects.
I, or other members of the Board of Directors of the Cliff Haven
Community Association, am available to meet with you and/or other
officials regarding this proposed project. Please do not
hesitate to contact us should you desire further clarification of
our concerns.
Thank you for this opportunity to comment.
Sincerely,
wl-t: lled Q
Mark G. Hoglund
Vice President
Cliff Haven Community
Enclosures
xc: Al Beaudette
Jerry King
Tom Redwitz
0
Association
10/04/91
Pat Tample,
James Rociuba
2215 Sixteenth St -
Newport Beach,CA
(714) 646 - 6625
I have reviewed the Castaways Marina Draft EIR's traffic
` circulation element, and feel additions need to be made.
1) The draft calls for a temporary road that extends from Dover
Drive and Sixteenth Street to the marina area. This road,was
deemed necessary to allow Coyote Landfill bound dirt hauling
tracks leaving the marina development site to access PCH without
making a U-turn on Dover Drive. Alternatly, the trucks could
leave the development site's primary oatrance headed north on
Dover Drive, turn left on Westeliff Drive, turn right on Irvine
Ave., turn right on Bristol, then proceed to the Coyote
Landfill. This scheme eliminates the U-turn in question, therby
eliminating the used for the temporary road. This dirt hauling
. option needs to be examined.
2) Why does the Upper Castaways development concept have a permanent
access to the temporary road? Since the Castaways Marina site
is to be developed long before the Upper Castaways site, the
Upper Castaways site does not need permanent access to the
temporary road. Does the Upper Castaways permanent access to
the temporary =cad mean the temporary road in the Castaways
Marina draft EIR is not temporary?
3) If the temporary road is built, when will the temporary road be
permanently closed?
4) when the temporary road is closed, what will it be permanently
replaced with and when?
5) The Irvine Ave. and Wastcliff Drive intersection, along with
the Irvine Ave. and Sixteenth Street intersection, will be
impacted by the Castaways Marine development- This impact
needs to contained in the EIR.
6) Finally, the trattic impact needs to be analyzed on Costa
Mesa's East Sixteenth Street between Newport Blvd. to
Irvine Ave. This is a residential street segment that is
not on the county's master plan of highways, and whose
residents are sensitive to traffic increases due to this
ma=ina development.
please answer all six issues in the EIR. If any issue is vague or
unclear, contact me by phone or mail.
IV. F-1
IV. F-2
IV. F-3
IV. F-4
IV. F-5
IV. F-6
IV.F
CITY OF NEWPORT BEACH
EO. BOX 1768, NEWWRT BEACH, cA 92659-1768
ENVIRONMENTAL QUALITY AFFAIRS
EIR SUBCOMMITTEE
September 2011991
COMMITTEE
gust 1 comments Volume I aways Marina Draft Environmental impact Report,
Of 11-
1.. The 121-boat alternative significantly.reduces concerns regarding 6-3)]Iv, G_1
wetlands destruction, primarily due to the reduced dredging. (•
2- Traffic safety requires signaiization.of the project entrance at Dover IV. G-2
Drive/Cliff Drive intersection. (6-9)
3. Timing of the construction should be carefully planned to cause least �
disruption to the reproductive cycle of the birds and -fish. Iv. G-s
• (Tables 1.21, 5.4-4). -
4. Attention should be given to changing "could" to "should" in the last
paragraph regarding aesthetic impact of the Alternative Site Access IV. c 4
Design. (6-9)
May Lou Zoglin, Chairperson
EIR Subcommittee
i and Lue rs, Chairman
Environmental Quality Affairs Committee
3300 Newport Boulevard, NewportBeach
IV.G
aBAYSHORES COMMUNITY ASSOCIATION
2889 Bayahore Drive, Newport Beach, California 92863
r
A4i
September 25, 1991 718191101i-;ry; �S_n.�F
• ,J
Ms. Patricia Temple
City of Newport Beach
3300 Newport Blvd.
` Newport Beach, CA 92663
Re: Castaways Marina
Draft EIR
Coast Highway & Dover Drive
Dear Patty:
The Board of Directors of the Bayshores Community Association has met and
reviewed the Draft EIR on the Castaways Marina project.
The Board has voted to approve the project with the condition that the
• alternate access plan as detailed in Section 6.4 of the EIR be incorporated
into the overall project. This requires the entrance of the marina to IV. H-1
be located at the Cliff Drive extension to Dover Drive with the development
of a new access road.
Should you require any further information or clarification, please feel
free to give me a call at (714)833-7657.
Very truly yours,
BAYSHORES COMM,,UU�NNITY ASSOCIATION
Kevin M. Green
President
KMG:pt
cc: Christine Padilla
Jack Teal
•
IV.H
B. CONCEPTUAL BIOLOGICAL MITIGATION PLAN FOR LOSS OF MUDFLAT
AND SHALLOW SUBTMAL HABITAT
~BIOLOGICAL -' MI
TIGATION
OFM
Oss" '* UDF
DRTHEL
4,f,(
LLM'. U BTI DAL HABITAT...
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sways a n
IF"
rnnm6n MD 11 dcf Repo
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p
ASSOCIATES
OCrOBER 9,
1991,
DRAFT CONCEPTUAL BIOLOGICAL MITIGATION PLAN
FOR THE LOSS OF MUDFLAT AND SHALLOW SUBTIDAL HABITAT
CASTAWAYS MARINA
ENVIRONMENTAL IMPACT REPORT
State Clearinghouse #88081016
Prepared for.
Michael Brandman Associates
2530 Redhill Avenue
Santa Ana, California 92705
(714) 250-5555
Contact: ]EL Lee Jones
Director, Resources Management
L I
Prepared by:
EIP Associates
80 South Lake Avenue
Suite 600
Pasadena, California 91101
(818) 568-1363
Contact: Robert R. Ware, Senior Associate
October 9, 1991
•
TABLE OF CONTENTS
Section
Page
1 INTRODUCTION....................................................
1-
1.1 Objectives and Goals of the Draft Conceptual Mitigation Plan ....................
1.2 Document Organization ............................................... 1-1
2 CASTAWAYS MARINA OVERVIEW ..................................... 2-1
3 PROPOSED MITIGATION AREA ........................................ 3-1
3.1 Site Selection......................................................
3-1
3.2 Site Description.................................................... 3-1
3.3 Existing Condition ................................................. 3-2
4 PROPOSED AND ALTERNATIVE CONCEPT DESIGNS ...................... 4-1
4-1
4.1 General. ................................................
•
4.2 Proposed Habitat Design ..............................................
4-1
4-1
4.3 Alternatives.......................................................
•
5 OPPORTUNITIE4 AND CONSTRAINTS ASSOCIATED
WITH THE PROPOSED PROJECT .......................................
5-1
5-1
5.1 Opportunities ......................................................
5-1
5.2 Constraints.......................................................
6 PROJECT TASKS .................................................... 6-1
6.1 Agency Coordination ................................................ 6.1
6.2 Preparation of Final Conceptual Design 6-1
6.3 Permitting 6-1
6.4 Construction Level Specification ........................................ 6-1
6.5 Salt Marsh Transplant ................................................ 6-1
6.6 Habitat Construction ......................................... 6 ....... 6-2
6.7 Post -Construction Topographic Survey .................................... 6-2
6.8 Monitoring and Habitat Restoration Evaluation .............................. 6-2
7 PROJECT SCHEDUL NG.............................................. 7-1
i
TABLE OF CONTENTS (continued)
• 8 PROJECT STAFF ......... ..................... ..................... 8-1
9 PERSONS AND AGENCIES CONSULTED ................................. 9-1
10 LITERATURE CITED ................................................ 10-1
n
U
0
LIST OF TABLES
Table
Pape
2-1 Estimated Dredging Requirements For Shallow Subtidal and Mudflat Impacts
forAlternative Marina Designs ......................................... 2-3
4-1 Alternatives to Proposed Project Design ................................... 4-3
5-1 Existing Habitats in the Project Area and Projected Losses
of Each Habitat Type ................................................ 5-2
iii
I•
I•
LIST OF FIGURES
Emm Pao
2.1 Project Vicinity Map ................................................. 2-2
3.1 Shellmaker Island and Proposed Mitigation Site .............................. 3-3
3.2 Habitat and Vegetation Types .......................................... 3-6
4.1 Proposed Habitat Design .............................................. 4-2
4.2 Plan View of Proposed and Alternative Designs .............................. 4-5
4.3 Alternative 1 Habitat Design ........................................... 4-6
4.4 Alternative 2 Habitat Design ........................................... 4-7
LIST OF APPENDICES
Appendix
1 Partial Topographic Survey Map of Shellmaker Island
iv
0
L INTRODUCTION
Ll OBJECTIVES AND GOALS OF THE DRAFT CONCEPTUAL MITIGATION PLAN
The Draft Conceptual Mitigation Plan has been prepared to augment the Castaways Marina Find ML
The objective is to design a conceptual mitigation program that meets county, state, and federal guidelines
for the no net loss of in -kind habitat resulting from the removal of intertidal mudflat and shallow subtidal
fishery babitat at the proposed Castaway Marina site. The mitigation plan goal is to restore mudflat
habitat for use as shorebird foraging habitat and shallow water nursery habitat for young -of -the -Year
(YOTY) halibut, Parahchthvs califomicus, within Upper Newport Bay.
The Project Applicant, California Recreation Company (CRC), has entered into a preliminary agreement
with the California Department of Fish and Game (CDF&G) to restore additional shallow subtidal habitat.
Funds for this put of the restoration work will be contributed by the CDF&G through a maintenance
dredging mitigation built administered by the City of Newport Beach
0 L2 DOCUMENT ORGANIZATION
0
The cornxpnul mitigation plan is divided into six sections.
• Section 2 reviews the proposed marina development project and expected marine biological
impacts that require mitigation.
• Section 3 identifies an on -site mitigation area in Upper Newport Bay and describes the existing
biological conditions within the proposed mitigation area.
• Section 4 describes proposed and alternative concept designs for the restoration of mudflat and
subtidal habitats.
• Section S identifies -potential opportunities and constraints related to the mitigation effort
• Section 6 outlines tasks that will be required from the selection of the final concept design through
the completion of mitigation monitoring.
• Section 7 provides the phasing for the tasks outlined in Section 6.
91333 1-1
2. CASTAWAYS MARINA OVERVIEW
California Recreation Company (CRC) proposes to comsuuct and operate a marina at the lower Castaways
site in the City of Newport Beads, Orange County, California. The site is immediately north of the Coast
Highway Bridge at the intersection of Dover Drive and Coast Highway (Figure 2.1).
The proposed marina project will consist of floating, pile -supported, and land -based facilities to support
a total of 125 boats. Sixty-one of the boat slips or side ties will be located within a marina basin and
sixty-four wr71 be located in the main channel of Upper Newport Bay.
The construction and operation of the marina will require the dredging of 24,000 Cubic yards of bottom
sediments from the main charnel of Upper Newport Bay using a ciamshell dredge. Based on marine
biological habitat and community impact analysis for the project ER Mchad Brardman Associates,
1991), dredging will result in the permanent reduction in the amount of intertidal mudflat areas that are
foraging habitat for shorebirds, and a permanent reduction in shallow subtidal channel habitat that ,is
considered to be not only important fishery habitat in general. but particularly important nursery habitat
for young -of -the year (YOTY) halibut. These losses are considered to be significant, long tens impacts
that can be mitigated to a level of insignificance by the successful restoration of these habitats within the
Upper Newport Bay system.
In accordance with California Emromnemal Quality Act guidelines, alternative marina designs were
analyzed in an attempt to reduce the environmental impacts associated with the project. These are
reviewed in the E1R. A summary of the reduction in habitat losses associated with the various marina
design alternatives, compared to the proposed project, is provided in Table 2.1. Of the three alternatives
considered, the 121 slip alterative is environmentally superior to the proposed project because it reduces
the amount of "wet" material dredging required and the loss of shallow subtidal and mudflat habitat by
approximately 46 percent. Consequently, this alternative was selected to be the model for the conceptual
mitigation plan.
The 121 slip option is also considered to be an economically feasible alternative by the applicant and
along with the proposed project (125 slip marina), is under consideration by the City of Newport Beach
as a viable project in the DEIR.
Despite the significant reduction in the amount of dredging required under the 121 slip marina altemative
(46%), unavoidable losses of mudflat and shallow subtidal halibut nursery habitat are still expected to
occur. These losses can be mitigated to an insignificant impact upon the successful compensation of
2-1
Project Vicinity Map
Shellmaker Island Mitigation Project Figure 2.1
TABLE 2-1
ESTIMATED DREDGING REQUIREMENTS AND
SUBTIDAL AND MUDFLATJMPACTS
FOR ALTERNATIVE MARINA DESIGNS
Proposed
Project 121-Boat 84-Boat 50-Boat
(125-Boat) Alternative Alternative Alternative
A. Estimated Amount of Dredging
Dry Material (cy)'
56,000
56,000
56,000
3,500
- Wet Material (cyp
24,000
11,000
11,000
13,000
Total (cy)
801000
67,000
67,000
16,500
B. Hellbut (YOTY Nursery)
Removed (acres)°
-0.34
-0.24
-0.28
-0.28
Created (acres)
+0.06
+0.03
+0.02
+0.02
Net Loss (acres)
-0.21
-0.21
-0.26
-0.26
R Halibut (Juvenile)
Removed (acres)
0.00
0.00
0.00
0.00
Created (acres)
+2.96
+2.50
+2.50
+0.10
Net Gain (acres)
+2.96
+250
+250
+0.10
D. Mudtlat
Removed (acres)
-0.74
0.34
0.65
0.65
Created (acres)
+0.05
0.00
0.00
0.00
Net Loss (acres) -0.69 -0.34 -0.65 -0.65
cy . cubic yards
YOTY - young of year
• 'Dry Material" is material behind existing bukhead.
b "Wet Material" is material on bottom of bay.
• •Removed refers to the total amount of habitat that is altered to depth contours outside the defined
range for each habitat type.
'Created refers to the total amount of habitat that is altered to depth contours within the defined
range for each habitat type.
Source: Cash and Associates, 1991.
0
2-3
2. Castaways Marina Overview
• mudflat and halibut habitat. The pmjec t applicant proposes to compensate the loss at a ratio of 1.5 times
the amount of habitat removed as a result of dredging.
u
2-4
• 3. PROPOSED MITIGATION AREA
3.1 SrM SELECTION
Shetbnalcer. Island was selected as the mitigation site as a result of discussions between the project
applicant and their consultants, the City of Newport Beach, the California Department of Fish and Game,
United States Fish and Wildlife Service (USFWS), Army Corps of Engineers (ACOE), and the National
Marine Fisheries Service (NMFS) during meetings held at the project site on January 29, 1991. The
specific mitigation area on Shelimaker Island is located immediately with of a tidal channel cut that
bisects the island
In keeping with a primary objective of the'CDF&G Upper Newport Bay Management Plan to manage the
Upper Newport Bay Ecological Reserve for tidal and mudflat habitat use by fishes and shorebirds
(CDF&G, urqublisbed report), this project provides an opportunity to restore a dredge -spoil disposal area
to productive shallow water and intertidal mudflats by recomouring existing elevations and removing the
dredge spoils from the island.
• 3.2 SITE DESCRIMON
Shellmaker Island Is located one mile northeast of the proposed Castaways marina site, and immediately
north of the Dimes Marina launch ramp facilities (Figures 2.1 and 3.1). It is located at the southern
boundary of the Upper Newport Bay Ecological Reserve which has been under the stewardship of the
CDF&G since it was acquired from the County of Orange and the Irvine Company in 1974.
For many years, Shellmaker Island was used as a dredge spoil disposal site and dredge operations staging
area. Consequently, portions of the salt marsh and mudfLus were eliminated and transformed into higher
elevation open sandy areas, colonized by upland vegetation.
The southern one-fourth of Shellmaker Island is joined to the mainland by a dirt mad. Buildings formally
occupied by the Shellmaker Dredging Company are currently occupied by the CDF&G and are situated
atop dredge spoils that in some areas are as high as +17 feet Mean Lower Low Water (MLLW).
The southem part of the island was initially the preferred mitigation site by both the project applicant and
the CDF&G because it was easily accessible by large vehicles, highly degraded. and it was close to the
proposed center of the California Department of Fish and Game Wildlife Campaign interpretive facilities.
CDF&G subsequently determined that the site was the only designated dredging staging area for future
• Upper Bay projects. Therefore, this section is not currently available as a mitigation area. (Richard Nitsos,
CDF&G, personal communication, September 12, 1991).
3-1
3. Pmpowd Muigation Area
• At the same time, CDF&G also recommended a second mitigation site on Shellmaker island, which is now
the preferred mitigation area. It is located immediately north of a tidal channel cut that bisects'Shellmaker
Island (Figure 3.1). The tidal channel and surrounding mudflat areas was contoured by CDF&G in 1986.
Since that time, salt marsh vegetation has colonized the middle and high intertidal zones.
33 EXISTING CONDITIONS
Fleld iecoun issanc a surveys of the Shaninaker Island mitigation site were conducted on August 19 and
September 19, 1991. The surveys were undertaken to verify existing topographic map data of Shellmaker
Island that was produced in 1984 and 1985 for the Upper Newport Bay Restoration Project, and secondly,
to identify existing plant and animal communities in the project area. Additional information was obtained
from the CDF&G regarding the distribution of the state and federally endangered plant salt marsh bird's
beak (Cordvlanthus maritimus spp. maritima and from the Fish and Wildlife Service (USFWS) regarding
the distribution of the light-footed clapperrail (Raft lonaimstris levines) and Belding's savarmah sparrow
(Ammodmmus sandwichensis beldin ' , both of which use Shrnm"rer Island for breeding and foraging
purPoses.
33 t T000araohrr and Soil Types,
There are no current topographic survey maps available for the project area. The most recent information
was obtained from the "City of Newport Beach Public Works Department Sediment Control and Upper
• Newport Bay Restoration Project Access Chat nel Plan" (1985; M 5249-5, Sheets 6 and 7 of 28; scale 1
inch=100 feet), and a Jamrary 1991 aerial photograph of the Shellmaker Island area from Aerial Fombank
Inc„ Stanton, California (scale i inch = 200 feet). A partial reproduction of the topographic survey map
in the vicinity of the proposed mitigation site is provided in Appendix 1. Data provided from this map
and photograph were verified during a site visit by EIP Associates and Cash & Associates on September
19, 1991. From the topographic information collected during that survey. the elevations within the
proposed mitigation site appear to be about one foot lower in elevation than what was determined during
the earlier topographic survey.
Tie west facing side of Shellmaker, bordering the Upper Bay main channel. is steeply sloped at the
southern end of the project area and varies from salt marsh elevations (approximately +3.5 feet MLLW)
at the bottom of the slope to about +10 feet MLLW along the berm. Elevations on the plateau of the
island are quite variable because of dredge spoil deposition, and range from about +7 feet to +17 feet
MLLW. Most of the area proposed as the mitigation site averages about +13 feet MLLW.
Salt marsh and mudflats on the eastern section of Shellmaker Island (separated from the mitigation site
by a dirt mad) and areas north of the mitigation site are high -quality marsh habitats. The northernmost
area of the island has been partially developed as a least tern nesting area, but to date, tems have not used
the site.
•
3-2
` •+ r ,, INI.
t a' a .a .\7ri�'iFFF•'".:1�
' ' fig . J. ,t. I .. r1.•E I. j., 4 .... }.,�
.r.., �,' _s aA: qc r ri A`- [^Ti .1 f:+.r•� fw a
h}s '�^ v• ,�lsj Amy_ � w. .�t
tip ,,qq��I
3. proposed Mitigation Ana
• In the immediate area of the project site, mudflat contours (+3.5 to -iS f feet MLLW) extend 50 to 200
feet beyond the marsh. The wide mudflats conform to the shape of the island and reflect past deposition
patterns prior to the chancel dredging projects within the Upper Bay. Shallow subtidal halibut nursery
habitat 0.5 to -32 feet MLLW) extends another 15 to 50 feet into the main channel.
Mudflat and salt marsh sediments consist of fine stilts and sands. These sods grade into coarser dredged
material, composed of sands mixed with shell debris that make up the slopes, berm, and plateau of
Shellmaker Island. High salt marsh and upland vegetation are dominant on this soil type. These soils
likely overlay firner marsh sediments with a much higher content.
3..3.2 Vegetation and Wildlife Habitat and Vegetation Types in the Mitigation Area
Habitat and vegetation types in the mitigation area are shown in Figure 32.
Upland Vegetation Communities Sandy, upland areas (above +8 feet [ LLM) constitute 125 acres
in the mitigation area. These soils are covered by a sparse cover of ntderal grasses and forbs, a few
shrubs, and patches of strand transitional vegetation (sea -fig, Caroobrotos aeaut7atencs). Telegraph wad
(Heterotheca arandiflo , coastal wooly -bead (Nemamulis denude , western tansy -mustard 0 cscurainia
ion , and filarce (Erodiurn sp.) comprised most of the forbs at the time of the survey. Other are h7tely
to be presen, but were not found due to the late m of the flowering season. Small patches of mulefat
• tBaccharis set icifoli , coyote brush accaris vilulari , and saltbush Atri lex sp.) dominate the highest
elevations (+13 to +17 feet MLLW) in the southwestern comer of the site. Anoyo willow QIM
lasioleoisl, and myopocum (Mv000tum laetum occur in the highest areas, just north of the site, in the
middle of the sandy upland habitat at elevations between +10 to +13 fat (MILW).
Salt marsh. Salt marsh vegetation occurs between the mid -tide zone (+3.5 feet MLLW) and the Extreme
High Tide mark (about +7.8 fat MLLW). Salt marsh plans typically ocean in three broad, overlapping
zones based on their response to awiratmentai factors. These zones are the low salt marsh, middle salt
marsh, and high salt marsh. For this discussion, the zones are grouped into low to middle intertidal salt
marsh, and middle to high intertidal salt marsh. For mapping purposes, the zones are combined into a
general salt marsh category.
The salt marsh growing along the CDF&G tidal channel, south of the mitigation site, is relatively new
growth and has colonized the intertidal areas within the last few years. Low to mid -intertidal areas are
dominated by Bigelow's pickleweed Salicornia bi elovii with occasional patches of cordgrass S artina
folios . Saltwort (Batas maritime and common woody pickleweal Salicomia virginice am more
common in the mid -intertidal regions but extend into both the lower and upper salt marsh zones. On the
steeper slopes of the western and southern shores, high intertidal, transitional strand vegetation, and upland
annual grasses and forbs occur just above the picideweed zone. The gentle slopes of the eastern and
• northern shores outside the mitigation area are vegetated by a wide band (up to approximately 33 feet
wide) of high salt marsh, most of which is a salt cedar (Monanthochloe littoralis meadow'that occurs
3-5
Habitat and Vegetation Types
Shellmaker Island Mitigation Project
Figure 3.2
El 3-6 OP WI3
3. proposed Mitigation Area
above the pickleweed zone. in several areas north of the project site, the lower elevations of the salt cedar
meadow support salt marsh bird's beak (Cordvlanthus maridmus spp. maritime , a federal- and state -listed
endangered species (CDF&G, 1991; pens obs). None however, was located within the confines of the
project area Above the salt cedar zone, a dense cover of transitional strand vegetation [salt grass
(Distichlis spirate and, secondarily, sea -fig, and alkali heath (Frankenia saline)] merges with upland
grasses and forbs.
Salt marsh vegetation in the project area is limited to the western margin of the mitigation site, along the
main charnel and consists of a mixture of middle and upper salt marsh vegetation. It covers an area of
about 0.11 acre.
Mudflats. Mudflats are found between the Extreme Low Water mark (4.8 feet MLLW) and the Mean
Low Bigh Water mark -the begimring of salt marsh vegetation. In the mitigation area, about 1.88 acres
of mudflats occur along the main channel of the Upper Bay. Mudflats are critical sbonbird feeding areas
and important fish foraging habitat when the mudflats are inundated by the tides. Diatom and grecri algal
teats often cover the surface of the mudflats and are considered to be important because these plants
account for a huge part of the primary production in southern California coastal wetlands (2edler 1982).
Additionally, the green algae is used as a food source by herbivorous invertebrates, fishes, and birds.
Shallow Subtidal Environment The shallow subtidal habitat of Upper Newport Bay is an important
musery habitat for halibut as wen as other fishes such as gobies, topsuidt, anchovies, croakers, diamond
turbot, and sand bass. Halibut are consistently found between the Coast Highway Bridge and the dike.
Allen (1988) reported most individuals spurred between Sbeiimaker Island and the dike were YOTY (less
than 80 men in length) and second -year individuals (80 mm to about 160 mm). Additionally, halibut
abundances were positively correlated to increasing salinities (AIIat 1988).
The shallow subtidal habitat within the boundaries of the project site is limited to 0.67 acre, located in the
main channel of the Upper Bay.
Avian Use. A bird survey was conducted in the vicinity of the project area on August 19, 1991. Birds
were abundant along the channels, over the open water, and roosting on mudfiats and in the low and
middle salt marsh. Among the water birds, the marbled godwit imosa fedoa , elegant tern Sterna
ele , and Forester's tern Sterna forsteri were the most numerous, especially on the mudflats and in
the pickleweed habitat along the tidal channel bisecting Siullmaker island Other commonspecies seen
included snowy egret Chula , killdeer Charadrius vocifenu , willet (Catootronhorus
semioaimatus), whimbrd umenius phaeopu , and caspian tam Sterna is . Other observed were
pied -billed grebe (Podilvmbus podic , great blue heron (Ardea herodias), black -bellied plover (Plwy
scruatarril , greater yellowlegs Crringa melanoleucus), long -billed curlew 04menius amerimm , long -
billed dowitcher (Limnodromus scotonaceus), ring -billed gull (L=s delawarensis), California gull amus
califoroicus), and western gull ens occidentalis). Others that are expected to be present include various
3-7
3. Proposed MtiPdon Area
ducks, semipaimatedplover(Chandrius seminaimatus), short -billed dowitcher(Limnodmmus t<riesus), and
common tern (Sterna himndo .
Substantially higher aboodances and diversity are expected during the late fall through spring
overwimnng period of transients and winter. residents• The types of birds and numbers of birds are also
ezp aW to vary depending on the time of day and tidal conditions.
The site supports very poor habitat for lad birds; only the mounting vee Qmu ids mtmacro (w was
observed in large numbers. The doves were feeding on the dredge spoilamong Y)
vegetation in from of the CDF&G buildings. in addition to mourning doves, the American crow (COIYN
brachvfivchos), northern mockingbird (Ml_mus i o , European starling (Strums vul¢ad , and
house sparrows (Passer domesticus) were present. A number of bank swallows (lnnmdo mstica) were
observed hawking in== over the island, but were also foraging over nearby marshes and over the open
water Several turkey vultures artes aura were sees soaring over the open water and the island, and
might occasionally use the site should a food source be present. Other locally common land birds, such
as the blacks: phoebe (Savorriis id ' an and house fmch (Caroodacus meek are cgx=cd to be
occasionally present The preseoce of sensitive species of birds on Sbellmaker Island Is discussed below.
Sensitive Species. A California Natural Diversity Data Base (CNDDB) search was conducted to
determine the potential for sensitive species to be food in Upper Newport Bay and on Shellmaker Island.
Other informational sources included communications with California Depart nest of Fish and Game
personnel (John Scholl), USFWS personnel (Dick 7embal), and records of it = occurring on the
Bayside marsh peninsula near the De A=a mobile home park (Marsh 1985).
Several coastal insects have been classified as sensitive by Nagano (1982) because a reduction in their
coastal dune and mudfiat habitats has reduced their populations. Although no sensitive insects surveys
have been conducted on Shellmaker Island, there is suitable habitat, such as the dredge spoil "dune"
habitat and mudtlats surrounding the marsh, that could support sensitive insects. Sensitive insects that
have a potential to be found include the wandering skipper butterfly (Panocruina rem inoides errans ,
globose dune beetle (Coelus pjobo , Gabb's tiger beetle mcindela bbi , sandy beach tiger beetle
& hirticollis gravids , and the sand dune tiger beetle (rc latesi . The most hWy species to occur
on Shellmakr are the wandering skippm which associates with the high intertidal salt grass habitat, and
the globose dune beetle. Both were found on the Bayside peninsula during insect surveys conducted in
1984 by Gordon Marsh, of the University of California (Marsh 1985).
The distribution of the federal- and state -listed salt -marsh bird's beak (Cordvlanthus maritimus spp.
maritime) was recently mapped by Fred Roberts, of the University of California, Irvine for the C DF&G.
Stands of salt-marshh bird's beak are found in high salt marsh meadows on Shellmaker island dominated
by salt cedar, but begin about 500 feet north of the project site and extend to the northern tip of the island.
3-8
3. Proposed Mitigation Area
0
0
The California brackish water snail Crrvonia imitator is a federal endangered species category 2 candidate.
It occurs in Upper Newport Bay and prefers shallow, coarse sediments in low salinity (brackish) areas at
the mouth of the Santa Ana -Delhi civaruael and the San Diego Creek. It is also recorded from the main
channel off of Shellmaker Island, but in significantly lower densities and mostly during winter and spring
when storm water runoff reduces the salinity in the main channel (Marine Biological Consultants and the
Southern California Coastal Water Research Project 1980).
Two endangered species of birds nest and forage on Shelimaker Island. The federal- and state -listed
California light-footed clapper rail Mallus loneirostris Levi nests in the cordgrass habitat north and east
of the proposed mitigation area. Belding's savannah sparrow (Ammodramus fPasserculusl sandwichensis
1 in i , a state -listed species, new and forages in the piddeweed habitat on ShWmaker Island.
Territories of these birds may include habitat located new the mad or in the salt marsh growing along the
main channel. The state -listed California least tam (Sterna antillarum browni may forage in the waters
near the island; efforts by CDF&F to induce this species to nest on Shelimaker Island have not been
successful. CalMmia brown pelicans lecamrs occidentalis also forage in the Upper Bay. The
California black nil axerallus jamaicensis cotumiculus) was listed in the CNDDB as present in Upper
Newport Bay in 1970, its status on Shellmaker Island is currently unknown.
3-9
4. PROPOSED AND ALTERNATIVE CONCEPT DESIGNS
4.1 GENERAL
The loss of shallow subtidal fishery habitat and intertidal shorebird foraging habitat will be mitigated at
a compensation ratio of 13 to 1. A total of 0.51 acre of mudflat habitat will be restored for the loss of
0.34 acre: 032 acre of subtidal halibut nursery habitat will be restored for the loss of 0.21 acre.
Compensation for habitat losses at this ratio will insure that all habitat functions and values are restored
to the Upper Bay. Additional subtidal habitat will also be created with funds made available from the
CDF&G.
Under the proposed habitat designs, approximately 1.01 acres of Shellmaker Wad will be recontouted
to shallow subdW elevations (iS to -3.2 feet RdLLWJ) and mudflat elevations (-1S to +23 lv LW).
Additional rarontounng (0.48 acre) will be necessary to bring elevations up to existing grades between
the mudflats and upland areas which will create salt marsh and transitional strand vegetation babitat
43 PROPOSED HABITAT DESIGN
The proposed habitat design is illustrated in Figure 4.1 and includes:
• Creating halibut mnsery habitat by excavating a 25-foot wide semi -circular. permanent subtidal
channel from existing dredge spoils colonized by sparse nrden d vegetation;
• Lowering the island's upland elevations around the proposed tidal channel to mudflat elevations
between -1-5 feet and +2.5 feet MLLW,
• Re -grading above mudflat elevations to heights between +2.5 and +7.0 fed OILLW) for the
eventual colonization and establishment of a salt marsh community: and
• Creating a small marsh island as a consequence of constructing the tidal channel.
The proposed design acreages are summarized in Table 4.1 and include approximately 0.25 acre of upland
habitat with a maximum elevation of +83 feet MLLW,, 0.33 acre of salt marsh habitat at elevations
between +2.5 and +7.0 fed MLLW, 0.51 acre of mudflats at elevations between +2.5 and -1.5 fat
MC.LW', and 0-50 acre of halibut nursery habitat at depths between -13 and -3.2 feet MLLW.
The project applicant will be responsible for the mitigation of 0.32 acre (64 percent) of the subtidal fishery
habitat The additional amount of subtidal habitat to be,restored (36 percent, 0.18 acre) will be created
with funds from the CDF&G mitigation bank.
4-1
Proposed Habitat Design
•1
Altamathrw to Proposed ProJeet Design
Habitat type and Acreage
Salt
Channel
Upland
Matslt
t+Audtlat
•
ToWI
Proposed Project
0.25
0.33
0.51
0.50
1.59
Alternative #1
0.30
0.29
Om
0.69
1.81
Ahamative ;!C2
0.12
0.49
0.51
0.73
1.85
• Project applicant wig be responsible for the restoration of 13,939 ttz (0.32 acre) of subtidal
channel habitat. Remaining area will be restored with turxJs provided by the California
DepaRrtant of Fish and Gana.
Table 4
•
4-3
4. Proposed and Altema6ve Project Designs
. Proposed elevational grades vary with habitat type, depending on the width of the habitat (Figure 42) but
average about 1:4 for subtidal areas, 1:6 for mudflats; 1:6 for salt marsh, and 3:1 for transition areas
between the salt marsh and the existing elevations.
43 ALTERNATIVES
43A Alternative Designs
Alternative site designs were developed for the same location on Shellmaker island Tbese am illustrated
in Figures 42 through 4.4. The design differences are related to how much additional subtidal habitat can
be constructed with CDF&G funds. The proposed project provides a conservative estimate of CDF&G
involvement; Alternatives 1 and 2 sequentially increase the amount of subtidal habitat to be added to the
site. Alternative 2 also lowers the elevations on the island from primarily upland habitat to entirely salt
marsh elevations.
43.2 Alternative Site Locations
Two other locations in Newport Bay were considered as possible mitigation areas. The fits[ site
alternative was the area on Shelimaker Nam south of the tidal channel, but it was rejected because it is
• a staging area for fume dredge activities in the Upper Bay. Arras farther north on Shellmaker Island in
the vicinity of the uninhabited least tam nesting sites were also considered, but were rejected based on
the high biological sensitivity of the site associated with the presence of salt marsh bird's beak.
CI
Them are no other available sites that could be recontouted concurrently for both halibut nursery habitat
and shorebird foraging areas. The CDF&G Upper Newport Bay Restoration Site, northeast of the dike
was considered as a possible site. However, it was rejected because the bracidsh (low salinity) water
conditions limit the use of the subtidal channels by juvenile and young -of -the -year halibut.
4-4
u
• •
Plan View of Proposed and Alternative Habitat Designs
+12'
+7
+2
-3
r 1
A. Propbsed Project
13' Existing Conlours 13' 1
— — — — — — — — us n' 10,
10"�—�� UPland'
SaN Slarsy y Upland
Mudlyt Mu60+1 Sall llfarrb
Sublldal
Channel
45' 25' ` 25' 2S' 123' 10' 1 10'
B. Alternative 1.
13' Existing Conform 13'
-----------
10" .�.��. Upland
sits'Ifi
r+4
Mudtyt SubIWY
Ciarnd
1 60' 1 10' 1 25' 1 37.5'
C. Alternative 2.'
+12'
+7
Salt Marsh
+2
-3
40'
1 1
0' 20'
Horizontal Distance (FetQ
(West to East)
I
•
Figure 4.2
11'*
------- 5--..—_
UPlsnd
�\tMa
MudOal
2S'
13" Existing Contours' 13' 125' 11'
. .-------------�.--------------- --�1 10'
7Fansllkm
$altMecst'
Mudlht Subildol MUM%
Charred
15' 373' 25' 25' 12S'
60' 80' 100' 12W 140' 160'
10'
— Alternative 1 Habitat Design
Shellmaker Island Mitigation Project
c
A
Figure 4.3
Alternative 2 Habitat Design
Shellmaker Island Mitigation Project
Salt Marsh
Upland
4-7
Salt
Figure 4.4
Salt l
Marsh
Channel
Legend
Chsmd n
Mudfla
sakmarsh
Upland
m ama
eip
S. OPPORTUNITIES AND CONSTRAINTS ASSOCIATED
WITH THE PROPOSED PROJECT
SA OPPORTUNITMS
The srrccessw completion of the project will compensate for the significant loss of subtidal halibut
nursery habitat and mudflat areas at the Castaways Marina site and will restore wetland habitat to
Shellmaker Island.
Expected benefits will include an increase in numbers of invertebrates living on or in the mudflats, which
will enhance shorebird utilization of the area as a foraging habitat Newly created subtidal channel area
will provide protected, shallow watermursery and/orforaging habitat for Califomia halibut, otherflat5shes,
rays, sandbars, mullet, topsmelt, and sudperches.
The proposed mitigation project will also increase the amount of salt marsh habitat on Shellmaker island,
which will add critical habitat for both the light-footed clapper rail and Belding's savannah sparrow.
• The design of the mitigation project will be integrated with future interpretive and educational facilities
of the California Department of Fish and Game Wildlife Campaign and the County of Orange Upper
Newport Bay Regional Park program and will provide educational and raaeatim al opportunities for the
public, and a chance for researchers to study the short-term and long-term restoration of wetlands in the
Upper Bay.
S.2 CONSTRAINTS
5.2.1. Bioloeicai Constraints.
Expected habitat alterations to Shellmaker Island are listed in Table 5.1 and include:
• Replacement of 1.25 acres of open sandy habitat, and coastal dune scrub, and transitional
vegetation with higher quality salt marsh, mudflat, and subtidal channel habitat;
• Replacement of 0.11 acre of middle and upper salt marsh habitat that will be removed in the
process of creating a tidal inlet and
5-1
n
U
E
uplandrrmnsitional
'sax marsh
'MudOats
'Shallow subMal
Total
1. Sak marsh
2. Mudeats W
3. Depth rang
5. Opportunities and Consiraints Associated with the Proposed Project
• Deepening of 0.17 acre of mudilat habitat to shallow subtidal halibut nursery habitat depths (-1.5
It to -3.2 ft MLLW) in the main charmel.
The restoration project involves construction activities that could potentially disturb populations of
Belding's savannah sparrow, the light-footed clapper rail. and the California least tem that may rat and/or
forage nearby, outside the mitigation area. To avoid impacts to these species, all construction activities
will be limited to non -breeding periods of the year (September through February) for time species.
