HomeMy WebLinkAboutIS AND NEGATIVE DECLARATION BACK BAY SCIENCE CENTER*NEW FILE*
IS AND NEG DECLARATION
BACK BAY SCIENCE CENTER
NOTICE OF INTENT TO ADOPT A
NEGATIVE DECLARATION
To: From:
ElOffice of Planning and Research Department of Fish and Game
1400 Tenth Street, Room 121 South Coast Region
Sacramento, CA 95814 4949 Viewridge Ave.
San Diego, CA 92123
T1County Clerk, County of Orange (Orange County)
Public Services Division
P.O. Box 238 Date received for filing at OPR/County Clerk:
Santa Ana, CA 92702
Public review perlod: 7 a 3 through 9�1- as , 2003
Name of Project: Back Bay Science Center
Project Location: Shellmaker Island, Newport Beach (see attached Initial Study)
Project Description: Please see attached Initial Study
Public Meetings: No public meetings have been scheduled at this time.
Hazardous Waste List: The site is not on a list of hazardous waste sites as defined in
Government Code Section 65962.5(t)
Document Availability: Copies of the Negative Declaration and supporting materials are
available for public review at the following locations:
Newport Beach City Hall Newport Beach Public Library
Public Works Department 1000 Avocado Ave
3300 Newport Blvd. Newport Beach, CA
Newport Beach, CA
A copy of the Initial Study containing the analysis supporting the adoption of a Negative Declaration Is
attached. Additional plans, studies and/or exhibits relating to the proposed project may be available for
public review.
If you wish to appeal the appropriateness or adequacy of this document, your comments should be
submitted in writing prior to the close of the public review period. Your comments should specifically
identify what environmental impacts you believe would result from the project, why they are significant,
and what changes or mitigation measures you believe should be adopted to eliminate or reduce these
impacts.
Written comments should be submitted to:
Department of Fish and Game
Attn: Theresa Stewart, Supervisor
Land Management and Monitoring Program
South Coast Region
4949 Viewridge Avenue
San Diego, CA 92123
868-467-4209
Date
C.F. Raysbr c
Regional Manager
r�.
Lead Agency: Department of Fish and Game
South Coast Region
Land Management and Monitoring Program
4949 Viewridge Avenue
San Diego, CA 92123
CIVIC SOLUTIONS, INC.
... communit development consulting in the public interest
INITIAL STUDY AND
MITIGATED NEGATIVE DECLARATION
BACK BAY SCIENCE CENTER
Lead Agency: Department of Fish and Game
South Coast Region
Land Management and Monitoring Program
4949 Viewridge Avenue
San Diego, CA 92123
Consultant
Assistance: Civic Solutions, Inc.
31726 Rancho Viejo Road, Suite 223
San Juan, Capistrano, CA 92765
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TABLE OF CONTENTS
A. PROJECT DESCRIPTION Page 1
B. ENVIRONMENTAL FACTORS POTENTIALLY Page 13
AFFECTED AND DETERMINATION
C. EVALUATION OF ENVIRONMENTAL Page 15
IMPACTS
D. REFERENCES Page 75
E. LIST OF PREPARERS Page 77
APPENDICES
1. BIOLOGICAL STUDY Page 81
2. SHELLMAKER ISLAND SPECIES LIST Page 85
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EXHIBITS
A-1.1
Vicinity Map
Page 2
A-2.1
Site Plan
Page 5
A-2.2
Elevation
Page 6
A-3.1
Looking West From Shellmaker Drive Entrance Road
Page 8
A-3.2
Looking Northwest From Parking Area
Page 8
A-3.3
Looking Northwest Across Upper Newport Bay Channel
Page 9
A-3.4
Looking South Along Western Edge of Site
Page 9
A-3.5
Amphitheater Area
Page 10
A-3.6
UCI Rowing Facility on Southern Portion of Shellmaker Island
Page 10
C-I.1
View Looking South From Eastbluff Neighorhood
Page 28
C-1.2
View Looking Southwest From Park Newport Apartments
Page 28
C-1.3
View Looking Southwest From Harbor Cove Neighborhood
Page 29
C-1.4
View Looking Southwest From Back Bay Drive
Page 29
C-1.5
View Looking West From Back Bay Drive
Page 30
C-1.6
View Looking West From Hyatt Newporter
Page 30
C-1.7
View Looking North From Bayview Park Site
Page 31
C-1.8
View Looking North From West Side of Newport Dunes Lagoon
Page 31
C-1.9
View Looking North from Coast Highway Across Newport Dunes
Page 32
C-1.10
View Looking East From Castaways Bluff Top Trail
Page 32
C-1.11
View Looking East From North Star Cul-de-Sac
Page 33
C-IV-1
Vegetation Plan
Page 42
C-IV-2
Location of Belding's Savannah Sparrow Sighting
Page 53
TABLES
Table 111-1
Ambient Air Quality Standards
Page 37
Table IV-1
Impact and Mitigation Summary
Page 54
Table XV-1
Parking Demand- Shellmaker Island
Page 72
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ENVIRONMENTAL CHECKLIST
A. PROJECT DESCRIPTION
1. PROJECT TITLE:
Back Bay Science Center
2. LEAD AGENCY NAME AND ADDRESS:
California Department of Fish and Game
South Coast Region
4949 Viewridge Avenue
San Diego, CA 92123
3. CONTACT PERSON AND PHONE NUMBER:
Theresa Stewart, Supervisor
Land Management and Monitoring Program
858-467-4209
4. PROJECT LOCATION:
Shellmaker Island is located at Upper Newport Bay Ecological Reserve, in Upper
Newport Bay, Orange County, California . The majority of the Upper Bay is an estuarine
at Upper Newport Bay Ecological Reserve, salt marsh system with considerable
freshwater input from its 145-square-mile watershed. The Upper Bay extends in a north -
to -northeasterly direction from the Pacific Coast Highway Bridge for a distance of about
3.5 miles and is bounded by the bluffs of the Newport Mesa on the west and the San
Joaquin Terrace on the east. The Upper Bay veers east at the remnant salt pond dike
and extends to the Jamboree Road bridge where the San Diego Creek flows into Upper
Newport Bay. At its southern end, Upper Newport Bay connects with Newport Harbor
(Lower Newport Bay) at the Pacific Coast Highway Bridge. Lower Newport Bay extends
1.5 miles in an east -west orientation. Its ocean entrance jetty is located at the eastern
(downcoast) end of the bay.
Shellmaker Island is located in the southern one-third of Upper Newport Bay immediately
north of the Dunes Marina Boat Launch facilities at the southern boundary of the Upper
Newport Bay Ecological Reserve. It has been under the stewardship of the California
Department of Fish and Game (CDF&G) since it was acquired from the County of Orange
and the Irvine Company in 1974.
The Back Bay Science Center project area is located on Lower Shellmaker Island. The
southern boundary is the Dunes Marina Launch Ramp Channel, the northern boundary is
the tidal channel cut separating Lower and Upper Shellmaker Island, the eastern boundary
is Back Bay Drive, and the western boundary is the —5 fit depth contour of the main
channel of Upper Newport Bay. (See Exhibit A-1.1 Vicinity Map)
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EXHIBIT A-1,1
VICINITY MAP
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5.
6.