Construction activities will be avoided in areas colonized by the endangered salt marsh bird's beak. The
USFWS has expressed some concern that open sandy habitat in the vicinity of the salt marsh bird's beak
stands may be important for ground -nesting bees that pollinate the salt marsh bird's beak (Dick Zembal,
USFWS. personal communication, September 20, 1991). Although this concern may be justified, there
will still be a significant amount of open habitat for ground -nesting bees north of the project site, once
the project is implemented.
To minimize damage to the other existing plant life in the area and disturbance to wilWe, construction
equipment and personnel movements will be restricted to the specified mitigation site.
Salt marsh plains must be removed fortbe construction of the tidal channel. Plants that are in the affected
habitat (approximatety (111 ace) will be collected and replanted in suitable habitat on Shellmaker Island
as designated by the CDF&G. This action will result in the full restoration of salt marsh plain that are
removed in the construction of the tidal channel.
$.22, Eneineerine Constraints.
Vehicular access to the proposed mitigation site on the north side of Shellmaker Island is unavailable
because the tidal charnel bisects the island. A temporary bridge, capable of withstanding loads from
trucks, bulldozers, bacidwes, and other vehicles must be built across the tidal inlet. Regulatory permits
may be required for this action.
Soils on Shellmaker will be excavated and then transported offsite for disposal in a Comity of Orange
landfill or on Irvine Company property. The City of Newport Beach has also expressed preliminary
interest in the dredge spoils as potential beach replenishment material (Tony Mellum, City of Newport
Beach, personal communication, August 13, 1991) A State of California Title 22 Hazardous Materials
Analysis will lilmly be required to determine the suitability of these materials for subsequent use or
disposal in a County landfill.
Clamsheil dredging, employing a barge and a crane may be required to contour the mudflat elevations to
lower subdW elevations because these areas may not be accessible using land -based equipment. The
• suitability of dredged "wet" sediments for land or ocean disposal, or use as beach replenishment material
5-3
5. Opportunities and Constraints Associated with the Proposed Project
• must also be determined, potentially by bioassay testing methods if the material is to be disposed at an
offsbore dumpsite (LA-3).
0
5.43 Re¢ulatory Pernrittine Constraints
E)dsting upland and wetland habitats must be recomoured to lower intertidal and subtidal elevations.
These alterations will require the acquisition of environmental permits from local, state, and federal
agencies. Permits that could be required include:
• Section 10 permit to locate a temporary bridge or to use dredge spoils for beach nourishment;
• State of California Coastal Development Permit for the developing in the coastal zone;
• State Lards Commission Permit for dredging in state tidelands;
• California Environmental Protection Agency/Regional Water Quality Control Board/NPDES
discharge permit to prevent the degradation of water quality during dredging activity;
• C learmx to use a County of Orange Landfill;
• City of Newport Beach grading and harbor permit;
• Section 404 permit fiom the U.S. Array Corps of Enginms for the disposal of dredged material
at an offshore dumpsite (if needed) or for use of the excavated sobs as beach nourishment
material;
• United States Environmental Protection Agency permit to use IA-3 Disposal Site, if an offshore
dumpsite is used;
• U.S. Coast Guard Aids to Navigation permit, if barges are involved; and
• Special written permission to remove salt marsh vegetation or to work within the Upper Newport
Bay Ecological Reserve from the State of California Fish and Game Commission and from the
California Department of Fish and Game Region 5 Manager.
F#7
& PROJECT TASKS
Tasks required for the planning, implementation, and monitoring of the Shellmaker island Mitigation
Project are defined below.
61 AGENCY COORDINATION
Planning meetings will be held with resou= agencies (CDF&G. USFWS, and the NMFS), regulatory
agencies (U.S. Army Corps of Engineers and the CaMmia Coastal Commission), the County of Orange
(Department of Harbors, Beaches, and Parks), and the City of Newport Beach These meetings will be
used to refine mitigation goals and objectives, and evaluate the results of each phase of the mitigation
pmgnm at key project milestones.
These meeting will also address issues of compliance with state and federal mitigation and regulatory
permitting requirements.
40 6.2 PREPARATION OF THE FINAL CONCEPTUAL DESIGN
Prior to preparing eonstrttc Lion level plans, a hydrologic and hydraulic study will be prepared. The
purpose of this document is to evaluate and refine the initial design contours such as channel widths, and
prqxned slopes, and provide'improvements to the hydrological or hydraulic design of the site plant.
D u
Permit applications for the project will be submitted to all regulatory agencies following the completion
of the final concept design. It is anticipated that Lire permitting process will be integrated into the overall
permit process for the Castaways Marina Project
C4 CONSTRUCTION LEVEL SPECIFICATIONS
Based on the final conceptual design plans, engineering level plans will be produced that will include
specifications for site construction. These will be produced by a qualified coastal engineering firm and
include, but not be limited to, the final grading per, disposal specifications, and site monitoring
., ill rl 4
6.5 SALT MARSH TRANSPLANT
Prior to habitat construction, salt marsh plants in the areas to be excavated for the tidal channel opening
will be removed and relocated m another area of Shellmaker island approved by CDF&G.
6.1
6. Project TMb
6.6 HABITAT CONSTRUCTION
The existing elevations of the Shellmaker Island site will be excavated by a qualified contractor with
expericnce in wetland habitat construction, and in accordance with the mitigation plan and design
specifications approved by the regulatory agencies. A qualified biologist -and coastal engineer will be
unite during the construction phase to monitor project progress, insure that the proper site contours are
attained, prevent damage to nearby sensitive habitats habitat. and to provide technical assistant to the
contractors. In additionthe project biologist will monitor wildlife use of the area during habitat
construction.
6.7 POST -CONSTRUCTION TOPOGRAPHIC SURVEY
A post -construction habitat topographic survey and diver reconnaissance survey of the shallow subtidal
habitat will be conducted within 60 days after site contouring is completed to evaluate the results of
habitat contouring. H original site specifications are not met, then the contractor will be requited to take
corrective measrres. Once the correct site contours ate attained, then the site contours will provide a
benchmait for topographic monitoring to be conducted during hoer mitigation monitoring phases of the
project
U MONITORING AND HABITAT RESTORATION EVALUATION
' Habitat and wildlife use monitoring surveys will be required to determine the degree to which the project
meets the goals and objectives of the mitigation project.
641 Touoemphic Surveva
Additional topographic surveys will be conducted at intervals at one year and two years following site
com-u=on. These will be conducted to assess the need for additional site remediation, based on
sediment accretion and erosion at the site.
6JU Shorebird and Fish Monitorinr Surveys
Mitigation monitoring surveys will be conducted to assess the use of the Shellmaker mitigation area by
fishes and shorebirds prior to and after habitat construction Shorebird use of the mudflats will be
monitored prior to and during construction, quarterly for the first year following creation of the mudflats,
and ammaily for the remaining four years (ten surveys). Monitoring sites will include the mitigation area
and a nearby mudflat, but outside the mitigation area.
Shorebird feeding activity will help determine the rate at which muudflat community function is being
restored and the degree to which the sediments are being colonized by bemhic hrvertebrates.
Fish surveys will be conducted prior to site constriction, quarterly during the first year, and armually for
the remaining four years (nine surveys) following site construction. In addition. the 60day, post-
6-2
6. Project Tasks
construction diver survey will be used to visually assess the use of the area by fishes. The primary
purpose of the monitoring surveys is to determine if the newly created subtidal habitat is functioning as
a halibut nursery and secondarily, as a nursery area for other fishes. Appropriate methods for sampling
YOTY halibut will be determined; however, it is expected that the most efficient way to sample these
young individuals is by otter beam trawls. Other methods, such as beach seining may also be needed. The
degree to which subtidal areas within the mitigation area are being used by halibut will be compared with
another site in Upper Newport Bay that is ]mown to be utilized by YOTY halibut
6 43 Area Maintenance and Additional Site Monitoring
Periodic maintenance at the mitigation site is recommended to clear debris, unwanted vegetation, and
monitor the development of the salt marsh plants once,they become established within the newly created
habitat Site maintenance should occur at six month intervals, or after large storm events that deposit
debris within the system. Studies that document the development and recolonization of the salt marsh
could be projects for CDF&G Wildlife Campaign and Upper Newport Bay Regional Park educational and
interpretive programs.
6.8.4 Mitigation Success Criteria
Short-term and long-term success criteria will be developed in association with wildlife agencift The
evaluation criteria will take into account the degree to which habitat contouring meets the criteria for use
by shorebirds and fishes. projected seasonal use of the area by birds and fishes, and expected abundance
and distribution of shorebirds and halibut in Upper Newport Bay.
6.M Reporting
Pre -and post -construction field survey results will be submitted to the Corps of Engineers and the resource
agencies in written report format within 30 days of each survey. The report will present field findings,
rate the level of mitigation success, determine wrlWe use of the area, and propose recommendations and
alternatives if the restoration project is not meeting mitigation success requirements. A final project report
at the end of the five-year period will be prepared, analyzing the long term success of the project and
making a final determination of restoration success.
6.8.6 Remedial Measures
Additional actions may be required if the mitigation success criteria are not met After each monitoring
survey, regulatory agencies and the pmject applicant will meet to determine if the project successfully
meets the objectives of the mitigation at that stage of the project If the objectives are not being met, then
remedial steps, such as additional site contouring will be taken.
&3
6. Project Tasks
6.&7 OR -site Mitigation
• In the event that the restoration site is determined to be unsuccessful by the regulatory agencies, off -site
mitigation measures will be implemented. Additional restoration measures could taken off -site in other
local Orange County wetlands such as the Huntington Beach (Talbert) Wetlands, Bolsa Chica, or Seal
Beads Wildlife Refuge.
•
64
• 7. PROJECT SCHEDULING
The mitigation project schedule will be incorporated into the project schedule for the development of the
Castaways Marina. Mitigation work on Shellmaker Island will be implemented prior to the initiation of
the construction for Castaways Marina.
7be following conceptual schedule is recommended
Phase 1-Final Planning
• Conduct a topographic survey for the project area.
• Prepare final exmxpt plans.
• Conduct California TStie 22 Hazardous Materials sediment analysis and dredge bioassays if
sediments an to be disposed at offshore dump site.
• Prepare wastniction level plans.
• Obtain regulatory permits.
• Conduct pre -construction site monitoring surveys for shorebirds and fishes.
•
Phase 2-Habitat Construction
• Construct an'access bridge across the tidal channel to the mitigation site
• Survey in required contours.
• Remove and transplant affected salt marsh plains to another area of Shelimaker Island
• Excavate dredge spoil material from Shellmaker Island (from ]arid) and transport material to
land511 or the City of Newport Beach for beach replenishment.
• Deepen contours to shallow subtidal habitat along the main channel of the bay (by barge and
dredge if required) and transport to landfill or offshore dumpsite.
• Open tidal channel inlet.
• Monitor habitat construction practices and conduct wildlife survey.
7-1
7. Project Scheduling
• Phase 3-Post-Construction Monitoring and Repotting
• Conduct post -contouring topographic and bathymetric surveys 60 days following habitat
conctrumon, one year, and two years following site construction.
• Monitor project progress at quarterly intervals during the first year and annually for the remaining
four years evaluate allematives if restoration is not meeting mitigation criteria.
• Take remedial measures or proceed with off -site mitigation options.
•
•
7-2
& PROJECT STAFF
California Recreation Company
Edward V. Power
EIP Associates
Robert R. Ware Senior Associate/Pmject Director
Mike Lott Staff Ecologist
Ellen Bush► Publication Coordinator
Dennis Mahaffey Word Processing
Michad Brandman Associates
• HJ. Jones
Director. Resources Management
Vince Coleman
Staff Ecologist
Mike Patten
Staff Ecologist
Curt Campbell
Staff Ecologist
Cash and Associates
Randy Mason
Coastal Engineer, Vice President
•
8-1
n
L.J
9. PERSONS AND AGENCIES CONSULTED
California Recreation Company ................................... Edward V. Power
Cash and Associates ............................................... Randy Mason
City of Newport Beach
MarineDepartment .............................................. Tony Mellum
County of Orange
Department of Harbors, Beaches, and Parks ............................. Nancy Borland
State of California
Department of Fish and Game ..................................... Fred Worthley
Richard Nitsos
Ead Laupee
John Scholl
John Anderson
University of California, at Irvine .................................... Fred Roberts
TheIrvine Company ............................................ Sat Tamaribuchi
United States Army Corps of Engineers .................................. Jerry Sales
United States Department of Commerce
National Marine Fisheries Service ................................... Bob Hoffman
United States Department of the Interior
U.S. Fish and Wildlife Service ......................
............. Richard Zembal
Nancy Gilbert
9-1
• 10.. LITERATURE CITED
Allen L. G. 1988 (December). Final Report. Results of a Two -Year Monitoring Study on the Fish
Populations in the Restored Uooermost Portion of Newport Bay, California: With Emphasis on the
Impact of Additional Esmarine Habitat on Fisheries -Related Species. Prepared for the National Marine
FUberies Service in fulfillment of Contract #WASC-85-OM16.
California Department of Fish and Game. (CDF&G). Upper Newport Bay Management Plan.
Unpublished Manuscript
California Natural Diversity Data Base (CNDDB). 1990. Data Base Record Search for information on
Threatened, Endangered, Rame, or otherwise Sensitive Species and Communities in the Vicinity of the
Newport, Long Beach, and Los Alamitos Quadrangles. Caltfomta Department of Fish and Game, State
of California Resources Agency Sacramento, California.
Marine Biological Consultants. Inc. (M BQ and the Southem California Coastal Water Research Project
(SCCWRp). 1990 (December). Irvine Ranch Water District Upper Newport Bay and Stream
Augmentation Program. Final Report. October 1979-August 1980.
Marsh, Gordon. 1985 (June). insects and related teneshdal arthropod assessment of the sand/spit marsh
ptininsula Chapter III in DeAnza (Bayside) Marsh Peninsula Marina Feasibility Study -Biological
Resources Assessment and Evaluation Prepared by MBC Applied Environmental Sciences, Costa Mesa
California, (and) Karlin and Gordon Marsh, Biological Consultants, SRverado, CA.
Michael Brandman Associates. 1991(August). Castaways Marina Draft Envimnmental Impact Report
Volume I of II. Prepared for the City of Newport Beach
Mellum, Tony. Cty of Newport Beach. Meeting held with Robert Ware, EIP Associates. August 16,1991.
Nagano, C. N. 1982. Population status of the tiger beetles of the gems Cincindela (Coleoptera:
C,mcindelidae) inhabiting the marine shoreline of southern California. Atala 8(2):33.42.
Nitsos, Richard California Department of Fish and Game. Letter to R. Ware, E 3? Associates. September
13, 1991.
10.1
9. literature Cited
`J
Scholl, John. Califomia Department of Fish and Game. Map of salt marsh bird's beak distribution sett
to R. Wan:, E1P Associates, September 25, 1991.
Zedler, J. B. 1982. The Ecology of Southem Califomia Coastal Salt Marshes: A Community Profile.
U.S. Fish and Wildlife Service Biological Services Program, Washington D. G. FWS/OBS.81/54.
110 pp.
Richard Zembal, U.S. Fish and WOdlife Service. Personal Communication, telephone conversation with
R. Wan:, EIP Associates on September 20, 1991.
10-2
Appendix 1.
Partial Topographic Survey Map of Shellmaker Island
(Sheet 6 of 27 of "City of Newport Beach Public Works
Department 1985 Sediment Control Plan and Upper Newport
Bay Restoration Project Access Channel Plan). Elevations
are relative to Mean Sea Level (MSL) and can be converted
to Mean Lower Low Water (MLLW) by adding a factor of
2.73 to each contour. Scale 1 "=100 ft. Approximate limits
of the Proposed Mitigation Site, and California Department
of Fish and Game Restoration Area are shown.
elp
a
41 V We 7
I 9;0�
fA 10
ADDITIONAL REFERENCES CITED
• Allen, L. G. 1976. Abundance, Diversity, Seasonality, and Community Structure of the Fish
Populations of Newport Bay, California. M.S. Thesis, California State University, Fullerton.
108 pp.
Allen, L. G. 1988. Final Report, Results of a Two -Year Monitoring Study on the Fish Populations
in the Restored, Uppermost Portion of Newport Bay, California; with Emphasis on the Impact
of Additional Estuarine Habitat on Fisheries -Related Species. Prepared for the National Marine
Fisheries Service in fulfillment of Contract #WASC-85-00216.
Allen, M. J., and Kevin T. Herbinson. 1990. Settlement of Juvenile California Halibut, Paralichthvs
californicus, Along the Coasts of Los Angeles, Orange, and San Diego Counties in 1989.
Ca1COFI Rep., 31:84-96.
EIP Associates. 1991. Draft Conceptual Mitigation Plan for the Loss of Mudflat and Shallow
Subtidal Habitat. Castaways Marina Environmental Impact Report. Prepared for Michael
Brandman Associates, Santa Ana, California, and California Recreation Company.
Ford, R. F. 1986 (Oct). Marine Resource Survey, Harbor Island East and West Basins, San Diego
Bay, California. Appendix A in Final Environmental Impact Report. Sunroad Marina, Harbor
Island. Prepared for Phillips Brandt Reddick, San Diego, California.
Hardy, R. A. 1970. The Marine Environment in Upper Newport and Sunset Bays, Orange County,
California. California Department of Fish and Game Report. MMR Reference No. 70-10.
• 84 pp.
Horn, M. H., and L. G. Allen. 1981. Ecology of Fishes in Upper Newport Bay, California:
Seasonal Dynamics and Community Structure. California Department of Fish and Game,
Marine Resources Technical Report No. 45. 102 pp.
•
Kramer, S. H. 1990. Habitat Specificity and Ontogenetic Movements of Juvenile California Halibut
(Paralichthy,californicusl, and other Flatfishes in Shallow Waters of Southern California.
Southwest Fisheries Science Center Administrative Report LJ-90-22. National Marine Fisheries
Service, La Jolla, California. 157 pp.
Kramer, S. H., and J. R. Hunter. 1988. Southern California Wetland/Shallow Water Habitat
Investigation, Annual Report for Fiscal Year 1988. Prepared by the National Marine Fisheries
Service, Southwest Fisheries Center, La Jolla, California. 8 pp., plus appendices.
Marine Biological Consultants. 1972. Baseline Study of Huntington Harbour. Unpublished report
prepared for the Huntington Harbour Corporation. 73 pp.
Marine Biological Consultants and the Southern California Coastal Water Research Project
(SCCWRP). 1980. Irvine Ranch Water District Upper Newport Bay and Stream Augmentation
Program, Final Report. (October 1979 to August 1980).
MBC Applied Environmental Sciences. 1984 (Oct). Outer Long Beach Harbor-Queensway Bay
Biological Baseline Survey. Prepared for the Port of Long Beach.
JB2/00640011.REF
MBC Applied Environmental Sciences. 1985. Mola Corporation Eelgrass Transplant Project. Site
• Reconnaissance Studies, Phase 1 surveys.
MBC Applied Environmental Sciences. 1986. Mola Corporation One- and Two -Year Eelgrass
Transplant Monitoring Survey Results and Evaluation of Transplant Success. 20 pp.
•
•
MBC Applied Environmental Sciences. 1988 (Oct). Portofino Cove Condominiums Eelgrass Bed
Survey. Prepared for Portofino Cove Condominium Association.
MEC Analytical Systems, Inc. 1988. Biological Baseline and Ecological Evaluation of Existing
Habitats in Los Angeles Harbor and Adjacent Areas. Draft Report. Volumes I -IV.
Posejpal, M. A. 1969. The population Ecology of the Benthic Icthyofauna of Upper Newport Bay.
M.S. Thesis, University of California, Irvine. 146 pp.
Soule, D. F., and M. Oguri (editors). 1988. The Marine Environment of Marina del Rey in 1987.
A Report to the Department of Beaches and Harbors, County of Los Angeles. Prepared by
Harbors Environmental Project, University of Southern California. Part 20 D.
Ware, R. R. Personal observations made during Huntington Harbour and Sunset Bay underwater
studies of eelgrass beds and unvegetated soft -bottom habitats between 1985 and 1988, while
employed as a marine biologist for MBC Applied Environmental Sciences.
JB2l00640011.REF
D. COUNTY OF ORANGE ORDINANCE NO.2200
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ORDINANCE NO. 1403 ,(lido Clark of ❑to Board AN ORDINANCE PSTABLL:H. of 8u=it at oBoard INO .PIER AND BULKHEAD County. GofomlA. BLAUM FOR UPPER NEWPORT BY MABRLL .mia. Y. R.
CASIMI
The DmM of suae."i.....r (SEAL)Deputy
nine marxeo Exhibit "A"
and made a part of ND Ordl•
' tit eaatloM Was Mealderld
section by section. and that the
MM. Including all data,
gold Ordinance WAS man passed
eYmboL and delineation con:
upon gold drawing and
and adopted go A Whole by me
following rote:
ma
me
AYES: SUPERVISORS C. M.
'hall take effect And be In full
MNA C P101. p9, WMRLH.
'era@ thirty (Sd) days from
Ind after Its parwge, and be.
HIRSTEIN AND WILLIS IL WAR•
HER
One the @epentlan of fifteen
15) days atlor the passage
NOESI SUPERVISORS None.
ABSENT: SUPERVISORS None.
hereof shall be published
N101 A In newaPewp r publish.
have WITNESS hereunto et malty hand and
d 1. the county of Orange.
Affixed the official seal of the
let@ of California, together
rlth the nAmn of the them.
BgoM of SUMMIS01 at the
County of Orange. State of Gel•
mot the Boats a1 Supervp•
forma. this Jet day of July, IB59.
n voting for and .Phut the
Ma.
, L R WALLACE,
WILLIS IL WARNER.
Chairman of the Board
County Clerk and ex•
effido Clerk of the Boardper
rvte
Of SuPeon at Orange
County, Callfamlg.
of SuvWn of Orange
County. California.
BY MABEL L CASTRIX,
ATTEST.
(SEAL Deputy
L R WALLACE.
County Clerk and ex.
Publish In fit, Newport 16rMr
Ensign. July 911959.
I0
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EXHIBIT ".
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E
CASTAWAYS MARINA
REPORT OF GEOTECHNICAL EXPLORATION
PROPOSED CASTAWAYS MARINA
NEWPORT BEACH, CALIFORNIA
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CCOC Project No. 90-32155-01
July 19, 1990
REPORT OF GEOTECHNICAL EXPLORATION
PROPOSED CASTAWAYS MARINA
NEWPORT BEACH, CALIFORNIA
Prepared For:
CASH & ASSOCIATES ENGINEERS
2599 EAST 28TH STREET
P.O. BOX 38
LONG BEACH, CALIFORNIA 90801
PREPARED BY: R. Radhakrishnan Staff Engineer
REVIEWED BY: William Beckley P E 41771 Project Engineer
APPROVED BY: Thomas J. Scheil R.G.E. 753 Vice President & Principal Engineer
Eng
Converse Consultants OC Consulting and Geologists srfi
Geologists
'^ Suite Jeronimo Road
Suite 123-A
Irvine, California 92718
• Irvine: 714 859-5587
Oceanside: 619 720-0059
July 19, 1990
LJ
Mr. Randy H. Mason, P.E.
Project Manager
Cash & Associates Engineers
2599 East 28th Street
P.O. Box 38
Long Beach, California 90801
Subject: Report of Geotechnical Exploration
Proposed Castaways Marina
Newport Beach, California
(CCOC Project No. 90-32155-01)
Dear Mr. Mason:
Presented herein are the results of our geotechnical exploration performed
for the proposed Castaways Marina to be located in the Upper Newport Bay at
the northeast corner of the intersection of Pacific Coast Highway and Dover
Drive in Newport Beach, California. This work was conducted in accordance
with our proposal dated May 31, 1990, which was accepted by you on June 6,
1990.
Thank you for the opportunity of working with you on this project. If there
are any questions, please contact us at the number above. We look forward
to assisting you during site grading and foundation construction.
Yours truly,
CONVERSE CONSULTANTS ORANGE COUNTY
Raghuram RadAakrishnan
Staff E gin r
Thom J. Scheil, R.G.E. 753
Vice resident & Principal Engineer
RR/WB/TJS:vy
Dist: (6) Addressee
Gvyxlr�'ft el—
William Beckler, P.E. 41771
Project
No. 41771
A Wholly Owned Subsidiary of
The Converse Professlonal Group
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TABLE OF CONTENTS
Page No.
INTRODUCTION...................................................... 1
PROJECT DESCRIPTION ............................................... 1
PURPOSE AND SCOPE OF STUDY ........................................ 1
Background...................................................... 2
FIELD EXPLORATION AND LABORATORY TESTING .......................... 2
Field Exploration ............................................... 2
LaboratoryTesting .............................................. 3
SITE AND SUBSURFACE CONDITIONS .................................... 3
Site Conditions ......................................... 3
Subsurface Soil Conditions ...................................... 4
Groundwater..................................................... 4
ENGINEERING EVALUATION, CONCLUSIONS, AND RECOMMENDATIONS .......... 5
Excavation& Dredging ........................................... 5
SiteGrading ............................................... 6
Building Foundations ......................................... 7
Building Lateral Resistance ..................................... 7
Steel Sheet Pile Bulkhead ....................................... 8
PileSupported Pier ..................................... 9
Floating Docks and Boat Slips ................................... 10
Lateral Loads For Piles ......................................... 10
RetainingWalls ............................................. 11
Corrosion Potential .......................................... 13
Liquefaction Potential .......................................... 13
Paving......................................................... 14
Utilities....................................................... 15
CLOSURE........................................................... 15
LIST OF TABLES, FIGURES, AND DRAWINGS
TABLES Page No.
Table
1 Soil Parameters for Bulkhead Design ..............
8
Table
2 Allowable Bulkhead Anchor Capacity ...............
9
Table
3 Lateral Pile Design Criteria - Steel Pipe Piles ..
11
Table
4 Retaining Wall Equivalent Fluid Presures .........
12
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FIGURES
Figure 1
Figure 2
Figure 3
Figure 4
r Figure 5
l Figure 6
DRAWINGS
Drawing No. 1
WA
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TABLE OF CONTENTS (Continued)
Site Plan
Subsurface Profile A -A'
Subsurface Profile B-B'
Subsurface Profile C-C'
Driven Single Pile Downward Capacity
Driven Single Pile Uplift Capacity
Location of Borings
LIST OF APPENDICES
APPENDIX
• A Field Exploration - Boring Logs - CPT Logs
B Laboratory Testing
C Logs of Previous Borings (shown on Drawing No. 1)
U
Follows Text
Follows Text
Follows Text
Follows Text
Follows Text
Follows Text
Follows Text
A-1 to A-36
B-1 to B-15
C-1 to C-23
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IN
• INTRODUCTION
` This report presents the results of our geotechnical exploration performed
for the proposed Castaways Marina located in Upper Newport Bay at the north-
east corner of the intersection of Pacific Coast Highway and Dover Drive in
the City of Newport Beach, California. A site plan is presented as Figure 1.
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PROJECT DESCRIPTION
We understand that the proposed Castaways Marina development will consist
primarily of excavating and dredging to and below sea level of a current land
area. The resultant water body will be rimmed by an anchored sheet pile
bulkhead system, and will include floating boat slips and gangways, a sanitary
pump -out station, three shower and/or storage structures, parking areas and
a retaining wall. An existing concrete bulkhead will be removed and a new
bulkhead with tied -back anchors or tension batter piles will be installed as
shown on Drawing No. 1. The majority of the planned marina will be situated
• west of the existing bulkhead with the pile supported pier and some floating
boat slips extending east of the existing bulkhead into the bay. About 60,000
cubic yards of material will be excavated and dredged and disposed of off -
site. The planned new dredge line will vary between EL.- 8 ft. to EL.- 10 ft.
(MLLW). We also understand that one of the shower/storage structures is
planned to be part of a pile supported pier extending to the U.S. Bulkhead
Line. Reference is made to a drawing dated December 12, 1989, prepared by
Cash & Associates entitled "Concept Layout" which provides details of the
development discussed in this report.
•
PURPOSE AND SCOPE OF STUDY
The purposes of this study were to: (1) obtain information on the subsurface
conditions within the project area, (2) evaluate the data, and (3) provide
conclusions and recommendations for design and construction of the facilities
as influenced by the subsurface conditions.
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. To accomplish these objectives, we:
1. Collected and reviewed project.data available to us and prepared an
exploration program.
2. Engaged two contractors to perform 8 test borings and 8 cone
penetration test (CPT) probes (soundings), located the borings and
probes in the field, obtained soil samples, and provided full-time
observation of the contractors' work.
3. Performed laboratory tests to aid in classification of the materials
sampled and to determine their engineering properties.
4. Correlated, interpreted, analyzed, and evaluated the data obtained,
and prepared this report of our conclusions and recommendations.
Background
• Two previous preliminary geotechnical investigations had been performed at
the site for two other planned developments. One report was by Converse
Consultants Inc. (Project No. 82-02161-01) dated August 16, 1982 and the other
by Converse Consultants Orange County (Project No. 86-32245-01) dated August
11, 1986.
From our observations during the field exploration, review of previous reports
and photographs of the site, and conversations with utility personnel, this
site had previously been used as a construction laydown/storage area and a
mobile home park. Apparently abandoned sewer and telephone lines exist across
the site.
FIELD EXPLORATION AND LABORATORY TESTING
Field Exploration
A total of 8 test borings were drilled and 8 cone penetration test probes were
performed on the site at the locations shown on Drawing No. 1, entitled
"Location of Borings." Boring locations were based on the structure
configuration shown on the Concept Layout dated December 12, 1989, prepared
. by Cash & Associates Engineers, Long Beach, California. The borings were
L Converse Consultants OC
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. drilled with a rotary wash drill rig'to depths ranging from 20 to 60 feet and
the cone penetration test probes were advanced with a CPT rig to depths
ranging from 10 to 60 feet. Logs of the subsurface conditions as encountered
in the test borings were recorded at the time of drilling and are presented
on the boring logs included in Appendix A. Logs of previous borings at the
site are enclosed in Appendix C.
Cone penetration test probes (soundings) are a rapid method of obtaining
subsurface soil information, especially frictional resistance of the soil.
We incorporated the use of CPT probes to supplement the borings regarding the
bedrock conditions around the site, primarily depth to competent bedrock.
Results of the CPT probes are also included in Appendix A.
Relatively undisturbed and disturbed samples of the subsurface materials were
obtained at appropriate intervals below the ground surface and were taken to
the laboratory for observation and testing. A brief description of the
drilling and sampling operation is included in Appendix A.
• Laboratory Testing
Representative samples were tested in the laboratory to obtain information on
the engineering properties of the soils. Laboratory tests included unit
weight, moisture content, shear strength, consolidation, expansion index, R-
value, sulfate and chloride content tests and corrosivity and resistivity
tests on selected samples. More detailed descriptions of the laboratory tests
along with a summary of the laboratory test results as well as some individual
test results are presented in Appendix B.
Soil samples are discarded 30 days after the date of this report, unless this
office had received a specific request and fee to retain the samples for a
longer period of time.
SITE AND SUBSURFACE CONDITIONS
Site Conditions
At the time of our field exploration the site was relatively level
• approximately at elevation +10 MLLW and enclosed by a chain -link fence. The
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central portion of the site was devoid of vegetation and covered with a
compacted sand and gravel mixture. The outer portions of the site were
partially covered with grasses, shrubs and trees. A bluff estimated at 60 to
u 80 feet high forming the Newport Beach highlands begins just inside of the
northern property line and extends up the western side of the bay. Slopes
from the bluff down to the marina site, in the vicinity of the northern
property line, are estimated to be from 3:1 (H:V) to nearly vertical.
Subsurface Soil Conditions
` Based on previous and recent test borings and CPT probes, beneath an upper
layer of compacted sandy gravel, the site is generally underlain by a
hydraulic fill, alluvium and bedrock. The upper compacted sandy gravel was
similar to a miscellaneous aggregate base material and extended to a depth of
about 1 foot. Underlying the sandy gravel, except in Borings B-2, B-4 and
B-5, were marine deposits and alluvium consisting primarily of loose to very
dense sands and very soft to stiff clays to depths ranging from 9 to 52 feet.
In Borings B-2, B-4 and B-5 a dredged fill consisting primarily of loose to
medium dense sands was encountered beneath the sandy gravel and overlying the
marine deposits and alluvium. The dredged fill ranged in depth from
approximately 7 feet in Borings B-2 to approximately 20 feet in Boring B-5.
Beneath these soils, bedrock consisting primarily of siltstone of the
Capistrano formation was found. Bedrock varies from the ground surface at the
northern portion of the site to approximately 52 feet below the ground surface
at the southern portion of the site.
The previously mentioned dredged fill also includes miscellaneous fill
materials, marine sediment deposits, and alluvial deposits. Because of the
similarity of these materials and deposits, the contacts between these
deposits were not easily distinguishable.
Groundwater
Groundwater was encountered in all of our test borings at the time of our
field exploration in June 1990, at depths ranging from approximately 3 to 10
feet below the existing grades. The groundwater level at the site is
• approximately at sea level, and is affected by tidal fluctuation in the
adjacent bay harbor channel.
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• ENGINEERING EVALUATION, CONCLUSIONS, AND RECOMMENDATIONS
Based on the results of our field exploration and laboratory tests combined
with our engineering analysis, experience and judgement, it is our opinion
that the site may be developed as planned. The major geotechnical
considerations are the 60,000± cubic yards to be excavated and dredged, the
installation of the sheetpile retainage, the variable characteristics of the
dredged fill, the installation and allowable lateral loads on the guide piles,
and the potential for liquefaction. Areas that contain loose sands are
susceptible to liquefaction and loss of shear strength during strong
earthquakes. As a result bulkheads that pass through such areas may encounter
loss of support in the event a strong earthquake occurs. The primary areas
of loose sands, as encountered in the borings, that are prone to liquefaction
are in the western and north western portions of the site.
Excavation and Dredging
As shown on Drawing No. 1, a new sheet pile bulkhead system will be installed
. around the marina perimeter and the subsurface material on the bay side of the
marina will be excavated or dredged to achieve a dredge line elevation of -8
to -10 feet (MLLW). The dredge line towards the land portion of the marina
is planned to be -8 feet MLLW, and the dredge line towards the bay portion of
the marina is planned to be -10 feet MLLW. We recommend that this transition
be constructed at a 6:1 (N:V) slope.
The total volume of material to be excavated or dredged is estimated at
approximately 60,000 cubic yards. Approximately 15,000 cubic yards of this
material is above the groundwater level. The remaining approximately 45,000
cubic yards will be below or sufficiently near the groundwater level to
warrant dredging operations.
Most of the material to be dredged is previous dredged fill, alluvial
deposits, marine deposits or bedrock. Portions of the bedrock may be
difficult to dredge, especially where the bedrock is close to the existing
ground surface.
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The CPT probes did not indicate a distinguishable difference between the
weathered bedrock or competent less weathered bedrock. However, the CPT
probings did indicate that portions of the bedrock within the marina site
contained dense layers.
A subsurface profile along the proposed bulkhead as encountered in our borings
is presented as Figures 2, 3, and 4 (X-Sections A -A', B-B' and C-C').
Site Grading
Recommended site preparation measures include the removal of all vegetation,
existing or abandoned utilities and any other deleterious materials in the
shower/storage structures and parking areas. On -site soils in the shower/
storage buildings and parking areas and to 3 feet beyond the building and
parking areas should be removed and recompacted to provide at least 1 foot of
compacted soil beneath building slabs and pavement sections. The exception
being the shower/storage structure on the pile supported pier.
The excavated on -site soils above the groundwater level may be reused as
compacted fill provided they are free of deleterious substances and have a
suitable moisture content to obtain proper compaction. Dredged soil would
have to be dried significantly before it could be used as compacted fill.
Also dredged soil may contain significant chlorides and sulfates such that it
may be corrosive to metal or concrete. Any soil imported from off -site
sources should be nonexpansive and be approved by the Soil Engineer or his
representative prior to placement.
Acceptable fill material should be placed in lifts not exceeding 8 inches in
thickness when loose and should be properly compacted to at least 90 percent
of the maximum dry density as determined by ASTM Test Method D1557. On -site
materials should be compacted with the water content at least 2 percent above
optimum as determined from ASTM Test Method D1557. The placement and
compaction of all fill should be performed under the observation and testing
of the Soil Engineer representative.
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• Building Foundations
Because of the variability of the dredged fill and the areas of potential
liquefaction we recommend that the shower/storage structure on the west side
of the site be supported by a mat foundation. Even though the structure is
anticipated to be relatively light with short spans, total settlement is
estimated to be approximately 1/2 inch because of the loose sands. However,
during a strong seismic event, if liquefaction occurs, total settlement could
be 1 inch or greater. The use of a mat foundation would virtually eliminate
idifferential settlement and, in the event of liquefaction, the structure would
most likely still be functional.
Mat foundations can be designed using an allowable net bearing value of
1500 psf.
The northernmost shower/storage structure can be supported by spread footings
founded on bedrock at least 2 feet below the lowest adjacent grade. These
footings can be designed using an allowable net bearing value of 2500 psf.
• The floor slab for this building can be supported on a 1-foot zone of
compacted fill overlying bedrock.
( We recommend that a moisture barrier such as a 8-mil visqueen be used under
interior slabs. The moisture barrier should be covered with 2 inches of
coarse sand to facilitate concrete curing and to protect the visqueen.
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Adequate provisions are to be made to limit and/or prevent moisture content
changes in the subgrade beneath footings and floor slabs. These should
include positive drainage away from building foundations with a minimum
gradient of 2 percent and properly sealed joints for interior piping beneath
interior and exterior slab areas.
Building Lateral Resistance
Resistance to lateral loads for the shower/storage structures can be assumed
to be provided by passive earth pressure and by friction acting on structural
components in permanent contact with the subgrade soils.
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• Passive earth pressure on the sides of footings may be assumed equal to that
exerted by an equivalent fluid weighing 200 pcf, subject to a maximum pressure
of 2000 pcf. A coefficient of friction of 0.3 may be assumed with dead load
forces of slab -on -grade or footings in permanent contact with subgrade soils.