PROJECT SPONSOR:
The project is jointly sponsored by the following agencies:
California Department of Fish & Game
South Coast Region
4949 Viewridge Avenue
San Diego, CA 92123
County of Orange
Health Care Agency
515 N. Sycamore
Santa Ana, CA 92701
City of Newport Beach
Harbor Resources Division
829 Harbor Island Drive
Newport Beach, CA 92660
An Interagency Agreement was executed on February 1, 2003 between the Department
of Fish and Game and the City of Newport Beach for planning and design services for a
Back bay Science Center. Under the agreement the City provides project management,
architectural design, environmental documentation and permitting on behalf of
Department of Fish & Game as lead agency.
GENERAL PLAN DESIGNATION:
Recreational & Environmental Open Space
ZONING:
Recreational & Environmental Open Space
PROJECT DESCRIPTION:
The California Department of Fish and Game, the County of Orange, and the City of
Newport Beach are jointly planning to construct a Back Bay Science Center and Water
Quality Testing Laboratory on Shellmaker Island. The new facility is designed to be
multifunctional, and would provide for the following:
• Facilities necessary to operate an educational and interpretive programs for
students in grades 7-12;
• An estuarine research center for students and teachers of local high schools,
colleges and universities;
• A state-of-the-art water quality testing facility operated by the County of Orange;
• Permanent office space for the California Department of Fish and Game Upper
Newport Bay staff.
The projects consists of removing or demolishing existing structures with a total of 8,594
square feet, including 4 buildings, 2 trailers and 2 storage containers. These will be
replaced by a permanent enclosed structure with 4 wings totaling 13,000 square feet.
The structures will be set back a minimum of 50' from the wetlands and buffered with
sand dunes. The existing teaching lab trailer will be temporarily relocated in order to
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allow space for the new facility. The structures will be designed as "state of the art"
sustainable, energy efficient systems. The low profile building will have a roof height of
15 to 16 feet with a small entry portion 28 feet in height.
Proposed site Improvements include the following:
• The existing outdoor educational areas will be expanded to include hands-on
Interpretive elements, testing areas, tanks, aquarium and tidepool exhibits.
• The existing trail system will be enhanced and signed with 15- to 20-foot sand
dune buffers between the trail and the wetlands. There will be several spur trails
leading to small observation/teaching areas;
• Construction of a wetlands rehabilitation demonstration project of approximately
10,000 square feet;
• Formalizing the existing parking area for 66 cars and one bus with pervious
paving;
• On -site storm and gray water runoff system from the building and parking area to
a fresh water pond with filtering plants;
• Refurbishing the existing native planting area and greenhouse area, the
amphitheater & dock bulkhead;
• New underground utilities, fire protection and security system;
• Relocation of the entry gate and widening of the access road to 20 feet.
The proposed Site Plan is shown in Exhibit A-2.1 and the proposed Elevation as Exhibit
A-2.2.
It is anticipated that project construction will occur during the fall and winter of 2004.06.
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EXHIBIT A-2.1
SITE PLAN
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EXHIBIT A-2.2
ELEVATION
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9. SURROUNDING LAND USES AND SETTING:
Historically, Shellmaker Island was used as a dredge material disposal site and dredge
operations staging area for about 50 years through the late 1980s. Consequently, about
24 acres of salt marsh and mudflat habitat along the main channel (3,000 feet long,
averaging 350 feet wide) were eliminated and transformed into higher elevation open
sandy areas. Parts of these supra -tidal areas have been colonized by dune and upland
vegetation. Other areas remain barren, or serve as facility areas for California
Department of Fish and Game, the County of Orange, and the University of California at
Irvine Rowing Facilities.
Currently, Shellmaker Island can be artificially divided into three regions. The eastern
2/3 of the island along Back Bay Drive consists of high quality salt marsh, mudflats, and
tidal channels. This section of island remains relatively undisturbed and supports a wide
range of wildlife, including endangered plants and breeding populations of endangered
birds.
The western one-third of the island is the site of previous dredging and disturbances.
Within this region, the southern one-fourth of Shellmaker Island (commonly referred to
as Lower Shellmaker Island) is joined to the mainland by Shellmaker Road, which
provides access to the University of California Rowing Facility, the California Department
of Fish and Game headquarters, and educational facilities. Temporary buildings are
situated atop dredge materials that are elevated as high as +17 feet Mean Lower Low
Water (MLLW). Portions of the extreme southern end of Lower Shellmaker Island have
been restored to salt marsh and mudflats through various small mitigation and
restoration efforts by the Department of Fish and Game and the County of Orange in the
mid 1980s and early 1990s (Coastal Resources Management 1995).
North Shellmaker (Upper Shellmaker) Island is located immediately north of a man-
made tidal channel that was dredged as part of a CDF&G restoration project in the mid
1980s. There is no direct access to Upper Shellmaker Island from Lower Shellmaker. A
large section of the disturbed section of North Shellmaker is open sandy habitat, at
supra -tidal elevations, while the fringes of North Shellmaker consist of salt marsh and
mudflats. A mitigation plan was developed in the early 1990s to restore approximately 3
acres of Upper Shellmaker to mudflat and salt marsh habitat as mitigation for the
proposed Castaways Marina project (Coastal Resources Management 1992) but was
never implemented since the marina project was also never built.
Photos of the site and surrounding properties are shown in Exhibit A-3.1 through A-3.6.
The University of California, Irvine rowing facility is located adjacent to the proposed
Back Bay Science Center but is not part of the current project. Reconstruction of that
facility is anticipated at an undetermined future time, and CEQA documentation will be
prepared separately prior to approval and construction.
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EXHIBIT A-3.1
LOOKING WEST FROM SHELLMAKER DRIVE ENTRANCE ROAD
EXHIBIT A-3.2
LOOKING (NORTHWEST FROM PARKING AREA
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EXHIBIT A-3.3
LOOKING NORTHWEST ACROSS UPPER NEWPORT BAY CHANNEL
EXHIBIT A-3.4
LOOKING SOUTH ALONG WESTERN EDGE OF SITE
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EXHIBIT A-3.5
AMPHITHEATER AREA
e
EXHIBIT A-3.6
UCI ROWING FACILITY ON SOUTHERN PORTION OF SHELLMAKER ISLAND
(Not a part of this project)
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10. OTHER PUBLIC AGENCIES WHOSE APPROVAL IS REQUIRED (e.g., permits,
financing approval, or participation agreement):
The actions and approvals required to implement the project, which are part of this
analysis, include the following:
• Approval of plans & specifications by the Department of Fish and Game and the US
Fish and Wildlife Service.
• Approval of a Coastal Development Permit by the California Coastal Commission
• Approval of building permits, certificates of use and occupancy, and funding
participation by the City of Newport Beach
• Allocation of grant funds by US Fish and Wildlife Service under the Wildlife
Conservation and Restoration Program
Other agencies having review or permit authority over the project will be identified during
the environmental review process.
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B. ENVIRONMENTAL FACTORS POTENTIALLY AFFECTED
The environmental factors checked below would be potentially affected by this project, involving
at least one impact that is a "Potentially Significant Impact," as indicated by the checklist on the
fnllowin a es
Aesthetics
I Aitricultural Resources
Air Quality
Bioloilical Resources
Cultural Resources
Geology / Soils
Hazards & Hazardous Materials
H drolo / Water Quality
Land Use / Planning
Mineral Resources
Noise
Population / Housing
Public Services
Recreation
Transportation / Traffic
Utilities / Service S stems
MandatorV Findings of significance
DETERMINATION: (To be completed by the Lead Agency)
On the basis of this initial evaluation:
❑ I find that the proposed project COULD NOT have a significant effect on the
environment, and a NEGATIVE DECLARATION will be prepared.
IZNJ I find that although the proposed project could have a significant effect on the
environment, there will not be a significant effect in this case because revisions in the project
have been made by or agreed to by the project proponent. A MITIGATED NEGATIVE
DECLARATION will be prepared.
❑ I find that the proposed project MAY have a significant effect on the environment, and an
ENVIRONMENTAL IMPACT REPORT is required.
❑ I find that the proposed project MAY have a "potentially significant impact" or "potentially
significant unless mitigated" impact on the environment, but at least one effect 1) has been
adequately analyzed in an earlier document pursuant to applicable legal standards, and 2) has
been addressed by mitigation measures based on the earlier analysis as described on attached
sheets. An ENVIRONMENTAL IMPACT REPORT is required, 'but it must analyze only the
effects that remain to be addressed.
❑ I find that although the proposed project could have a significant effect on the
environment, because all potentially significant effects (a) have been analyzed adequately in an
earlier EIR or NEGATIVE DECLARATION pursuant to applicable standards, and (b) have been
avoided or mitigated pursuant to that earlier EIR or NEGATIVE DECLARATION, including
revisions or mitigation measures that are imposed upon the proposed project, nothing further is
required.
o i v3
Signature Date
C. F. Raysbrook, Regional Manager
South Coast Region
Department of Fish and Game
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C. EVALUATION OF ENVIRONMENTAL IMPACTS
A brief explanation is required for all answers except "No Impact" answers that are adequately
supported by the information sources a lead agency cites in the parentheses following each
question. A "No Impact" answer is adequately supported if the referenced information sources
show that the impact simply does not apply to projects like the one involved (e.g., the project
falls outside a fault rupture zone). A "No Impact" answer should be explained where it is based
on project -specific factors, as well as general standards (e.g., the project would not expose
sensitive receptors to pollutants, based on a project -specific screening analysis).
All answers must take account of the whole action involved, including off -site as well as on -site,
cumulative as well as project -level, indirect as well as direct, and construction as well as
operational impacts.
Once the lead agency has determined that a particular physical impact may occur, then the
checklist answers must indicate whether the impact is potentially significant, less than significant
with mitigation, or less than significant. "Potentially Significant Impact" is appropriate if there is
substantial evidence that an effect may be significant. If there are one or more "Potentially
Significant Impact" entries when the determination is made, an EIR is required.
"Negative Declaration: Less Than Significant With Mitigation Incorporated" applies where the
incorporation of mitigation measures has reduced an effect from "Potentially Significant Impact"
to a "Less Than Significant Impact". The lead agency must describe the mitigation measures,
and briefly explain how they reduce the effect to a less than significant level (mitigation
measures from Section XVII, "Earlier Analyses", may be cross-referenced).
Earlier analyses may be used where, pursuant to the tiering, program EIR, or other CEQA
process, an effect has been adequately analyzed in an earlier EIR or negative declaration.
Section 15063(c)(3)(D). Earlier analyses are discussed in Section XVII at the end of the
checklist. In this case, a brief discussion should identify the following:
a) Earlier Analysis Used. Identify and state where they are available for review.
b) Impacts Adequately Addressed. Identify which effects from the above checklist were
within the scope of and adequately analyzed in an earlier document pursuant to applicable legal
standards, and state whether such effects were addressed by mitigation measures based on the
earlier analysis.
c) Mitigation Measures. For effects that are "Less than Significant with Mitigation
Measures Incorporated", describe the mitigation measures which were incorporated or refined
from the earlier document and the extent to which they address site -specific conditions for the
project.
Lead agencies are encouraged to incorporate into the checklist references to information
sources for potential impacts (e.g., general plans, zoning ordinances). Reference to a
previously prepared or outside document should, where appropriate, include a reference to the
page or pages where the statement is substantiated. A source list should be attached, and
other sources used or individuals contacted should be cited in the discussion.
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Supporting Information Sources: A source list should be attached, and other sources used or
individuals contacted should be cited in the discussion.
This is only a suggested form, and lead agencies are free to use different formats; however,
lead agencies should normally address the questions from this checklist that are relevant to a
project's environmental effects in whatever format is selected.
The explanation of each issue should Identify:
a) The significance criteria or threshold, if any used to evaluate each question; and
b) The mitigation measure identified, if any, to reduce the impact to less than significant.
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Less Than
Potentially
Significant
Less Than
No
Issues
Significant
With
Significant
Impact
Impact
Mitigation
Impact
Incorporated
I. AESTHETICS. Would'the proposal:
a) Have a substantial adverse effect on
X
a scenic vista?
b) Substantially damage scenic
resources, including, but not limited to, trees,
X
rock outcroppings, and historic buildings
within a state scenic highway?
c) Substantially degrade the existing
visual character or quality of the site and its
X
surroundings?
d) Create a new source of substantial
light or glare, which would adversely affect
X
day or nighttime views in the area?
II. AGRICULTURE RESOURCES. In determining whether impacts to agricultural
resources are significant environmental effects, lead agencies may refer to the
California Agricultural .Land Evaluation and Site Assessment Model (1997)
prepared by the California Dept. of Conservation as an optional model to use in
assessing impacts on agriculture and farmland. Would the project:
a) Convert Prime Farmland, Unique
Farmland, or Farmland of Statewide
Importance (Farmland), as shown on the
maps prepared pursuant to the Farmland
X
Mapping and Monitoring Program of the
California Resources Agency, to non-
agricultural use?
b) Conflict with existing zoning for
agricultural use, or a Williamson Act
X
contract?
c) Involve other changes in the existing
environment which, due to their location or
nature, could result in conversion of
X
Farmland, to non-agricultural use?
Ill. AIR QUALITY. Where available, the §ionificance criteria-establi§hed by the
applicable air quality management orair pollution contro4 district may, be relied
upon to make the4ollowing determinations. Would the.pro'ect:
a) Conflict with or obstruct
implementation of the applicable air quality
X
Ian?
b) Violate any air quality standard or
contribute substantially to an existing or
X
projected air quality violation?
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Less Than
Potentially
Significant
Less Than
No
Issues
Significant
With
Significant
Impact
Impact
Mitigation
Impact
Incorporated
c) Result in a cumulatively considerable
net increase of any criteria pollutant for which
the project region is non -attainment under an
applicable federal or state ambient air quality
X
standard (including releasing emissions,
which exceed quantitative thresholds for
ozone precursors)?
d) Expose sensitive receptors to
X
substantial pollutant concentrations?
e) Create objectionable odors affecting a
substantial number of people?
X
IV. BIOLOGICAL RESOURCES. Would the
projectA
a) Have a substantial adverse effect,
either directly or through habitat
modifications, on any species Identified as a
candidate, sensitive, or special status species
X
In local or regional plans, policies, or
regulations, or by the California Department
of Fish and Game or U.S. Fish and Wildlife
Service?
b) Have a substantial adverse effect on
any riparian habitat or other sensitive natural
community identified in local or regional
X
plans, policies, regulations, or by the
California Department of Fish and Game or
U.S. Fish and Wildlife Service?
c) Have a substantial adverse effect on
federally protected Wetlands as defined by
Section 404 of the Clean Water Act
(including, but not limited to, marsh, vernal
X
pool, coastal, etc.) through direct removal,
filling, hydrological interruption, or other
means?
d) Interfere substantially with the
movement of any native resident or migratory
fish or wildlife species or with established
X
native resident or migratory wildlife corridors,
or Impede the use of native wildlife nursery
sites?
e) Conflict with any local policies or
ordinances protecting biological resources,
such as a tree preservation policy or
X
ordinance?