Steel Sheet Pile Bulkhead
A sheet pile bulkhead system is planned to be installed in a "U" shape
around the site. Tieback or batter pile anchors are planned to be installed
r as part of the bulkhead system.
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During a significant seismic event loose sand layers below the dredge line may
liquefy and loose passive resistance which may result in toe kick -out of
sheeting not installed sufficiently deep. Therefore, for sheeting design
purposes, we recommend that passive resistance be neglected between -15 and
-25 MLLW for the western and southern sides of the proposed bulkhead.
The steel sheet piles may be designed using the allowable parameters presented
in Table 1.
TABLE 1
SOIL PARAMETERS FOR BULKHEAD DESIGN
Equivalent Fluid
11 Pressure (psf) 11
Active Earth Pressure 40
At Rest Earth Pressure 50
Passive Earth Pressure 200
Driving steel sheet piles may encounter hard driving when attempting to
penetrate bedrock. The use of vibratory hammers as well as impact hammers
may be considered.
Tiebacks can consist of drilled grouted anchors, deadman anchors or driven
batter piles. Drilled grouted anchors obtain resistance along the anchor
length while deadman anchors obtain resistance from passive earth pressure
against the anchor face. Driven batter piles obtain their resistance from the
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• frictional component of the soil -pile interaction. Anchor resistances for the
drilled grouted anchors, deadman anchors, and driven batter piles should be
calculated beyond a 35 degree line extending upward from the point of zero
moment in the bulkhead. Anchors to be located below the groundwater level
should be installed with techniques to prevent soil disturbances or the area
should be dewatered and observed by the soils engineer's representative prior
to placing grout or concrete. Drilled grouted anchors should be prestressed
to 150% of the design load prior to applying the working load. If drilled
` grouted anchors as described above are not feasible, we recommend the use of
t deadman anchors or driven batter piles.
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The allowable capacity of tieback anchors, deadman anchors, and driven batter
piles are presented in Table 2.
TABLE 2
ALLOWABLE BULKHEAD ANCHOR CAPACITY
Drilled Grouted Anchors* 750 DL
Deadman Anchors
Driven Batter Piles**
Notes:
200 A
70X + 2.5X2
D = Diameter of drilled anchor
L = Length of drilled anchor beyond the 35 degree line
A = Area of deadman parallel to bulkhead
X = Length of pile beyond the 35 degree line
• = For tiebacks drilled 20 degrees from horizontal
'* = For batter piles driven 20 degrees from vertical
Because of the liquefaction potential of loose sands near the groundwater
level at the western and northwestern portions of the site, we recommend the
use of deadman anchors in these two areas.
Pile Suaoorted Pier
The pile supported pier can be supported by driven piles consisting of
prestressed -precast concrete piles, pressure -treated timber piles, steel-H
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piles or concrete -filled steel pipe piles. Even though the on -site soils and
saltwater are corrosive to steel, concrete -filled steel pipe piles because of
their ease of installation with anticipated variable length piles, have
significant advantages over the other pile types.
Allowable vertical single pile capacities for 12-inch-diameter concrete -filled
steel pipe piles are presented in Figure 5. Uplift capacities of single piles
and capacities of batter piles are presented as Figure 6.
Center -to -center spacing between adjacent piles should be at least 3 pile
diameters. For piles spaced less than 3 pile diameters apart a pile group
efficiency factor will have to be incorporated.
We recommend that the hammer to be used to drive the piles have a driving
energy of 24,000 ft-lbs or less if the pile selected is a 12-inch-diameter
pipe pile. If another type or size pile is selected we can evaluate the
possible range of hammer energies or hammers selected.
Floating Docks and Boat Slips
The proposed floating dock guide piles are intended to provide lateral support
[ for the floating docks and boat slips due to waves, currents, and vessel
impacts. For these guide piles we have only considered 12-inch-diameter
concrete -filled steel pipe piles. These guide piles have been evaluated as
individually free standing piles. We expect very similar driving conditions
as previously stated under the section "Pile Supported Pier". The only
difference being that the depth to sound bedrock for the guide piles is
l expected to be more variable than for the piles supporting the pier because
of the larger area involved.
Lateral Loads For Piles
A laterally -loaded pile analysis was conducted using pile properties for a
hollow 12-inch-diameter steel pipe pile along with soil properties evaluated
for the subject site. The piles were assumed to have free heads with a
maximum horizontal deflection at the mudline of 0.5 inch. Two cases were
considered: (1) pile in bedrock; (2) pile in sand.
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Resulting lateral capacities, depths to maximum and zero moments, and minimum
pile embedments are presented in Table 3. The design values for sand soils
given in Table 1 generally are based on the assumption that the soils
penetrated by the driven piles will be at least firm and/or medium dense in
consistency. Some of the sediments may, in fact, be loose or soft, and
therefore, piles could be dislocated or knocked out of plumb by lateral loads
caused by a seismic event or other forces. We understand that piles so
affected will be reset and redriven. If the piles are filled with concrete,
the lateral capacity will be greater and could be analyzed if more lateral
capacity is desired.
TABLE 3
LATERAL PILE DESIGN CRITERIA
STEEL PIPE PILES
Case 1 Case 2
Free Head (Pilo in Bedrock) (Pile in Sand)
Lateral Capacity, P, kipsa 2.0 1.5
Maximum Moment, ft.-kipsb 40.0 30.0
Depth to Maximum Moment, ft.a 1.5 3.5
Depth to Zero Moment, ft.a 12.5 14.2
Minimum Pile Embedment
Length, ft.' 13.0 15.0
a) Lateral capacity is based on 0.5 Inch deflection at mudline.
b) Moment is for the horizontal load, P, applied at the top of pile; If the horizontal
load Is in kips, the moment will be in foot•kips.
c) Below mudline
Retaining Walls
The earth pressure behind any buried walls depends primarily on the allowable
wall movement, type of backfill materials, backfill slopes, wall inclination,
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surcharges, and any hydrostatic pressure. The equivalent fluid pressures
presented in Table 4 are recommended for vertical walls with no hydrostatic
pressure, and no surcharge. Also the equivalent fluid pressures recommended
for the hydraulic fill assumes a level backfill whereas the pressures
recommended for bedrock assumes a 2:1 (H:V) backfill.
TABLE 4
RETAINING WALL EQUIVALENT FLUID PRESSURES
Wall Movement Hydraulic Fill Bedrock
(pcf) (Pcf)
Free to Deflect 40 60
Restrained 60 SO
• These values are applicable for backfill placed between the wall stem and an
imaginary plane rising at 45 degrees from below the edge (heel) of the wall
footings. The surcharging effect of anticipated adjacent loads on the wall
( backfill (e.g., traffic, footings) should be included in the wall design.
Depending on whether the wall is free to deflect or restrained, 35 or 50
percent, respectively, of a maximum surcharge load located within a distance
equal to the height of the wall should be used in design for lateral earth
pressures.
Rockfalls or ravelling of the exposed weathered bedrock can expected along
the bluffs at the northern property line due to the steepness of the slope.
We recommend that consideration be given to an extension of the wall above the
slope (free board) and that a rockfall catch fence also be considered over
those portions of the retaining wall where debris could come down the slope.
Except for the upper 2 feet, the soil immediately adjacent to backfilled
retaining walls above the groundwater level (minimum horizontal distance of
about 2 feet measured perpendicular to the wall) should be free -draining
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is filter material. Weep holes and/or drain pipes should be installed at the
base of these walls. In lieu of filter material, crushed stone protected from
C clogging with the use of synthetic fabric between the natural soil and the
gravel may be used.
II
Corrosion Potential
Laboratory chemical tests previously performed on soil samples from the site
indicated sulfate concentrations between 385 and 398 ppm, chloride
concentrations generally between 408 and 1215 ppm, and pH between 7.65 and
7.8. Laboratory resistivity tests indicated values between 600 and 850 ohm -cm
for the on -site soils.
Soils with sulfate concentrations less than 1000 ppm generally are considered
to have a low corrosive effect on ordinary concrete, and, therefore, a Type
I portland cement may be considered for concrete that will be exposed to the
on -site soils. Soils with a chloride concentration more than 700 ppm and less
• than 1500 ppm generally are considered to have a severe corrosive effect on
mild grade steel. The resistivity test indicate that the on -site soils
generally are conducive to severe electrolytic -type corrosion. A corrosion
consultant familiar with the marine environment should be retained for the
development in light of the use of concrete bulkheads, pipe piles, and steel
sheet piles in the bay.
Liquefaction Potential
The term "liquefaction" describes a phenomenon in which a saturated
cohesionless soil loses strength and acquires a degree of mobility as a result
of strong ground shaking during an earthquake. The factors known to influence
liquefaction potential include soil type and depth, grain size, relative
density, groundwater level, degree of saturation, and both the intensity and
duration of ground shaking.
Liquefaction potential is reduced with increasing depth of overburden and is
generally not a concern at depths greater than 40 feet. However, since our
• borings encountered loose sands below groundwater within the upper 20 to 30
feet, liquefaction potential is moderate to high during strong ground shaking.
Converse Consultants OC
ai
14 W
• The areas of potential liquefaction are primarily on the western and
southwestern portions of the site. We recommend that in these areas shower/
storage structures be supported by a mat foundation and the bulkhead be
anchored by deadman anchors or batter piles.
Paving
All areas to be paved should be graded in accordance with the general
recommendations for site grading presented under "Site Grading". Prior to
placing base course or subbase material, the subgrade should be scarified to
a depth of at least 6 inches, moisture conditioned as required to obtain
optimum moisture conditions, and recompacted to at least 90 percent of the
maximum dry density.
Based on the laboratory R-value test of 10 obtained from a previous
exploration at the site for the on -site soils (the R-value will depend on the
` actual soil at the subgrade level after grading) and selected traffic index
values indicated below, the following minimum flexible pavement sections were
. computed. Our computations were based on the Caltrans Highway Design Manual,
4th edition.
Pavement Components (TI = 4) (TI = 6)
Asphalt Concrete 3 3.5
Aggregate Base 6 11.5
Total Pavement Thickness 9 15.0
Additional pavement sections can be presented upon request for imported fill
subbase or for different traffic index values. Selection of the traffic
indices should be made by your civil engineer based on his knowledge of
traffic flow and loadings. Base course should be crushed aggregate base or
processed natural material conforming with Section 200-2.2 or 200-2.4 Standard
Specifications for Public Works Construction.
Converse Consultants OC
isa
15 W
• Utilities
The on -site sandy soils are suitable for backfill of utility trenches from one
` foot above the top of the pipe to the surface, provided the material is free
of organic matter and deleterious substances. It is anticipated that most
natural soils will provide a firm foundation for site utilities. Any soft
and/or unstable material encountered at pipe invert should be removed and
replaced with an adequate bedding material.
r The on -site soils are not considered suitable for bedding or shading of
l utilities. Therefore, we recommend that nonexpansive granular soils be
imported for that purpose. Trench backfill soils should be compacted to at
least 90 percent of the maximum dry density as determined by ASTM Test Method
D1557.
CLOSURE
This report has been prepared for the exclusive use of Cash & Associates
• Engineers to assist the Project Engineer in the design of the proposed
development. It is recommended that we be engaged to review the final design
drawings and specifications prior to construction. This is to verify that the
t recommendations contained in this report have been properly interpreted and
are incorporated into the project specifications. If we are not accorded the
opportunity to review these documents, we can take no responsibility for
misinterpretation of our recommendations.
I r
•
We recommend that we be retained to provide soil engineering services during
construction of the excavation and foundation phases of the work. This is to
observe compliance with the design, specifications, or recommendations and to
allow design changes in the event that subsurface conditions differ from those
anticipated prior to start of construction.
The findings of this report are based upon our evaluation and interpretation
of the subsurface conditions encountered in the exploratory borings and the
results of the laboratory testing program. The soil conditions on the subject
Converse Consultants OC
7D
16 W
• site have only been determined at the specific boring locations. Conditions
between or beyond the borings may vary, and interpretation or extrapolation
of the results may not be appropriate, especially at shallow depths.
•
C
E
If the project plans change significantly (e.g., locations, building loads or
type of structures), we should be retained to review our original design
recommendations and their applicability to the revised construction. If
conditions are encountered during construction that appear to be different
than those indicated in this report, this office should be notified
immediately. Design and construction revisions may be required.
Our findings and recommendations were obtained in accordance with generally
accepted professional principles and practice in geotechnical engineering.
We make no other warranty, either express or implied.
Converse Consultants OC
t
E.m
Baerri
33 Lrgnt
<ir 'Lln.,��nr�
1�I�A 34—
i ;, O
Jgor- Harbor
4< QJQr
C Ught
Bay Ir-
park`. `'� �'�� �1`�'i 1' ",}•\' 23•::r.; •'.' `' 7n' '
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aq
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Par£%,
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'IsTarrd 1.
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_ trvme CoS:
j'',__ 7"—�\ ` BM
Country Cl
'err--- .T --"-Be¢COn�•��' :Irvine 7
Collins L—.mT--a�,r- nin �nrnrr-.l`rJi• _
tee
ch
N _ boa
1/
ark/n r f �W R y ;i7gQ�h�
L.'%P - _36
<...'
Light•`'I� c.
,
Reference: U.S.G.S., Newport Beach Quadrangle, 1965 (Photorevised 1972) p'1
ti
Scale: 1" = 2000'
Note: Map may be distorted due to reproduction process
SITE 'MAP
Castaways Marina Project No.
Newport Beach, California 90-32155-01
For: Cash & Associates Engineers
Figure No.
�... Converse Consultants Orange County 1
0 AT East
POINT 01
OFFSET 30
08 04
40 -10
06
0
I
Dredge
Marine Deposits
or Alluvium
Bedrock
Capistrano Formation
SB Yee 1DV GV.
DISTANCE ALONG PROFILE, FEET
SUBSURFACE PROFILE A -A'
Castaways Marina
Newport Beach, California
For: Cash & Associates Engineers
Converse Consultants Orange County
July 1990
Project No.
90-32155-01
Figure No.
2
0 AT East 0 North SO 260 AT East 26e North SO
POINT 03 es
-28
OFFSET
Dredge Fill (possibly ly some
Dredge Fill (possibly some
6-
bridge abutment fill in the
bridge abutment fill in the
g
of B_5'
vicinity of B-51
v1C vicinity
10-
IS
-
ze
Marine Deposits
PRE
and Alluvium
WW 3e-
40-
Bedrock
46-=
Capistrano Formation
60
B60
-
BE
0
20
40 Be Be 108 12e 148 ISO ISO 200 220 240
DISTANCE ALONG PROFILE, FEET
SUBSURFACE PROFILE C-C' JUIW 1990
Castaways marina Project No.
Newport Beach, California 90-32155-01
For: Cash & Associates Engineers
Figure No. 3
County
Converse Consultants Orange
0
0 AT East 30 North 0 350 AT East 30 North 350
POINT 03 02 01
OFFSET 10 10 -S
e
Dredge Fill
se
.'
Marine Deposits
'
and Alluvium
1
2e
2
F
30
W
_
w
x
0,
p, 3
w
A
•
ae
Bedrock
a
Capistrano Formation
60
S
60
6
0 SB 100 1.50 200 2S0 300 350
DISTANCE ALONG PROFILE, FEET
SUBSURFACE PROFILE B-B' July lase
Castaways Marina Project No.
Newport Beach, California 90-32155-01
For: Cash & Associates Engineers
�/►� Figure No.
Converse COnsultants Orange County 4
m
n
15
i 20
^ 25
++
a
30
c
35
40
a
u_
a
ALLOWABLE VERTICAL DOWNWARD CAPACITY (kips)
FOR SINGLE 12-INCH-DIAMETER PIPE PILES
in is 20 25 30
WSJ
DRIVEN SINGLE PILE DOWNWARD CAPACITY (kips)
Project Na
Castaway's Marina
Newport Beach, California 90-32155-01
For: Cash & Associates Engineers
Figure Na
Converse Consultants Oeotechnlcel Engineedng 5
orange County and Applled Sclences
0
a
I
i�
15
20
25
4j
v
w
� 30
a
w
0
35
40
ALLOWABLE UPLIFT CAPACITY (kips)
FOR SINGLE 12-INCH-DIAMETER PIPE PILES
5 10
15 20 25 30
DRIVEN SINGLE PILE UPLIFT CAPACITY (kips)
Castaway's Marina ProjmtNa
Newport Beach, California 90-32155-01
For: Cash & Associates Engineers
Figure Na
Converse Consultants Deolechnleal Engineering 6
Orange County and Applied Sciences
n
Z�
0
EXPLANATION
\ p Br Number and approximate location of boring by Converse Consultants.
�./ Orange County for this report
\" f
o•30.CCOC-1- . Number and approximate location of boring by Converse Consultants
R woo, 9
.-
Orange County, see report dated August 11, 1986
• -' -� .�,•./ ,' !� - !' � Oran
L G 35'
CCI-1+ Number and approximate location of boring by Converse Consultants,
Inc see re rt d ted A
�. •. po a ugust 16 1982
J At i i
r \ '� Number and a penetration test (CPT)
\ ` 1 C-1 approximate location of cone
�. � ,' !.• 2G.89' y I R. 110.00"AD � ` \ �- r'1 ` �, � ,.( 1, \ 1 � sounding by Converse Consultants for this report.
Contours of approximate top of bedrock elevation (feet NLLN)/
-01
000,
00
60
' 4
N�3' IO' 58 E •�� _ B-B \. • \ /
4•ll•19'07"
R•37930'
L+ "74 93'
d•47.33•Q6"
• 7 1 00'
• sa.e3' �;
r
,
CCI-5101IZ5.F (RAP)
5.
-C-4
CCI-4
C 1A \ APPROXIMATE LOCATION OF
SHOWER/STORAGE STRUCTURE, V
CCI-30.
8 ss,�°r \ Approximate Location of CCI-6
Art \ Proposed Bulkhead B-7 eA Qp
i"
-5
\ CCI-1 Tom' 4zoo
-
c
Scale:_ IN = 40-
i CCI-7 \ \ - CCOC- 8 EA D L IN E
\CCOC-1 APPROXIMATE, P U 5. t3UL,K14
LOCATION
_.
e EXISTING, OF APPROXIMATE LOCATION OF
B-5 \ CCI-?_ -
u gtoo.4� � BULKHEA PILE SUPPORTED PIER AND
SHOWER/STORAGE STRUCTURE
C,
It &V
to
6,4
�.�•p •LINE
_�• Note: This drawing is part of Converse Consultants Orange County
CCOC-2 project number 90-32155-01 and report dated 7/19/906,
LOCATION OF BORINGS
Castaways Marina "as shown
Newport Beach, California °'~ 7/19/90 90-32155-01
For: Cash 8 Associates Engineers "•andby LHG °rn"DN0
Chockod
424 Converse Consultants Orange County �, RK j I
L
C
A-1
FIELD EXPLORATION
The field exploration included a site reconnaissance and subsurface drilling.
During the site reconnaissance, the subsurface site conditions were noted and
the approximate locations of the test borings were determined.
The test borings were advanced using a CME 55 rotary wash drill rig equipped
for soil sampling. The soils were continuously logged by technical personnel
from our office, and visually classified in the field in general accordance
with the Unified Soil Classification System. The field descriptions have been
modified as appropriate to reflect laboratory results.
Relatively undisturbed samples of the subsurface soils were obtained at
appropriate intervals in the borings using a drive sampler (2 1/2-inches
inside diameter, 3-inches outside diameter) lined with sample rings. The
thin -walled steel sampler was driven into the bottom of the borehole with
• successive drops of a 140-lb hammer falling 30 inches. The blows for each six
inches of penetration were recorded and are shown on the Boring Logs. The
soil was retained in the brass rings of 2.50 inches in diameter and 1.00 inch
in height.
Where noted on the boring logs, standard penetration test (SPT) samples were
obtained using a 32-inch long split -spoon sampler, 2 inches outside diameter,
driven with successive drops of a 140-lb hammer falling 30 inches. The blows
were recorded from each 6 inches of penetration for a total penetration of 18
inches. The sum of the number of blows for the last 12 inches of an 18-inch
penetration is referred to as the "N" value.
The core penetration test is a method whereby the soil characteristic is
correlated to measurements taken from instruments within a core that is
` continuously pushed below the ground surface at a constant rate. The results
of the soundings present sleeve friction (FS), tip resistance (QC) and the
ratio between these two measurements. From the results the soil type and
• correlation to soil strength can be made.
A-2
• Elevations of the ground surface were determined at the boring location at the
time of drilling by estimation from a topographic map, dated November 29,
1989, prepared by Cash & Associates Engineers. The datum for the topographic
map was evaluated to be Mean Low Low Water (MLLW).
A key to soil symbols and terms, and logs of the borings are presented in the
following pages of this Appendix. Included on the logs are the soil
C descriptions, and pertinent field observation data.
r1
U
•
Page A- 4
904 Converse Consultants LOG OF BORING NO. 01
• �0 Orange County Sheet 1 of 4
C Project Castaway's Marina Project No. 90-32155-01 Date Drilled 6/7190
tN
c
7
•
Drilling Company/Driller Datum/Keith Equipment Rotary Wash Drill
Driving Weight (lbs)
140
Average Drop (in.) 30
Hole Diameter (in.) 3 7/8
Elevation +10 MLLW ft
Depth to Water
6.0 ft After hrs on
Geol/Engr R.K.
SUMMARY OF BORING
.oa
This log is part of the report prepared by Converse Consultants
4.1
E
Orange County for the named project and should be read together
wiEh that report for complete interpretation. This summary applies
the time drilling. ub-
Remarks
a
only at the location of this boring and at of
surface conditions may differ at other locations and may change at
1
C
a
a
N j
this location with the passage of time. The data presented is a
A
y
L j1
m L
simplification of actual conditions encountered.
O
N
m
O V)
7 el
D E S C R I P T I O N
A.C. = 3 inches A.B. = 6 to 12 inches
SC
Alluvium/Marine Deposits
Clayey Sand- loose, moist, brown to dark gray,
micaceous, fine- to medium -grained, rootlets
3
4
5
5
4
4
=
=
Bedrock Capistrano Formation
Siltstone; very weak, wet, dark gray, bedding
10
=
spacing .25 to 2 inches, light brown to brown where
highly weathered, claystone and sandstone interbeds,
jointed and fractured, staining at joints, gypsum
along bedding and joints, forams, micaceous
49
50/2"
=
weak to moderately, strong, dark olive green and
drown interbeds, laminated
15
50/3"
Page A- 5
L
04 Converse Consultants
• tO Orange County
•
0
LOG OF BORING NO. 01
Sheet 2 of 4
Project Castaway's Marina Project No. 90-32155-01 Date Drilled 6/7/90
Drilling Company/Driller Datum/Keith Equipment Rotary Wash Drill
Driving Weight (lbs)
140
Average Drop (in.)
30 Hole Diameter (in.) 3 7/8
Elevation +10 MLLW
ft Depth to Water 6.0
ft After hrs on
Geol/Engr R.K.
tu
0.
0
❑
ttl
S
E
•
to
to
a"
0
-+
m
H -a
a
C E
L 71
ON
.Oa
❑
m I
Lt a
to L
70
SUMMARY OF BORING
This log is part of the report prepared by Converse Consultants
Orange County for the named protect and should be read together
with that report for complete interpretation. This summary applies
only at the location of this boring and at the time of drilling. ub-
surface conditions may differ at other locations and may change at
this location with the passage of time. The data presented is a
simplification of actual conditions encountered.
OESCRIPT ION
Ramarkz
Bedrock Capistrano Formation
Siltsione; weak to moderatel strong, wet, dark
y2 light brown
gray, bedding spacing .25 to inches, to
brown where highly weathered, claystone and
sandstone interbeds jointed and fractured, staining
at Joints, gypsum along bedding and joints, forams,
micaceous
3
4
=
very weak, brown sandstone lenses, trace caliche
5
25
7
8
30
4
8
9
35
10
12
Page A- 6
404 Converse Consultants LOG OF BORING NO. 01
• �V Orange County Sheet 3 of 4
f Project Castaway's Marina Project No. 90-32155-01 Date Drilled 6/7/90
r
0
11
r
•
I
Drilling Company/Driller Datum/Keith Equipment Rotary Wash Drill
Driving Weight (lbs) 140 Average Drop (in.) 30 Hole Diameter (in.) 3 7/8
Rlevstinn +10 MLLW ft Denth
+1
41
W
O
U.
10
U)
f0
3
^i
m
U
IL
L 7
O N
H
0
E
W
U) 7
U) L
D O
r
DI
15
26
47
45
50/5"
50
13
44
50/5"
55
Page A- 7
C
r
r
L
r
Converse Consultants
Ig K06 Orange County
0
LOG OF BORING NO. 01
Sheet 4 of 4
Project Castaway's Marina Project No. 90-32155-01 Date Drilled 6/7/90
Drilling Company/Driller Datum/Keith Equipment Rotary Wash Drill
Driving Weight (lbs) 140 Average Drop (in.) 30 Hole Diameter (in.) 3 7/8
Elevation +10 MLLW ft Deoth to Water 6.0 ft After hrs on Geol/Engr R.K.
+i
Y
si
Ia
O
n.
i
pl
3
H
at
H ti
a
i M
ON
-'
a
E
N
m I
N L
0O
SUMMARY OF BORING
This his part of the report prepared by Convene Consultants
Orange County for the named project and should be read together
with that re ort for complete interpretation. This summary applies
p S
only nE the location of this boring and at the time of drilling. ub-
surface -conditions may differ at other locations and may change at
this location with the passage of time. The data presented is a
simplification of actual conditions encountered.
D E S C R I PT I0N
Remarks
End of boring at 60 feet
Free groundwater encounteredat 6 feet
Hole backfilled with drill cuttings on 6/7/90
65
70
75
Page A- 8
r
0
0
Converse Consultants
Orange County
LOG OF BORING NO. 02
Sheet 1 of 3
Project Castaway's Marina Project No. 90-32155-01 Date Drilled 6/6/90
Drilling Company/Driller Datum/Keith Equipment Rotary Wash Drill
Driving Weight (lbs) 140 Average Drop (in.) 30 Hole Diameter (in.) 3 7/8
Elevation +8 MLLW ft Depth to Water 6.0 ft After hrs on Geol/Engr R.K.
-'
SUMMARY OF BORING
n°
This log is part of the report prepared by Converse Consultants
+i
a
Orange County for the named project and should be read together
N
0
with that report for complete interpretation. This summary applies
p 9
time drilling.
Remarks
..,
only of the location of this boring and at the of ub-
surface conditions may differ at other locations and may change at
41
a
a
a a
to M
this location with the passage of time. The data presented is a
n.
a
E
e
o
0
e e
L a
U a
N a
simplification of actual conditions encountered.
O
nl
m
om
t9
D E S C R I PT 1 0 N
A.B. = 6 to 12 inches
SP
Dredged an Fill
Sand; loose, wet, brown, medium- to coarse -grained
3
5
5
Sz
2
SC
llvtm nn
clayey Sit= loose, wet, dark gray, medium- to
3
fine-grained, rootlets
10
17
medium dense
5
15
I
1
2
CL
Silty Clay; soft, wet, olive
Page A- 9
,04 �n Converse Consultants
V Orange County
LOG OF BORING NO. 02
Sheet 2 of 3
f Project Castaway's Marina Project No. 90-32155-01 Date Drilled 6/6/90
IC
r
0
Drilling Company/Driller Datum/Keith Equipment Rotary Wash Drill
Driving Weight (lbs) 140 Average Drop (in.) 30 Hole Diameter (in.) 3 7/8
Rlevatlnn +R MLLW £t Deoth to Water 6.0ft After hrs on Geol/Engr R.K.
SUMMARY OF BORING
a
This log is part of the report prepared by Converse Consultants
+i
E
Orange County for the named project and should be read together
t
a ti to
C.
with that report for complete interpretation. This summary applies
only at the location of this boring and at the time of drilling 8ub-
may differ at other locations and may change at
Remarks
.r
e
M t a
U I E U)j n
surface conditions
this location with the passage of time. The data presented is a
G.
~N
simplification of actual conditions encountered.
o
N
O N OL
D E S C R I P T I O N
CL
Atluvi}tm/MarituL ppms 5
Silty Clay; Wit, wet, olive
4
firm, olive green and dark gray, some gravels,
4
trace fine-grained sand
25
3 SP
Sand; loose wet, dark gray, medium- to
fine-grained, some olive silty clay
2
30
4 CL
Silty Clay; firm, wet, olive green, some dark gray
5
sand
35
2 ML
3
Sandy Silt and Clayey Silt; firm, wet, olive, some
4
dark gray sand and olive green clay
Page A- 10
0
0
4�04 Converse Consultants
.n�
V Orange County
LOG OF BORING NO. 02
Sheet 3 of 3
Project Castaway's Marina Project No. 90-32155-01 Date Drilled 6/6/90
Drilling Company/Driller Datum/Keith Equipment Rotary Wash Drill
Driving Weight (lbs) 140 Average Drop (in.) 30 Hole Diameter (in.) 3 7/8
Elevation +8 MLLW ft Deoth to Water 6.0 ft After hrs on Geol/Engr R.K.
-'
SUMMARY OF BORING
aThis
log is part of the report prepared by Converse Consultants
4+
E
orange County for the named project and should be read together
u ..,
U)
with that re ort for complete interpretation. This summary applies
only at the location of this boring and at the time of drilling. 3ub-
may differ at other locations and may change at
Ramarka
un.
3
a a
m j
surface conditions
this location with the passage of time. The data presented is a
IL
a
e
a
D
„{
9 t:
4 ]I
o D
m a
simplification of actual conditions encountered.
o
N
m
O N
n O
D E S C R I P T 1 0 N
ML
Alluvium//Marine Deoaci�
Sandy Silt and Clayey.Silt; firm, wet, olive, some
dark gray sand and olive green clay
14
=
Bedrock Capistrano Formation
15
=
Siltstone; very weak, wet, dark gray, bedding
spacing .25 to 2 inches, light brown to brown where
highly weathered, claystone and sandstone interbeds,
jointed and fractured, staining at joints, gypsum
=
along bedding & joints, forams, micaceous
45
8
16
7
50
11
=
olive, thinly bedded
12
55
6
12
dark brown with dark gray sandstone layers,
_—
End of boring at 58 feet
Free groundwater encountered at 6 feet
drill on 6/6/90
Hole backfilled with cuttings
Page A- 11
LConverse Consultants LOG OF BORING NO. 03
KoOrange County Sheet 1 of 4
( Project Castaway's Marina Project No. 90-32155-01 Date Drilled 616190
I r
A
Drilling Company/Driller Datum/Keith Equipment Rotary Wash Drill
Driving Weight (lbs) 140 Average Drop (in.) 30 Hole Diameter (in.) 3 7 8
Elevation +8 MLLW ft Depth to Water 10.0 ft After hrs on Geol/Engr R.K.
-'
SUMMARY OF BORING
a+
r
This to is part of the report prepared by Convene Consultants
Orange County for the named project and should be read together
,,
H .a
W
with that reFort for complete interpretation. This summary applies
p 9
only at the location of this boring and at the time of drilling ub-
Remarks
0
surface conditions may differ at other locations and may change at
u0
3
E
0
N ]
this location with the passage of time. The data presented is a
n.
u
E
E
0
o
e
L a
U o
V a
simplification of actual conditions encountered.
O
N
in
ON
Mfg
D E S C R I PT I0N
A.B. = 6 to 12 inches
Alluvium/Marine Deposits
SC
Clayey Sand; loose, moist, olive gray, medium- to
fine-grained
2
3
5
5
12
SP
Sand; medium dense, wet, dark olive gray, medium-
14
L7 to fine-grained
to
=
10
13
14
l5
13
SM
Silty Sand; medium dense, wet, dark olive gray
19
Page A- 12
r
FI
•
A
04�.n� Converse Consultants
� / Orange County
LOG OF BORING NO. 03
Sheet 2 of 4
Project Castaway's Marina Project No. 90-32155-01 Date Drilled 6/6/90
Drilling Company/Driller Datum/Keith Equipment Rotary Wash Drill
Driving Weight (lbs) 140 Average Drop (in.) 30 Hole Diameter (in.) 3 7/8
Elevation +8 MLLW ft Depth to Water 10.0 ft After hrs on Geol/Engr R.K.
-'
SUMMARY OF BORING
aThis
log is part of the report prepared by Converse Consultants
+�
E
Orange County for the named project and should be read together
N
N
with that report for complete interpretation. This summary applies
the time drilling.
Remarks
..�
as
onlpy at the location of Chia boring and at of ub-
aurface conditions may differ at other locations and may change at
a=i
o.
3
I
N E
this location with the passage of time. The data presented is a
a
0
E
a
0
E
L a
to 0
N L
simplification of actual conditions encountered.
O
N
m
O N
:) O
D E S C R I P T 1 0 N
SM
Alluviym/Marine Deposits
Silty Sand; medium dense, wet, dark olive gray
1
1
SC
Clayey Sand; very loose wet, dark olive green,
medium- to fine-grained
2
25
2
CL
Clay; soft, moist, olive green, plastic
3
30
2
5
stiff, some olive brown sand
5
35
13
16
—
aedr rock Capistrano Formation
Page A- 13
404 Converse Consultants LOG OF BORING NO. 03
•��2n
Orange County Sheet 3 of 4
( Project Castaway's Marina Project No. 90-32155-01 Date Drilled 6/6/90
:
•
•
Drilling Company/Driller Datum/Keith Equipment Rotary Wash Drill
Driving Weight (lbs) 140 Average Drop (in.) 30 Hole Diameter (in.) 3 7 8
Elevation +8 MLLW ft Deoth to Water _1.0.0 ft After hrs on Geol/Engr R.K.
+1
w
:
0.
e
[!
O.
E
E
N
3
0
,a
m
0
: a
I E
L a
O ttl
M
E
to
N 1
U 0
N s
DO
SUMMARY OF BORING
This log is part of the report prepared by Converse Consultants
orange County for the named project and should be read together
with that report for complete interpretation. This summary applies
onlyy at the location of this boring and at the time of drilling ub-
aurfacc conditions may differ at other locations and may change at
this location with the passage of time. The data presented is a
simplification of actual conditions encountered.
D E S C R I P T 1 0 N
Remarks
Bedrock Capistrano Formation
Siltstone; very weak, wet dark gray and olive
green, bedding spacing E to 2 inches, light brown to
brown where highly weathered, laminated, tointed and
fractured, staining at joints, gypsum along bedding &
joints, forams, micaceous
4
5
7
—
olive, brown staining, olive green sandstone
45
=
lenses
25
50/4"
so
—
weak to moderately strong, dark gray to black
17
28
48
55
503„
=
some caliche
Page A- 14
404 Converse Consultants LOG OF BORING NO. 03
KV Orange County Sheet 4 of 4
I Project Castaway's Marina Project No. 90-32155-01 Date Drilled 616190
I a
•
Drilling Company/Driller Datum/Keith Equipment Rotary Wash Drill
Driving Weight (lbs) 140 Average Drop (in.) 30 Hole Diameter (in.) 3 7/8
Elevation +8 MLLW ft Depth to Water 10.0 ft After hrs on Geol/Engr R.K.
aLi
tt
u
Cl
i
e
a
fD
a"
0
-1
0
a .n0
• e
S. 7
ON
-'
.oD
to 11
0 D
al t.
70
SUMMARY OF BORING
This his part of the report prepared by Converse Consultants
Orange County for the named project and should be read together
with that report for complete interpretation. This summary applies
only at the location of this boring and at the time of drilling ub-
surface conditions may differ at other locations and may change at
this location with the passage of time. The data presented is a
simplification of actual conditions encountered.
D E S C R 1 PT 1 0 N
Remarks
End ogfr boring at 60 feet
Hole 6/6/90
backflled with drillicutttingslonf
65
70
75
Page A- 15
r
t
L
46./n�n' Converse Consultants
.�
V Orange County
•
10
LOG OF BORING NO. 04
Sheet I of 4
Project Castaway's Marina Project No. 90-32155-01 Date Drilled 6/11/90
Drilling Company/Driller Datum/Keith Equipment Rotary Wash Drill
Driving Weight (lbs) 140 Average Drop (in.) 30 Hole Diameter (in.) 3 7/8
Elevation +10 MLLW ft Depth to Water 8.0 ft After hrs on Geol/Engr R.K.
Q
SUMMARY OF BORING
.on
This his part of the report prepared by Converse Consultants
be together
+i
E
Orange County for the named project and should read
with that repart for complete interpretation. This summary applies
the time drilling ub-
Remarks
t
+
a
3
a .0
it)0j
only at the location of this boring and at of
surface conditions may differ at other locations and may change at
this location with the passage of time. The data presented is a
IL
E
o
Y e
1.. 71
o 0
In L
simplification of actual conditions encountered.
O
N
m
co N
n O
D E S C R I P T I O N
A.B. = 6 to 12 inches
predg
SP
�Snd medium dense, moist, brown and gray,
fine-grained, some silt and clay
medium- to
2
7
9
5
Q
41
45
Sc
Alluvium/Marine Deposits
Clayey Sand; dense, wet, brown, some silt,
to
very
medium- to fine-grained
I
CL
Sandy Silty Clay; very soft, wet, brown, plastic,
I
fine-grained
15.
8
8
=
13 dr k Capistrano Formation
0
Page A- 16
404 Converse Consultants LOG OF BORING NO. 04
WOrange County sheet 2 of 4
Project Castaway's Marina Project No. 90-32155-01 Date Drilled 6111190
Drilling Company/Driller Datum/Keith Equipment Rotary Wash Drill
Driving Weight (lbs) 140 Average Drop (in.) 30 Hole Diameter (in.) 3 7/8
Elevation +10 MLLW ft Depth to Water 8.0 ft After hrs on Geol/Engr R.K.
.L
0.
a
❑
r
a
e
sl
N
a
0
-1
m
ti .1
a a
sl E
L 3
O N
-
M
N
N j
to 0
to L
O
SUMMARY OF BORING
This log is part of the report prepared by Converse Consultants
Orange County for the named project and should be read together
with that re ort for complete interpretation. This summary applies
only at the location of this boring and at the time of drillinq� ub-
au yace conditions may differ at other locations and may change at
this location with the passage of time. The data presented Is a
simplification of actual conditions encountered.