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Less Than
Potentially
Significant
Less Than
No
Issues
Significant
With
Significant
Impact
Impact
Mitigation
Impact
Incorporated
f) Conflict with the provisions of an
adopted Habitat Conservation Plan, Natural
Community Conservation Plan, or other
X
approved local, regional or state habitat
conservation plan?
V. CULTURAL RESOURCES. Would the Project:
a) Cause a substantial adverse change
in the significance of a historical resource as
X
defined in §15064.5?
b) Cause a substantial adverse change
In the significance of an archaeological
X
resource pursuant to § 15064.5?
c) Directly or indirectly destroy a unique
paleontological resource or site or unique
X
geologic feature?
d) Disturb any human remains, including
those interred outside of formal cemeteries?
X
V1. GEOLOGY AND SOILS. Would the roject:
a) Expose people or structures to
potential substantial adverse effects,
X
Including the risk of loss, injury, or death
involving:
1) Rupture of a known earthquake fault,
as delineated on the most recent Alquist-
Priolo Earthquake Fault Zoning map, issued
by the State Geologist for the area or based
X
on other substantial evidence of a known
fault? Refer to Division of Mines and
Geology Special Publication 42.
li Strong seismic ground shaking?
X
III) Seismic -related ground failure,
X
Including liquefaction?
IV) Landslides?
X
b) Result in substantial soil erosion or
X
the loss of topsoil?
c) Be located on a geologic unit or soil
that is unstable, or that would become
unstable as a result of the project, and
X
potentially result in on- or off -site landslide,
lateral spreading, subsidence, liquefaction or
collapse?
d) Be located on expansive soil, as
defined in Table 18-1-B of the Uniform
X
Building Code (1994), creating substantial
risks to life or property?
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Less Than
potentially
Significant
Less Than
No
Issues
Significant
With
Significant
Impact
Impact
Mitigation
Impact
Incor orsted
e) Have soils incapable of adequately
supporting the use of septic tanks or
alternative wastewater disposal systems
X
where sewers are not available for the
disposal of wastewater?
All. HAZARDS AND HAZARDOUS MATEMALS.
Would the project:
a) Create a significant hazard to the
public or the environment through the routine
X
transport, use or disposal of hazardous
materials?
b) Create a significant hazard to the
public or the environment through reasonable
foreseeable upset and accident conditions
X
involving the release of hazardous materials
into the environment?
c) Emit hazardous emissions or handle
hazardous or acutely hazardous materials,
X
substances, or waste within one quarter mile
of an existing or proposed school?
d) Be located on a site which is included
on a list of hazardous materials sites
compiled pursuant to Government code
X
Section 65962.5 and, as a result, would it
create a significant hazard to the public or the
environment?
e) For a project located within an airport
land use plan or, where such a plan has not
been adopted, within two miles or a public
X
airport or public use airport, would the project
result in a safety hazard for people residing
or working in the project area?
f) For a project within the vicinity of a
private airstrip, would the project result in a
X
safety hazard for people residing or working
in the project area?
g) Impair implementation of or physically
Interfere with an adopted emergency
X
response plan or emergency evacuation
Ian?
h) Expose people or structures to a
significant risk of loss, Injury or death
involving wildland fires, including where
wildiands are adjacent to urbanized areas or
X
where residences are intermixed with
wiidlands?
Back Bay Science Center Initial Study/Mitigated Negative beclaration
July 16, 2003 Page 20
Civic Solutions, Inc.
as Than
Potentially
Significant
Less Than
No
Issues
Significant
With
Significant
Impact
Impact
Mitigation
Impact
Incorporated
Vill. HYDROLOGY AND WATER QUALITY. Would theproject:
a) Violate any water quality standards or
X
waste discharge requirements?
b) Substantially deplete groundwater
supplies or interfere substantially with
groundwater recharge, such that there would
be a net deficit in aquifer volume or a
lowering of the local-groundwater1able level
X
(e.g., the production rate of pre-existing
nearby wells would drop to a level which
would not support existing land uses or
planned uses for which permits have been
granted)?
c) Substantially alter the existing
drainage pattern of the site or area, including
through the alteration of the course of a
X
stream or river, in a manner which would
result in substantial erosion or siltation on- or
off -site?
d) Substantially alter the existing
drainage pattern of the site or area, including
through the alteration of the course of a
X
stream or river, or substantially increase the
rate or amount of surface runoff in a manner,
which would result in flooding on- or off -site?
e) Create or contribute runoff water
which would exceed the capacity of existing
or planned stormwater drainage systems or
X
provide substantial additional sources of
polluted runoff?
f) Otherwise substantially degrade water
X
quality?
g) Place housing within a 100-year flood
hazard area as mapped on a federal Flood
X
hazard Boundary of Flood Insurance Rate
Map or other flood hazard delineation map?
h) Place within 100-year flood hazard
area structures, which would impede or
X
redirect flood flows?
i) Expose people or structures to a
significant risk of loss, injury or death
X
involving flooding, including flooding as a
result of the failure of a levee or dam?
j) Inundation by seiche, tsunami, or
X
mudflow?
Back Bay Science Center Initial Study/Mitigated Negative Declaration
July 16, 2003 Page 21
C1vic Solutions, Inc.
It LAND USE AND PLANNING. Would the project:
a) Physically divide an established
X
community?
b) Conflict with any applicable land use
plan, policy, or regulation of an agency with
jurisdiction over the project (Including, but not
limited to the general plan, specific plan, local
X
coastal program, or zoning ordinance)
adopted for the purpose of avoiding or
mitigating an environmental effect?
c) Conflict with any applicable habitat
conservation plan or natural community
X
conservation plan?
X. MINERAL RESOURCES. Would the ro Oct:
a) Result in the loss of availability of a
known mineral resource that would be a
X
value to the region and the residents of the
state?
b) Result in the loss of availability of a
locally important mineral resource recovery
site delineated on a local general plan,
X
specific plan or other land use plan?
XI. NOISE. Would the project result in:
a) Exposure of persons to or generation
of noise levels in excess of standards
established in the local general plan or noise
X
ordinance, or applicable standards of other
agencies?
b) Exposure of persons to or generation
of excessive groundborne vibration or
X
roundbome noise levels?
c) A substantial permanent increase in
ambient noise levels in the project vicinity
X
above levels existin without the project?
d) A substantial temporary or periodic
Increase in ambient noise levels in the project
X
vicinity above levels existing without the
project?
a) For a project located within an airport
land use plan or, where such a plan has not
been adopted, within two miles of a public
X
airport or public use airport, would the project
expose people residing or working in the
ro act area to excessive noise levels?
f) For a project within the vicinity of a
private airstrip, would the project expose
people residing or working in the project area
X
to excessive noise levels?
Back Bay Science Center Initial Study/MiQgated Negative Declaration
July 16, 2003 Page 22
Civic Solutions, Inc.
XII. POPULATION AND HOUSING. Would the project:
a) Induce substantial population growth
in an area, either directly (for example, by
X
proposing new homes and businesses) or
indirectly (for example, through extension of
roads or other Infrastructure)?
b) Displace substantial numbers of
existing housing, necessitating the
X
construction of replacement housing
elsewhere?
c) Displace substantial numbers of
people, necessitating the construction of
X
replacement housing elsewhere?
XIII. PUBLIC SERVICES. Would the,project result in substantial adverse physical
impacts associated with the provision of new or physically altered governmental
facilities, need, for new or physically altered governmental facilities, the
construction of which could cause significant environmental impacts, in order to,
maintain acceptable service ratios, response times or other performance
objectives for an of the public services:
a) Fire protection?
X
b) Police protection?
X
c) Schools?
X
d) Parks?
X
e) Other public facilities?
X
XIV. RECREATION.
a) Would the project increase the use of
existing neighborhood and regional parks or
other recreational facilities, such that
X
substantial physical deterioration of the
facility would occur or be accelerated?
b) Does the project include recreational
facilities or require the construction or
expansion of recreational facilities, which
X
might have an adverse physical effect on the
environment?
n
' Back B;
July 16,
Civic Solutions, Inc.
XV. TRANSPORTATIONITRAFFIC. Would the project.
a) Cause an increase in traffic, which is
substantial in relation to the existing traffic
load and capacity of the street system (i.e.,
result In a substantial Increase in eltherthe
X
number of vehicle trips, the volume to
capacity ratio on roads, or congestion at
Intersections)?
b) Exceed, either individually or
cumulatively, a level of service standard
established by the county congestion
X
management agency for designated roads or
highways?
c) Result in a change in air traffic
patterns, including either an increase in traffic
X
levels or a change in location that results in
substantial safety risks?
d) Substantially Increase hazards due to
a design feature (e.g., sharp curves or
X
dangerous intersections) or incompatible
uses e.., farm equipment)?
e) Result in Inadequate emergency
X
access?
f) Result in Inadequate parking
X
capacity?
g) Conflict with adopted policies, plans,
or programs supporting alternative
X
transportation (e.g., bus turnouts, bicycle
racks)?
XVI. UTILITIES AND SERV)CE SYSTEMS. Would the project:
a) Exceed wastewater treatment
requirements of the applicable Regional
X
Water Quality Control Board?
b) Require or result in the construction of
new water or wastewater treatment facilities
or expansion of existing facilities, the
X
construction of which could cause significant
environmental effects?
c) Require or result in the construction of
new storm water drainage facilities or
expansion of existing facilities, the
)(
construction of which could cause significant
environmental effects?
d) Have sufficient water supplies
available to serve the project from existing
X
entitlements and resources or are new or
expanded entitlements needed?
e) Result in a determination by the
wastewater treatment provider, which serves
or may serve the project that it has adequate
X
capacity to serve the project's projected
demand In addition to the provider's existing
commitments?
Back Bay Science Center
July 16, 2003
Initial Study/Mitigated Negative Declaration '
Page 24
Civic Solutions, Inc.
f) Be served by a landfill with sufficient
permitted capacity to accommodate the
X
ro'ecfs solid waste disposal needs?
g) Comply with federal, state, and local
statutes and regulations related to solid
X
waste?
XVII. MANDATORY FINDINGS OF SIGNIFICANCE.
a) Does the project have the potential to
degrade the quality of the environment,
substantially reduce the habitat of a fish or
wildlife species, cause a fish or wildlife
population to drop below self-sustaining
X
levels, threaten to eliminate a plant or animal
community, reduce the number or restrict the
range of a rare or endangered plant or animal
or eliminate important examples of the major
periods of California history or prehistory?
b) Does the project have impacts that
are individually limited, but cumulatively
considerable? ("Cumulatively considerable"
means that the incremental effects of a
project are considerable when viewed in
X
connection with the effects of past projects,
the effects of other current projects, and the
effects of probable future projects.)
c) Does the project have environmental
effects, which will cause substantial adverse
effects on human beings, either directly or
X
Indirectly?
Back Bay Scie
July 16, 2003
Civic Solutfons, Inc.
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Back Bay Science Center Initial Study/Mitigated Negative Declaration
July 16, 2003 Page 26
P
Civic Solutions, Inc.
' ENVIRONMENTAL ANALYSIS
' This section provides the explanations and supporting analysis for the impact categories and
questions contained in the previous checklist, and identifies mitigation measures where
applicable.
I. AESTHETICS
r
1
1
1
F
II
1
Would the project:
a) Have a substantial adverse effect on a scenic vista?
Less Than Significant Impact. Policies contained in the City's General Plan and the
Coastal Act address impacts on public views. Public views are those from public streets and
property, as opposed to private views from homes and other private property. There are no
Coastal Act or City policies addressing private views. The site is visible from Back Bay Drive, a
public road adjacent to the east, from the Bayview Landing Park site, and from Coast Highway.
Across the bay to the west, the site is visible from the blufftop trail adjacent to Castaways park,
and from the Newport Aquatic Center. Existing views of the site from these locations are shown
in Exhibits C-1.1 through C-1-11. The site is also visible from several residential areas, including
Harbor Cove, Park Newport Apartments and Eastbluff, as well as the Hyatt Newporter resort on
the east side of the bay. Across the bay to the west are residential areas with views of the site.
The site is also visible from portions of the Newport Dunes resort and Back Bay Cafe.
Since the property is currently occupied with several structures, the evaluation of view impacts
should compare the existing appearance of the property to its appearance upon completion.
Since the existing facilities are mostly very basic trailer -type structures and storage sheds, the
new buildings would represent an improvement to the aesthetics of the site.
The entry portion of the new structures would have a maximum roof peak of 28 feet while the
wings would have a roof peak of 15-16 feet. This would be similar to the roof heights of other
single -story structures in the vicinity such as Back Bay Cafe and Newport Dunes.
The project would have a beneficial effect on both public and private views since the permanent
buildings would be more attractive than the existing temporary facilities. There may be a
temporary negative visual impact during grading and construction activities but this is not
considered significant. No mitigation measures are necessary.
Back Bay Science Center Initial Study/Mitigated Negative Declaration
July 16, 2003 Page 27
Civic Solutions. Inc.
EXHIBIT C-1.1
VIEW LOOKING SOUTH FROM EASTBLUFF NEIGHBORHOOD
EXHIBIT C-1.2
VIEW LOOKING SOUTHWEST FROM PARK NEWPORT APARTMENTS
Back Bay Science Center Initial Study/Mitigated Negative Declaration
July 16, 2003 Page 28
r.
�� T �. � t R �
ttfi r
�: i
i �"•`
""� '"•> 3'"��ti '�W'`M�{��r."!'�'�'r�-+�m�F-:�,K•yf1� --.�- .'or+ -:;'r.+�.z"..'c".'.ft�S�-!"
�� r
+a4+' } ny t'' a 11yi ti +� �•.� Z y(t�!;-Y �y.�� ' �r y(�+j
! 1 1
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Civic Solutions, Inc.
EXHIBIT C-1.5
VIEW LOOKING WEST FROM BACK BAY DRIVE
EXHIBIT C-1.6
VIEW LOOKING WEST FROM HYATT NEWPORTER
Back Bay Scionce Center Initial Study/Mitigated Negative Declaration
July 16, 2003 Page 30
Civic
Inc.
EXHIBIT C-1.7
VIEW LOOKING NORTH FROM BAYVIEW PARK SITE
EXHIBIT C4.8
VIEW LOOKING NORTH FROM WEST SIDE OF NEWPORT DUNES LAGOON
Back Bay Science Center Initial Study/Mitigated Negative Declaration
July 16, 2003 Page 31
Civic Solutions, Inc
. ter.