D E S C R I P T I O N
Remarks
Bedrock Capistrano Formation
Siltstone; very weak, wet, brown and gray, bedding
spacing .25 to 2 inches, light brown to brown where
highly weathered, claystone and sandstone interbeds,
jointed and fractured, staining at joints, gypsum
along bedding & joints, forams, micaceous
2
3
=
laminated
4
=_
zs
11
4
1
30
5
—
6
6
35
=
sandstone lenses
weak to moderately strong, trace caliche
28
50/4"
Page A- 17
I C
9
i.� Converse Consultants
�2 Orange County
LOG OF BORING NO. 04
Sheet 3 of 4
Project Castaway's Marina Project No. 90-32155-01 Date Drilled 6111190
Drilling Company/Driller Datum/Keith Equipment Rotary Wash Drill
Driving Weight (lbs) 140 Average Drop (in.) 30 Hole Diameter (in.) 3 7 8
Elevation +10 MLLW ft Depth to Water 8.0 ft After hrs on Geol/Engr R.K.
t
a
a
o
4
E
a
N
a
3
,�
m
U
.y .�
r 0
li 2
L 3
O N
y
N
0.
to a
in L
30
SUMMARY OF BORING
This his part of the report prepared by Converse Consultants
Ornnge County for the named project and should be read together
with that repart for complete interpretation. This summary appplies
only at the location of this boring and at the time of drilling Sub-
surface conditions may differ at other locations and may change at
this location with the passage of time. The data presented is a
simplification of actual conditions encountered.
D E S C R I P T 1 0 N
Remarks
Bedrock Capistrano Formation
Siltstone; weak to moderately strong, wet, dark
inches, light brown to
gray, bedding spacing .25 to 2
brown where highly weathered, claystone and
sandstone interbeds jointed and fractured, staining
at Joints, gypsum along bedding & joints, forams,
micaceous
15
35
50/5"
45
32
—
brown sandstone lenses
50/5"
so
=
20
5015"
55
—
dark gray sandstone lenses
40
50/3"
Page A- 18
04 Converse Consultants LOG OF BORING NO. 04
10 Orange County Sheet 4 of 4
[ Project Castaway's Marina Project No. 90-32155-01 Date Drilled 6111190
r
0
i
Drilling Company/Driller Datum/Keith Equipment Rotary Wash Drill
Driving Weight (lbs) 140 Average Drop (in.) 30 Hole Diameter (in.) 3 7/8
PUmntinn +10 MLLW ft Denth to Water 8.0 _ft After hrs on Geol/Engr R.K.
++
yLi
0
0.
O
G.
E
y
tll
(0
3
0
m
H ..�
a 0
E
y a
O N
-�
a
E
31
W
N Q.
p D
r<! s_
=0 O
SUMMARY OF BORING
Thie log is part of the report prepared by Converse Consultants
Orange County for the named protect and should be read together
wikh that report for complete interpretation. This summary applies
only at the location of this boring and at the time of drilling ub-
surface conditions may differ at other locations and may change at
this location with the passage of time. The data presented is a
Simplification of actual conditions encountered.
D E S C R I P T I O N
Remarks
End of boring at 60 feet
Free groundwater encountered at 8 feet
Hole back£illed with drill cuttings on 6/11/90
65
70
75
Page A- 19
0
C
c
Converse Consultants LOG OF BORING NO. 05
K0Orange County Sheet 1 of 3
Project Castaway's Marina Project No. 90-32155-01 Date Drilled 6/8/90
Drilling Company/Driller Datum/Keith Equipment Rotary Wash Drill
Driving Weight (lbs) 140 Average Drop (in.) 30 Hole Diameter (in.) 3 7 8
Elevation_+8 MLLW ft Depth to Water 7.0 ft After hrs on Geol/Engr R.K.
41
4.
X
Y
O
0
6
I
10
to
3
m
4 .a
p• ,p
L a
O N
-'
A
B
to j
N 0
D O
SUMMARY OF BORING
This log is part of the report prepared by Convene Consultants
Orange County for the named protect and should be read together
with that re ort for complete interpretation. This summary appliea
p 3S
only at the location of this boring and at the time of drilling ub-
surface conditions may differ at other locations and may change at
this location with the passage of time. The data presented is a
simplification of actual conditions encountered.
D E S C R I P T 1 0 N
Remarks
A.B. = 6 to 12 inches
r i
SP
and; loose, moist, brown, some gravels, shells,
medium -grained, clay, micaceous
8
7
5
4
SZ
1i
medium dense, wet, dark gray
to
26
27
dense
15
12
7
medium dense
Page A- 20
404 Converse Consultants LOG OF BORING NO. 05
• tO Orange County Sheet 2 of 3
j Project Castaway's Marina Project No. 90-32155-01 Date Drilled 618190
M1
f
Drilling Company/Driller Datum/Keith Equipment Rotary Wash Drill
Driving Weight (lbs)
140
Average Drop (in.)
30 Hole Diameter (in.) 3 7 8
L'lnvet;nn aR MT.T.W
ft T)enth to Water 7.0
ft After hrs on
Geol/Engr R.K.
a+
.c
C.
a
0
E
a
A
U
ti
m
12. E
L a
O W
-
a
E
n,
U O
In L
n 0
SUMMARY OF BORING
This log is part of the report prepared by Converse Consultants
Orange County for the named project and should be read together
with that refort for complete interpretation. This summary appplies
only at the location of this boring and at the time of drilling. Sub-
surface conditions may differ at other locations and may change at
this location with the passage of time. The data presented is a
simplification of actual conditions encountered.
D E S C R I P T 1 0 N
Remarks
SP
Alluv um/M rine Deposits
Sand; medium dense, wet, brown, some gravels,
medium -grained, micaceous
25
very dense
50/5"
'
25
14
26
dense
30
37
50/5"
.
very dense, coarse -grained
a
35
6
SC
13
]4
Alluvium/Marine Deposits
Clayey Sand; medium dense, wet, gray and olive
mottled, some cobbles
ON
Page A- 21
Converse Consultants LOG OF BORING NO. 05
• Orange County Sheet 3 of 3
Project Castaway's Marina Project No. 90-32155-01 Date Drilled 6/8/90
r
L
n
•
A
Drilling Company/Driller Datum/Keith Equipment Rotary Wash Drill
Driving Weight (lbs) 140 Average Drop (in.) 30 Hole Diameter (in.) 3 7/8
Elevation +8 MLLW ft Depth to Water 7.0 ft After hrs on Geol/Engr R.K.
'
SUMMARY OF BORING
.3
This log is part of the report prepared by Converse Consultants
H
N
Orange County for the named project and should be read together
with that report for complete interpretation. This summary applies
location this boring and at the time of drilling ub-
Remarks
a
ti
C a
only at the of
may differ at other locations and may change at
.c
G
o,
E
a
o
0
S 0
S
m 11
ii D
surface conditions
this location with the passage of time. The data presented is a
u
E
t
W 0
simplification of actual conditions encountered.
o
to
m
0In
3o
D E S C R I PT I0N
SC
Alluvium/Marine Deposits
Clayey Sand; medium dense, wet, gray and brown
mottled, some cobbles
3
CL
Silty Clay; firm, wet, olive green, micaceous, some
4
shells
45
5
3
SC
Clayey Sand; loose, wet olive green to dark gray,
micaceous, medium- to Fine-grained, some silt
3
50
5
—
Bedrock Capistrano Formation
5
=
Slltstone; very weak, moist, dark gray, bedding
spacing .25 to 2 inches, light brown to brown where
highly weathered, laminated, jointed and fractured,
staining atjoints, gypsum along bedding & joints,
=
forams, micaceous
55
3
3
6
End of boring at 58 feet
Free groundwater encountered at 7 feet
Hole backfilled with drill cuttings on 6/8/90
Page A- 22
C
Fa
r
0
0
n� Converse Consultants LOG OF BORING NO. 06
�.V Orange County Sheet I of 3
Project Castaway's Marina Project No. 90-32155-01 Date Drilled 6/8/90
Drilling Company/Driller Datum/Keith Equipment Rotary Wash Drill
Driving Weight (lbs) 140 Average Drop (in.) 30 Hole Diameter (in.) 3 7/8
Elevation +10 MLLW ft Denth to Water 10.0 ft After hrs on Geol/Engr R.K.
-'
SUMMARY OF BORING
S1
This log is part of the report prepared by Converse Consultants
+J
a
Orange County for the named project and should be read together
4
-
t\D
to
y
with that re ort for complete interpretation. This summary applies
p 9
the location of this boring and at the time of drilling. ub-
Remarks
tn.
s
.a
only. at
surface conditions may differ at other locations and may change at
4.
E
3
0
C E U u
this location with the passage of time. The data presented is a
simplification of actual conditions encountered.
s
O
a
0)
m
a 71 m a
ON DO
D E S C R I PT I0N
A.B. = 6 to 12 inches
Alluvium [[Mgrt ep3,00sits
CL
Sandy Clay_; stiff, moist, brown, mottled, some
gravels, shells
6
5
SC
ClSand; loose, et, brown and dark gray,
3
mottledayey, some shells, swome silt
5
2
10
24
=
Bedr Capistrano Formation
37
—
rock
Sfltstone; weak to moderately strong, wet dark
ggray, brown and olive bedding spacing .23 to 2 inches,
li ht brown to brown where highly weatheredt
claystone and sandstone interbeds, laminated, jointed
and fractured, staining at joints, gypsum along
bedding & jolnts,forams, micaceous
15
11
21
27
C
Page A- 23
I r
Converse Consultants LOG OF BORING NO. 06
Orange County Sheet 2 of 3
( Project Castaway's Marina Project No. 90-32155-01 Date Drilled 6/8/90
Drilling Company/Driller Datum/Keith Equipment Rotary Wash Drill
Driving Weight (lbs) 140 Average Drop (in.) 30 Hole Diameter (in.) 3 7/8
Elevation +10 MLLW ft Denth to Water 10.0 ft After hrs on Geol/Engr R.K.
4
.N
p
O
a
9
(a
_
3
..3
M
n. ,00
i 0
ON
13 -3
J3
rn j
so L
0O
SUMMARY OF BORING
This log is part of the report prepared by Converse Consultants
Orange County for the named project and should be read together
with that report for complete interpretation. This summary appliea
only at the location of this boring and at the time of drillin8 9ub-
surface conditions may differ at other locations and may Change at
this location with the passage of time. The data presented is a
simplification of actual conditions encountered.
D E S C R I PT I0N
Remarks
Bedrock Capistrano Formation
Siltstone; weak to moderately strong, wet, dark
gray, bedding spacing .25 toy inches, light brown to
brown where highly weathered, claystone and
sandstone interbeds jointed and fractured, staining
36
—
at joints, gypsum along bedding & joints, forams,
15
=
micaceous
25
5
8
15
30
—
20
27
35
—
13
23
38
Page A- 24
Converse Consultants LOG OF BORING NO. 06
• Orange County Sheet 3 of 3
i Project Castaway's Marina Project No. 90-32155-01 Date Drilled 618/90
`]
r
Drilling Company/Driller Datum/Keith Equipment Rotary Wash Drill
Driving Weight (lbs) 140 Average Drop (in.) 30 Hole Diameter (in.) 3 7/8
Elevation +10 MLLW ft Denth to Water 10.0 ft After hrs on Geol/Engr R.K.
a+
0.
•
0
•
a
11
IN
fD
a"
0
-+
in
H ..�
a a
• e
L 71
ON
M
N j
0 0
N L
70
SUMMARY OF BORING
This to is part of the report prepared by Converse Consultants
Orange County for the named pprotect and should be read together
with that report for compleke intarprekation. This summary appplies
andy at the location of this boring and at the time of drilling. Sub -
surface Conditions may differ at other locations and may Change at
this location with the passage of time. The data presented is a
simplification of actual conditions encountered.
D E S C R I PT 1 0 N
Rsmairks
—
Bedrock Capistrano Formation
siltstone; weak to moderatelyy strong, wet, dark
gray, bedding spacing .25 to 2 inches, light brown to
row bn where highly weathered, claystone and
29
=
sandstone interbeds jointed and fractured, staining
at joints, gypsum along bedding & joints, forams,
50/4
—
micaceous
45
—
19
30
49
50
34
50/5"
Ss
15
33
50/5"
_=
End of boring at 58 feet
Hole backf led on 6/8/90ered at 10 feet
Page A- 25
J
It
0
Converse Consultants
Orange County
LOG OF BORING NO. 07
Sheet I of 2
Project Castawav's Marina Project No. 90-32155-01 Date Drilled 6111190
Drilling Company/Driller Datum/Keith Equipment Rotary Wash Drill
Driving Weight (lbs) 140 Average Drop (in.) 30 Hole Diameter (in.) 3 7/8
Elevation +10 MLLW ft Depth to Water 8.5 ft After hrs on Geol/Engr R.K.
~
Z
4.
a
O
C
E
o
7l
a"
a
4
41
ti .i
a ,a
S E
4 E
ON
-'
J3
N
to j
0 0
V 4
7t7
SUMMARY OF BORING
This his part of the report prepared by Converse Consultants
Orange County for the named project and should be read together
with that report for complete interpretation. This summary appplies
only at the location of this boring and at the time of drilling. Sub-
surface conditions may differ at other locations and may change at
this location with the passage of time. The data presented is a
simplification of actual conditions encountered.
D E S C R I1)T I0N
Remarks
Bedrock Capistrano Formation
Siltstone; very weak moist, brown, bedding spacing
.25 to 2 inches, weathered, lointed and fractured,
bedding & joints,
staining at joints, gypsum along
forams, sandstone and claystone lenses
3
4
5
_—
5
Sz
23
=
wet, gray brown, laminated
24
10
44
50/5"
_—
weak to moderately strong
15
38
50/5"
Page A- 26
,04 Converse Consultants LOG OF BORING NO. 07
• KO Orange County Sheet 2 of 2
6 Project Castaway's Marina Project No. 90-32155-01 Date Drilled 6/11/90
r
L
A
Drilling Company/Driller Datum/Keith Equipment Rotary Wash Drill
Driving Weight (lbs)
140
Average Drop (in.)
30 Hole Diameter (in.) 3 7 8
Elevation +10 MLLW
ft Depth to Water 8.5
ft After hrs on
Geol/Engr R.K.
y
0.
e
[I
EL
e
e
N
3
0
,a
m
a
e E
s.
ON
a
In 7
Ct 0
m a
70
SUMMARY OF BORING
This to is part of the report prepared by Converse Consultant
Orange County for the named protect and should be read together
with that re ort for complete interpretation. This summary applies
onlyy at the location of this boring and at the time of drilling. ub-
aurfaee conditions may differ at other locations and may change at
this location with the passage of time. The data presented is a
simplification of actual conditions encountered.
D E S C R I PT 1 0 N
Remarks
End of boring at 20 feet
Free groundwater encountered at 8.5 feet
Hole backfilled with drill cuttings on 6/11/90
25
30
35
0
Page A- 27
401 Converse Consultants LOG OF BORING NO. 08
• iw Orange County Sheet 1 of 2
[ Project Castaway's Marina Project No. 90-32155-01 Date Drilled 6/11/90
r
l
I r
•
•
Drilling Company/Driller Datum/Keith Equipment Rotary Wash Drill
Driving Weight (lbs) 140 Average Drop (in.) 30 Hole Diameter (in.) 3 7/8
Elevation +10.5 MUNWt Deoth to Water 3.0 ft After hrs on Geoi/Engr R.K.
SUMMARY OF BORING
M
This to is part of the report prepared by Converse Consultants
be together
4+
E
to
Ora nge County for the named project and should read
with that report for complete interpretation. This summary applies
the time drillin6
Remarks
s
a
ti a
:
only at the location of this boring and at of ub-
surface conditions may differ at other locations and may change at
No.
C
to 11
this location with the passage of time. The data presented is a
u
a
-3
a
a L
simplification of actual conditions encountered.
a
(a
m
O N
::1O
D E S C R I P T I O N
A.B. = 6 to 12 inches
Alluvium/Marine Denosits
Clayey Sand; loose, moist, brown, micaceous,
SC
rootlets
Q
3
4
5
s
2
10
2
CL
Sandy Silty Clay; soft, wet, brown
2
2
firm, olive green
3
15
6
=
r ck Capistrano Formation
9
0
Page A- 28
u:�Converse Consultants LOG OF BORING NO. 08
• -i Orange County Sheet z of z
E Project Castaway's Marina Project No. 90-32155-01 Date Drilled 6/11/90
L
•
r
0
Drilling Company/Driller Datum/Keith Equipment Rotary Wash Drill
Driving Weight (lbs) 140 Average Drop (in.) 30 Hole Diameter (in.) 3 7/8
Elevation +10.5 MLLWft Depth to Water 3.0 ft After hrs on Geol/Engr R.K.
43
w
jC
Q.
a
O
Q.
e
•
to
-
as
0
-f
m
a a
� 3
L 3
ON
-'
a
N j
O o
to L
30
SUMMARY OF BORING
This log is part of the report prepared by Convene Consultants
Orange County for the named project and should be read together
with that report for complete interpretation. This summary ap lies
p pp
only at the location of this boring and at the time of drilling. Sub-
surface conditions may differ at other locations and may change at
this location with the passage of time. The data presented is a
simplification of actual conditions encountered.
D E S C R I P T I0N
Remarks
Bedr Capistrano Formation
rock
Siltstone; very weak, wet, dark gray, bedding
spacing .25 to 2 inches, light brown to brown where
highly weathered, ciaystone,and sandstone interbeds,
jointed and fractured, staining at joints, gypsum
along bedding & joints, forams, micaceous
7
7
8
25
End of boring at 25 feet
Free groundwater encountered at 3 feet
Hole backfilled with drill cuttings on 6/11/90
30
35
SLEETONS/SC
(FS)
TIP
TANCCEE fOC)
FRICTION/SG
RCENT
ATIO (F6/OC)
FON
TREE
FT
4
2
0
0
60 I00
ISO
200
0
4
8
0
0
10
-
10
20
20
90
30
m
m
y
�
x
x
40
40 z
z
m
m
m
60
50
60
60
70
70
60
60
CONE PENETRATION TEST SOUNDING NUMBER: C-1
PROJECT NAME CONVERSE/CASTAWAY LOCATION : NE4PORT BEACH
THE EARTH TECHNOLOGY
C CORPORATION
PROJECT NUMBER : 90-230-6604 DATE 06-11-1990
C
r
I
SLEEVE
FRICTION
(FS)
TIP RESISTANCE
(0C)
FRICTION
RATIO
PERCENT
(FS/OC)
TONS/SO
FT
TONS/SO
FT
4
2
0
0
SO 100
ISO
200
0
4
8
0
0
10
IO
20
20
30
30
co
rn
0
m
—�i
x
x
40 z
z 40
m
rrn
n
SO
SO
60
60
70
70
60
60
CONE PENETRATION TEST SOUNDING NUMBER: C-1A
PROJECT NAME CONVERSE/CASTAWAY LOCATION NEWPORT BEACH
� THE EARTH TECHNOLOGY
d CORPORATION
PROJECT NUMBER + 90-230-SB04 DATE 06-i1-1990
C
I'
c
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SLSSTONSRICTFON
(FS)
TIP
(GC)
FRIC71ONN
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(FS/OC)
TONS/SO
FT
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2
0
0
SO 100
ISO
200
0
4
S
0
0
10
10
20
20
30
30
o
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2
z 40
_
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n
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m
m
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SO
60
60
70
80
BO
CONE PENETRATION TEST SOUNDING NUMBER: C-2
PROJECT NAME : CONVERSE/CASTAWAY LOCATION NEWPORT BEACH
THE EARTH TECHNOLOGY
PROJECT NUMBER : 90-230-SSO4 DATE 06-11-1990
C CORPORATION
I'
SLEEVE
FRICTION
(FS)
TIP RESISTANCE
(GC)
FRICTION
RATIO
PERCENT
(FS/GC)
TONS/SO
FT
TONS/SG
FT
4
2
O
0
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ISO
200
0
4
S
0
0
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10
20
30
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0
m
s
x
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40
z
Z
m
m
m
-
SO
SO
SO
SO
701
L
70
80
90
TOP 2.0
FT IS OISTU"M
601L
CONE PENETRRTION TEST SOUNDING NUMBER: C-3R
PROJECT NAME : CONVERSE/CASTAWAY LOCATION NEWPORT BEACH
THE EARTH TECHNOLOGY
ECORPORATION
PROJECT NUMBER : 90-230-5604 DATE : 06-11-1990
I
I
I
SLEEVE
FRICTION
(FS)
TIP RESISTANCE
TONS/SG
IGCI
FT
FRICTIONN
RATIO
PERCENT
(FS/OC)
TONS/SO
FT
4
2
0
0
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ISO
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8
0
0
10
10
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x
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f
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SO
SO
SO
70
70
80
80
CONE PENETRATION TEST SOUNDING NUMBER: C-4
PROJECT NAME CONVERSE/CASTAWAY LOCATION = NEWPORT BEACH
THE EARTH TECHNOLOGY
PROJECT NUMBER 90-230-5604 DATE = 06-11-1990
CORPORATION
1
r
0
SLEEOOTTN(FS)
SLEEVE
TIP RESISTANCE
IOC)
FRICTIOPRATTIIO
PERCENT
(FS/GC)
TONS/SO
4
2
0
0
s0 t00
ISO
z00
0
4
8
0
O
10
t0
zG
za
30
30
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FR
x
40 Z
— 40
z
n
m
m
m
so
s0
80
80
70
70
80
80
CONE PENETRATION TEST SOUNDING NUMBER: C—S
PROJECT NAME CONVERSE/CASTAWAY LOCATION : NEWPORT BEACH
THE EARTH TECHNOLOGY
C CORPORATION
PROJECT NUMBER 90-230—SSO4 DATE s OS—I1-1990
r
I•
SLEETONS//FRICTION
(FS)
TIP
FT (OCl
FRICTION
RATIO
(FS/GCI
CEN
SG
FT
TONSSTANCESO
4
2
0
0
SO too
ISO
zoo
0
4
8
0
10
10
20
20
30
30
m
x
_
40
z 40
=
m
m+
m
SO
SO
80
60
70
70
80
80
CONE PENETRATION TEST SOUNDING NUMBER: C-S
PROJECT NAME CONVERSE/CASTAWAY LOCATION = NEWPORT BEACH
THE EARTH TECHNOLOGY
PROJECT NUMBER 90-230-5604 ORTE t 06-11-1990
CORPORATION
) m
r
L
L
SLEEVE
FRIC
FTN (FS)
TIP RESISTANCE
(GC)
FRICTIOTONS/8
PERATIO
(FS/GC)
FT
4
2
0
0
SO 100
ISO
200
0
4
6
0
0
10
10
20
20
30
30
m
m
-I
=
40
40 z
z
m
m
m
-
SO
SO
60
60
70
70
SO
SO
CONE PENETRATION TEST SOUNDING NUMBER: C-7
PROJECT NAME s CONVERSE/CASTAWAY LOCATION NEWPORT BEACH
THE EARTH TECHNOLOGY
C
PROJECT NUMBER: 90-230-6604 DATE 06-11-1990
CORPORATION
is
n
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LABORATORY TESTING
General Comments
A laboratory test program is designed for each project to evaluate the
physical and mechanical properties of the soil and rock materials encountered
at the site during the field exploration program. This appendix summarizes
the purposes of and procedures followed in performing the most frequently
assigned tests. The laboratory testing program for this project did not
L include all of the tests described herein. Results of the tests performed
for this study are included at the end of this appendix.
i r
The soil samples stored in CCOC's laboratory for this project are discarded
30 days after the date of this report unless a request and retainer to store
the samples for a longer period of time has been received within that 30-day
period.
Classification
• Classification testing is performed to identify differences in material
behavior and to correlate the results with shear strength and volume change
characteristics of the materials. Classification testing includes moisture
content, unit weight, grain -size analysis, sand equivalent, and Atterberg
limits. The classification tests are performed in general accordance with
procedures of the American Society for Testing and Materials (ASTM).
Test ASTM Method
Moisture Content
D2216
Unit Weight
02937
Grain Size Analysis
Sieve
C136
Hydrometer
D422
Sand Equivalent
D2419
Atterberg Limits
D4318
Volume Change
Consolidation tests are performed in general accordance with ASTM test method
D2435 to determine the load -deformation characteristics of the soils. The
soil specimen, contained in a 2.42-inch-diameter, 1.00 inch high sampling
ring, is placed in a loading frame under a seating pressure of about 0.1 ksf.
G
[M
• The pressure is then increased to about 0.5 ksf, and the specimen is allowed
to consolidate. The specimen is subsequently loaded in increments equal to
the previous pressure and allowed to consolidate under each increment. The
vertical deformation is recorded as a function of time.
When the pressure reaches a pre -selected effective overburden pressure and
the specimen has consolidated under that pressure, the laboratory technician
adds water to the test cell and records the vertical movement. After the
specimen reaches equilibrium with addition of water, the technician continues
the loading process, usually up to a pressure of about 8 ksf. The results of
the test are presented in terms of percent volume change versus applied
vertical stress.
The potential for soil and rock expansion due to wetting is evaluated from
results of an expansion index test performed in general accordance with
r Uniform Building Code Standard 29-2. In this test, a specimen is compacted
to a degree of saturation between 40 and 60 percent in a 4.01-inch-diameter,
1.00 inch high ring. The specimen is subjected to a seating pressure of 144
• psf, water is added to the test cell, and swell is monitored until the
expansion stops. The volume of swell is converted to an expansion index.
r
Other methods to measure expansion potential due to wetting include a swell
test and a swell -pressure test. In a swell test the sample, either at natural
moisture content, air dry, or remolded to 90 percent of maximum density at
optimum moisture, is subjected usually to a seating pressure of 60 psf. Water
is then added to the test cell, and the expansion of the soil is monitored.
The final expansion is reported as percent swell.
L
In a swell -pressure test, the specimen, contained in a sampling ring and at
natural moisture content, is placed in a loading frame and subject to a
seating pressure of about 100 psf. Water is added to the test cell, and the
volume change is recorded until it essentially ceases. After the swelling is
complete, the technician loads the specimen in increments equal to the
previous load and allows the specimen to consolidate under each load. The
W
specimen is consolidated back to zero volume change; the corresponding
pressure is called the swell pressure. The swell pressure test is sometimes
performed on a remolded specimen compacted to about 90 percent of maximum
density and at optimum moisture content.
Shear Strength
Estimates of undrained shear strength of cohesive soils can be obtained with
a hand (pocket) penetrometer. In this test, a small diameter, hand-held probe
[ is pushed a specified distance into a soil sample, and the shear strength is
estimated from the compression of a calibrated spring.
The direct shear test, performed in general accordance with ASTM D3080, is
used to measure the shear resistance of both cohesive and granular materials.
In this test, the specimen, in a 2.42-inch-diameter, 1.00 inch high ring, is
usually allowed to soak under a seating pressure of about 100 psf. A vertical
stress is applied to the specimen, and the specimen is allowed to reach an
equilibrium state (swell or consolidate). The specimen is then sheared under
a constant rate of deformation. The rate of deformation for a slow test is
• selected from computed or measured consolidation rates to allow full drainage
(full dissipation of any tendency for pore water pressure changes) during
r shear. The rate of deformation for a quick test is usually taken as 0.05
in./min, which results in failure being reached within two to three minutes.
Residual shear resistances of fast tests are obtained by shearing the specimen
past the peak shear resistance, resetting the specimen to zero displacement,
shearing to a constant resistance, and repeating the process three to five
times until the shear resistance has stabilized. In the case of slow tests,
the residual shear is measured by cycling the specimen between deformations
of about ±7 percent of the specimen diameter until an equilibrium shear stress
is reached.
Three methods are used to obtain data points to construct a failure envelope
from quick direct shear tests. Tests are performed on three or more specimen,
each under different vertical stresses; three or more tests are performed on
a single specimen, but the specimen is shifted for each test under different
vertical stresses so new surfaces are sheared each time; three tests are
performed on a single specimen in a multiple stage test. In a multiple stage
Is
M
IL
M
I
test, we stop the shear test near but before failure is reached. The
displacement is reset to zero, a higher vertical load is applied, and the
shear process is repeated. Finally, the displacement is reset to zero, the
largest vertical load is applied, and the specimen is sheared to failure. In
the case of slow tests, usually three or more specimens are used, each at
different consolidation pressures to generate a failure envelope.
Pavement design includes an assessment of subgrade resistance, which is
measured by an "R"-value or a bearing ratio test, CBR (California Bearing
Ratio). The R-value test is performed in general accordance with ASTM Test
Method D1883.
Compaction
Compaction tests provide information on the relationship between moisture
content and dry density of the soil compacted in a given manner. The maximum
density is obtained for a given compaction effort at an optimum moisture
content. Specifications for earthwork are in terms of the unit weight (or
• density) expressed as a percentage of the maximum unit weight and the moisture
content compared to the optimum moisture content. The compaction test is
performed in general accordance with ASTM D1557.
Sulfate Test
Soluble sulfate concentrations of soils are measured in general accordance
with California Department of Transportation test procedure 417 to provide
information on the potential for concrete in contact with the soil to
deteriorate because of soluble sulfates.
I"
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SUMMARY OF MATERIAL PROPERTIES
Castaway's Marina - Dover Dr. 8 PCH, Newport Beach
90-32155-01
POINT DEPTH ASTM LL PI FINES WATER DRY VOID SATUR- MA%.DRY OPT. PHI CORE- CONSOL
IDENTIF- CLASSIF- CONTENT DENSITY RATIO ATION DENSITY MOIST. ANGLE SION
ICATION feet ICATION R % % % pcf SG=2.7 % pcf % deg. ksf
............................................................................................................
01 9.80 31
01 19.80 28
01 29.80 77 62 63 1.6895 100
01 39.80 66 60 1.7902 99
01 59.80 35 82 1.0556 90
02 2.30 47
02 12.50 17
02 22.50 44
02 32.50 40 80 1.1158 98
02 36.80 82 59
02 42.50 37 83 1.0290 98
02 52.50 52 64 1.6203 87
03 3.80 27 20
03 9.80 23
03 19.80 23
. 03 29.70 63 1.6576 17 0.19
03 29.80 51 69 1.4368 96
03 39.80 47 73 1.3015 97
03 49.80 55 66 1.5592 95
03 59.80 43 78 1.1613 100
04 9.80 21 106 0.5835 95
04 19.80 61
04 39.80 53 67 1.4977 96
04 49.80 38 77 1.1995 86
04 59.80 49 70 1.3970 95
05 2.50 20
05 12.50 SP-SM NP NP 5 19
05 22.50 21 104 0.6258 90
05 32.50 19 110 0.5264 95
05 42.50 88 55 66 1.5349 97
05 52.50 51 70 1.4020 99
06 2.50 18
06 12.50 97 51 67 1.5213 91 22 0.73
06 22.50 53 67 1.5202 95
06 32.50 79 53 2.1906 97
06 42.50 72 57 1.9581 99
06 52.50 47 72 1.3528 94
CONVERSE CONSULTANTS June 1990
1of2
I
u
t3
•
I
SUMMARY OF MATERIAL PROPERTIES
Castaway's Marina - Dover Dr. & PCH, Newport Beach
90-32155-01
POINT DEPTH ASTM LL PI FINES WATER DRY VOID SATUR- MAX.DRY OPT. PHI COME- CONSOL
IDENTIF- CLASSIF- CONTENT DENSITY RATIO ATION DENSITY MOIST. ANGLE SION
ICATION feet [CATION % % % % pcf SG=2.7 % pcf % deg. ksf
------------------------------------------------------------------------------------------------------------
07 9.80 44 74 1.2783 93
07 19.80 39 79 1.1434 92
08 9.80 30 93 0.8175 100
08 19.80 64 50 2.3388 74
CONVERSE CONSULTANTS June 1990
2of 2
w
9m
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i
I
UNIFIED SOIL CLASSIFICATION
BOULDERS & I
GRAVEL
I SAND
SILT OR CLAY
COARSE
I FINE
ICOARSEI
MEDIUM
I INE
COBBLES I
U.S. SIEVE SIZE IN INCHES I U.S. STANDARD SIEVE No. HYDROMETER
3 3/4 3/8 4 10 20 40 60 140 200 0
10
20
8C
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1000 100 10 1 0.1 0.01 0.001
CIRAIN SIZE IN MILLIMETERS
Boring LL PI
Symbol Number Depth, ft D/o Mo Descrintion
❑ 01 29.8 Olive Sand with Silt (SP-SM)
GRAIN SIZE DISTRIBUTION
Castaway's Marina Project No.
Dover Dr. & PCH, Newport Beach 90-32155-01
Converse Consultants Orange County
A
Min
•
U
UNIFIED SOIL CLASSIFICATION
BOULDERS &
GRAVEL
SAND
SILT OR CLAY
COARSE
FINE
COARSE
MEDIUM
FINE
COBBLES
U.S. SIEVE SIZE IN INCHES U.S. STANDARD SIEVE No. I HYDROMETER
3 3/4 3/8 4 0 20 40 60 140 200 0
10
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11100
1000 100 10 1 0.1 0.01 0.001
GRAIN SIZE IN MILLIMETERS
Boring LL PI
Symbol Number Depth, ft °/D /b Description
❑ 02 36.8 Dark Bn Clay with Sand Organic (CL)
GRAIN SIZE DISTRIBUTION
• Castaway's Marina Project No.
Dover Dr. & PCH, Newport Beach 90-32155-01
Converse Consultants Orange County
IN
B-9
i
•
A
UNIFIED SOIL CLASSIFICATION
BOULDERS &
GRAVEL
I SAND
SILT OR CLAY
COARSE
I FINE
COARSE
MEDIUM
FINE
COBBLES
U.S. SIEVE SIZE IN INCHES
I U.S. STANDARD SIEVE No. I HYDROMETER
3 3/4 3/8
10 20 40 60 140 200 0
10
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OR(AIN SIZE IN MILLIMETERS
Boring LL PI
Symbol Number Depth, ft D/D % Description
O 03 3.8 Gray Bn Silty Sand Lumps of Clay (SM-SC)
GRAIN SIZE DISTRIBUTION
Castaway's Marina Project No.
Dover Dr. & PCH, Newport Beach 90-32155-01
Converse Consultants Orange County
W
•
0
0
UNIFIED SOIL CLASSIFICATION
BOULDERS &
GRAVEL
SAND
SILT OR CLAY
I COARSE
I FINE
COARSE
MEDIUM
FINE
COBBLES
U.S. SIEVE SIZE IN INCHES U.S. STANDARD SIEVE No. HYDROMETER
3 4 3/8 4 10 20 40 60 140 200 0
10
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GRAIN SIZE IN MILLIMETERS
Boring LL PI
Symbol Number Deoth, ft % % Description
❑ 05 12.5 NP NP Dark Gray Sand with Shells (SP)
GRAIN SIZE DISTRIBUTION
Castaway's Marina Project No.
Dover Dr. & PCH, Newport Beach 90-32155-01
Consultants
D-11
•
F
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4
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UNIFIED SOIL CLASSIFICATION
BOULDERS &
GRAVEL
SAND
SILT OR CLAY
COARSE
FINE
COARSE
MEDIUM
FINE
COBBLES'
U.S. SIEVE SIZE IN INCHES U.S. STANDARD SIEVE No, HYDROMETER
3 3/4 3/8 4 0 20 40 60 140 200 0
10
8
20
F
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m
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1000 100 10 1 0.1 0.01 0.001
GRAIN SIZE IN MILLIMETERS
Boring LL PI%
Svmbol Number Depth, ft % Description
❑ 05 42.5 Dark Gray Silt with Organic (ML/MH)
GRAIN SIZE DISTRIBUTION
Castaway's Marina Project No.
Dover Dr. & PCH, Newport Beach 90-32155-01
Converse Consultants Orange County
if-14
PJ
UNIFIED SOIL CLASSIFICATION
BOULDERS &
GRAVEL
I - SAND
SILT OR CLAY
COARSE
I FINE
COARSE
MEDIUM
FINE
COBBLES
U.S. SIEVE SIZE IN INCHES U.S. STANDARD SIEVE No. I HYDROMETER
3 3/4 3/8 4 0 20 40 60 140 200 0
1Oc
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3 6
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80
2
100
1000 100 10 1 0.1 0.01 0.001
GRAIN SIZE IN MILLIMETERS
Boring LL PI
Symbol Number Denth, ft % % Description
❑ 06 12.5 Dark Bn Consol. Silt (ML)
GRAIN SIZE DISTRIBUTION
Castaway's Marina
Dover Dr. & PCH, Newport Beach
Converse Consultants Orange County
Project No.
90-32155-01
D-1J
0
1
F
x
O
H
W
x
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5
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100
VERTICAL STRESS,
ks£
Boring Number :
07
Description
Dark Bn Silty Clay Lenses of Sand (CL-ML)
Depth, It
9.8
Liquid Limit
Specific Gravity :
2.70
Plastic Limit
Moisture
Dry Density
Percent
Void
Content, %
pcf
Saturation Ratio
Initial
48.1
72.2
97
1.336
Final
73.9
47.3
78
2.564
Note: Sample was Saturated @ 1.50 ksf
CONSOLIDATION TEST
. Castaway's Marina
Dover Dr. & PCH, Newport Beach
Converse Consultants Orange County
Project No.
90-32155-01
C
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1.
dF I I I I I I I L
.0 0.5 1.0 1.5 2.e 2.5 3.0 3.5 4.0
NORMAL STRESS, ksf
Boring Number : 03 Description
Olive & Gray Silty Clay (CL-ML)
Depth, ft 29.7 Cohesion, ksf
0.19
Specific Gravity : 2.70 Friction Angle, degrees
17
Moisture Dry Density Void
Normal
Shear
Content, % pcf Ratio
Stress, kef
Stress, ksf
62.3 62.2
1.00
0.49
61.3 63.4
2.00
0.80
58.5 64.7
4.00
1.40
Note: Rate of Deformation 0.05 in/min
Plot Corresponds to Peak Values
DIRECT SHEAR TEST RESULTS
. Castaway's Marina Project No.