..11 ' ::r... ;^' •-.: .•.ate;
EXHIBIT C-1.9
VIEW LOOKING NORTH FROM COAST HIGHWAY ACROSS NEWPORT DUNES
EXHIBIT C-1.10
VIEW LOOKING EAST FROM CASTAWAYS BLUFFTOP TRAIL,
Back Bay Science Center Initial Study/Mitigated Negative Declaration
July 16, 2003 Page 32
Civic Solutions, Inc.
Civic Solutions. Inc , '
b) Substantially damage scenic resources, including, but not limited to, trees, rock
outcroppings, and historic buildings within a state scenic highway?
Less Than Significant Impact. Coast Highway (SR-1) is designated a state scenic
highway. There are no rock outcroppings or historic buildings on the project site. There is a
large ficus tree along the western edge of the property, which will be retained in the proposed
plan. A small grove of eucalyptus trees and other exotic species located on the southern
portion of the site would be removed as part of the project, but, this is not considered a
significant scenic resource.
The primary scenic resource in the vicinity of the project site is Upper Newport Bay. There is
also a coastal bluff across Back Bay Drive to the east, which may be considered a significant
scenic resource. The project would not substantially alter public views of these scenic
resources. No mitigation measures are necessary.
c) Substantially degrade the existing visual character or quality of the site and its
surroundings?
Less Than Significant Impact. See discussion under La and Lb, above. No mitigation
measures are necessary.
d) Create a new source of substantial light or glare, which would adversely affect day
or nighttime views In the area?
Less Than Siqnificant Impact With Mitigation. Since the site is currently developed, the
proposed project would not create a new source of light, although exterior lighting of the new
facilities could cause glare and adversely affect nighttime views from nearby properties if not
properly controlled. In order to minimize the potential for light spillage and glare, the following
mitigation measure will be Imposed on the project.
Mitigation Measure
MM 1-1
Exterior on -site lighting shall be shielded and confined within site boundaries. No direct
rays or glare are permitted to shine onto public streets or adjacent sites or create a
public nuisance. "Walpak" type fixtures shall not be permitted. Parking area lighting
shall have zero cut-off fixtures and light standards shall not exceed 20 feet in height.
This mitigation measure would reduce potential impacts to a level that is less than significant.
Back Bay Science Center
July 16, 2003
initial Study/Mitigated Negative Declaration
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Civic Solutions, Inc.
IL AGRICULTURE RESOURCES
Would the project:
a) Convert Prime Farmland, Unique Farmland, or Farmland of Statewide Importance
(Farmland), as shown on the maps prepared pursuant to the Farmland Mapping and
Monitoring Program of the California Resources Agency, to non-agricultural use?
No Impact. No agricultural activities occur in the project vicinity. No mitigation
measures are necessary.
b) Conflict with existing zoning for agricultural use, or a Williamson Act contract?
No Impact. The site is not zoned for agriculture and there are no Williamson Act
contracts in the vicinity. No mitigation measures are necessary.
c) Involve other changes in the existing environment which, due to their location or
nature, could result in conversion of farmland, to non-agricultural use?
No Impact. The project would not involve any changes that could result in the
conversion of farmland. No mitigation measures are necessary.
III. AIR QUALITY
Where available, the significance criteria established by the applicable air quality
management district or air pollution control district may be relied upon to make the
following determinations. Would the project:
a) Conflict with or obstruct implementation of the applicable air quality plan?
No Impact. The project site is within the South Coast Air Basin (SCAB), which includes
Orange County and the non -desert portions of Los Angeles, Riverside, and San Bernardino
counties. Air quality conditions in the Basin are under the jurisdiction of the South Coast Air
Quality Management District (SCAQMD). The SCAQMD and the Southern California
Association of Governments (SCAG) are responsible for formulating and implementing an Air
Quality Management Plan (AQMP) for the Basin. The current AQMP was approved in 1997.
Implementation of the AQMP is based on a series of control measures that vary by source type,
such as stationary or mobile, as well as by the pollutant targeted. Since the AQMP is based on
growth projections reflected in local general plans, only new or amended general plans, or
projects that exceed the level of development contemplated in the general plan have the
potential to conflict with the AQMP. The proposed project is consistent with the Newport Beach
General Plan, therefore no conflict with the AQMP would occur. No mitigation measures are
required.
b) Violate any air quality standard or contribute substantially to an existing or
projected air quality violation?
' Back Bay Science Center Initial Study/Mitigated Negative Declaration
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Civic So/utions, Inc.
Less Than Significant Impact. The project would result in short-term emissions during
construction (e.g., dust, construction equipment exhaust) and long-term emissions due to traffic
generated by the project after construction is completed.
Emissions Standards. California and Federal Ambient Air Quality Standards are shown on
Table 111-1. In Its CEQA Air Quality. Handbook. the SCAQMD provides specific criteria for
determining whether the potential air quality impacts of a project are significant. These
thresholds are as follows:
Thresholds of Significance for Construction Emissions
■ 75 pounds per day of ROC or 2.5 tons per quarter
■ 100 pounds per day of NOx or 2.5 tons per quarter
■ 550 pounds per day of CO or 24.75 tons per quarter
■ 150 pounds per day of PM10 or 6.75 tons per quarter
• 150 pounds per day of sulfur oxides (SOx) or 6.75 tons per quarter
Thresholds of Signiflcance for Operational Emissions
■ 55 pounds per day of ROC
■ 55 pounds per day of NOx
■ 550 pounds per day of CO
■ 150 pounds per day of PM,o
■ 150 pounds per day of SOx
Localized Criteria Pollutants Concentration Standards
California State 1-hour standard of 20.0 ppm
California State 8-hour standard of 9.0 ppm
Protect Emissions. Tables 6-2 and 6-3 of the AQMD CEQA Handbook provide guidance for
determining whether a project could exceed these thresholds of significance during construction
or operations. For construction remissions, the threshold for an office project is 559,000 square
feet of gross floor area. The proposed project would contain approximately 13,000 square feet
of gross floor area, therefore it is well below the threshold of significance. The threshold for
grading is 177 acres. The proposed project would require that a maximum of 3.5 acres be
graded or disturbed, therefore the project is below the threshold of significance for grading
activities. For demolition, the threshold is 23,214,000 cubic feet of building area. The facilities
to be demolished contain approximately 86,000 cubic feet of space, which is also far below the
threshold.
Back Bay Science Center Initial Study/Mitigated Negative Declaration
July 16, 2003 Page 36
Civic Solutions, Inc.
TABLE III-1
Ambient Air Quality Standards
California Standards t
Federal Standards'
Pollutant
Avaraging Timo
Concanlration'
Method
Pdmary't
Secondary JO
Method'
I [lour
0,09 ppm(IB4palid)
012 ppm(235pF/m)`
'
Ozone (0,)
Ullmviala l'holomdry
(HtmvtoldrWatomy
fl lluor
—
o0sppn057 pzrni)°
same. hlo.q Swan
Respirable
24 Hour
501twor,
fmnmd^eor Um
Isopyni
foam[ScPmoluaund Gmvimrmr
ParticulateSemc
Art..,[.'
a Pomary SlmduN
Arct)
Mailer (PM70)
Moral
ArtlooArMan
20pgM�
SUhu/m'
Fine
24 Hour
No&lanm5mmsoobol
fd Pa4i
Particulate
Samea PAmq StmdaW
Inmul Sery ANul)u. Gnvimvm)e
Matter(PM2.5)
Aurt.l
i2 Gmvimadc or Ilan
Ya''nr
151 yn1
Andimmm Man
Anenwllan
&[[our
90 fpnt (mmSrm')
9'.(10 mgln')
Carbon
Monoxide
", Non•DLrnnrvu lnfmnJ'
M000mary(NDIIQ
Nanc
Non DmrmrwlnfmtN
V1.1omey(NDUH,
Illuur
2d Ppm (P my4n)
IS m40'
fY l TS(^!�i•
kllour (Uke
'GpPin (7 m�i)
—
(CO)
hhoal
Amwl
0051 PPm(100p)Im}
Nitrogen
Arnhmclm\Inn
Go Moro
Samaas PomorystmdaN
G.('h°.a chnnd'Wo.na:
Dioxide (NO,)
Ce milumu%sanrc
I [lour
0151rymt (4lOpprm)
—
Amwl
—
0100 pm luo Par.')