Dover Dr. & PCH, Newport Beach 90-32155-01
Converse Consultants Orange County
B-15
r
r
6
4
4
3
el 1 1 1
0.0 0.6 1.0 1.6
0 3. 6 4.0
NORMAL STRESS, ksc£
0
Boring Number : 06 Description
Dark Bn Consol. Silt (NIL)
Depth, ft 12.5 Cohesion, ksf
0.73
Specific Gravity : 2.70 Friction Angle, degrees
22
Moisture Dry Density Void
Normal
Shear
Content, % pcf Ratio
Stress, ksf
Stress, ksf
58.0 64.2
1.00
1.11
57.5 61.8
2.00
1.53
56.9 64.3
4.00
2.30
Note: Rate of Deformation 0.05 in/min
Plot Corresponds to Peak Values
DIRECT SHEAR TEST RESULTS
Castaway's Marina Project No.
Dover Dr. & PCH, Newport Beach 90-32155-01
Converse Consultants Orange County
C-1
{ 1 B O R I N G N O ,.
Converse Consultants
SHEET
Orange County
•CASTAWAYS 1MVRINA oar 5/21/86
PROJECT NAME
PROJECT NO.
86-32245-01 DRILLING COMPANY INTERSTATE DRILLING
gWIPMENT HOLLOW STEM AUGER
DRIVING WEIGHT 140 #
I AVERAGE DROP (IN.) 300 HOLE DIAMETER 5. ELEVATION
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Ni]FNITD fT A
`"'o
PERCENT
cLL
a'
"x
DE SCR I PTI CN
morn ]uo-.nE
LL"
a
BORING 1' BELOW WATER SURFACE
wet
med.
0-95-5
SP
TOP OF
ense
SAND
medium gray, fine sand, micaceous, trace
non plastic fines, no visible organics, but
NR
moderate organic odor
II I shell bed 1" thick
CL SANDY CLAY
1 light gray, some fine sand, medium plastic,
micaceous, slightly organic odor
CLAY
2 trace sand
Is" thick medium sand, interbedded with 1/2 to
3/8" thick light brown & olive gray clay
streaks, 1/161 thick organic layer at 10
fine sand slyers 1/32" thick between clay
band partings (intensely laminated)
15 2 intensely laminated clays as above
torganic layer 1/8" thick in tip of sample
*22
0-30-70 10.51 35.1 91 141- 8
1.
0-5-95
L
�. jer
intensely laminated clay with sand streaks
3 organics at 19.6' 1/16" thick
i * Corrected N-Values 1f Pocket Penetrometer Test
4 (Continued) n Sample sheared at normal loads
*23
7.8174.51 59 13F4.5
*25
Pk Converse ConsUttants
Count
1 C-2
SHEET 2 CP 3
Orange
3
GarF 5/21/86
PROJECT NAME CASTAWAYS HARINA
�
GRILLING COMPANY
INTERSTATE URILLINO
PROJECT N0._,$f> 32215-
i "
DRIVING WEIGHT
HOLLOW STEI1 AUGER
:1401
j �IaMENr
5' ELEVATION
GROUNDWATER
ENP(GEO 6ND
7 AVERAGE DROP PIN.)
30" HOLE DIAMETER
1
SUMMARY OF B0R I NG
VISUAL
FIELD
W
W
�E
w '-'
ESTIMATE
a
o
E
[i1aY
f„[f y,�w,ir f+rLtcf w.r �i rre �punw a r"n ealro �.a AT f,c
caotnwf ,.r O1i:41 AT OM. L6fTWA
W
y
y a
3 i
u r
y W
i a
y
SYulM1.
TI,E P OiiLLIW. fSMA,iILE
YO INr OWL£ 1T 1Ntf LQASIOt Yt T1 rK TTWI V T AM M tY1lf
0 .11t1I1 OQ[i[IYq p@MTRi,D•
F
W
C >
Z
p4LliNim [T ]IMl[ItGrtlfa
O C.
u O
PEA T
'd. ,•
L
i
n
O
J
_
❑ E S C R I P T I 0 N
2
Y,fYF L•f.O•I f1E
W LL
LL M
J
Y
y
CL
CLAY
ois
very
of,
0-5-95
trace sand, alternating medium brown, olive
green medium plastic clay 1/2" to 3/8" thick
thick)
to
hard
`occasional gray to light green, 1/8
1
1/16-1/8" fine sand at partings
' 25
30
35
medium sand ;-�" thick along partings
clay beds 95%+ fines
sand beds 90p+ sand
41 I 1/16- 1/32" sand layers, fine grained along
partings
BEDROCK - CAPISTRANO runewllun
DOLOSTONE
dark gray, hard, massive to 37'
n
1 I CLAYSTONE & SANDSTONE
dark brown clay, trace fine sand,
slight gray sand, trace fines,
hard drilling
40 (Continued)
* Corrected N-Values
a Sample sheared at normal loads
of 1 n 17a and 4.0 kSf.
0-10-90 17.8 �9.5 1 85
*50
40.6
*65
■
f ► Converse Consultants
Orange County
...3Auavc MARTNA
B 0 R I N-G
N 0 s. 1
SHEET�3
PRO.ItI:,I_rvu.
-
140
HOLLOW STEM AUGER DRIVING WEIGHT
ELLUIPMENT
•
GRCUNOWATER
ENOLL
GND
(IN.) �• HaLE CIAMETER 5__.--ELEVATION
AVERAGE DROP
S U M M A R Y O F B O R I N G
i
VISUAL
FIELD
j
a
M
SyaE
w
ESTIMAT-e
0
:_ E
C
p16F
IE3 paY .T TE , a T"IS pOIIM SIC AT TK
THIS Sl.wr war OI::Y< AT L53TIW
e
N
C
W
a
]
- F
a a
„
Z
SYwSd.
TT%M'
T116 Q p61LLIM. THt S�]IFKi CRatTI[+�f
IW. TkC.
MSY Gu,6 AT THIS lGC3TIOS vi1N S,f F.lSSOfi G: TI!£. 1HI DATA
2
T
=
= x
a a
-
5 ^
a
.,a
Px3dna IS ! 3{,Il1FIGT{OI V IC1W1. CJCIZlCS3 pfdNRSFII.
O �
PFALSSIT
a
3 J
y Y
O E S C R Z P T I C N
9
U O
0 AM-3YO•II,E
G LL
G M
CAPISTRANO FORMATION
mots
hard
0-5-95
I
BEDROCK -
to
0-95-5
CLAYSTONE 8 SANDSTONE
very
0-5-95
CLAY ONE
dark olive green, moderately weathered,
soft, (hard to very stiff), slightly
moist, massive, forams, consistantly hard
drilling below 41h'
45
6
End of boring at 45' S"
50
L-4
1
B 0 R I N G N O 2
Converse Consultants
orange County SHEET 1 OF 1
oar 5/22/86
PROJECT NAME
CASTAWAYS MARINA
PRo.IECT No.
86 32245-01 DRILLING COMPANY INTERSTATE DRILLING
HOLLOW STEM AUGER DRIVING WEIGHT 140 #
gggp ENT 6N0
AVERAGE DROP (IN.1 30- HOLE DIAMETER
5. EL NATION -8.0't GROUNDWATER ENQ/GEO
S U M MAR Y O F B O R I N 6 VISUAL V
to a- FIeLD ° -s
IK
' Ai 11R IGEATid O txl3 ATINTYtl A TfIE (1 ITfLLIM. SUIHAfACE CdWl OIiREII Ai 0111ER IT • UATAT TXIS LWTI°. VITH TE •.lSb! Y TIIE. TE tulA'O W 2IS A SIX•LIIIGTIfM V AC1UK C>GlTtdf CfSM.FOp��TWw3-
'�' a 0 E S C R I P T I 0 N wfvfl•!uo-•IlE G N a< X 3 ., x
CL TOP OF BORING 7' BELOW WATER SURFACE wet irm 0-5-95
SILTY CLAY
dark olive brown, trace of fine -sand, very
intensely laminated with 1/32" thick fine
sand streaks
BEDROCK - CAPISTRANO FORMATION
CIAYSTONE
10 dark olive brown, trace fine sand, soft
(verstiff to claystone, interbeddedmwithv1 4-1/8beddin9 In
"
sandstones
1
sandstones 1/16" thick, spaced 6",
2 abundant forams in claystone
15 End of boring at 141 6"
0-5-95
*10
7.11 49 170 (1.2
a 2.7
* ' Corrected N-values ■ Sample soaked prior to shearing at normal
loads of 1.0, 2.0 and 4.0 ksf.
(I
1,
4
A
L
L�
C—b
^ B 0 R I N G N 0 8
isl Converse Consultants'
Orange County s/86
PROJECT NAM..
CASTAWAYS MARINA GATE 5/28/86
86 32245 O1 ORILLINO COMPANY INTERSTATE DRILLING
PROJECT N0. 140 #
IPMENT HOLLOW STEM AUGER ORIVINO WEIGHT
r,u t 30' HOLE DIAMETER 5! ELEVATION —5.0lt GROUNDWATER ENR/GED GNO
S U M M A R Y O F B O R I N G
` F
VISUAL
L
a
t
�
SHSLE
]r THE Lounw o THn ealw uu ]r TE
111
H �
ESTIMATE-
>
m LL
3
�
,]se]]t
war
SYMIQ.
THIa llwRr ]].LIE] w.r
TIM wILLIrO. !IMl1PIY.'E cTaITIw] WT OIfIEA IT OTHER L63' TIT!
TE �]ff.CE fP TI,E. TM "TA
W
r W
O
u an
p
S Y
y
¢ p
1;
y
yp Wr O.Yf6 1T THI! L=TIW VIM
,
RESd1ID IS I. ]IML]FIGTid rf .LTW- O XTIC,] ]%yMTERtD.
O C
yEP(',plT
> Y
9 ¢a
t
y
D E S C R I P T I D N
9
c] C
Im]vEt ]uo-n.E
sl.
loos
0-80-20
SH
FILL SILTY SAND
moil
light brown, fine to medium sand, 1-2
fragments of shale
*18
1
noist
firm
0-10-90
CL
SILTY CLAY
olive brown, mottled orange, trace fine
9.2
0.3
81
$4.5
1
sand
5
2
shale fragments to 1"
*18
claystone fragments in silty clay matrix
4.0
34.9
73
44.5
2
t0
3
shells & clay in tip
*13
15
BEDROCK - CAPISTRAND FORMATION
hard
0-5-95
42.1
51.2
66.3
3
CLAYSTONE
light gray to dusky yellowish brown
trace fine sand, moist, soft (very stiff
to hard), abundant forams
`� (Continued)
C-6
B O R I N G N O f.
6Converse Consultants
'�Orange County S� 2 2
°F
Dare S1781SA
PROJECT NAME CASTAWAYS MARINA
PROJECT NO.
86-32245-01 DRILLING COMPANY IMTRSTATE ORILLIN6
EyRJIPMENi
HOLLOW STEM AUGER ORIVINO WEIGHT 140�
AVERAGE DROP (IN.) 30- HOLE OIAMETc7i
5% ELEVATION GROUNOWATER ENG/GEO ENO
25
L*
r
S U M M A R Y O F B 0 R I N G
W sAf.Lc
it+t� raao f„ta furAr fPM.l:a var AT T,6 Lourxw a. T"la ewva fro Ar x,e
— srNEC(, Tx� OatLL11O. 3U017FfIr3 CO9tTlwa w, otFYEII Ai oilU1 L1"Lnwf
= uO wT O,.ILY AT Tnxa L=Ttw vfM Tt
TE �fffYX 6 ,4. tlE WA
> Ie sm= If A fl�iF,GTtw of aC1UAL COiTtOtf OCCMIEam•
J C E 5 C R I P T I 0 N
3 �
BEDROCK - CAPISTRANO FORMATION'
4 CLAYSTONE
dusky yellowish brown, with h" thick
green clayey sandstone interbeds,
spaced 6" apart, sand streaks along
claystone partings spaced 1-4", slightly
moist, soft, forams throughout, massive
bedding in claystones
4
@ 27-30' alternating 4-6" layers, hard
& soft
End of boring at 31.5'
y
VISUAL
y
ca
FIELD
m
Z
rT-
ESTIMATE
t
H
-
n
a
n
PFN.F71T
- Y
W O
> y
SI
C
U O
ORAK1•fY0•.I,E
O LL
LL Y
E J
if Y
0-10-90
7.1 �2.8 155
2.1
a 2.1
4.0
*74
a
a
a Sample soaked prior to shearing at normal
loads of 1.0, 2.0 and 4.0 ksf.
SUMMARY
A3 0-7
BORING NO. B-1
DATE DRILLED:
7-14-82
THIS SDMMARY AFFLIE! ON FACE AT THE ILLATION OF THIS BORING AND AT THE
TIME OF DlI LLING. SUSSURFACC CONDIPONS MAY OIFiE SATOTMEN LOCATIONS S( J
THE DATA a�i
p�}'I/
(t}p
+'te,
/ JS F'
DEPTH
�.
G;
AND MAT CHANGE AT THIS LOGTION HPd THE PASSAGE OF TIME.
PRESENTED 1! A SIMPLIFICATION OF ACTUAL CONDITIONS IONS ENCOUNTERED. ��
`LPS}
C�TS
}}}
/ Sp1?'D
Ae
FEET
`
4
ep�
9.1't
�
CIO'yi
ELEVATION•
SM
dry loose light FILL -SILTY SAND
to yellow fine to medium
medium gray with abundant shell
moist dense fragments (Pectens &
II Gastropods)
&
moderate l with interbeds of Sandy
15
5
1
moiverst gray II Clay and Silt
brown with Carbonized root (?)
v
fragments
-
I
wet
I
$M
—
loose green BEACH DEPOSITS -SILTY
i
ML
gray & SAND -fine to medium
moderat� with abundant shells and
7
Z
red occasional lens of firm
brown Sandy Clay and Clayey
loose to Silt, and occasional
!
11
medium rock fragments
#
#
dense micaceous
I
moderatedark BEDR -CLAYEY 51LT-
hard green STONE -with occasional
31
black ( Silty Sand seams
85
711
t 5
1
& dark moderately fractured
gray slightly weathered
green laminated
micaceous
31-50 dip of beds
I
very
1
moist
95•
44.0
71
20
dark occasional shell fragments
or
green
to
I
. 66
black
108
//*
1 .47
47
11"
45.9
69
4.90
rl
2
i
03
25
free ground water end of boring at 25.0'
encountered at 6.5', 28
t
hours after time of drilling
�
o
2
a
i
n
'
1
v
I 30
*Sample
soaked & drained before shearing
a
at
1.0, 2.0, & 4.0 ksf
PROPOSED CASTAWAYS COMMERCIAL SITE
holed
Nc.
Newport Beach, California
82_02161-01
for: The Irvine Company
Figure
No.
634
ConveCse
Consultants
A-t
O
j'
SUMMARY
BORING NO. B-2
DATE DRILLED: 7-14-82
THIS SUMMARY APPLIES ONLY AT THE LOCATION OF THIS BORING AND AT TN[
.k T I MCOFDRILLING. SUCSURFACE GONG I T I ON S MAY O IF r E A A T OTH CA L OCAT IO AS
AHD MAT CMANOE AT THIS LOCATION WITH THE PASSAGE OF TIME. THE DATA
DEPTH t}1% p�' /IIES ENTED IS A SIMPLIFICATION Or ACTUAL CONDITIONS ENCOUHTEIIEO. l
IN p T�° 6,3'
FEET S `O 0A ELEVATION f
0 7��dry very light FILL -SILTY SAND
loose gray fine to medium
sli htl yellow with little fine Gravel,
i1
IN
HE
is
20
25
moist y
brown trace coarse Sand
7dus'yabundant shells 8 shell froc
trace Silt
with occasional thin layers
moist
SID
v. moist
oae Sandy Silt, few
red Carbonized root
fragments & trace shells
wet
brown
loose
medium BEACH DEPOSITS- SILTYSAN
to
green fine, with abundant shells
medium
gray I micaceous
dense
medium SAND
Sp
gray clean, fine, micaceous
with occasional Silty
Sand layers
trace medium Sand
I
few shells
micaceous
dense
I
P
gray to
green
Olive
medium gray
dense
m. dense gr. grn.
& stiff & It gra
fine to medium
with occasional thin
layers of Clayey
& Silty Clay
Ic1
21
23
67
45
IMMIMA
A4 C-8
D9
�4y ?9fy�OS
!pA w�AA '^Acf
30 (Continued)
PROPOSED CASTAWAYS COMMERCIAL SITE ?roleo: No.
Newport Beach, California 82-02161-01
for: The Irvine Company
Figure No.
Converse Consultants A-2
a
SUMMARY
BORING NO. B-2 (Continued)
T", SUMMARY TIME Or OE LLLIN0.CATION
's UCSUII r AC E CONO ITI,$ ONLY AT TME IOMS MAT 051 AaC ATOOT M[S LOCATIONS
* TIME
MAY CNAMOE ATAlo THIS LOCATION WITN TM[ rAtl AGC Or TIML. TNC OAT•
DEPTH bT'S� °v RESENTED IS A SIMPLIFICATION Or ACTUAL CONOITIOMS ENGOUIN
xi CAL O.
N
FEET 5y1 L011 y °
30 SW wet medium gray ALLUVIAL DEPOSITS
ML dense green I CLAYEY SILT & SILTYCLAI
CL & & light interlayered (1/8" to 211
stiff gray & �h,jc a Ooo she Is, distin-
moderate CLAYEY SILT&SILTYCLAY
ML stifLng
f (olive I
JCL green with some Sandy Clay
interlayered
35
EN
45
50
55
C
SILTYCLAY&CLAYEYSILT
ML I interlayered
with occasional very this
Silty Sand layers
gray I
green
to
dusky with interla ered Sand
olive Y
gray I
olive BEDROCK-CLAYEYSILTSTONE
green
micaceous, with
gray
abundant forams
laminated, moderately
&
moderate
weathered -
moderately fractured
brown
with occasional hard
I
thin beds
green
_
slightly weathered
black I
unoxidized, with occ.
thin Sand seams along
bedding, distinctly
bedded with 1°-3°
dip
60
free 1 ground water encountered at 6.3'
01 MlL1.[ mf+er drillina
L-y
0
Jra,�9 e 4eSa 'c+O�ss mo�,'�q
�"t f
12
20
41.2I 77 I0,65�
1.38
1.68
31
10711
end of boring at 60.01 ;")ample soaked and drained before
shearing at 1.0, 2.0, and 4.0 ksf
PROPOSED CASTAWAYS COMMERCIAL SITE
Newport Beach, California
for: The Irvine Company
Converse ConsultantsAPPIIIIIII
82-02161-01
Figure No.
A-3
SUMMARY
BORING NO.B-3
Ab C-10
M
r,
DATE DRILLED: 7-15-82
THIS lUMMAPY APPLIES GHLT AT THE LOCATION OF THIS EONINO AMO AT THE
{. TIME Of AT
S,%SQR F AC E C O HOITIOHS MAY OIfFEN AT OTN[N LOCATIONS 0( J
TIME
MAY CHANGE AT TNIS LOCATION WITH THE PASSAGE Or TIME. THE DATA
7EPTM QNy,SF'pov PN[S CNTCO IS A SIMPLIFICATION OF ACTUAL CGNOITIONS ENCOUNTERED. ?f
FEET yf�`o'l'e" ELEVATION: 7.21E
e I SM dry 71oosemedium FILL -SILTY SAND
dusky fine to medium, with
moistveIlow I occasipngll Gravel
SM ver light red with some k.. tayey a it
I �ML moist brown I interlayers 7
to gray
5 olive
green
SP medium medium Itsc+ n VLI VJl I -
dense gray fine, with little medium
t & lid occasional
light an35
2I gray I coarse Sand and Silty
Sand lenses
10
fine to medium.
with few rock fragments
t
28
3
____ _
abundant_shell zone
at14'to15'
15
medium
moderate finer some medium Sand
dense to
gray occasional shell frogmen
dense
micaceous
I (clean Sand)
33
4
20
I
SCICL
looseALLUVIAL
DEPOSITS
&firm
CLAYEY SAND&SANDY
5
5
CLAY -with fine to
coarse Sand
25
medium SAND -SANDY CLAY
SW
JCL
green
gray & fine to coarse
interlayered
medium
dusky
lg
6
gray
30
(Continued)
01
'9_ 'AAAy tF.
PTolee: NO.
PROPOSED CASTAWAYS COMMERCIAL SITE
Newport Beach, California 52-02161-01
for: The Irvine Company o. ______gure No.N
Fi
Converse Consultants A-4
A
ll
SUMMARY
BORING NO. B-3 (Continued)
A7G-11
DEPTH
IN
FEET SQ O {
M
f
35-
Ir
40-
7
r
rr 45-
!
IT
1i
It
'IJ
f
50-
55•
THIS SUMMARY APPLIES ONLY AT THE LOCATION Or THIS BORING AND AT THE
TIMEOr DRILLING, sussuRrACE C ONO IT IONS MAY o VrER AT OTHER LOCATIO NS
AND MAY CHANGE AT THIS LOCATION WITH THE PASSAGE OF TIME. THE DATA
PRESENTED IS A SIMPLIFICATION OF ACTUAL CONDITIONS ENCOUNTERED.
p° la t , �4fsss
ss c •f Qtis 3`DT,�9
7
` gSW
wet
loose &
firm
•grn gr
dusk r.
ALLUVIAL
DEPOSITS
SAND & SANDY CLAY
17
soft
medium BEDROCK
gray
green (
CLAYEY SILTSTONE
moderately weathered
very fractured
micaceous, with oxide
stains along fractures
1
laminated
slightly weathered_
--
Sand -
with occasional Sand_
stone interbeds
micaceous
abundant forams
16
61.7
61.
0.677
0.54
1.92j
ig t
gray &
gray
green &
dusky
ellow
rown
—
thinly laminated to
laminated
moderately fractured
slightly weathered
with very thin Sandstone
interbeds
abundant forams
nearly horizontally
bedded (well bedded)
1°-2° dip of beds
12
gray
green &
light I
gray &
dusky
yellow
med. brn.1
light
ra &
medium
gray
green &
very
moist
moderate
hard
dark
gray
thin laminated
in
dark
olive
olive
I
uly
89
9
1 p79
1
�a g free water encountered at 8.2' end of boring at 59.5' * Sample soaked and drained before
22 hours after time of drilling shearing at 1.0, 2.0 and 4.0 ksf
PROPOSED CASTAWAYS COMMERCIAL SITE ?IoleDt ro
Newport Beach, California
for: The Irvine Company 82-02161-01
Ficure No.
Converse Consultants A-5
1 •
n
L�
SUMMARY
BORING NO. B-4
DATE DRILLED. 7-1 5-82
THIS SUMMARY ALLIES ONLY AT THE LOCATION OF THIS SORJNO AND AT THE
.k TIME Of ORILUxO, S U83URFACE CONDITIONS MAY DIFFER AT OTHER LOCATIONS
AXD MAT CNAxGE AT THIS LOCATION WITH THE PASSAGE OF TIME. THE DATA
DEPTH tQS� PR ESEXTED IS A SIMPLIFICATION OF ACTUAL CONDITIONS ENCOUNTERED.
IN ♦ 0 8P71,y,
FEET `+Q La I;' ELEVATION,
0 I SM dry case gray - LT A
ND
green fine to medium
moist I IT
with some shells
AB C-12
9 ' O<p (qy + fSs
¢ s,D 9yy vOf '� s}fT
I
SP very medium SAND
moist red fine to medium
brown with trace coarse Sand
5 occasional shell
SM wet I SILTY SAND
fine
o
N
ip
2
I
$P
medium
dense
medium BE
gray
SANDECH EPOSITS
fine, micaceous
31
I
I
trace Silt in lenses &
pods, with occasional
rock fragments
is
I
23
3I
'gray
20
15
medium
gray
4i
25
fine to medium
with trace Clayey Silt
lenses
11
medium
gray to
dark
gray &
I
5
green
gray
with Clayey Sand layers
30 (Continued)
PROPOSED CASTAWAYS COMMERCIAL SITE ?mlect ND.
Newport Beach, California 62-02161-01
for: The Irvine Company
Figure No,
Converse Consultants A-6
I
I
I
I
I�
SUMMARY
BORING NO. 4 (Continued)
Ag C-13
DEPTH
• N
FEET
30 -
35 -
r 40 -
r
r
45-
ro
If
�r
z
a
0
a
50 -
55 -
60 .
THIS SUMMARY APPLIES ONLY AT THE LOCATION Of THIS OOOING AND AT THE
�. TIME Of DRILLING..
SUBSURFACE CO NDI TI DNS MAY OIFTERAT OTNEN LOCATIONS
1(G AND MAY CHANGE AT THIS LOCATION WITH THC PASSAGE OI TIME. THE DATA
,$ OV PRESENTED IS A SIMPLIFICATION OF ACTUAL CONDITIONS ENCOUHTERED.
y
aka JpJ gAyo ? �pf y, s?f�
4 s gym soTyq
{ f�LNA4 TAA. ff
cr e
1 SP
wet
medium
medium
-
BEACH DEPOSITS
9
27.1
92
0.80
dense
gray to
SAND
1.63
'
dk. gray
with Clayey Sand layers
3.00
& green
gray
CL
soft
gray
ALLUVIAL
DEPOSITS
green &
SILTY I-NDVP��
bi
medium
5
SM
loose
gray
SILTY SAND
--
SANDY SILT
i
MIS
gray
MH
black (
with Clay
3
7
I
soft
light BEDROCK
gray
CLAYEY SILTSTONE &
green
& SILTY CLAYSTONE
&
medium I
interbedded
very weathered
5
58.0
gI
olive
very fractured
gray
thinly laminated to
I
laminated
well bedded
20-40 dip
moderately weathered
very
moist
I
moderately fractured
12
to
wet
micaceous
thinly bedded
v
8
1
kL.arlrinucul ; Jamplu 5UUKGu UIIu
shearing at 1.0, 2.0, and 4,0 ksf
PROPOSED CASTAWAYS COMMERCIAL SITE rrclec:
Newport Beach, California
for: The Irvine Company 82-02161-01
Figure No.
Converse Consultants A-7
SUMMARY
BORING NO. B-4 (Continued)
A10 C-14
DEPTH
IN t TO
FEET '9 `p 9A
65
70•
i 75
1•
ME
ti
Lm
0
a
THIS SUMMARY
TIME Df ORtLL
APPLIES ONLY
'MG.3UR3URf
AT THE LOCATION
ICE C ORDI TIONS
LOCATION WIT. THE
OF THIS SORiNO AND AT THE
MAYDVI CRAT OTHER LOCATIONS J� ,f
PASSAGE Of TIME. THE DATA O;�i
4A,Ij
,YD�@
O
CSG •4�
AND MIT CHAHDE
PRESENTED
AT THIS
13 A SIMPLIFICATION
OE ACTUAL
CONDITIONS ENCOUNTERED. �l
��C
09 �d
yA
A}
ery
soft
light BEDROCK
CLAYEY SILTSTONE &
foist
green
SILTY CLAYSTONE
o
gray
&
with occasional thin
ret
green
Sandstone bed
olive
moderately weathered
gray
I
moderately fractured
&
thinly laminated to
dusky
laminated
gray I
well bedded
2D-4D dip
Sand interbeds are
medium -grained
trace Silt
moderate
dark
CLAYEY SILTSTONE
eery
noist
hard
green
slightly weathered
black
moderately fractured
distinctly bedded
unoxidized
with abundant forams
76
;round water
encountered
end
of boring at 76.5'
of 7.2',
18 hours
after
time of drilling
Project No.
PROPOSED CASTAWAYS COMMERCIAL SITE
Newport Beach, California 82-02161-01
for: The Irvine Company
Figure No.
Converse Consultants A-8
It
f
it
SUMMARY
All
C-!b
BORING
NO. B-5
DATE DRILLED.
7-16-82
THIS SUMM/Av
Of OEILUNG,
APFLICS ONLi
SUSSDN,AC
AT THE LOCATION OF TNIS S011IxG AND AT THE
E CO NDITION!MAI OI(fCP AT LOCATIONS d( 1,,
THE DATA O�J
Q<O
'F}dj
<'p}
D
OC'
+ fy,S
.yP
T4
�.
TIME
AMO MAr CHANGE
IS
AT TNIS
A SIMPLIFICATION
Time.
LOCATION .ITN THE PASSAGE Of TIMC.
or ACTUAL CONOIT ION! CNCOUNTLCCO. ?J
}is
f0C'F'
f. 01
DEPTH
FEET "R.
EPS� p'�
dx241
PNESLMto
ELEVATION'
9.41y
�'A}
jCf
SM
dry
loose
brown FILL
SILTY SAND
gray
fine to coarse
slightly
dark
moist
dusky with abundant shell
gray I fragments
brown
moist
very
vs
medium
7
= 1
wet
yellow
brown
BEACH DEPOSITS
$W
loose
to
SAND
medium
fine to coarse
I
10
dense
with shell fragments
21
2
brown —
with trace fine Gravel
gray — — — — —
i
I
dusky fine to medium, trace
gray coarse, micaceous
brown
oose
SILTY SAND
JALLUVIAL
1s
3i
3
I
blue
DEPOSITS
SILTY SAND & SANDY
r
gray
& gray
SILT -with some Clay
green
I
& occasional fine
Gravel, micaceous
20
SANDY SILT
8*
ML
light
1
blue
with some Clay
gray
fine to medium Sand
CLAYEY5ILT&SANDYSILT
H
�ML
with few shells
laminated
I
gray blue
25
2
very porous
4*
47,8
72
0.27�
'x
micaceous
Q:b3
30 (Continued) * Sample soaked & drained before
shearing at 1.0, 2.0, & 4.0 ksf
PROPOSED CASTAWAYS COMMERCIAL SITE
Newport Beach, California g2-02161-01
for: The Irvine Company
Figure No.
Converse Consultants A-9
DEPTH
IN
FEET
30
35
401
50
55
60'
SUMMARY
BORING NO, B-5 (Continued)
THIS SUMMARY APPLIES ONLY AT THC LOCATION Or THIS BONING AND AT THE
* TIME Or DRILLING. SUBSURrAC E CO NOITIONSMATOIrrERATOTHCRLOCATIONS
AND AT CHANGE AT THIS LOCATION WITH THE PASSAGE Or TIMC. THE DATA
I,'ESENTED 13 A SIMPLIPICATION Or ACTUAL CONDITIONS ENCOUNTERED.
SQt 2.1 �0
Al2C-16
4 :pO eq}
4}yy,
6A� �y,�ftiy, �, a�Yti4
1 ,
MH/ML
wet
loose
ALC
TS
3
I
4
graay &
AYEYSILTO&ISANDYSIL
purple
gray
soft
blue BEDROCK
gray &
CAYEY SILTSTONE &
medium
gray
SILTY CLAYSTONE
with occasional thin
9
I
5
green
Sandstone lenses
& light
thinly laminated to
gray
laminated
micaceous
well bedded with 10-30
dip
very weathered
I
moderately fractured
�
i
11
i
medium
dusky
6
red
brown I
moderately weathered
very
mod.
II
moist
hard
green
with occasional thin
black I
Siltstone & Shalebeds
& light
unoxidized
gray
d
(Continue )
PROPOSED CASTAWAYS COMMERCIAL SITE ProjectNo.
Newport Beach, California 82-02161-01
for: The Irvine Company
Figure No.
Converse Consultants A-10
SUMMARY
BORING NO. B-5 (Continued)
A13 0-
1-
II
THIS SUMMARY AI/LIES OHLT AT THE LOCATION OF THIS CONIHO AHG AT THE
ATIONS
THE DATA e�ply�i'
STHIS
f, (q} }qf S\
Oq}
ACG.�,F' qS
DEPTH
* AMOEMA YCMANOE ATL.,ATIOON WITMHTHEAF ASISAOE OF TiwC.
FMCS CHTCD IS A SIMPLIFICATION OF ACTUAL CONDITIONS CMCDUNTCIILD. ?f
oy�jq
�,5�
,C Gq F
IN
FEET
E�y� Cr
QS �,0
S
41 F. rF
Lp y; ..
60
verymod. green BEDROCK
7 hard black CLAYEY SILTSTONE
83
moit
g, with interbeds of
light Sandstone
fine to medium grained
gray
thinly laminated to very
thinly bedded
moderately weathered
65
8I I moderately fractured
110
ground water Tend of boring at 66.5'
lfree
encountered at 5.8'
5 hours after drilling
70
PROPOSED CASTAWAYS COMMERCIAL SITE PICIeC: NO.
Newport Beach, California 82-02161-01
for: The Irvine Company
Figure No.
Converse Consultants A-11
M
it
11
t
V
iI
�o
C
0
SUMMARY
B-6
A14 C-1
BORING NO.
w
•T
DATE DRILLED: 7-16-82
THIS SUMMARY APPLIES ONLY AT THE LOCATION Of THIS SORINO ANO AT THE
IONS MAYO IF FERATOTMER LOCATIONS
q
*
TIME Of D RILLINO. SUCSURF ACE CONOIT
MAYCNTCD IS 1 lIMPLIfIGTIOAT THIS N Of ACTWL CONDITIONS TIONS ENCOUNTERED. ON V IN THE PASSAGE Or TIME. THE ATA J%
�?
(}�iSA LNL �(•O gD1'f�1
/c'S'�P
DEPTH
IN
�(Sw Ow'
Ql �a
`+
P'0
I
9.2 f
T}} rf
FEET
LG yA
ELEVATIONS
o
SM
dry loose gray FILL- SILTY SAND
to brown wit Suaave1F—ft=--.
Sp
moist
medium light SAND
dense yellow fine, very micaceous
15
1
brown horizontally stratified
with occasional shell
very fragments
moist
5
SM
wet medium SILTY SAND
dusky fine
11
v
OH�T
brown BEACH DEPOSITS
soft &
CLAY -with Peat
gray SILTY
& (totally carbonized roots)
I
to
black stratified,_ laminated to
Sp
medium
medium
SAND
1
dense
brown
fine, very micaceous
with abundant shells
38*
26.0
98
gray
I
is
soft
olive
BEDROCK
t
green
CLAYEY SILTSTONE &
3
gra
&y
SILTY CLAYSTONE
6
i
green &
thinly laminated to
edi
laminated
very weathered
20
medi
gm
very fractured
olive
green &
c
very miaceous
abundant forams
i
gray
well bedded
20
4`
green
I
25
very
od,
dark
CLAYEY SILTSTONE-with
with interbeds of f• to m.
;
moist
and
olive
thin Sandstone layers
129
_I
glien
mod, weathered, mod.
fractured, thinly lam,
i
to v, thinly bedded
o—d -
(dip
I
free ground water encountered
end of boring at 28.5'
I
at 8.21, 68 hours after drilling
PROPOSED CASTAWAYS COMMERCIAL SITE
Prolec; ND
Newport Beach, California
82-02161-01
for: The Irvine Company
Figure No.
Converse Consultants
A-12
�O
SUMMARY A15 C-19
BORING NO, B-7
GATE DRILLED:
7-16-82
THIS SUMMARY APPLIES ONLY AT TMC LOCATION 0/ iNl3 10111NG AND AT TNC .Q4 S �e}Q �jACLf.s'•S
�. TI ME of ON ILL I NO. !UlSYRf ACE CONO ITIOHS MAY OIff ENAT OTNEN LOCATIONS A� /. ASP
ANo MAY CHANGE AT THIS LOCATION IT" THE PASSAGE Of TIME. [RE DATA C}'% �O, CLti S YT'P
DEPTH �pSF' Ov I. sc.TEo I! A SIMPLYICAT10N Of ACTUAL CONDITIONS IONS ENCOUHYFN [RED. f,S} G) D (.
IN t 7.11y
FEET SQ LO` d ELEVATION:
0
5-
In
WE
15—
20 —
25 —
30 -
y
SM
dry
loose
brown
gray
FILL
SILTY SAND
fine to coarse
moist
with abundant shells
very
moist
1)
ML
YSM
SANDY SILT&SILTY SAND
with some Clay & trace
rock fragments
y
29
medium
black
wet
Sp
j
imedium
25
dense
medium BEACH
gray
I
DEPOSITS
SAND
fine, very micaceous
with occasional trace
Silt & abundant shells
2I
I
fine to medium
17
3I
p
/SW
medium
gray
to
light
gray
Sp
fine, with trace medium
Sand layers &
occasional shellzones
ense
& rock fragments
(Continued)
PROPOSED CASTAWAYS COMMERCIAL SITE PTolecc No.
Newport Beach, California
for: The Irvine Company 82-02161-01
Figure No.
CConverse Consultants A-13
IL
SUMMARY A16 C-20
BORING NO. B-7 (Continue
q�.
THIS SUMMARY APPLIES ONLY AT THE LOCATION Or THIS CORING AND AT THE
ORILLIMO. SUSSURFACECOMDITIONSMAYOIFFLRATOTHE
i1MC 0I R LOCAT IO NS
Of TIME. THE DATA
A S
CLti
DEPTH
AND MAY CHANGE AT THIS LOCATION Y/ITM THE PASSAGE
PRESENTED IS A SIMPL IF ICATIOM OF ACTUAL COMDIT IONS EXGOVMTCREO.
�1EQ}�OOv
4
FEET
(10 41
30
4
Sp
VSW
wet
dense
medium
gray to
BEACH
SAND
SAND
56
35
40
50
55
im,
n
0
0
light
gray
medium
gr ay &
dusky
fine, with trace medium
Sand layers &
occasional shell zone
& rock fragments
indistinctly stratified
green
fine to coarse
SW Foose with trace Silt
loose medium I ____
SM gray & I SILTY SAND
light with trace Clay
green fine to coarse
CL
soft
olive
IALLUVIAL
DEPOSITS
gray
SILTYCLAY &SANDYCLA
with Sandy Silt
interlayered
SANDY SILT
MH
dark
dusky
with some Clay
gray
fine to coarse
brow
—_
SILTY CLAY
light
%OL
gray
I
with Sandy Silt
green
micaceous, organic
light
gray &
IBEDROCK
CLAYEY SILTSTONE-with
medium
Silty, fine, Sandstone
gray
interbeds, thinly larr
green &
to lam., disturbed in
dusky
zones, well bedded
olive
(mod. to steeply
00
mrodPr f9act4ured very
weathered
(Continued)
4
5
E
PROPOSED CASTAWAYS COMMERCIAL SITE PIDIeC: No.
Newport Beach, California 82-02161-01
for: The Irvine Company
Figure No.
Converse Consultants A-14
SUMMARY A17 C-21
BORING NO. B-7 (Continued) w
10 DEPTH
IN
FEET
r 60
65
! 70
r
75
ZIN
Q
0
9
THIS SUMMARY ArIUC3 ONLY AT THE LOCATION or THIS 30RING AMO AT THE �QrO Ce} if.]14.
T< TIMED' ORILLIHO. SU3SHIITACECOHOITIONSMAYo1rFERATOTHER LOCATIONS0�.(•f
TIM MAY CHANGE AT THIS LOCATION MIT% THE PA33AGE Or TIME. THE DATAAND
yQt ��QS�QOr PRESENTED I] A SINrLl1ICATION Or ACTU?L CONDITIONS EHCOUXT[RLO. 4-�'CS}P ` a'h} OAS
�o y+
wet
soft
light i
&
BEDROCK
CLAYEY SILTSTONE-with
gray
dusky
Silty, fine, Sandstone
olive
interbeds, thinly lam.
green
rMV
to laminated
distinctly bedded at
medium
gray
20°-30° dip
13
8
olive
micaceous
with abundant forams
green
I
& occasional Sandstone
lenses & pods
very weathered
moderately fractured
dark
laminated
very
mod,
moist
hard
olive
unoxidized
1
green
moderately weathered
to slightly weathered
moderately fractured
I
13�9
free ground water end of boring at 76.5'
encountered at 7.2'
22 hours after drilling
ProjeCl No.
PROPOSED CASTAWAYS COMMERCIAL SITE
Newport Beach, California $2-02161-01
for: The Irvine Company
Figure No.
Converse Consultants A-15
L
F1
DEPTH
IN
FEET
0
S.
fa
15
KIII
25
3C
SUMMARY
BORING NO. B-8
DATE DRILLED: 7-19-82
THIS SUMMARY APRLICS ONLY AT THE LOCATION Or THIS BORING AND AT THE
ANDCMA TCHANIGE BATS THIS LOCAT IU5URf ACE CON WITH THEONG IT IOS AR SYO ISAOC Or TIMfFCR AT E. LOCATIONS THE DATA
r ROENTED IS A SIMPLIr ICATION Or ACTUAL CONDITIONS ENCOUNTERED.
60 D
a � O
A18C-22
w
. aTD eqj +ttyS
.pAfT
�} f�4As
'
LD I;I
SM
ELEVATION
dry
0.4
loose
light FILL
-SILTY SAND & GRAVEL
brown
fine to medium.
moist
gray to
micaceous
medium
with occ. shell fragments
brown
very
_�
moist
SAND
SP
fine to medium
1I
wet
micaceous
8
shells abundant in zones
soft &
medium BEACH
DEPOSITS
ML
loose
reen
SANDYSILT&CLAYEYSILT
&SM
!gray
live
SILTY SAND
loose to
2
4L
medium
ra
medium
fine, with medium to
coarse Sand layers
16
dense
gray
& trace Clay
brown
(
oose
soft
medium ALLUVIAL
DEPOSITS
CH
blue
SILTY CLAY
4
57,1
3
green
with some Clayey Silt
micaceous
I
trace Sand
i
soft
BEDROCK
i
light
CLAYEY SILTSTONE
7
75.3
4
blue
very weathered
green &
very fractured
light
disturbed in upper zone
green I
gray
micaceous
very thinly laminated to
laminated
with very thin .
Tuffaceous beds (?)
5
dip 100-150, occ, very
12
thin Sandstone seams
& lenses
CLAYEY SILTSTONE &
light
olive
SANDSTONE interbeds
gray
kV ul ll l I lu CiuI
Project No.
PROPOSED CASTAWAYS COMMERCIAL SITE
Newport Beach, California 82-02161-01
for: The Irvine Company
Figure No.
Converse Consultants A-16
SUMMARY 11 , _J%
DEPT
IN
FEET
30
35
40
45
50
55
.m
A19C-23
BORING NU. o—v �� VIII IIIVc /
• THIS S°MM1XY AP/LIES ONLY AT TNC LOCATION Ol TNIS EONING ANO AT THE .09; (0}° 4.9LFS01/I.
* TIME OF ONILLI NO. SGlSUNFAEE CONDITION!MAT DIFFCN AT OTNES LOCATTONS J� } SS ,
ANO MAY CHANGE AT THIS to -IT" THE PASSAGE of TIME. THE DATA C�'i ,yO CL.�, �'F 77,Q
i ,,e19�00v IRESENTCD IS A SIMPLIFICATION OF ACTUAL CONOITIONS CNCOYNTENCO. �CO ��}} D -F
}F
Q` y?F
S
Lo2 9{
wet
soft
light BEDROCK
10
6
olive
CLAYEY SILTSTONE &
gray
SANDSTONE interbeds
&
fine to medium grained
medium
well bedded (50-10°dip)
gray
thinly laminated to
brown
thinly bedded
moderately fractured
10
i
7
very weathered
with abundant forams
micaceous
CLAYEY SILTSTONE &
SILTY CLAYSTONE
8!
micaceous
thinly laminated to
15
medium
gray
laminated (5°-10°dip)
green I
&
with abundant forams
and occasional
green
Sandstone lense
gray
very
moist
dark
CLAYEY SILTSTONE &
mod,
hard
green
SANDSTONE
brown
fine to coarse
&
dark
bed thickness to 611
distinctly bedded
70
9
olive
with very thin fine Sand
green
lenses in Siltstone
thinly laminated to
thinly bedded
dip 1°-4°
micaceous
117
1
9"
free ground water
end of boring at 56.5'
encountered at 8.01
40 minutes after drilling
PROPOSED CASTAWAYS COMMERCIAL SITE PrD,EEIN°'
Newport Beach, California
for: The Irvine Company 82-02161-01
Figure No.
Converse Consultants A-17
CASTAWAYS MARINA
TEST EXCAVATION OF A PORTION OF CA-ORA-84
NEWPORT BEACH, ORANGE COUNTY, CALIFORNIA
1 X
(�EGEIYED
Cp'14 &'S TATES
0
Test Excavation of a Portion of
CA-Ora-84, Newport Beach
Orange County, California
PREPARED FOR:
Michael Brandman Associates
Carnegie Center
2530 Red Hill Avenue
Santa Ana, California 92705
PREPARED BY•
RMW Paleo Associates, Incorporated
23352 Madero, Suite J
Mission Viejo, California 92691
(714) 770-8042
FAX (714) 458-9058
RMW Project Number 89-1180
AUTHOR•
Ronald M. Bissell
9 May 1990
MANAGEMENT SUMMARY
A portion of archaeological site CA-Ora-48 was explored
through surface examination, posthole excavation and excavation
of one controlled unit. The work was undertaken in that part of
the site which will be impacted by a proposed road.
CA-Ora-48 was found to be a well developed shell midden
containing very few artifacts. The midden averages about 30 to
40 centimeters depth in the studied portion of the site.
Any ground disturbance necessary to construct the proposed
road should be observed by an archaeologist prepared to document
and recover any significant material which may appear.
• ii
cm; INCH EQUAL-5 FORTY fEET
A PORTION OF
ARCHAEOLOG-ICAL SITE
CA— OA A— f a
I •
O PosTNOLE
O EXGAVATIol/ '/Nrf
ARcH19CO IL"'CA 4
srrd 8o&pv0ARY
Ic
.9 tc'
1C
i
� 3c
3c O*
tc
0
7.6 \r
rC
,
1
ti
23352 Madero, Suite J
Mission Viejo, CA 92691
r
1
I
RMW
PaleoAssociates
•
During early August 1989 employees of RMW Paleo Associates
completed a cultural resources reconnaissance of property known
as the Castaways Marina, Newport Beach, Orange County,
California. One of the archaeological sites discussed in that
report (Becker 1989) was CA-Ora-48. This deposit was determined
to be an extensive shell midden, but no excavation was
accomplished, so its exact subsurface extent, content and degree
of preservation were unknown. Surface remains indicate that the
site extends from the bluff top at the eastern extent of the
property to the rear of existing construction extending into the
property from the west. See the Site Location Map on the
following page.
Proposed work at the lower (southern) part of the property
requires that a road be installed which will cross the western
• part of CA-Ora-48. The proposed approximate routing of this road
is also shown on the page 2 Site Location Map. The proposed road
will impact CA-Ora-48, but the extent of the impact could not be
assessed due to the lack of excavation data. The project
described in this report was designed to determine the impact of
the road construction. No grading will be necessary in that
portion of the proposed road which crosses CA-Ora-48, but
clearing and surface preparation will be required.
The current project consisted of a detailed examination of
the surface, excavation of a series of postholes and excavation
of one controlled unit measuring one by one meter in surface
extent.
PROJECT DESCRIPTION
The field portion of the project was accomplished by Ken
1
•
P
�Jir��_. �_r�rerm �/•
'1 KILOMETER F!4
SITE LOCATION MAP: A portion of the USGS
7.5 minute Newport Beach quadrangle, 1965.
Photorevised 1981. Approximate site locations
are marked.
23352 MADEROm SUITE J
MISSION VIEJO CA 92691
(714) 770-8041
J
Becker, RMW Paleo Associates Field Director and Stuart Evans, RMW
. Paleo Associates Archaeologist. The author of this report served
as Principal Investigator. Mr. Chris Crespin was the project
Native American Monitor. Becker holds a Bachelors degree in
Anthropology and Evans holds a Bachelors degree in History. The
author holds a Masters degree in Anthropology and is certified by
the Society of Professional Archaeologists as a Field
Archaeologist.
Various shell remains were noted during the surface
examination, but no artifacts were seen. The surface shell was
not collected.
Twenty two post hole excavations were made. These began at
the northern extent of the proposed road and proceeded to the
south and east along the right of way across CA-Ora-48. Holes
were placed in the center of the right of way and at the eastern
and western extent of the right of way. The attached map depicts
the location of the excavated postholes.
Each posthole was approximately 30 centimeters in diameter.
• Excavation was accomplished using hand operated clamshell digging
equipment. All material was screened through one eighth inch
wire mesh. A rough level was maintained by steel tape measure
from the lip of the hole as each excavation proceeded.
The only artifact recovered during the posthole excavation
was a brick fragment encountered in one of the southernmost
holes. However, shell was recovered in sufficient quantities to
permit definition of the studied portion of the site. Table 1 on
the following page summarizes the distribution of midden shell.
Table 1 shows that the site boundaries are fairly well defined in
the area to be impacted by the road. The project map contains
the site boundary as determined by the post hole excavation.
One excavation unit was placed within the densest
concentration of midden shell. This unit was one by one meter in
surface extent and was excavated in arbitrary levels of 10
centimeters. All material was screened through 1/8 inch wire
3
•
TABLE 1: Shell Distribution in Posthole Excavations
Hole Number
lA
1B
1C
2A
2B
2C
3A
3B
3C
4A
4B
4C
5A
5B
5C
6A
6B
6C
7A
7B
7C
Range of Shell Depth Shell Quantity
Surface Very light
None
None
None
None
Surface
Surface to 85 cm
Surface to 60 cm
Surface to 60 cm
Surface to 80 cm
Surface to 80 cm
Surface to 70 cm
Surface to 80 cm
Surface to 60 cm
Surface to 60 cm
Surface to 50 cm
Surface to 30 cm
Surface to 40 cm
None
None
Surface to 50 cm
4
Very light
Moderate
Moderate
Moderate
Heavy
Heavy
Heavy
Very Heavy
Moderate
Moderate
Moderate
Light
Moderate
Very light
mesh. No artifacts were encountered in the excavation, but
• quantities of shell were recovered. The test unit also revealed
that the shell midden is easily differentiated from the
underlying soil, which is a distinctly lighter color and contains
only very few shell fragments. In the area where the excavation
was placed the shell midden varied from about 15 centimeters to
as much as 35 centimeters depth. The change in soils can be
distinctly seen in the photograph which appears on the following
page.
CONCLUSIONS
1. CA-Ora-48 is a well developed shell midden. Artifacts are
rare in the deposit.
2. The deposit at CA-Ora-48 begins at the surface and is dense
to a depth averaging 30 to 40 centimeters in the central
part of the studied portion of the site.
3. The proposed road will impact a portion of CA-Ora-48. Any
scraping to remove vegetation or scarification to prepare
• the road surface will disturb the archaeological deposit.
RECOMMENDATIONS
1. An archaeologist should observe all ground disturbing
activity within the site limits as depicted on the project
map accompanying this report.
2. The archaeologist must be prepared to fully document and
recover archaeological data from any significant material
which appears. Such recovery work may necessitate some
delays in grading if complex deposits are encountered.
3. All work should be described in written reports which
receive sufficient distribution to insure their availability
to future researchers.
4. All material collected during the project should be donated
to a local institution which has the proper facilities for
curation, display and use by interested scholars and the
general public.
• 6
L11111ir �C& ';F.46
EA -Sr WALL "�r
li
E
Ronald M. Bissell
Principal Investigator
REFERENCE CITED
Becker, Kenneth M.
1989 Cultural Resources Reconnaissance of the Proposed
Castaways Marina, Newport Beach, Orange County,
California. On file at the Archaeological Survey,
University of California, Los Angeles and at RMW Paleo
Associates.
•
ENGINI
AUGM
1$�i
IA. Ross Cash
E
9Elliott H. Boone
Randy H. Mason
Wilfrido B. Simbol
CASH &ASSOCIATES
ENGINEERS August 26, 1987
AGL,OR4NCgVpMigV
2599 East 28th Street
P.O. Box 38
.ong Beach, CA 90801
(213) 426-6145
California Recreation Company/
The Irvine Company
1137 Bayside Drive
Corona Del Mar, CA 92625
Attention: Mr. Ed Power
Subject: CASTAWAYS MARINA, ENGINEERING
STUDY AND FEASIBILITY REPORT
(C&A Project No. 2492.01)
Gentlemen:
Transmitted herewith are six copies of "Castaways Marina, Engineering Study
and Feasibility Report - Final". A draft report was submitted to you on June 15
for review and comment and the Final Report has incorporated the comments
received to date. A report- entitled "Preliminary Geotechnical Investigation,
Proposed Castaways Marina", dated August 11, 1986, by Converse Consultants is
in your possession from a previous transmittal and is referred to in this report
but is not contained herein. An estuary evaluation entitled "Castaways Marina
Qualitative Analysis of Hydrodynamics and Sedimentation" is included herein as
Appendix 6.2. Our comments and recommendations responding to the estuary
evaluation have been added in Section 2.2 in the body of the Report. A list of
agencies and persons contacted in the course of the study in included herein as
Appendix 6.3. The schedules, shown as Exhibits 30 and 31 have been changed
to weeks and months, respectively, instead of specific dates as in the Draft
Report.
The Final Report is essentially unchanged from the Draft Report except for the
added items mentioned above.
We have enjoyed this project and look forward to helping in the process of
obtaining permits which will enable the Marina to become a reality.
Very truly yours,
CASH LarAND ASSOCIATES
ry . / Nye,
Project Manager
LWN: gla
Enclosures
CASTAWAYS MARINA
ENGINEERING STUDY AND FEASIBILITY REPORT
PREPARED FOR
THE IRVINE COMPANY
0
TABLE OF CONTENTS
1.0 INTRODUCTION
1.1
Letter of Transmittal
1.2
Table of Contents
1.3
List of Exhibits
1.4
Scope and Purpose of Report
1.4.1 Scope
1.4.2 Purpose
1.5
Site Description
1.5.1 General
1.5.2 Historical
1.5.3 Access
1.5.4 Recent Use as a Marina Construction Staging Site
1.5.5 Vertical Clearance at Bridge
1.6
Description of Recommended Scheme
2.0 TECHNICAL ISSUES
2.1 Geotechnical
2.2 Estuary Analysis
2.3 Structures and Facilities
2.3.1
Bulkhead
2.3.2
Guide Piles
2.3.3
Slips
2.3.4
Floating Main Walks
2.3.5
Floating Slip Fingers
2.3.6
Pile Supported Pier
2.3.7
Pierhead Line
2.3.8
Parking
2.3.9
Buildings
2.3.10
Fire Protection
2.3.11
Lighting
2.3.12
Landscaping and Planting
2.4 Dredging
2.5 Utilities
2.5.1
Water Service
2.5.2
Sanitary Sewer Service
2.5.3
Telephone
2.5.4
Electrical
•
is
Table of Contents (Continued)
3.0 PERMITTING
3.1 City of Newport Beach Planning Department
3.2 U.S. Army Corps of Engineers
3.3 California Coastal Commission Permit
3.4 State Regional Water Quality Control Board
3.5 City of Newport Beach Building Department
4.0 ENVIRONMENTAL ISSUES
4.1
Developmental Constraints
4.1.1
Coastal Bluffs
4.1.2
Intertidal Zone
4.1.3
Easement for 30" Water Line
4.2
Construction Operations
4.2.1
Dredging, Dewatering and Disposal
4.2.2
Construction Traffic
4.2.3
Construction Noise and Dust
4.3
Wildlife
4.4
Traffic
Generation
4.5
Coastal
Access
5.0 MARINA DEVELOPMENT SCHEMES
5.1 Alternative Schemes
5.2 Recommended Scheme
6.0 APPENDICES
6.1 Preliminary Geotechnical Report
6.2 Qualitative Analysis of Hydrodynamics and Sedimentation
6.3 Castaways Contacts
•
•
Exhibit No.
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
25
26
27
28
29
30
31
32
LIST OF EXHIBITS
Description
Project Location
Existing Topography
Aerial Photograph
Newport Bay Prior to Development
Lower Castaways Site Used as a Marina
Site
Construction Staging
Developmental Constraints and Environmentally Sensitive Areas
Tidal Zones
P.C.H. Bridge - Vertical Clearance
Former Castaways
Marina
Recommended Float
Construction
Existing Utilities
Preliminary Design
Concept
- Scheme A
Preliminary Design
Concept
- Scheme B
Preliminary Design
Concept
- Scheme B-1
Preliminary Design
Concept -
Scheme C
Preliminary Design
Concept -
Scheme C-1
Preliminary
Design
Concept -
Scheme
D
Preliminary
Design
Concept -
Scheme
E _
Preliminary
Design
Concept -
Scheme
F
Preliminary
Design
Concept -
Scheme
G
Preliminary
Design
Concept -
Scheme
H
Preliminary
Design
Concept -
Scheme
J
Preliminary
Design
Concept -
Scheme
A
Preliminary
Design
Concept -
Scheme
L
Preliminary
Design
Concept -
Scheme
M Recommended Scheme
Scheme M Cross -Sections
Summary of
Estimated Project
Costs
Cash and Associates Letter of May 29, 1987, Castaways
Marina, Estimated Costs and Schedule
Preliminary Construction Cost Estimate - Scheme M
Schedule for Acquisition of Permits
Construction Schedule
Alternative Marina Buildings Preliminary Design Concept
• 1.0 INTRODUCTION
•
1.1 Letter of Transmittal
1.2 Table of Contents
1.3 List of Exhibits
1.4 Scope and Purpose of Report
1.4.1 Scope
The scope of this report, as originally outlined in our proposal
of March, 1986, is as follows:
1. Conduct a study of all existing utilities at Dover Drive and
Pacific Coast Highway to determine:
a. Location
b. Existing capacity
c. Easements
d. City or County future plans
2. Meet with The Irvine Company project manager in -charge of
development of the Castaways site to determine:
a. Utility requirements for on -site development
b. Proposed site layout and restrictions for marina related
improvements.
3. Meet with the County of Orange Tidelands Administration,
California Coastal Commission, Army Corps of Engineers,
City of Newport Beach Planning Department and California
Water Quality Control Board regarding design considerations
and constraints for the:
a. Marina
b. Deflection barriers
c. Dredging
d. Site utilities
4. Administer a geotechnical investigation to enhance the
previous geotechnical report prepared for the site. This
investigation will include the proposed northerly extension
water area, the existing water area and the proposed land
development area between PCH bridge and the bluff. The
purpose of the investigation is to establish design criteria
for all marina structures.
1
• 5. Administer a qualitative estuary evaluation of the proposed
site. This evaluation will be on the basis of existing data
and knowledge of site conditions. No measurements or
modelling will be conducted in this phase of the evaluation.
The evaluation will identify potential problems associated with
the site, but will not provide quantitative data sufficient for
final design.
6. Administer a topographic survey of the project site including
soundings at the proposed water areas, elevations at the
land development area, and locations of existing structures.
7. Provide a report consolidating the results of all research.
S. Provide conceptual drawings with alternative plans, if
applicable, for the following:
a. Marina (docks) including practical limit of northerly
extension
b. Bulkhead
c. Barriers
d. Utilities
9. Provide calculations, if necessary, to support the concepts
indicated in item 8 above.
• 10. Meet with the Owner to discuss our findings and concepts.
11. Provide an Opinion or Probable Construction Cost for the
Marina development recommended in the report.
During the course of the investigation, the following items were
added to the scope:
1. Coordinate the Lower Site Schemes with the Upper Site
Concept Studies.
2. Study the land parcel for use as a Marina only, without
commercial use.
a. Evaluate parking, access and traffic
b. Locate and plan Marina buildings
c. Evaluate geotechnicai conditions for the land parcel
3. Investigate developmental constraints for the bluff areas and
lower site.
1.4.2 Purpose
The purpose of this report is to assist The Irvine Company in
• evaluating the marina development option for the Lower
Castaways Site. The report attempts to establish design
criteria, identify permitting issues and estimate costs associated
with pursuing the construction of a marina at the site.
K
1.5 Site Description
1.5.1 General
The site is generally referred to as the Lower Castaways Site.
It is an area of just over 4 acres bordered on the south by
Pacific Coast Highway, on the west by Dover Drive, on the
north by an abrupt 60 foot high bluff and on the east by
Upper Newport Bay. Refer to exhibits 2 and 3.
The site is essentially level at an_elevation of about +8 above
mean sea level. The site is presently clear of structures,
except a concrete bulkhead seawall on the east.
1.5.2 Historical
Previously, the site was utilized as a trailer park and included
a marina with space for 67 boats and a boat hoist. When the
present Pacific Coast Highway Bridge was constructed, approxi-
mately one half of the water area of the former marina was
covered by the bridge. The marina structures and launching
ramp were demolished, leaving only the seawall. The trailer
park was removed prior to the construction of the bridge.
Prior to the construction of the existing seawall, much of the
Lower Castaways Site was a part of the back bay. The seawall
was built and soil was dredged from the bay and deposited
behind the seawall, creating the level site which now exists.
Lack of compaction and fill material selection account for the
present structural weakness . of the soils at the site. Existing
bedrock contours confirm the existence of an ancient inlet in
the bay.
Along the northerly edge of the Lower Castaways Site, skirting
the toe of the south -facing bluff is the roadbed of the original
Pacific Coast Highway. This area is level, at an elevation of
about +12 above Mean Sea Level. Soil conditions are generally
better in this area from the remainder of the site because of its
prior use as a roadbed. The original highway crossed the back
bay at the north eastern corner of the site. Debris from the
demolition of the original bridge still exists on the bottom of the
bay and can be seen at low tide. The location of the original
roadbed probably accounts for the steep, exposed sandstone
face of a portion of the existing south facing bluff. The
original highway was built very close to the bluff to avoid the
inlet which existed at that time south of the roadway. The
bluff was probably cut to provide good roadway alignment at
the bridge approach.
0
1.5.3 Access
A bicycle path/sidewalk, which was constructed in conjunction
with the new PCH bridge, borders the site on the south and
west. It extends under the bridge to the south and along
Dover Drive to the north.
A driveway exists at the north west corner of the site. It is
incorporated into a turnout for an existing bus stop. The
proximity of the driveway to the intersection of PCH and
Dover, make safe access to the site an issue. The site access
will probably be limited to "right turn in" and "right turn out".
This should not pose a problem for a development which is
limited to marina traffic only.
1.5.4 Recent Use as a Marina Construction Staging Site
The Lower Castaways site has recently served an important role
in the local harbor community as a marina construction staging
site. Marina contractors have constructed or assembled float
structures at the site and lowered them into the bay via a land
based crane over the existing seawall. The floating structures
are then towed to their point of use. Exhibit 5 shows such an
operation which was conducted in 1987. Access to the water
for prefabricated marina components is essential to the Newport
Harbor area both for new construction and for maintenance.
While Scheme M, the scheme recommended in this report, will
essentially eliminate the site for use as a construction staging
area, it will still _provide access to the water for prefabricated
floating structures. A crane located in the westerly parking
area could lift components from trucks and place them in the
fairway area along the southern edge of the proposed basin.
1.5.5 Vertical Clearance at Bridge
The new PCH bridge provides a vertical clearance of 20 feet for
boats navigating between the lower and upper bays. Refer to
Exhibit 8. This limits boat traffic to power boats and very
small sail boats. Thus, the proposed marina consists of 35 to
45 foot slips for power boats. This is consistent with current
demand for slips, as reported by California Recreation
Company.
1.6 Description of Recommended Scheme
Exhibit 24, entitled, "Castaways Marina, Preliminary Design Concept
Scheme M" shows the proposed Castaways Marina in the configuration
currently recommended. This configuration is the result of exhaustive
site analyses, discussions with the Irvine Co., discussions with
governmental agencies, cost analyses, geotechnical evaluation, and
• concern for the environmental aspects of developing the site. This
scheme represents a viable development option for the lower castaways
site which has the potential to satisfy the goals of the Irvine Co.
rl
• without compromising community or environmental concerns. In Section
4.0 of this report, the relevant environmental issues and developmental
constraints are discussed. Scheme M is a concept drawing and a wide
range of variations within this basic concept are possible.
2.0 TECHNICAL ISSUES
2.1 Geotechnical
Geotechnical investigations were conducted in 1982 and 1986 by
Converse Consultants.
The 1982 report is entitled "Preliminary Geotechnical Investigation -
Proposed Castaway's Commercial Site, Newport Beach, California",
Converse Project No. 82-02161-01, August 6, 1982. It was conducted
for the Irvine Company. The report focused upon the land area west
of the existing bulkhead and was conducted for the purpose of
establishing foundation design criteria for structures in the event the
site is developed for commercial purposes, i.e. restaurants, offices,
shops, etc.
The 1986 report is entitled "Preliminary Geotechnical Investigation,
Proposed Castaways Marina East of Dover Drive and North of Pacific
Coast Highway, Newport Beach, California", Converse Project No.
86-32245-01, August 11, 1986. It was conducted for Cash and
Associates Engineers. The report focuses upon the area immediately
waterside and landside of the existing bulkhead and the water area
from the bulkhead northerly along the bluffs approximately 1400 feet
from the Pacific Coast Highway Bridge. The purpose of the investi-
gation and report is to establish design criteria for marina structures,
i.e. pilings, bulkheads, etc. and to extend the previous report.
The reports indicate that the site is generally underlain by sand and
silty sand marine sediment deposits over bedrock.
The bedrock varies greatly in depth. At the landsite, the bedrock
varies from elevation -46 near Pacific Coast Highway Bridge to
elevation 0 at the bluff. In the channel, the bedrock varies from
elevation -50 at the center of the channel to elevation 0 at the base of
the bluff. (Elevations in the geotechnical report are referenced to
0 = Mean Sea Level, MSL).
The soils at the land site include compacted fills, noncompacted fills,
dredged fill, beach sand, alluvium and marine terrace deposits. The
soils are considered weak, compressible and subject to liquefaction.
Groundwater exists at the land site at approximately elevation 0 MSL.
The 1984 report recommended that support for structures on the
landsite be by piles, driven to bedrock, designed as end bearing
units. Pile lengths were estimated at between 15 and 75 feet.
• The 1986 report analyzes three cases for guide piles for floating
structures; 1. pile driven into bedrock, 2. pile in clay soil, 3. pile in
sandy soil. Minimum imbedments and approximate lateral capacities are
given in Table I of the report.
Bulkhead design will be strongly affected by the potential for lique-
faction of the retained saturated sands during a significant seismic
event. The recommended Marina Scheme, Scheme M, places the
bulkhead line near PCH on the south, near Dover Drive on the west
and near the bluff on the north, reflecting the concept which would
dredge out most of the land site and create a water basin for marina
float construction. This concept had not been considered prior to the
geotechnical investigation. As a result, borings were not taken
specific to the presently proposed bulkhead locations. If the bulkhead
is to be built in accordance with Scheme M, additional borings will be
required along the bulkhead line. We believe that the additional
geotechnical investigation will result in construction cost savings since
geotechnical conditions may be better for bulkhead design at the
proposed location than along the existing bulkhead as was originally
anticipated.
2.2 Estuary Analysis
The estuary analysis was provided by Rivertech, Inc. with assistance
and advice from Dr. Frederic Raichien, Professor of Hydraulics at the
California Institute of Technology.
The report of the analysis is titled "Castaways Marina, Qualitative
Analysis of Hydrodynamics and Sedimentation" and is included as
Appendix 6.2 to this Feasibility Study. The conclusions and
recommendations from the estuary analysis are discussed below.
2.2.1 Wind and wave effects on the Marina structures will be
addressed in the final design of the Marina.
2.2.2 Flood and tidal current velocities will be included in the
parameters for the final design of the Marina.
2.2.3 The 760 long section of floating docks, including slips 61
through 125, can easily be divided into three sections by
providing a short, hinged bridge between sections. However,
the utilities will require flexible connections which will add to
the cost of the Marina. This effect will be studied during the
final design.
2.2.4 A "guiding van", or deflector structure, can be designed as a
fixed structure or floating structure held in place by guide
piles. The effect of the construction of such a structure on
the wildlife must be evaluated. Also, the efforts to restrict the
entry of floating debris to the upper bay may reduce, or elimi-
nate, the necessity of the deflector. We recommend that this
structure not be built until the experience of the marina with
floating debris indicates that it is required.
6
• 2.2.5 As noted in paragraph 1.5.5, the use of the Marina will be
essentially restricted to power boats which, in general, have
shallower draft than sail -boats. The recommended water depth
of six feet (see paragraph 2.4) is based on the criteria
developed in "Layout and Design Guidelines for Small Craft
Berthing Facilities" provided by the State of California,
Department of Boating and Waterways. This criteria has proved
to be adequate in other marinas for power boats of the sizes
which Castaways Marina will accommodate. However, we
recommend that the consideration of improving tidal exchange
rates should be included in the final design. We estimate that
the additional dredging costs to provide the depth recommended
in the Estuary Study will add less than $70,000 to the Total
Estimated Construction Cost.
2.3 Structures and Facilities
2.3.1 Bulkhead
Our recommendation
'for bulkhead
construction is a tied -back
steel sheet pile wall
with concrete
cap and
deadman. This is
because the depth of bedrock varies greatly.
Steel sheet piles
can be driven into
the bedrock or into the
sand, to varying
depths as required.
Coating and
cathodic
protection will be
required.
2.3.2 Guide Piles
Our recommendation for float guide piles is a combination of
prestressed concrete piles and composite (concrete encased steel
H-section) piles. This is due to the varying depths of bedrock.
Prestressed concrete piles can be driven in sand or clay, composite
piles can be driven into bedrock. The rock -imbedded portion of the
piles would be exposed steel H-section in this case. All of the piles
will appear to be the same from an aesthetic standpoint; number and
placement of piles will be determined from calculations performed
in the design phase of the project. Scheme M shows the
estimated number and locations which have been used to develop
the preliminary cost estimate.
2.3.3 Slips
The recommended scheme consists of 35 foot to 45 foot long
single berth powerboat slips. Recommended berth widths are as
follows:
Slip Length Clear Slip Width
35,
15'-0"
38,
15'-6"
40'
15'-6"
• 42'
16'-0"
45'
17'-0"
7
• 2.3.4 Floating Main Walks
The recommended minimum mainwalk width is 61. The
recommended design is similar to Exhibit 10, incorporating
precast concrete floats, glue laminated wood stringers, wood
plank decking and wood fascias.
Scheme M shows a main walk extending northerly of the pier
and gangway a distance of 750 feet. This is the maximum float
length recommended by the State of California, Resources
Agency Department of Boating and Waterways.
2.3.5 Floating Slip Fingers
The recommended finger width is 4' for slips in the 35 foot to
45 foot length range. The recommended design is similar to
Exhibit 10, incorporating steel torsion bar, plastic floats, glue
laminated wood stringers, wood plank decking, and wood
fascias.
2.3.6 Pile Supported Pier
The pier structure indicated on Scheme M is required to
provide gangway access to the slips in the bay without
restricting flow of water from the near shore area north of the
pier. By providing an adequate opening in the marina
structures, via the clear area under the pier, water quality in
the near shore area north of the pier will be maintained and
_. debris which may flow from the back bay will be allowed to flow
through the marina area rather than collect. It should be
noted that future debris from storm flow into the back bay
should be significantly reduced by the construction of sediment
and debris collection basins upstream in San Diego Creek. This
construction is being accomplished within the Upper Newport
Bay Enhancement/Sediment Management Project.
We recommend that the pier be constructed of pressure -treated
wood framing on concrete support piles with either pressure -
treated wood or concrete decking.
2.3.7 Pierhead Line
No pierhead lines are established in the project area. The
existing bulkhead is very close to the "Adjudicated Line of
Ordinary High Tide", which is a line established to differentiate
legally between the land and the water. This line runs around
the entire back bay. Corps of Engineers, County and City
officials were questioned by Cash and Associates regarding
placement of the pierhead line. None responded with any
preference, except that adequate navigational lanes should be
maintained. Scheme M shows the limit of structures along a line
twenty feet west of the navigational channel designated in the
Back Bay Enhancement Dredging Project. The navigational
channel is typically 100 feet wide, but widens to 200 feet at the
PCH Bridge, corresponding to the clear spans between three
bridge piers.
2.3.8 Parldng
The City ordinance requires 0.75 parldng spaces per slip for
marinas. Thus, since no commercial or other non -marina
activity is planned at the lower Castaways site, a marina with
125 boat ships, similar to Scheme M, would require a minimum
of 94 parldng spaces. Scheme M indicates 108 parking spaces.
The 14 additional spaces, while not required, could help satisfy
requirements for service, maintenance, or parking for public
access to the pier, should this be required.
2.3.9 Buildings
The marina requires restroom facilities, showers, storage for
supplies, a screened trash bin area, and housing for main
electrical and telephone equipment. Scheme M indicates two
buildings. The larger of the two would contain restrooms and
showers for men and women, plus facilities for storage, trash
accumulation and utilities. The smaller building would contain
only minimal restroom and trash facilities. The smaller building
. is recommended because the distance from the extreme northerly
slips to the large building exceeds county guidelines and is
inconvenient.
An alternative plan for restrooms to that shown on Scheme M is
to construct a building on the pier structure incorporating
restrooms, showers and storage areas for the marina plus an
elevated public viewing platform. Refer to Exhibit 32,
"Preliminary Design Concept". This plan would provide an
additional architectural element and focal point for the
development, while providing an enhanced view of the back
bay. Providing public access to this area may be a condition of
approval. Refer to Section 4.6, Coastal Access.
2.3.10 Fire Protection
Fire protection for the floating structures and boats will be
provided by fire hose cabinets with 75 foot hoses. The
cabinets will be spaced a maximum of 150 feet apart and within
75 feet of the extreme limits of structures to provide full
coverage via the fire hoses. Water supply for fire protection
must be capable of delivering 40 GPM at 40 psi at any fire hose
cabinet.
The land area will require a minimum of two fire hydrants
placed so that all structures are covered. Number and location
should be verified with the Newport Beach Fire Department
during design.
9
0 2.3.11 Lighting
The marina floating walkways, gangways, bulkhead walkways
and building areas must be provided with lighting sufflcient for
safety and security.
On the floats, lighting should be provided via low fixtures
mounted on or adjacent to walkways. These fixtures should be
integral with dock boxes or power pedestals.
Parking lot and building areas should be lighted by' a
combination of pole and wall mounted fixtures. All lighting
design should utilize down -lighting or shielded fixtures to
prevent disturbance of the residential views from above and the
roadways adjacent to the site.
2.3.12 Landscaping and Planting
All non -paved areas of the site should receive irrigated
landscaping with the exception of the bluffs. Plant materials
and ground cover for the lower bluff areas which are affected
by this project should be drought resistant so that minimal
irrigation is required on the bluff area. All lower bluff areas
exposed by grading operations should be stabilized immediately
and receive ground cover planting.
An assortment of trees remain on the property from the
previous trailer park development. Most will be displaced by
the new construction. The palm trees are relocatabie and may
be utilized in the new landscape plan or moved to another site.
2.4 Dredging
Scheme M, the recommended scheme, requires dredging in the existing
water area to achieve sufficient water depth and on the existing land
area to create a basin for marina float construction.
The minimum recommended water depth for power boats in all navigable
areas is six feet. Thus the recommended bottom elevation is -8.0 feet
referenced to "Mean Lower Low Water" or -10.7 feet referenced to
"Mean Sea Level".
The material removed from the land site must be disposed of at an
upland disposal site. Disposal cost will be greatly influenced by the
distance to the disposal site. The preliminary cost estimate assumes
Coyote Canyon landfill as the disposal site. The status of Coyote
Canyon at the time of construction is, therefore, a matter to be
pursued. An alternative to the Coyote Canyon site is Irvine Co.
property in the vicinity of the project site. The structural quality of
the material should not limit its use as fill at an upland site. Its
weakness at the present site is due to saturation in the tidal
groundwater environment and uncompacted placement when the site was
originally filled.
10
• Since the soil at the site is generally wet below elevation 0 MSL, the
dredging and disposal process will require spreading and drying at the
site prior to hauling. This increases the time and the cost.
The material which will be dredged from the bay may be either
disposed of at sea at an EPA approved dredge disposal site, or hauled
to an upland disposal site. The upland alternative would require
spreading and drying at the site prior to hauling. The disposal at sea
alternative would require bioassay, bulk elutriate and grain size
analysis of the material, particularly beneath the former castaways
marina floats. Upland disposal would probably require bulk elutriate
and grain size analyses only. Bioassay, including bulk elutriate and
grain size analysis could cost between $30,000 and $45,000. The cost
for bulk elutriate and grain size only could be about 2/3 this cost.
2.5 Utilities
Refer to Exhibit 11, Existing Utilities, incorporated herein.