—
Andoon"Flan
2411.,
OD4w.11054Yrmr)
O.W PMn(30 ps"c')
—
Sulfur Dioxide
Spwvuplmmmary(Ponrommhnc
'(SO')
Ultm.iola Fluoraca%c
MaM1otg
311.
—
'—
a5'u1(t3Wtt0m)
Illour
025 ppm(a55 pgrmr)
—
—
30Day Avomge
Idp✓tn'
—
—
Ihgh Volmnesampiamd
Lead'
Aucen: ANo"oo
Atomic Aluoigion
hlrndm Qwda
—
IS pDni
Sameu Pnmary$tandaN
h\tmmm�cocleaumaro.23po-kikm%ta—a,anhtyar'
,
Visibility
toandpamora(007-3umdaormomrmiaka'hhoo
NO
Reducing
9llpur
due tolnnidao4tm raLuvehumiddybla. Wvt 70
Particles
Pant. Melhud:Hcu AuWoc6Mmd TnMannnat
thmazh FdlaTopc.
Federal
Sulfates
24 Hour
25pym'
Ionchmnw'rurly
(
Hydrogen
tllour'
O,OJ ppm �J21tF'�^°)
Ultmvloln Fluarearna
Sulgde
Standards'
vinyl CIWorlds
24 Hour
001 PI•^rMpLJm)
G.'Chrmmtogmph)•
a On June 20, 2002, the Air Resources Board approved staffs recommendation to revise the PM10 annual average standard Wit pg/m' and to
establish an annual average standard for PM2.5 of 12 Pgte. These standards will take effect upon final approval by the Office of AdmlNstralive Law,
which is expected In February 2003. Information regarding these revisions can be found at hllpJ/www arb.w govlresearcldaagsfstd.rsfsld.m htm.
See also footnotes on next page...
California Air Resources Board (119103)
Back Bay Science Center Initial Study/Mitigated Negative Declaration
July 16, 2003 Page 37
Civic Solutions, Inc.
TABLE III-1 Continued
1. California standards of ozone, carbon monoxide (except Lake Tahoe), sulfur dioxide (1 and 24
hour), nitrogen dioxide, suspended particulate matter-PM10, PM2.5, and viability reducing
particles, are values that are not to be exceeded. All others are not to be equaled or exceeded.
California ambient air quality standards are listed in the Table of Standards in Section 70200 of
Title 17 of the California Code of Regulations.
2. National standards (other than ozone, particulate matter, and those based on annual averages or
annual arithmetic mean) are not to be exceeded more than once a year. The ozone standard Is
attained when the fourth highest eight hour concentration in a year, averaged over three years, is
equal to or less than the standard. For PM10, the 24 hour standard is attained when 90 percent
of the daily concentrations, averaged over three years, are equal to or less than the standard.
For PM2.5, the 24 hour standard Is attained when 98 percent of the daily concentrations,
averaged over three years, are equal to or less than the standard. Contact U.S. EPA for further
clarification and current federal policies.
3. Concentration expressed first in units in which it was promulgated. Equivalent units given in
parentheses are based upon a reference temperature of 25°C and a reference pressure of 760
torr. Most measurements of air quality are to be corrected to a reference temperature of 250C
and a reference pressure of 760 toor;ppm in this table refers to ppm by volume, or mlcromoles of
pollutant per mole of gas.
4. Any equivalent procedure which can be shown to the satisfaction of the ARB to give equivalent
results at or near the level of the air quality standard may be used.
5. National Primary Standards: The levels of air quality necessary, with an adequate margin of
safety to protect the public health.
6. National Secondary Standards: The levels of air quality necessary to protect the public welfare
from any known or anticipated adverse effects of a pollutant.
7. Reference method as described by the EPA. An "equivalent method" of measurement my be
used but must have a 'consistent relationship to the reference method" and must be approved by
the EPA.
8. New Federal 8-hour ozone and fine particulate matter standards were promulgated by U.S. EPA
on July 18, 1997. Contact U.S. EPA for further clarification and current federal policies.
9. The ARB has identified lead and vinyl chloride as toxic air contaminants' with no threshold level of
exposure for adverse health effects determined. These actions allow for the implementation of
control measures at levels below the ambient concentrations specified for these pollutants.
Back Bay Science Center Initial Study/Mitigated Negative Declaration ,
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Civic Solutions, Inc.
J
The screening threshold for operational emissions is 245,000 square feet for a research center
project. The project proposes 13,000 square feet, which is below the threshold.
Project Design Features and Standard Conditions
Sc 111-1
In order to reduce construction related fugitive dust, SCAQMD Rule 403 will be
implemented during construction. Rule 403 requires that fugitive dust be controlled with
best available control measures so that the .presence of such dust does not -remain
visible in the atmosphere beyond the property line of the emission source,
Implementation of these dust suppression techniques can reduce dust generation and
PM10 by 50 to 75 percent. Implementation of the following measures will reduce short-
term fugitive dust impacts on nearby sensitive receptors.
• Apply non -toxic chemical soil stabilizers according to manufacturers'
specifications to all inactive construction areas (previously graded areas inactive
for 10 days or more).
■ Water active sites at least two times daily. (Locations where grading is to occur
will'be thoroughly watered prior to earthmoving.)
■ All trucks hauling dirt, sand, soil, or other loose materials are to be covered, or
should maintain at least two feet of freeboard in accordance with the
requirements of California Vehicle Code Section 23114 (freeboard refers to the
vertical distance between the top of the load and the top of the trailer walls).
• Pave construction access roads at least 100 feet onto the site from the main
road.
■ Traffic speeds on all unpaved roads shall be limited to 15 mph or less.
■ Revegetate disturbed areas as quickly as possible.
• All excavating and grading operations shall be suspended when wind speeds (as
instantaneous gusts) exceed 25 mph.
■ All streets shall be swept once a day if visible soil materials are carried to
adjacent streets. Water sweepers with reclaimed water are recommended.
■ Install wheel washers where vehicles enter and exit unpaved roads onto paved
roads, or wash trucks and any equipment leaving the site each trip.
Back Bay Science Center
July 16, 2003
Initial Study/Mitigated Negative Declaration
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SC 111-2
Plan specifications shall Include a statement that the contractor shall attempt to reduce
VOC emissions by 9) using precoated/natural colored building materials; 2) using water -
based or low-VOC coating; and 3) coating transfer or spray equipment with high transfer
efficiency, such as high -volume low-pressure (HVLP) spray method, or manual coatings
application, such as paint brush, hand roller, trowel, spatula, dauber, rag, or sponge.