2.5.1 Water Service
Water service is readily available at the site. The site is
bordered on three sides by City water lines. On the north, a
30" water main runs west to east from Dover Drive across the
site and across the channel. An existing fire hydrant is
served from the 30" line. On the west, a 24" water main exists
in Dover Drive. On the south, a 24" water main exists along
the northerly edge of Pacific Coast Highway. An 8" lateral and
fire hydrant is served from this line. Use of this lateral to
supply water service to the site would not require trenching in
the street.
2.5.2 Sanitary Sewer Service
An underground gravity sewer main exists in Dover Drive.
The project site is low with respect to the street. Onsite
sewers from the proposed toilet buildings will be gravity sewers
to a point adjacent to Dover Drive, then a pump station will
pump the flow, under pressure, to the Orange County
Sanitation District sewer in Dover Drive.
2.5.3 Telephone
An underground telephone conduit system and two manholes
exist on the site. The system is in use now, serving an
existing submarine cable. This cable will be abandoned soon by
Pacific Telephone Co., rendering all of the onsite telephone
facilities inactive. The existing underground duct systems may
be utilized or abandoned as the project dictates. The value of
the existing facilities is in the fact that the underground
. conduit is connected to the main system in Dover Drive,
therefore no trenching in the existing street will be required.
11
• 2.5.4 Electrical
An underground electrical conduit system exists in Dover
Drive. When Dover Drive was recently rebuilt, a 4" conduit
was extended from a So. California Edison Co. vault to the
Castaways site. The conduit is immediately north of the
existing driveway and can be utilized to supply power to the
site. Therefore, no trenching in Dover Drive should be
required for electrical power.
3.0 PERMITTING
Refer to Exhibits 27 and 29, C&A Letter of May 29, 1987 (Exhibit 28) and
Schedule for Acquisition of Permits (Exhibit 30), respectively.
3.1 City of Newport Beach Planning Department
The permitting process begins with application to the Planning
Department. The following items and information should be included in
the submittal:
3.1.1
Plot Plan of Proposed Development
3.1.2
Cross -Sections looking north and west through the new basin
and looking north at the bay.
•
3.1.3
Preliminary floor plans and elevations of the proposed
buildings.
3.1.4
A preliminary drawing of the bulkhead and float detail.
3.1.5
Cut, fill and dredge quantities.
3.1.6
Parking requirement and provision.
3.1.7
Calculations of site areas dedicated to paving, buildings,
landscaping, water.
Filing
fee is $3,250. Use plan fee is $700.00.
The
City Planning Department will make a determination that the
project
•
a. is categorically exempt,
b. is not exempt, but has no potential for significant effect on the
environment (Negative Declaration),
c. does have the potential for significant effect upon the
environment, therefore requires an Environmental Impact Report
(EIR), under the provisions of the California Environmental Quality
Act (CEQA) of 1970.
12
• Based on conversations with the Planning Department, we believe that
this project will require an E.I.R. The City Planning Department will
develop a scope for the environmental document and will solicit
proposals from a short list of firms qualified to do the work. With the
concurrence of the Irvine Co., the City will select a firm and
authorize the commencement of the work. The Irvine Co. will be
required to deposit funds with the City equal to the cost of the E.I.R.
plus 10% prior to the commencement of the work.
The scope of the E.I.R. should include concerns for such issues as
water quality, dredge disposal, traffic, wildlife habitat, and coastal
resources.
3.2 U.S. Army Corps of Engineers
A U.S. Army Corps of Engineers permit is required under Section 10,
of the Rivers and Harbors Act of 1899 for any work within the
navigable waters of the United States. The Corps permit process may
be coincidental with the City Planning Department permit process.
However, since the state and federal wildlife agencies are within the
review and comment loop of the Corps permit process, it is considered
prudent that the pertinent environmental information developed in the
E.I.R. be included in the Corps submittal. For this reason, the
submittal of an application to the Corps of Engineers should be delayed
• until the E.I.R. is complete and accepted by the City.
3.3 California Coastal Commission Permit
A standard permit from the C.C.C. will be required.
Application to the C.C.C. requires prior "approval in concept" from
the City. Therefore, this permit process cannot begin until the
E.I.R. has been reviewed and approved by the City. The final
E.I.R. must be reviewed by the C.C.C. also. Verification is required
that an application to the U.S. Army Corps of Engineers has been
submitted and that state and federal agencies within the Corps permit
loop have reviewed the project. Thus the submittal of the C.C.C.
permit application must follow completion of the E.I.R., submittal to
the Corps, and review by key state and federal agencies.
The C.C.C. permit filing fee for this project will be $1,500.
3.4 State Regional Water Quality Control Board
This agency will require a permit for discharging water from hydraulic
fill and dewatering operations during construction into the bay.
3.5 City of Newport Beach Building Department
After acquisition of City planning approval, Corps of Engineers permit
• and C.C.C. permit, the project may proceed to the preparation of
construction documents (i.e., working drawings and specifications).
The construction documents, along with a final geotechnical report and
design calculations must be submitted to the City of Newport Beach
13
•
40
Building Department for review and approval. Upon approval, the
Building Department will issue a building permit and construction may
proceed. The fee for
project. The building
Is customarily paid by
his bid price.
4.0 ENVIRONMENTAL ISSUES
plan checking is approximately $6,600 for this
permit fee will be approximately $10,000. This
the Construction Contractor and is included in
4.1 Developmental Constraints
Exhibit 6, entitled "Developmental Constraints and Environmentally
Sensitive Areas" shows elements of the site which limit or effect any
plan for development.
4.1.1 Coastal Bluffs
The bluff faces are discussed in the City of Newport Beach,
Land Use Plan. Natural coastal bluffs (defined as steeper than
2 horizontal to 1 vertical and higher than 25 feet) are
considered a significant scenic and environmental resource. In
general, grading and development are limited on or adjacent
to these areas. The east facing bluffs meet the definition for
steepness and height and are natural. The south and, west
facing bluffs do not meet the definition for steepness, except
where previous grading for old Pacific Coast Highway and
Dover Drive have left portions of the bluff steeper than 2 to 1.
Even though these areas are not "natural" bluffs meeting the
strict definition of "Bluff" in the LCP, they may be considered
scenic resources by the Coastal Commission. This issue should
not impact the project as currently proposed since no develop-
ment is proposed on the bluff faces. Minimal grading will be
required near the toe of the south facing bluff to accommodate
parking.
4.1.2 Intertidal Zone
The intertidal zone indicated on Exhibit 6 is a narrow mudflat
area lying along the toe of the east facing bluff. At .present,
the area is accessible to pedestrians from the lower castaways
site during low to medium tides. During high tides the area is
inundated and essentially inaccessible. The proposed project
would remove a small portion of this intertidal area near the
intersection of the south and east facing bluffs. The proposed
bulkhead railing would render the remaining intertidal areas
inaccessible.
Exhibit 7, entitled "Tidal Zones", indicates mudflat habitat in
the intertidal zone between elevations +2.7' MLLW and
-2.0' MLLW. Referenced to Mean Sea Level, this range is from
0 MSL to -4.7' MSL.
14
• The issue of most concern with regard to the mudflat area is its
use for loafing and feeding by endangered bird species,
particularly the least tern and the clapper rail. The concern
involves two elements:
1. Removal of a portion of the intertidal area
2. Disturbance to a portion of the remaining intertidal area
through the introduction of people and boats associated
with the extension of a floating mainwalk and slips
north of the proposed bulkhead.
The "value" of the area to the endangered birds is a function
of their frequency of use. No information exists with regard to
actual use of the area by the endangered species. The National'
Marine Fisheries Service has indicated that they would prefer
replacement of the intertidal areas which are to be removed on
a one-to-one basis in the Upper Newport Bay Ecological Reserve
as an acceptable means of mitigation. Mitigation for the loss of
value to the remaining intertidal areas is not so easily
approached since its present value is not known and since the
degree of disturbance is not easily quantified. One important
mitigating measure inherent in the proposed project is that the
direct access of pedestrians to the intertidal area will be
• removed by the bulkhead railing. The pedestrians and boat
traffic associated with the marina floats will be physically
separated from the intertidal area. The boat traffic is not a
newly introduced element, since the area in question is open to
navigation presently. The difference with respect to
disturbance lies in the increase or decrease in boat traffic near
the shore. The change is not easily defined because the near
shore traffic will be limited to those boats which are moored at
the 25 shore side slips. The marina will actually shield the
intertidal area from casual boat traffic which currently is
allowed to navigate in the near shore area.
4.1.3 Basement for 30" Water Line
A 30" diameter City of Newport Beach water line traverses the
property west to east near the toe of the south facing bluff.
The City has requested an easement 24 feet wide along the
water line route. No permanent structures would be allowed
within this easement. This easement would facilitate excavation
of the water line for repair and minimize possible damage to
structures in the event the line ruptures. The present
alignment of the pipeline presents a problem for the proposed
bulkhead near the northwesterly corner of the proposed basin.
It may be necessary to relocate a portion of the water line to
avoid difficulty in constructing the bulkhead tie -back system
and, of even greater importance to protect the bulkhead from
• possible future damage.
15
4.2 Construction Operations
4.2.1 Dredging, Dewatering and Disposal
Construction dredging involves three types of operations:
a. Suction dredging in the channel to achieve water depth.
b. Excavation of dry material at the land site.
c. Bucket dredging of material saturated in ground water at
the land site.
Our preliminary recommendation is to haul all of the excess
material to a land disposal site. This will result in the
necessity to dewater and dry all of the material obtained in
dredging operations a and c above. The dewatering process
will involve discharging waste water into the bay. This will
require a Regional Water Quality Control Board permit and
measures to control the quality of the effluent.
One possible procedure for carrying out the dredging and
disposal project is as follows:
a. Excavate dry material at the site to create a dewatering
basin.
b. Suction dredge in the bay and deposit the material in
the
basin.
• c. Dewater, dry, excavate and haul the material to
the
disposal site.
d. Dredge the material which is below the water table
and
deposit it in dewatering basins.
e. Dewater, dry, excavate and haul the material.
The disposal issue will be addressed in detail during
the
permitting phase.
4.2.2 Construction Traffic
Most of the traffic generated during the construction project
will be during the dredge material disposal phase. Because of
the dredging, drying and hauling sequence required this traffic
will not be concentrated, but will be spread over a relatively
long period of time. The entire disposal phase could take 16
weeks and could require 6,000 truck trips to Coyote Canyon or
an alternative site. This traffic issue including route and
timing will be addressed in detail during the permitting phase.
4.2.3 Construction Noise and Dust
Construction noise and dust should not be major issues because
the site is not closely bordered by sensitive uses. The
residential area to the west across Dover Drive is a
• consideration, but is buffered by traffic noise generated by
Dover Drive. These issues will, however, be dealt with in the
permitting phase.
16
4.3 Wildlife
Wildlife issues at the site are predominated by concern for the
endangered bird species indigenous to the back bay. No known
nesting sties for endangered bird species exist within the project area.
Mudflat areas are a valuable resource with regard to the endangered
birds. The mudflat areas are used for loafing and feeding during low
tide conditions. The actual value with regard to use of the mudflats
affected by this project is not known because no site specific studies
have been conducted. Conversations between Cash and Associates and
the National Marine Fisheries Service have revealed that an acceptable
form of mitigation for mudflat areas eliminated by the project would be
replacement in kind somewhere within the back bay ecological
preserve. Mitigation for disturbance of remaining mudflat areas is a
question to be resolved in the permitting process. Refer to Section
4.1.2 for a discussion of the disturbance issue.
The marine environment can be both enlarged and enhanced by this
project. The simple fact that more sub -tidal marine habitat will exist
as a result of the project is a plus for fish species. In conversation
between Cash and Associates and the California Department of Fish and
Game, the concept of creating a basin in the Lower Castaways site
drew favorable response from responsible C.D.F.G. personnel. They
expressed concern for water quality within the basin. Thus, water
quality will be an issue to be addressed in the permitting process.
It appears that the recommended • project, with proper attention to
wildlife issues, could result in significant gains in wildlife habitat
value over the present undeveloped site.
4.4 Traffic Generation
Traffic generated by the proposed development of the Lower Castaways
site is a locally sensitive issue. The intersection of Pacific Coast
Highway and Dover Drive is highly congested. The proximity of the
lower Castaways entrance to this intersection is an item of concern for
the City. The City will strongly favor right turn in and right turn
out as the means of ingress and egress. There is local neighborhood
resistance to signalizing the intersection of Dover Drive and Cliff
Street to serve Lower Castaways from Upper Castaways.
For these reasons, the development of Lower Castaways for marina use
only is a concept which should meet with little or no resistance from
the standpoint of traffic generation. Restricting ingress and egress to
right turn in, right turn out will not degrade the property for marina
use, whereas this would be a problem for most commercial uses.
To address the traffic generation issue adequately, data is needed to
quantify and substantiate the amount of traffic which will be generated
by the "marina only" development concept. The City does not have
traffic generation data for marinas without mixed uses such as
. commercial. It is anticipated that traffic generated by the marina
alone will be substantially less than any mixed use. Thus, it would
17
E
0
0
benefit this project to obtain traffic counts or allow the City to obtain
traffic counts at a local Irvine Co. Marina where traffic is limited to
that generated by the marina alone.
4.5 Coastal Access
The recommended scheme does not limit public access to the parking
areas, bulkhead walkways, or pier. The floats will be accessible only
to marina tenants. This restriction will be accomplished by locked
gates at the gangways. Marina tenants will be issued keys.
Restroom facilities will also require a key for entry. Thus, the public
is not restricted from the coastal view provided by the bulkhead and
pier. This coastal view could be accentuated and enhanced by the
construction of a viewing platform on the pier. Conversely, the public
could be restricted from the site through the use of a fence and
traffic control gate. The issue of public access will be addressed in
the City Planning Department Review process and the California
Coastal Commission permit process. If public access is provided or
required, an allowance for parking must be made. Scheme M includes
fourteen spaces which are not required for the marina, but little
opportunity exists to provide more parking because of the limited
space at the site.
5.0 MARINA DEVELOPMENT SCHEMES
5.1 Alternative Schemes
Exhibits 12 thru 25 show alternative schemes which were developed
during the study activities. When the study began, the Lower
Castaways Site was being considered by the Irvine Co. for commercial
development. Thus, the marina was essentially restricted to the
existing water area as shown in Schemes A and B. Scheme C
proposed the creation of a basin at the Lower Castaways site and was
an attempt to coordinate the development plans for the upper and
lower sites. The creation of the basin and the dedication of the entire
lower site to marina use will ease many of the concerns over traffic
generation and wildlife habitat degradation which are inherent in most
development plans. This plan also makes it possible to go ahead with
the development of the lower site since it is not dependent upon or
interactive with any upper site development plans. A marina at the
lower site is compatible with and will enhance almost any future upper
site development.
Cost estimates were prepared
analyses were performed by the
that the minimum costs associate
for a marina require a slip count
d
for some of the schemes. Payback
Irvine Co. Generally, it was found
with construction of support facilities
in excess of 100 slips.
18
! 5.2 Recommended Scheme
Scheme M, Exhibit 25, was developed through a one year iterative
process and is the result of many meetings and discussions with the
Irvine Co. Agencies which have been contacted directly by Cash and
Associates regarding the project include:
o City of Newport Beach Planning Department
o City of Newport Beach Engineering Department
o City of Newport Beach Marine Department
o County of Orange
o California Department of Fish and Game
o U.S. Fish and Wildlife Service
o National Marine Fisheries Service
o California Coastal Commission
o U.S. Army Corps of Engineers
o Orange County Sheriff's Department - Harbor Patrol
While none of these agencies has responded officially to the project, no
real opposition has been voiced. Concerns have been expressed and
they are addressed in this report, but it appears that a project similar
to Scheme M would not meet with strong resistance by any of the
agencies involved in the permitting process.
Exhibit 26 is a preliminary construction cost estimate for Scheme M.
6.0 'APPENDICES
6.1 Preliminary Geotechnical Report
(Transmitted previously under separate cover)
6.2 Qualitative Analysis of Hydrodynamics and Sedimentation (Estuary
Analysis)
6.3 Castaways Contacts. A list of persons contacted during the study.
19 -
POOR.
QUALITY
ORI'GINAL (S)
r'r
0
E
CAST A`J�'AYS MARINA
OUALITATIVE ANALYSIS
OF
HYDRODYNAMICS
AND
SEDIMENTATION
PREPARED FOR
CASH & ASSOCIATES - ENGINEERS
RI VERTECH
.i..._..� o INC
JULY 1987
_= Rl VERTECH
i p INC CONSULTANTS IN WATER RESOURCES ENGINEERING
July 16, 1987
Mr Larry W. Nye, P.E.
Cash & Associates Engineers
2599 East 28th Street
P.O. Box 38
Long Beach, CA 90801
Dear Mr. Nye,
Rivertech Inc. Is pleased to submit our attached report entitled "Castaways
Marina, Qualitative Analysis of Hydrodynamics and Sedimentation".
This report has been prepared with assistance and advice from Dr. Frederic
Raichlen, Professor of Hydraulics at the California Institute of Technology.
We have enjoyed working with you on this project and look forward for the
• opportunity to work with you again.
Sincerely,
•
A-Ia'ERTECH INC.
L714101 �,�o L, — ,
Hasan Nour4/
President
1400 QUAIL STREET / SUITE 210 / NEWPORT BEACH; CA 92660 1 (714) 752 - 8722
•
DESCRIPTION
TABLE OF CONTENTS
PAGE
CONCLUSIONS AND RECOMMENDATIONS 1
INTRODUCTION 2
TIDE CYCLE 2
DEPTH CONSIDERATION 3
WAVE CONSIDERATION 3
CURRENT AND CIRCULATION CONSIDERATION 4
EROSION AND DEPOSITION CONSIDERATION S
FLOATING DEBRIS CONSIDERATION 6
•
•
AND RECCMMENDATIONS
• Based on a qualitative analysis and a reconnaissance level study of
sedimentation and hydrodymamics of the proposed Castaways Marina, Rivertech
makes the following conclusions and recommendations:
1. Wind and ship generated waves are significant design parameters for the
proposed Castaways Marina. Their magnitudes should be computed and
their dynamics should be considered in the design. Although the
designer is cautioned about their presence and magnitude, nevertheless,
they do not pose a major problem.
2. Flood and tidal current velocities along the navigation channel could be
very high. It is recommended that the design of the marina be based on
the occurrence of the simultaneous events of the 100-year storm and the
mean ebb tide.
3. To provide better tidal exchange rates between the marina and the
navigation channel and to improve the flexibility of the 750 feet long
floating dock, it is recommended that it be divided into three seperate
components.
•' 4. To prevent excessive influx of sediment and floating debris into the,
marina a guiding van should be installed at the north end of the marina
extending from the shoreline.
5. Assuming the marina will be used by vessels requiring a draft of 4 feet,
it is recommended that the bottom of the marina be dredged to elevation
- 12.5 feet (MSL). This would allow a clearance of 3.6 feet between the
bottoms of the basin and the vessel during the occurrence of extreme low
tide. Adequate clearance will also improve tidal exchange rates between
the marina and the main estuary.
-1-
n
INTRODUCTION
Cash & Associates Engineers has recently completed a report entitled "Castaways
Marina, Engineering Study and Feasibility Report". The report was prepared for
The Irvine Company and its draft copy was submitted on June 15, 1987. Cash &
Associates Engineers has asked Rivertech to prepare this report which
qualitatively analyzes the hydrodynamics, water quality and sedimentation
aspects of the recommended scheme.
The Irvine Company with assistance from Cash & Associates Engineers is
evaluating the development of a 4-acre site in Newport Bay to a marina. As
shown in Figure 1 (also Figure 5), the site is located just north of the
Pacific Coast Highway Bridge in Newport Beach.
Results of the qualitative analysis described in this report are based on
information obtained from field observations, previous reports, meetings,
telephone interviews and Rivertech's experience with similar estuaries.
TIDE CYCLE
The tide cycle at the mouth of Newport Bay with the Pacific Ocean are diurnal
having an approximate period of 24 hours. These type of tides are produced by
the phase relation of the sun, the moon and the earth. The relative ranges of
the two daily tides continuously vary from small to large over a 28-day period.
. The characteristics of tide cycle in Newport Bay at the Pacific Coast Highway
(Project site) is approximately the same as that at its mouth. The following
represents the estimated parameters of the tide cycle in the project site.
•
Mean lower low water = 0.00 feet
Mean high water lunitidal interval = 5.13 hours
Mean low water lunitidal interval = 11.15 hours
Mean range of tide = 3.69 feet
Mean tide level = 1/2 (mean high water + mean low water) = 2.79 feet
Mean sea level = the mean of the hourly heights = 2.76 feet
Mean high water diurnal inequality = 0.75 feet
Mean great diurnal range = 5.40 feet
Diurnal tide level = 2.70 feet
Mean high water = 4.65 feet
Mean low water = 0.93 feet
Mean higher high water = 5.40 feet
Highest observed = 7.86 feet on January 28, 1983
Lowest observed = 2.14 feet on December 29, 1955
The actual elevation reached by a particular tide is further influenced by wind
set-up on the ocean and in Newport Bay. In addition, magnitude of stormwater
runoff from the area tributary to Newport Bay affects its elevation
considerably.
-2-
n
/ NORTH
I �I
� MILES
—, 0
<� Santa Ana — E--- Peters Canyon Wash ? \
Detht Channel
Q Newport Bay
San ) Diego Watershed Boundary
r�Creek
2�
r2 //
A
Vr s NDIeG0
•DOVER OR a Sand Canyon
Wasb
t— Newport Bay el
1�7 /
O PACIFIC COAST HWY r
t; t
L�
PROJECT SITE
Pacific
�Qeah
RI VERTECH FIGURE
0 INC LOCATION MAP
0
•
DEPTH CONSIDERATION
The recommended scheme which is depicted in Figure 2 (Scheme M shown as Exhibit
25 in Cash & Associates' report) describes that the basin for the Castaways
Marina will be dredged to a depth of - 10.7 feet mean sea level (MSL). Assuming
a draft of 4 feet for the vessels, this arrangement at extreme low tide will
allow a clearance of only 1.8 feet. This is shown in Figure 3. The
corresponding clearance for the floating docks is estimated to be 2.8 feet.
Rivertech believes that these clearances may not be adequate. It is
recommended that the marina basins be dredged to an elevation of at least 12.5
feet (MSL). This would permit adequate clearance as well as allowance for any
sedimentation which may occur.
The extreme high tide has been measured to be 5.1 feet above mean sea level.
Thus, one could expect a tidal excursion of the order of between 10 and 11
feet. This is not as much of a concern as the extreme low tide but is
mentioned here as just the fact that there should be awareness of this tidal
range in designating the various components of the marina.
WAVE CONSIDERATIONS
A brief review of literature in evaluating the problem of boat generated water
wave revealed that there are some related concerns that the designer of the
Castaways Marina should consider. Area "A" which is between the 750 feet
floating dock (slips 61 through 125) and the wetlands, shown in Figure 2, is
more critical since excessive wave generation could promote erosion, disturb
the marine life and reduce the habitat values along the shoreline.
Our reconnaissance level analysis revealed that a cabin cruiser of about 3 tons
displacement would generate waves with maximum wave heights between 6 inches
and 1 foot at a distance of 100 feet away from the sailing line of the vessel
when it is traveling at speeds of 5 to 6 knots. For the same speed, a 40-foot
U.S. Coast Guard cutter generates maximum waves that are about 1 foot high
about 100 feet away from the vessel. For both of the above cases, the wave
period is about 2 seconds.
Slips 61 through 98 would be subject to ship generated waves, since there may
be more high speed activity along the navigation channel. For example, at a
ship speed between 10 and 15 knots a 4-foot U.S. Coast Guard cutter generates
wave heights of 2 feet at a distance of 100 feet from the sailing line.
Similarly, a 3-ton cabin cruiser generates waves of the order of 0.7 feet at
the same distance and speed.
Another type of wave which may be present at the proposed marina are those
generated by wind. Spring and fall Santa Ana winds blow down the Newport Bay
estuary and can generate waves upto 2 feet high at high tide when the fetch is
long. Lesser waves would be expected at lower tides. Still another type of
waves as that generated by on -shore breezes. Their range is estimated to be up
to 6 inches.
Although we do not believe that any one of the type of waves described above is
a problem for the proposed Castaways Marina, nevertheless, one should consider
them in the design analysis.
-3-
r
�J
3 11
n
a
9 (j1
z � i
.G
u 99F9 •<
v
x
/ x x x
NOTES
IQ oamm a xw-AD To BE RacvED
2O PROPoED BASW DREDGED To-10 M5L
® PROPOSED sIEEIL si$r PILE at+a•eAD
x z x ® /�pvp�\ Rocx PROTEC7p aCPe
Q5 I PROPOSED ROATAIG DOCKS
© �ROPOS®I GANGWAYS
YO SAWr PIAPOUf STATION
© PROI-OSEDIPiE S.FPORTED PER
x x fPR� LZRIGAY® PLANTING '
r�veurt 12 RECONSiRL aTr:D 1MNEWAY
13 SIDEWALK —
® et'asT"'G Bra PATH
5 oaSTM BRIDGE
ib E)05nNG PROPER'I7{p.)c�
x z FRMP D RETAWM WALL
/ — I) PROP0SED TOQ.Ef aMMM
/ �IussrsTDva 19 PROPOSED RAn G.
M aC�L.pT Wi_ � •
GUIDE VAN
/ PROPOSED BY RNERTECN
ov
17
y
.p 9 as .� �• � a � i / / �--'-- >
J ' y { S a 19 3% { / / /� / / SCHEME N a
n • { 9 � '� 1x e � q' { z / / m
SLIP COUNT
,! I SaE rawer Tara FcmT
0 / / / / 45' SLIPS 52 2250 ~
s / o s ` _ / / / 47 SLIPS 39 1638
38' SLIPS 19 722
Is z 35' SLIPS 8 280
/
b / SIDE TIES 7 280
TaT� 125 5270
94 PARKING SPACES REQUIRED €
108 PARKING SPACES r" 20VIDED
3
FIGURE 2,��2_�
r
2.76'
2.14'
Q VESSEL
-V7EXTREME LOW TIDE
4.0' DRAFT
3.6' CLEARANCE
RECOMMENDED BY RIVERTECH --I
FEASIBILITY REPORT ESTIMATED BOTTOM
•
Rl VERTECH
v IN
MSL=O
MLLW
CLEARANCE LIMITS
SLIP
3.0'
4.6' CLEARANCE I
FIGURE
3
• CURRENT AND CIRCULATION CONSIDERATION
The rise and fall of the ocean, combined with the presence of pools and
constrictions that characterize upper and lower Newport Bay produce tidal
currents at various locations in Newport Bay. These currents are strongest at
constrictions such as the section of the bay at Pacific Coast Highway and
weakest at locations where the estuary widens.
Velocity measurements made on December 20, 1983 by the Orange County
Environmental Management Agency (OCEMA) at the Pacific Coast Highway Bridge are
shown in Figure 4. On this date, The National Oceanic and Atmospheric
Administration's (NOAA) station in Newport Beach shows the following tidal
measurements.
Low water = 2.50 feet at 02.0 hours
Higher high water = 7.15 feet at 08.5 hours
Lower low water = 0.96 feet at 15.9 hours
High water = 3.76 feet at 22.3 hours
A comparison of these measurements with the mean tide cycle values, described
previously, indicates that on this date very high and low tides were present in
Newport Beach. In fact the higher high water elevation is only 0.71 foot less
than the highest recorded value which occurred in January of the same year.
Therefore, the measured values shown in Figure 4 are close to the upper limit
of velocities which may be present at the Pacific Coast Highway Bridge in the
Bay. This figure shows that tidal velocities exceed 3 feet per second in the
navigation channel and reduce to zero close to the bridge abutment.
Velocities may increase significantly at the navigation channel'in the vicinity
of the Pacific Coast Highway Bridge during major storm events. During the
storm of March 1, 1983, the harbor master has estimated the current speed to be
in excess of 10 knots (17 feet/sec.). His estimate was based upon engine
revolutions required to maintain a steady boat position in the channel.
Rivertech believes that this estimate is probably higher than actual. It is
possible that wind resistance was also a contributing factor.
The designer of the proposed Castaways Marina is cautioned to note the
proximity of the high velocity field of the navigation channel to the marina.
The floating dock which houses slips 61 through 125 would be most susceptible
to damage by high velocity currents.
A review of the velocity field at the bridge shows that velocities quickly
reduce to negligible values when the location changes from the channel to the
abutment. In addition, field observation indicated evidence of sediment
deposition adjacent to the western bridge abutment. Construction of the
proposed marina probably would not alter these currents appreciably.
Therefore, the desired level of circulation in areas "B" and "C" of the marina
shown in Figure 2 may not be achieved at all times. The opening under the
gangway which is located adjacent to slips number 1 and 39 allows surface water
circulation and should enhance the water quality.
Rivertech recommends that the channel adjacent to the pile supported pier
• (labeled as 8 in Figure 2) be maintained as large and unobstructed as
possible. This is because the marina in the vicinity of the pier has a major
constriction which would probably cause excessive velocities.
—4—
r-1
3
C11
0+00 10+00 11+00 12t00 13+00 14+00 15+00 16+00
DISTANCE IN FEET
3
J
W
W
1L
2
O
h
0 Q
W
J
0 W
.0
.0
0.0
2.0
4.0
6.0
C�
10 RIVER
v ANC
TIDAL VELOCITY DISTRIBUTION
AT PACIFIC COAST HIGHWAY BRIDGE OVER NEWPORT BAY (LOOKING NORTH)
REMAXIMUM
J�t
• Assuming economy permits, we recommend that the 750 feet long floating dock be
divided into three sections. This is to improve the tidal currents between the
navigation channel and the shoreward located mud flats. We recommend that the
region of berths 111-112 and 86-87 be replaced by a walkway connecting the two
sections. In addition, in the region of berths 122-123 and 75-76 a similar
break in the dock be provided. With these openings the following advantages
can be achieved:
1. Tidal exchange rates between the navigation channel and Area "A" will be
increased.
2. The tidal and flood velocities at the pier, labeled 8 in Figure 2, will
be reduced.
3. Improved flexibility for the 750-foot long floating dock.
The above recommendation is of particular significance since the 750-foot long
dock would be subject to high flood velocities as well as wind and boat
generated waves.
•
EROSION AND DEPOSITION CONSIDERATIONS
During the past few years, an effective and rigorus sediment control management
has been practiced in the Upper Newport Bay. If current practice of sediment
control management in Upper Newport Bay continues, very little maintenance and
dredging will be required in the Lower Newport Bay and in the vicinity of the
proposed Castaways Marina.
San Diego Creek Channel (see Figure 1) is the major source of sediment yield to
Newport Bay. Its sediment load can be classified as : -
o Wash load
o Suspended load
o Bedload
Nearly all of the bedload and suspended load settle in the sediment traps
constructed in the lower reaches of San Diego Creek Channel or Upper Newport
Bay. During the last few years, large quantities of sediment deposits were
removed from the sediment traps and from the Upper Newport Bay. If the
existing trapping efficiency in the sediment traps and in Upper Newport Bay is
maintained, it would be very unlikely for bedload and suspended load to reach
Lower Newport Bay or the area in the vicinity of the Pacific Coast Highway.
Washload, however, behaves differently. In freshwater, wash load particles
repel each other because their ions have like charges. Once freshwater is
mixed with saltwater, ion exchanges occur and particles become cohesive. In
this manner, aggregates are formed and estuarine deposits are produced. When
this accumulation grows thicker, the weight of the deposit crushes the lower
aggregates in the bed, making the b--- more dense and stronger.
-5-
• The interface between freshwater and ocean water can happen anywhere in Newport
Bay upstream of the Pacific Coast Highway, depending on the volume of
stormwater and phase of tide cycle. Therefore, the phenomenon of cohesion and
aggradation can occur anywhere in the Newport Bay upstream of the Pacific Coast
Highway.
The new deposits are often disturbed and resuspended by wave action that occurs
during windy periods and passage of vessels. Subsequently, tide currents
redistribute this suspended material into regions where wave action and
turbulence is less intense.
It is the preceding process that would cause deposition of material in the
proposed Castaways Marina. Field observation at the proposed marina site
showed very little evidence of organic or fine material deposits. The high
currents which are present in and in the vicinity of the navigation channel may
be the reason behind the absence of this type of deposits.
At some isolated locations, such as the area adjacent to the bridge abutment
evidence of deposition was noted. This is probably because the combination of
the existing bulkhead, bridge pier and bridge abutment has caused a stagnation
zone and hence has promoted the process of deposition.
The area to the west of the proposed 750 feet long floating dock will probably
have the tendency to erode rather than to deposit. As explained previously,
this area is subject to strong wave action and is a relatively higher velocity
zone. The division of the 750 feet long floating dock into three components,
would provide better tidal communication between the navigation channel and the
marina area west of the dock. In addition, we recommend that some type of a
guide van be installed at upstream of this area. Its approximate location is
shown in Figure 2. Installation of such a guide van will have the following
advantages:
o Reduces wave action in Area "A"
o Enhances the habitat values of the mud flat along the shore .
o Reduces the high velocity currents which may exist at the pier between
Area "A' and Area "B" during major storms and during ebb of spring tides
(high range tides).
o Reduces the chance of sediment and floating debris entering the marina
area.
FLAATING DEBRIS CONSIDERATION
Although the problem of floating debris is not a major concern in Newport Bay,
nevertheless, it would probably become a problem in the future. The watershed
which is tributary to Newport Bay is currently experiencing the dynamics of the
development. With the continued rate of development in the watershed, floating
debris will probably become a major problem in Newport Bay in the future.
• As far as floating debris is concerned, the marina areas designated by "A" and
"B" in Figure 2 should have minimal problems. This is because currents are
strong at they— entrance and in all- probability would transport the floating
debris away from the proposed marina.
sm
• The City of Newport Beach has installed a debris trapping boom in Upper Newport
Bay to mittigate this problem. The location of this boom is shown in Figure
5. The direction of current at this location is such that the boom has to be
extended into the Bay only for about 1/3 of the channel width. Most of the
floating debris is carried to the North Star Beach and is trapped by the boom.
•
0
-7-
FLOATING DEBRIS
NORTH STAR
BEACH
14
BACK
DEBRIS TRAP BAY
BOOM
PROPOSED
CASTAWAYS
MARINA
RIVERTECH
W ESTCLIFF
OR
DOVEERR
BALBOA
ISLAND
NORTH Pacific Ocean
1 MILE
SURFACE DEBRIS TRAP
AT UPPER NEWPORT BAY
Upper
Newport
Bay
EAST
BLUFF DR
Newport
Bay
BACK
BAY
DR
NEWPORr CENTER
FIGURE
5
CASTAWAYS CONTACTS
AGENCY PERSON TYPE OF CONTACT TOPICS DISCUSSED
1. County of Orange Bob Wingard Meeting Permitting, Pierhead line
Tidelands Admin.
2. County of Orange Steve Blanchard Telephone Bulkhead line; County/City
Tidelands Admin. (714) 567-5104 jurisdictional boundaries
3. City of Newport Beach, John Wolter Meeting City dredging projects; Permitting;
Engineering Dept. Pierhead line
4. City of Newport Beach, Patti Temple Meeting Permitting; Environmental issues;
Planning Dept. Environmental documentation
S.
City of Newport Beach,
Tony Mellum
Meeting
Navigation; Pierhead line
Marine Department
6.
City of Newport Beach,
Jim Upton
Tale hone
Fire protection of structures;
Fire Department
(714) 644-3109
Access; Fire water sources
X-3106
7.
City of Newport Beach,
Gil Gomez
Telephone
Water sources
Water Department
(714) 644-3011
08.
Telephone
Sewer Manhole
County Sanitation
connection;
District
(714) 962-2411
reference elevation
9.
City of Newport Beach,
Jeff Staneart
Telepphone
30" Water line reconstruction
Engineering Department
(714) 644-3311
10.
Pacific Telephone Co.
Chuck Gibo
Telephone
Location and status of underground
Marylin Cole
(714) 966-6231
facilities; Maps of underground
facilities
11.
Southern California
Telepphone
Maps of underground facilities
Gas Company
(714) 634-3117
12.
Southern California
Chris Cartwright
Meeting
Service, maps of underground
Edison Company
facilities
13.
California Department
Dick Nitsos
Meeting
Wildlife issues (Marine)
of Fish and Game
Earle Lauppe
14.
U.S. Fish and Wildlife
Jack Fancher
Meeting at Site
Wildlife issues (Intertidal)
Service
15.
National Marine
Bob Hoffman
Meeting at Site
Wildlife issues (Endangered Birds)
Fisheries Service
16.
California Coastal
Praveen Gupta
Tale hone
Permitting
Coamission
Chris Kroll
(213) 590-5071
1
*AGENCY PERSON
17. U.S. Army Corps of Dan Muslin
Engineers Cheryl Hill
Glen Lukos
TYPE OF CONTACT TOPICS DISCUSSED
Tale hone Permitting; Pierhead line
(213) 894-5401
(213) 894-5606
18.
Cal Trans
John McNeil
Telephone
Drawings; Right -of -Tray; Utilities
Chuck Barthel
(213) 620-3760
19.
Orange County Sheriffs
Captain Gage
Meeting
Pierhead line; Navigation
Dept. Harbor Patrol
20.
Bill Harris
Telephone
Dredging
(714] 644-0550
21.
Irvine Company
Ed Power
Meetings
Daryll Landrum
Jim Kelley
Sam Couch
Charles Nilson
David Dmowhowski
22.
WZ!H Group, Inc.
Paul Barnard
Meetings
Coordination with Upper Site
David Goodale
Development Schemes
0
2
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-DEVELOPMENTAL CONSTRAINTS AND
+
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ENVIRONMENTALLY
SENSITIVE AREAS•EXHIBIT
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noun•
2493.07
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Dislichlis
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SALT MARSH
Spartina
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MUDFLAT
Eelorass
AARINI
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ELEVATION
4 MEAN •
LOWER
3 LOW
2 WATER
TIDAL ZONES
EXHIBIT 7
0 Ids ABUT
�o e
t ABUT
PIER 2 PIER 3 PIER 4 PIER 5 PIER 6 , PIER 7 PIER 8
�q3
COAST
Iae
1
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INSTALL BRIDGE
a+� PIER PROTECTION,
NEWPORT BAY SEE SP CIIALTION PROVISIONS.
PLAN
I" = 100,
PACIFIC COAST HIGHWAY4RIDGE
'B'T 8
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FORMER CASTAWAYS MARI
SLIPS
•67
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E ERLASTAWAYSi1ARINA•
EXHIBIT .
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4"_ l -CASTAWAYS MARINA ;- NONE a
arr. •q
:_THE IRVINE COMPANY: -CONCEPT 3 FEASIBILITY -STUD' 249201
.pitf: _ - - ClfOMt>noR- - p _ - sE"^"'�•'•'•-'• - ::.RECOMMENDED- FLOATDETA!LIA:
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• a UTILITY PLAN
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EXHIBIT 14
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PARKItJ4�EQUIi�HErdf'OOD�M° 17SSfALES
- >71171F14 �AAPAcI"fY 3330
tpiAt- PAP.KHJG R6Qawr=D 944. I,S 2L9 5pALrS
'(OTAL PAaKINb moo tgv 712'5
MCAMOCrAL USE MOM- T"1zG9•03
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EXHIBfT 18
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SCHEME F
82 - 45 BLIPS
11 SIDE TIES
'
•65 PARKING SPACES REQUIRED
75 PARKING SPACES PROVIDED
EXHIBIT IS.
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4 - 46 SLIPS
63 - 36 SLIPS
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/ /
4
63 PARKING SPACES REOUIR�D
76 PARKING SPACES PROVIDED
x
s
M1< GAO
EXHIBIT 20
A`� :
i x
x x
NOTES
IQ EXISTING B AKI-EAD TO BE REMOVED \
x x O PROPOSED BASINOREDGm To -lo MSL
i
.` Q PROPOSED cONCRETE aia•EAO 43o LP)
` ® ROCK PRoTECTID SLOPE
' OO BOATING DOCKS
© GANGWAYS
0 SANITARY PLbF-OUT STATION
i ® PILE SLPPORTED PIE32
Q� OILET BU i
s- x / x x x lJ
` IRRIGATED PLANT x i
/ 12 ING DRIVEYNAY
© STING SIDEWALK
-'.`•' ' : / \ . ' , Ib 1NG BIKE PATH ,
I5 STING BRIDGE
i
����:• - ,/G /� 16 STWG PROPWTY-CiPE--
2
/ / w
1 // xx x
J / y j
J {`
• x
P
O $/ x
Ib ``�,`` J,9 3. OAS 1Il erwm / / a + P— — -- -- --
9 A i' i Jjjj
1p
SCHEME
x < m
SLIP COUNT � m
SIM NA TOTAL FOOTAGE W F
45' SUPS - 51 2340
•.\ - .c�__ —'T_� /O`\� %7 \ 'P `�� �^ 3, "38'$IPS - 61 2318 = a
35 SLIPS - 9 315 > o
. _ SIDE TIES - 8 320
} COq —' i TorAi 129
I C 96 PARKING SPACES REQUIRED
— 96 PARKING SPACES PROVIDED m
W
x
EXHIBIT z�ax_oT
_„_ 2 7
13
i �u
i F
r� 4
d
x 9
L6 3 . d Fri,
-
x
-.-w
M
x
P
'x
x
x
x
x
-.-w
M
x
P
'x
x
x
x
x
NOTES
d
EXISTFB B14-Fq TO HE Remoym
2O.
PROPOSED HASV DREDGED TO -IOMSL
x 30
PROPOSED CONCRETE DLW-EAD CUO LF1
®
ROCK PROTECTED SLOPE
- Q
AT
RO@VG DOCKS
©
GANGWAYS
Q
$ANTTARY PIIyP-OUT STATION
©
OSED PA.E SLPPORTED V"
91FDOSTLNG DRNL�IAY
® SIDEWA4K
WE PATH
=QE`rARa4G-
ROPE�Zmr:LY - -
WAIL
i i%
� x x
c
i p
i ?
I
op
8
d -----------
4+
&
r
/�,�
dd
S
�;8 a i<•�,�3_
SCHEME J
•S ,p
x
SLIP COLNT
�'
'S✓ E N16M TOTAL FOOTAGE
+e
-E
p
46 SLIPS 52 2250
38' SLIPS 58 2204
35' SLIPS 8 1 280
x
_ x
SIDE TIES 7 ' 280
=AL 125 5014
i'
-
94 PARKING SPACES REQUIRED
-- --
94 PARKING SPACES P20VIDED
\—
vvi
x
NE
EXHIBIT 22 2402.01
. rrrr
1
/ NOTES
• - - " "i - - - - IQ.O EXISTM B AXW-AD TO W QE%4OVW
•'• - %_ 2p- PROPOSED BASW DREDG® TO d0 MSL
PROPOSED CCNCWM w 1 IaFAD C240I n
x ROG: PWFECiiD SLOPE
' 0 FLOATWG DOCKS
• _ ,© GANGWAYS
i
7O SANITARY R-M -OW STATION
. y ®Pl.E SLPPORTEO P932
® STWG ORIVEAAY
% ® WG SIDEWALK
® SAM PATH
. - n © WRI 6 BDGE
A ` _
` ® STWG PROPEZLY lME'
41
s
•'a 5 � � �16
` for o'``` , � a a J � x
ss------------------ >
\• a 9�xso . 4 .SCHEME K O v>
\ SLIP COUNT
10
- Y\ .•� e . "d a�J:/- 6 C a 5� TorALI'OOTA6EVI - o
'45• SLIPS 52 2250
s 39 SLIPS 55 2090
35' SLIPS8 250 i
SIDE TIES 7 280
00 122 4900 Lf. `> x
• d - �,�i�'"'•\ I -� 92 PARKING SPACES REGUIRED i w
92 PARKING SPACES PROVIDED <
_ 2492.01
EXHIBIT 23 .........
NOTES
(D
oasrwsa� eAo To eEr�uovm
0
PROPDXM BASW DREDGED TO -10 MSL .
x (9)
PROPOS® CONCRETE BLLKI-EAD 0008 LP) '
®
ROCK PROTECTED SLOPE
05
FLOATWG DOCKS
- ©
GANGWAYS . -
TO
SAMTARY PL P-CUi STATION '
- ®
PLLE SI.PPORTED PIS32
3
i
-
I
-
x x x '"�'�" x
:
I{32IGAT7® PLANT'Q ISTWG DRIVEWAY
® SIDEWALK .�
• - i ® STING Ma! PALM —
�{ \ ® STWG BRIDGE I
\�6 / \ I� Sl'W6 PROP6tTY-Lm i
- x } O j x - x _© RETAW WC+ WfLLi
/ B M34S AND WOM36 TOILETx
13
2 1
II y \ -/ / s
/ ? \4PP
SCNEME L O W) F
3 s �s x i W r �•
SUP•CQUNTcr
W m
,1.1 •- '�> : ;7 S_ - 9 7scm
_ wi. p *1 a / / • / 45' SLIPS 52 2250 o
I�iaiC �' �, • ! i 3 \ i / - / / / / / 47 SLIPS 39 1638
38' SLIPS 19 722 `
.i4 �. • 15 x—' I x / 35' SLIPS 8 280 i
-- - SIDE TIES 7 280 m
TOTAL 125 '' 5270 ; •-' E$f{
1 / � W 1
PARKING SPACES RECLI[ReD
104 PARKING SPACES PROVIDED `o 0
EXHMT
y•TM `r-
• _ -: -- ••
e.�
__
_ _
-
ry^.
_
X X X
%
NOTES
OnsTm al*eA io eeQexwID
"
2O
PROPOSED BASIN DREDGED TO.10 MSL
30
PROPOSED Si®. SIFT PN.E B t ri_an
®
ROOK PROSEC• ` D SLOPE
E
Q5 FLOATING DOCKS
© GANGWAYS
'
Q SANITARY FLLfF OUT STATION
PLE SLPP_ OPTED PIB2
.
0 PROOPOSED OLEf
OSED
IRRIGATED F'LLJN'T
2 OPOSED QECON5TRUCTED IVEWAY
Q IST6i1G SIDEWALK
1® ING BIKE PATH
IS ISTM ERIDGE
® Sf1NG PROP6ITY-hNE'
i SED RETAWRJG WALL
'
PROPOSED TOILET BUILDING l
/ \\ � --
/ 19 PROPOSED RAIUdG
`mane.+eo.r�
•�
C'6mwIIr wires � i
Ta �-
iNf
i
It A
17
,
/
+ P
X
---.X-
\
16
Toeo- urr /
4 ♦ ♦ /— — — — —
\
II \
P /
—
bly
SCHEME M
SLIP COUNT
/SCE
MAIXR TOTAL. ♦OQiA�
45' SLIPS 52 2250
•
` / /
/ /
/ 42• SLIPS 39• 1638
/
y
/
38' SLIPS 19 722
35' SLIPS 8 280
SIDE TES 7 ' 280
I
\ 0 TOTAL: 125 5270
< S
y� I i 94 PARKING SPACES REQUIRED o
\� B - 108 PARKING SPACES PROVIDED o o r
-
2492.01 "
-
. , EXti1t3lT 25 ..
7
Is
To
-10
ELIVATIGM SHIPlitENCED
""MIR MOM,!
E.0
T 1.0
N.
C
L 0
0
K A N
G
-N 0 R T H
75
SS 0 PACIFIC -COAST HMW AY.
20
Irf
to
S E..0
T 1 0
N.
A
L.0,0
K I.N.6
W E S T
33
-------------
COVER DRIVE
77444
WNT
xn 4
�-T �xr-
ff"WAYMNS "FEAEK=P
TO 0-MEAM SEA LEVEL
'S E
C
T 1.6
N.
L 0
0
K I N
G
N 0 R T H
2
I
0
SUMMARY OF ESTIMATED PROJECT COSTS
Engineering Study and Feasibility Report
City Planning Department Fees
E.I. R.
U.S. Army Corps of Engineers filing fee
Documentation for Corps permit
Dredge Material Tesing for disposal
California Coastal Commission filing fee
Documentation for C.C.C. permit
Consulting Engineers fee during permitting
Total Estimated Permitting Cost
Engineering Fee for Construction Documents
City Plan Check Fee
City Building Permit Fee
•Estimated Construction Cost
Engineering Services During Construction
•
Total Estimated Project Cost
$ 75,500
3,950
30,000
100
12,000
30,000
1,500
11,000
23,000
$ 111,550
$ 150,000
6,600
10,200
4,454,000
45,000
$4,852,850
*Refer to Exhibit 28 Cash a Associates letter of May 29, 1987 for a discussion of
these costs.
EXHIBIT 27
`J
PRELIMINARY CONSTRUCTION COST ESTIMATE
Project: Castaways Marina
Preliminary Design Concept - Scheme M
Client: The Irvine Company
CAA
Job No: 2492.01
Date:
Rev. 5/28/87
Item
Quantity
Unit Price
Total
1.
Mitigation for Tidal Hab. Loss
4,000
CY
$ 12.00
$ 48,000.00*
2.
Demo. Exist Blkhd.
8,016
SF
$ 4.50
$ 36,072.00
3.
Demo. S.D. Headwall
1,000
SF
4.50
4,500.00
4.
Upland Dredging, Dry
25,000
CY
10.00
250,000.00
5.
Upland Dredging, Wet
31,000
CY
12.00
372,000.00*
6.
Water Dredging
20,000
CY
12.00
270,000.00*
7.
New Bulkhead (S.S.P.)
1,000
LF
800.00
800,000.00*
(Incl. Cathodic Protection)
8.
Rock Revetted Slope
5,000
SF
6.00
30,000.00*
9.
Grading
78,000
SF
.10
7,800.00
10.
. 11.
Retaining Wall
Sidewalk
750
4,750
SF
SF
15.00
2.25
11,250.00
10,690.00
12.
Curb
2,250
LF
4.00
91000.00
13.
Paving (3" A.C. on 6" C.A.B.)
37,500
SF
1.35
50,625.00
14.
Bulkhead Railing _
815
LF _
50.00
40,750.00
15.
Landscaping
41,000
SF
3.00
123,000.00
16.
Lighting
6 Poles
8,000.00
48,000.00
17.
Storm Drain System
L.S.
15,000.00
18.
Sanitary Sewer System
L.S.
25,000.00
(Incl. Lift Station)
19.
Water Supply System
L.S.
20,000.00
20.
Fire Hydrants
2
ea.
2,000.00
4,000.00
21.
Electrical Power Supply
L.S.
20,000.00
22.
Piles
162
ea.
2,400.00
389,000.00
23.
Pile Supported Pier
1,200
SF
21.50
25,800.00
24.
Floats
32,500
SF
35.00
1,137,500.00
25.
Gangways
4
ea.
81000.00
32,000.00
26.
Pump -A -Head
1
ea.
10,000.00
10,000.00
27.
Toilet A Shower Building
2,500
SF
80.00
200,000.00
28.
Toilet Building
800
SF
80.00
64,000.00*
Subtotal
$4,053,987.00
Contingency 10%
400,000.00
TOTAL ESTIMATED CONSTRUCTION COST
$4,453,987.00*
EXHIBIT
29
I•
01
0
Schedule Name: 'E IRYI►E CIL, CASTAM MARINA
ProInt Kalloer: LAW ME
As of date: 2-7uir87 1:47= Schedule File: B:0 TAWAl
CITY OF NEWPDRT BERC14 CORPS OF ENGDEERS AND CA C88STAL CO0! PERMITS
WEEKS
0
1 2 3 4 5 6
7 8 9 10 11 12 13 14 15 16 17 18 19 20 21
22 23 24 25 26
27 28 29 30 31 32 33 34 35 36
A/ CITY PLANNING PER
C K
A101 OWES. FOR CITY CIA
C
A201 SUBMIT M CITY CIA
C
A20/ t
. . .
A25/ CITY REVIEW CIA
C
PZ/ � .
00/ DEIt7dMINATION
C
A30/.f .
A35/ MIRON. DOCUIE CIA
C
.Am/
A40/ CITY REVIEW CAA
R
. .
A40/
A451 CITY COIIENIS CiR
. .
A45/ 110001mm
. . .
A50/ ANSWER CITY CiA
. .
A50/ . . .
AM/ FINAL REVIEW CiA
R
A /.
470/ C.U.P. ISSUED
. .
.
470! P(
Bl CORPS PERMIT
B/ K
B10/ CORPS DRW6.S CiA
810/
815/ CORPS ENNIRON.
oC
. . .
B15/
B201 DREDGE KATL. TE CIA
EeO/.
35/ SLOUT TO CORPS CIA
C
. .
B25/
.
B301 CORPS REVIEW CiA
C
. .
B30/ .
B35/ AXIC NOTICE CiA
RC
. .
B351 a .
..
. . . . . .
B40/ AGENCY REVIEW CiA
C
_. B40/
B45/ CORPS REVIEW CL4
C
. .
. .
B451.�
B50/ ANSWER CORPS CIA
AC
B50/ i . . . .
B55/ ADDITIONAL INFO C&4
C
. .
. . .
B55/ .
B60/ RELIC HFA INGS CiA
DC
. . .
. .
B601 ■ . .
865/ COE PERMIT ISSU
PC
. .
. .
865/ N .
C/ CA MAST COW PER
. . .
C/ N
CIO/ AM IN CONCEPT
n
. .
C101 m
.
C15/ SLC LETTER
p
. . .
C15/ ■
. .
C20/ EVID. CIE 9JNL
o
. .
C20/ 1t
.
C251 REV. WILDLIFE A
pp
. .
C25/.■
I
C30/ SU& TO CA CO C
p
. .
. .
.C30/.§
C351 CCC REVIEiW
Cis/ ummmmmmmmmmi-,
C40/ NEARING
n
. .
. .
.
045/ DETERMINATION
p
. .
. . .
CC/ i
C50/ RESPONSE
. .
. .
C5D/ � . .
C55/ ISSIE PERMIT
. .
. .
D Dore +• Task
- Slack time (as' or
C critical ass Started task
Resource delay (—w
R Resource conflict K Nilestone
) Conflict
D (Martial dependency
Scale: Each character equals I day
I
TIE LINE Gantt Chart Resat strip ITIE LINE Gantt Chart Rem Strip 2
EXHIBIT 30
Schedule Name: THE IRVINE CO., CASTAWAYS MARINA
• Protect Manager: LARRY NYE
As of date: 29-May-87 12:57om Schedule File: B:CASTAWA2
WORKING DRAWINGS, BIDDING AND CONSTRUCTION
I •
•
10/ IRVINE CO. NTP
20/ CONSTR. DOCIS.
30/ SUBMIT TO CITY
40/ CITY REVIEW
50/ PC REVISIONS
GO/ ISSUE BLDG PERMIT
65/ BIDDING PHASE
70/ CONSTRUCTION
75/ OCCUPY MARINA
MONTHS
0 1 2 3 4 5 6 7 8
C ■
C&A+ C
C&A+ C 30/ ■ .
CNB+ C 40/ ,
C&A+ C . . 50/. .
CNB+ C GO/ i .
C-P C 65/
C-P C 70/
C
D Done � Task - Slack time (i ), or
C Critical ■■■ Started task Resource delay C on)
R Resource conflict M Milestone > Conflict
o Partial deflendency
Scale: Each character equals 1 week
TIME LINE Gantt Chart Report
9 10 11 12 13 14 15 16 17 18
. . . . . . . . . . . . . . . . . .
. . . . . . . . . . . . . . . . . .
. . . . . . . . . . . . . . . . . .
.75/. ■
Strio 1 -,!ME LINE Gantt Chart Report
Strin 2
EXHIBIT 31
I •
E L E V A T I O N
P L A N
L,
BULKHEAD S RARING
BULKHEAD A RAILING �I
t c, ' ABmo
C}.Y .
s=
GANGWAY 5Q, STO7-�
E L E V A T I O N
m f, A%0aQ 5 • EIMERS
(213)"41 s
;i .
MEN -
..... OMEN
JAN
Ili �
GANGWAY it
O
° I P L A N N
.I
q o 0 1&
OCALE IN FEET
EXHIBIT 32
CASTAWAYS MARINA /
CONCEPT S FEASIBILITY STUDY G
ALTERNATIVE MARINA BUILDINGS 2492.01
PRELIMINARY DESIGN CONCEPT savaximm
REVI
L-A
9
CASTAWAYS MARINA
QUALITATIVE ANALYSIS OF HYDRODYNAMICS
AND SEDIMENTATION
0
r
U
CASTAWAYS MARINA
QUALITATIVE ANALYSIS
OF
HYDRODYNAMICS
AND
SEDIMENTATION
PREPARED FOR
CASH & ASSOCIATES - ENGINEERS
R/ VERTECH
,siftev INC
JULY 1987
0
RI VERTECH
lN[ CONSULTANTS IN WATER RESOURCES ENGINEERING
July 16, 1987
Mr Larry W. Nye, P.E.
Cash & Associates Engineers
2599 East 28th Street
P.O. Box 38
Long Beach, CA 90801
Dear Mr. Nye,
Rivertech Inc. Is pleased to submit our attached report entitled "Castaways
Marina, Qualitative Analysis of Hydrodynamics and Sedimentation".
This report has been prepared with assistance and advice from Dr. Frederic
Raichlen, Professor of Hydraulics at the California Institute of Technology.
We have enjoyed working with you on this project and look forward for the
opportunity to work with you again.
Sincerely,
RIVERTECH INC.
asa�Nou� `
President
1400 QUAIL STM
1 ■
TABLE OF CONTENTS
•
DESCRIPTION
PAGE
CONCLUSIONS AND RECOMMENDATIONS 1
INTRODUCTION 2
TIDE CYCLE 2
DEPTH CONSIDERATION 3
WAVE CONSIDERATION 3
CURRENT AND CIRCULATION CONSIDERATION 4
EROSION AND DEPOSITION CONSIDERATION 5
FLOATING DEBRIS CONSIDERATION 6
Pi
0
r�
AND RECOMMENDATIONS
• Based on a qualitative analysis and a reconnaissance level study of
sedimentation and hydrodymamics of the proposed Castaways Marina, Rivertech
makes the following conclusions and recommendations:
1. Wind and ship generated waves are significant design parameters for the
proposed Castaways 'Marina. Their magnitudes should be computed and
their dynamics should be considered in the design. Although the
designer is cautioned about their presence and magnitude, nevertheless,
they do not pose a major problem.
2. Flood and tidal current velocities along the navigation channel could be
very high. It is recommended that the design of the marina be based on
the occurrence of the simultaneous events of the 100—year storm and the
mean ebb tide.
3. To provide better tidal exchange rates between the marina and the
navigation channel and to improve the flexibility of the 750 feet long
floating dock, it is recommended that it be divided into three seperate
components.
• 4. To prevent excessive influx of sediment and floating debris into the
marina a guiding van should be installed at the north end of the marina
extending from the shoreline.
•
5. Assuming the marina will be used by vessels requiring a draft of 4 feet,
it is recommended that the bottom of the marina be dredged to elevation
— 12.5 feet (MSL). This would allow a clearance of 3.6 feet between the
bottoms of the basin and the vessel during the occurrence of extreme low
tide. Adequate clearance will also improve tidal exchange rates between
the marina and the main estuary.
—1—
IN
INTRODUCTION
Cash & Associates Engineers has recently completed a report entitled "Castaways
Marina, Engineering Study and Feasibility Report". The report was prepared for
The Irvine Company and its draft copy was submitted on June 15, 1987. Cash &
Associates Engineers has asked Rivertech to prepare this report which
qualitatively analyzes the hydrodynamics, water quality and sedimentation
aspects of the recommended scheme.
The Irvine Company with assistance from Cash & Associates Engineers is
evaluating the development of a 4-acre site in Newport Bay to a marina. As
shown in Figure 1 (also Figure 5), the site is located just north of the
Pacific Coast Highway Bridge in Newport Beach.
Results of the qualitative analysis described in this report are based on
information obtained from field observations, previous reports, meetings,
telephone interviews and Rivert-ech's experience with similar estuaries.
TIDE CYCLE
The tide cycle at the mouth of Newport Bay with the Pacific Ocean are diurnal
having an approximate period of 24 hours. These type of tides are produced by
the phase relation of the sun, the moon and the earth. The relative ranges of
the two daily tides continuously vary from small to large over a 28-day period.
The characteristics of tide cycle in Newport Bay at the Pacific Coast Highway
. (Project site) is approximately the same as that at its mouth. The following
represents the estimated parameters of the tide cycle in the project site.
•
Mean lower low water = 0.00 feet
Mean high water lunitidal interval = 5.13 hours
Mean low water lunitidal interval = 11.15 hours
Mean range of tide = 3.69 feet
Mean tide level = 1/2 (mean high water + mean low water) = 2.79 feet
Mean sea level = the mean of the hourly heights = 2.76 feet
Mean high water diurnal inequality = 0.75 feet
Mean great diurnal range = 5.40 feet
Diurnal tide level = 2.70 feet
Mean high water = 4.65 feet
Mean low water = 0.93 feet
Mean higher high water = 5.40 feet.
Highest observed = 7.86 feet on January 28, 1983
Lowest observed = 2.14 feet on December 29, 1955
The actual elevation reached by a particular tide is further influenced by wind
set-up on the ocean and in Newport Bay. In addition, magnitude of stormwater
runoff from the area tributary to Newport Bay affects its elevation
considerably.
-2-
a
Santa Ana —
Delhi Channel
DOVER DR
PROJECT SITE
R/VERMCH
..�g8M�j v
Sand Canyon _.
Wash
Newport Bay
• PACIFIC.COAST HWY
jOQojfi0-\
San Diego
Creek
NORTH
MILES
0 11 2
Peters Canyon Wash
Newport Bay
Watershed Boundary
LOCATION MAP
FIGURE
1
DEPTH CONSIDERATION
• The recommended scheme which is depicted in Figure 2 (Scheme M shown as Exhibit
25 in Cash & Associates' report) describes that the basin for the Castaways
Marina will be dredged to a depth of - 10.7 feet mean sea level (MSL). Assuming
a draft- of 4 feet for the vessels, this arrangement at extreme low tide will
allow a clearance of only 1.8 feet. This is shown in Figure 3. The
corresponding clearance for the floating docks is estimated to be 2.8 feet.
Rivertech believes that• these clearances may not be adequate. It is
recommended that the marina basins be dredged to an elevation of at least 12.5
feet (MSL). This would permit adequate clearance as well as allowance for any
sedimentation which may occur.
The extreme high tide has been measured to be 5.1 feet above mean sea level.
Thus, one could expect a tidal excursion of the order of between 10 and 11
feet. This is not as much of a concern as the extreme low tide but is
mentioned here as just the fact that there should be awareness of this tidal
range in designating the various components of the marina.
WAVE CONSIDERATIONS
A brief review of literature in evaluating the problem of boat generated water
wave revealed that there are some related concerns that the designer of the
Castaways Marina should consider. Area "A" which is between the 750 feet
floating dock (slips 61 through 125) and the wetlands, shown in Figure 2, is
more critical since excessive wave generation could promote erosion, disturb
the marine life and reduce the habitat values along the shoreline.
• Our reconnaissance level analysis revealed that a cabin cruiser of about 3 tons
displacement would generate waves with maximum wave heights between 6 inches
and 1 foot at a distance of 100 feet away from the sailing line of the vessel
when it is traveling at speeds of 5 to 6 knots. For the same speed, a 40-foot
U.S. Coast Guard cutter generates maximum waves that are about 1 foot high
about 100 feet away from the vessel. For both of the above cases, the wave
period is about 2 seconds.
•
Slips 61 through 98 would be subject to ship generated waves, since there may
be more high speed activity along the navigation channel. For example, at a
ship speed between 10 and 15 knots a 4-foot U.S. Coast Guard cutter generates
wave heights of 2 feet at a distance of 100 feet from the sailing line.
Similarly, a 3-ton cabin cruiser generates waves of the order of 0.7 feet at
the same distance and speed.
Another type of wave which may be present at the proposed marina are those
generated by wind. Spring and fall Santa Ana winds blow down the Newport Bay
estuary and can generate waves upto 2 feet high at high tide when the fetch is
long. Lesser waves would be expected at lower tides. Still another type of
waves as that generated by on -shore breezes. Their range is estimated to be up
to 6 inches.
Although we do not believe that any one of the type of waves described above is
a problem for the proposed Castaways Marina, nevertheless, one should consider
them in the design analysis.
-3-
0
•
O
0
x
ST6
x
x
e
to- w
x � x
x
x
x
NOTES
IQ
EXISTING a L *,-AD TO Be REMOVED
2Q
PROPOSED BASIN DREDGED TO -10 MSL
3Q
PROPOSED STE-'. S-EcET PILE B-UaZAD
x ®
aS ROOK PROTEC21 SLOPE
QSt
jmep
PROPOSE FLOATMG DOCKS
©
`
PROPOSED GANGWAYS
7Q
FROPOSE9 SANITARY PLMP- Lrr STATION
®
PROPOSED PLLE `3PPORTE7 Pa2
U�iPROPOSED IRRIGATED FLANi1NG x
IZ yPROPOSED REC.M6TRUCTED DRIVEWAY
13 9 smi G SIDEWALK
I® �tlSTIN—
G BII� PATH
I5 E aSRNG BRIDGE
I6 EXISTING PROPEa TX-6R•E—
1 L PROPCSEO RETAINING WALL
/ / �1x--- — is PROPOS= TOIIF EUILDING
msrove 19 PROPOSED RAIUNC•
P ®NLGi YLiI_ �
/ Z UIDE VAN
PROPOSED BY RIVERTECH -�
1
x / , t>L / wnurxa
x Cows
IB
R40 t d
/
�$d
a / /
tp
9 de+ \/� 19 �rSSj �O S / / / / / / SCHEME A/ O
a / U
^' 0 a 7 r / / / SLIP COUNT
A Jj 6 �c / / m
r / / C sr� N.r.+� :orn�r-oornre
s hI ,p
45• SLIPS 52 2250
47 SLIPS 39 1638
38' SLIPS 19 722
35• SLIPS 8 280
/ SIDE TIES 7 280
/ roves 125 5270
94 PARKING SPACES REQUIRED
108 PARKING SPACES PROVIDED
FIGURE 2 2;o2.o,
MSL=O
12.76' - -
VESSEL
-------------------
EXTREME LOW TIDE
MLLW
3.0'
SLIP I
4.6' CLEARANCE
3.6' CLEARANCE
RECOMMENDED BY RIVERTECH
FEASIBILITY REPORT ESTIMATED BOTTOM
RIVERTECH
INC
CLEARANCE LIMITS
FIGURE
3
i
NlFq
CURRENT AND CIRCULATION CONSIDERATION
• The rise and fall of the ocean, combined with the presence of pools and
constrictions that characterize upper and lower Newport Bay produce tidal
currents at various locations in Newport Bay. These currents are strongest at
constrictions such as the section of the bay at Pacific Coast Highway and
weakest at locations where the estuary widens.
Velocity measurements made on December 20, 1983 by the Orange County
Environmental Management Agency (OCEMA) at the Pacific Coast Highway Bridge are
shown in Figure 4. On this date, The National Oceanic and Atmospheric
Administration's (NOAA) station in Newport Beach shows the following tidal
measurements.
0
Low water = 2.50 feet at 02.0 hours
Higher high water = 7.15 feet at 08.5 hours
Lower low water = 0.96 feet at 15.9 hours
High water = 3.76 feet at 22.3 hours
A comparison of these measurements with the mean tide cycle values, described
previously, indicates that on this date very high and low tides were present in
Newport Beach. In fact the higher high water elevation is only 0.71 foot less
than the highest recorded value which occurred in January of the same year.
Therefore, the measured values shown in Figure 4 are close to the upper limit
of velocities which may be present at the Pacific Coast Highway Bridge in the
Bay. This figure shows that tidal velocities exceed 3 feet per second in the
navigation channel and reduce to zero close to the bridge abutment.
Velocities may increase significantly at the navigation channel in the vicinity
of the Pacific Coast Highway Bridge during major storm events. During the
storm of March 1, 1983, the harbor master has estimated the current speed to be
in excess of 10 knots (17 feet/sec.). His estimate was based upon engine
revolutions required to maintain a steady boat position in the channel.
Rivertech believes that this estimate is probably higher than actual. It is
possible that wind resistance was also a contributing factor.
The designer of the proposed Castaways Marina is cautioned to note the
proximity of the high velocity field of the navigation channel to the marina.
The floating dock which houses slips 61 through 125 would be most susceptible
to damage by high velocity currents.
A review of the velocity field at the bridge shows that velocities quickly
reduce to negligible values when the location changes from the channel to the
abutment. In addition, field observation indicated evidence of sediment
deposition adjacent to the western bridge abutment. Construction of the
proposed marina probably would not alter these currents appreciably.
Therefore, the desired level of circulation in areas "B" and "C" of the marina
shown in Figure 2 may not be achieved at all times. The opening under the
gangway which is located adjacent to slips number 1 and 39 allows surface water
circulation and should enhance the water quality.
Rivertech recommends that the channel adjacent to the pile
(labeled as 8 in Figure 2) be maintained as large and
possible. This is because the marina in the vicinity of the pier
• constriction which would probably cause excessive velocities.
—4—
supported pier
unobstructed as
has a major
0
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SUBSEA NUMBERS
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8
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8.0
6.0
4.0
2-0
0
MAXIMUM TIDAL VELOCITY DISTRIBUTION 1
_2
_4
_0
AfTl
9+00 10+00 11+00 12+00 13+00 14+00 15+00 16+00
DISTANCE IN FEET
3
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RI VGRj GCH
./ t 2 INC
MAXIMUM TIDAL VELOCITY DISTRIBUTION
AT PACIFIC COAST HIGHWAY BRIDGE OVER NEWPORT BAY (LOOKING NORTH)
FIGURE
4
Assuming economy permits, we recommend that the 750 feet long floating dock be
divided into three sections. This is to improve the tidal currents between the
navigation channel and the shoreward located mud flats. We recommend that the
region of berths 111-112 and 86-87 be replaced by a walkway connecting the two
sections. In addition, in the region of berths 122-123 and 75-76 a similar
break in the dock be provided. With these openings the following advantages
can be achieved:
1. Tidal exchange rates between the navigation channel and Area "A" will be
increased.
2. The tidal and flood velocities at the pier, labeled 8 in Figure 2, will
be reduced.
3. Improved flexibility for the 750-foot long floating dock.
The above recommendation is of particular significance since the 750-foot long
dock would be subject to high flood velocities as well as wind and boat
generated waves.
EROSION AND DEPOSITION CONSIDERATIONS
During the past few years, an effective and rigorus sediment control management
r has been practiced in the Upper Newport Bay. If current practice of sediment
control management in Upper Newport Bay continues, very little maintenance and
dredging will be required in the Lower Newport Bay and in the vicinity of the
proposed Castaways Marina.
San Diego Creek Channel (see Figure 1) is the major source of sediment yield to
Newport Bay. Its sediment load can be classified as
C o Wash load
0
o Suspended load
o Bedload
Nearly all of the bedload and suspended load settle in the sediment traps
constructed in the lower reaches of San Diego Creek Channel or Upper Newport
Bay. During the last few years, large quantities of sediment deposits were
removed from the sediment traps and from the Upper Newport Bay. If the
existing trapping efficiency in the sediment traps and in Upper Newport Bay is
maintained, it would be very unlikely for bedload and suspended load to reach
Lower Newport Bay or the area in the vicinity of the Pacific Coast Highway.
Washload, however, behaves differently. In freshwater, wash load particles
repel each other because their ions have like charges. Once freshwater is
mixed with saltwater, ion exchanges occur and particles become cohesive. In
this manner, aggregates are formed and estuarine deposits are produced. When
this accumulation grows thicker, the weight of the deposit crushes the lower
aggregates in the bed, making the bed more dense and stronger.
-5-
r
The interface between freshwater and ocean water can happen anywhere in Newport
Bay upstream of the Pacific Coast Highway, depending on the volume of
stormwater and phase of tide cycle. Therefore, the phenomenon of cohesion and
aggradation can occur anywhere in the Newport Bay upstream of the Pacific Coast
Highway.
The new deposits are often disturbed and resuspended by wave action that occurs
during windy periods and passage of vessels. Subsequently, tide currents
redistribute this suspended material into regions where wave action and
turbulence is less intense.
It- is the preceding process that would cause deposition of material in the
proposed Castaways Marina. Field observation at the proposed marina site
showed very little evidence of organic or fine material deposits. The high
currents which are present in and in the vicinity of the navigation channel may
be the reason behind the absence of this type of deposits.
At some isolated locations, such as the area adjacent to the bridge abutment
evidence of deposition was noted. This is probably because the combination of
the existing bulkhead, bridge pier and bridge abutment has caused a stagnation
zone and hence has promoted the process of deposition.
The area to the west of the proposed 750 feet long floating dock will probably
have the tendency to erode rather than to deposit. As explained previously,
r this area is subject to strong wave action and is a relatively higher velocity
zone. The division of the 750 feet long floating dock into three components,
would provide better tidal communication between the navigation channel and the
marina area west of the dock. In addition, we recommend that some type of a
guide van be installed at upstream of this area. Its approximate location is
shown in Figure 2. Installation of such a guide van will have the following
advantages:
o Reduces wave action in Area "A"
o Enhances the habitat values of the mud flat along the shore .
o Reduces the high velocity currents which may exist at the pier between
Area "A' and Area "B" during major storms and during ebb of spring tides
(high range tides).
o Reduces the chance of sediment and floating debris entering the marina
area.
FLOATING DEBRIS CONSIDERATION
Although the problem of floating debris is not a major concern in Newport Bay,
nevertheless, it would probably become a problem in the future. The watershed
which is tributary to Newport Bay is currently experiencing the dynamics of the
development. With the continued rate of development in the watershed, floating
debris will probably become a major problem in Newport Bay in the future.
As far as floating debris is concerned, the marina areas designated by "A" and
"B" in Figure 2 should have minimal problems. This is because currents are
strong at their entrance and in all probability would transport the floating
debris away from the proposed marina.
—6—
0
The City of Newport- Beach has
Bay to mi.ttigate this problem
5. The direction of current
extended into the Bay only
floating debris is carried to
0
0
installed a debris trapping boom in Upper
The location of this boom is shown in
at this location is such that the boom has
for about — 1/3 of the channel width. Most
the North Star Beach and is trapped by the
—7—
Newport
Figure
to be
of the
boom.
m
L i
FLOATING DEBRIS
NORTH STAR
BEACH
DEBRIS TRAP
BOOM
r.
BACK
BAY
DR
DOVER
DR
W ESTCLIFF
DR
r"
Upper '
Newport
Bay
EAST
BLUFF DR
BACK
E-BAY
DR
NEWPORT CENTER
BALBOA H
ISLAND ll
PROPOSED Newport
CASTAWAYS Bay
MARINA
NORTH pacific Ocean
1 MILE
RI VERTECM SURFACE DEBRIS TRAP FIGURE
y ,NC AT UPPER NEWPORT BAY 5
CASTAWAYS MARINA
LOCATION AND STATUS OF SUBMARINE
CABLE IN NEWPORT BAY
0
M E M 0 R A M D U M
TO: Randy Mason (C&A)
FROM: Jim Pence (C&A)
DATE: November 1992
SUBJECT: Location and Status of Submarine Cable
in Newport Bay
. . . . . . . . . . . . . . . . . . . . . . . . . . . . . .
I have met with Mal Brown (Engineering Department of Pacific Bell
714-25974478) and he gave me a schematic drawing (see attached)
of the telephone manholes on the proposed site of the new Castaways
Marina. Their records show the manholes are still in place and the
cable that goes across Newport Bay was disconnected and abandoned
in place.
Their records now indicate that this cable is not in use.
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ISSUE 10-17—�
SEG. NO. 1410 7636
CZ
AM SEE=CEFT " 9O
THE PAC. TEL AND TEL CO.
HIFTIOO OF:
5306 (rWTJ DIVISION _AN T N 4,JF.
EXCHANGE NCYIPORT BEACH
(LE IB)
C.O. DISTFUCT COSTA MESA
L( G CA
SCALE: G
SHEET NO. r 7
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