The plan specifications shall be approved by the Department of Fish and Game or its
designee.
SC 111-3
In order to reduce operational energy usage and reduce energy production air
emissions, the project is required to comply with Title 24 of the California Code of
Regulations established by the California Energy Commission regarding energy
conservation standards.
With the standard conditions listed above, potential impacts would be less than significant. No
mitigation measures are necessary.
c) Result in a cumulatively considerable net increase of any criteria pollutant for
which the project region is non -attainment under an applicable federal or state ambient
air quality standard (including releasing emissions which exceed quantitative thresholds
for ozone precursors)?
Less Than Significant Impact. See Section Ill.a, above.
d) Expose sensitive receptors to substantial pollutant concentrations?
Less Than Significant Impact, See Section Ilia, above.
e) Create objectionable odors affecting a substantial number of people?
Less Than Sianificant Impact. Diesel -powered equipment used for construction could
cause odors and emissions that may be offensive to sensitive receptors. The closest sensitive
use to the project area is the Back Bay CafB, located more than 300 feet from most portions of
the site. This would be a temporary impact and is not considered significant, therefore no
mitigation is necessary.
IV. BIOLOGICAL
Would the project:
a) Have a substantial adverse effect, either directly or through habitat modifications,
on any species identified as a candidate, sensitive, or special status species In local or
regional plans, policies, or regulations, or by the California Department of Fish and Game
or U.S. Fish and Wildlife Service?
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Less Than Significant Impact With Mitigation. In order to determine the potential impacts of the
project on biological resources, Rick Ware of Coastal Resources Management and Kathleen
Keane of Keane Biological Consultants were retained to conduct a biological assessment of the
site. The following information is drawn from CRM's analysis, as well as a field survey
conducted by Keane Biological Consultants, which is included as Appendix 1.
1. Biological Characteristics
Site analyses were conducted at Shellmaker Island during several field visits between April 2002
and April 2003. The following discussion presents a review of the general biological communities
and common plants and animals present at the Lower Shellmaker Island project site, and a review
of site -specific information obtained during previous work conducted on Shellmaker Island.
Additional information on the vegetation and bird use of Upper Shellmaker Island (Coastal
Resources Management 1992) also was used as historical information for Lower Shellmaker,
since the areas are likely to have similar associations. Exhibit C-IV.1 shows the existing vegitation
and habitat of the site.
Regions of Shellmaker Island discussed within the following section include:
• Lower Shellmaker Island. This area includes the waters, shoreline, and land located
between the Dunes Marina and the CDFG tidal channel cut which separates Lower
Shellmaker Island from Upper Shellmaker Island
• UCI Crew Base Channel. This back channel is located on the eastern side of Lower
Shellmaker Island and connects to the Dunes Marina launch ramp channel
• Dunes Marina Launch Ramp Channel. Located on the south side of Lower
Shellmaker Island that intersects with the main channel of Upper Newport Bay.
• Marine Science Center and CDFG Facility Area and Parking Lot. Facilities located on
Lower Shellmaker Island
• Amphitheater. Teaching and Interpretive area located immediately north of CDFG
headquarters.
Upland Habitat and Vegetation Community. Sandy upland areas, composed of previously filled
dredge materials are located above approximately +10 feet [MLLW]). These areas also include
raised, berm -like areas scattered throughout the southern marsh and open habitat within the
Marine Science Center/CDFG Facility, and UCI Rowing Center. These soils are covered by a
sparse to moderate cover of ruderal grasses and forbs, a few shrubs, and transitional strand
vegetation (sea -fig, Carpobrotus aeguilaterus). The dominant forbs in the sandy upland areas
typically include telegraph weed (Heterotheca grandiflora), coastal wooly -head (Nemacaulls
denuda), western tansy -mustard (Descurainia pinata), and filaree (Erodium sp). Mulefat
(Baccharls salicifolia), coyote brush (Baccharis pilularis), and saltbush (Atriplex sp.) are also
bound on Shellmaker Island, although these occur at higher elevations (+13 to +17 feet MLLW).
Myoporum (Myoporum laetum) and Eucalyptus trees are found near the UCI Rowing Center, and
one Indian Laurel (Ficus) tree is located at the western edge, near the Marine Science Center
dock facility.
Transitional strand habitat and vegetation. Transitional strand vegetation includes an array of
plants that grow on loose, sandy soils between the salt marsh and higher upland habitats. This
habitat is common throughout the fringes of the salt marsh habitats up to the roadways, and
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EXHIBIT C-IVA
VEGITATION PLAN
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elevated berms scattered throughout the marsh. Transitional vegetation common within the area
includes salt grass (Distichlis spicata), sea -fig, and alkali heath (Frankenia satin (-Frankenia
grandifoliaj)
Salt marsh habitat and vegetation. Salt marsh habitat extends around the perimeter of Lower
Shellmaker Island between the UCI Rowing Facility Access Channel and' the Main Channel of
Upper Newport Bay with the largest stand of salt marsh concentrated at the southern tip of Lower
Shellmaker. Salt marsh vegetation grows at elevations between approximately +3 feet and about
+7.5 feet- MLLW. Salt marsh plants typically occur in three broad, overlapping zones based on
their response to environmental factors including elevation, soil salinity, and competition. These
zones are the low, mid, and high salt marsh.
The salt marsh growing at the southern tip of Shellmaker Island consists of a mixture of long-
standing vegetation mixed with newer vegetation that colonized the intertidal areas following
restoration efforts by CDFG and the County of Orange in 1995. Lowest elevations within the salt
marsh support pockets of cordgrass. There are a few moniform stands of cordgrass (Spaitina
foliosa) in the low marsh, along the marsh channel banks of the Dunes Marina Access Channel,
and at the terminus of the UCI Rowing Center Access Channel. Typically however, the salt marsh
is dominated by a combination of both pickleweed (Sallcornia virginica and sp. bigelovii) and
cordgrass (Spartina follosa). Saltwort (Batis maritima) and common woody pickleweed (Salicornia
virginica) are most commonly found at a range of elevations. High salt marsh vegetation includes
pickleweed, salt grass, and sea blite (Suaeda californica).
Salt marsh bird's beak (Cordylanthus maritimus spp. maritima), a federal -and state -listed
endangered species, is found in several localities on Lower Shellmaker Island and Upper
Shellmaker Island (Brian Shelton, California Department of Fish and Game, pers. com). Distinct
stands of bird's beak are found along the periphery of the Lower Shellmaker Island salt marsh and
transitional habitats and on high spots within the marsh itself, mixed with salt grass, salt wort, sea
blite, and sea fig. This species is also found in many other areas on Upper Shellmaker and the
eastern marsh of Shellmaker Island (CDF&G, 1991; CRM 1992). Patches of it also occur at the
northern end of the pathway next to the CDF&G tidal channel at the juncture of Lower and Upper
Shellmaker Island.
The salt marsh and transitional vegetation along the main channel of Upper Newport Bay near the
Marine Science Center boat dock and within the UCI Rowing Center Access Channel grows
within a narrow band, the result of a steep elevational gradient.
Mudflats. The mudflat habitat is the transition zone between the open water channels and the
salt marsh at elevations between —2 ft and +3.5 ft MLLW. Diatoms and green algae often cover
the surface of the mudflats and are considered to be important because these plants account for a
large part of the primary production in southern California coastal wetlands (Zedler 1982).
Additionally, the plants are a food source for herbivorous invertebrates, fishes, and birds. The
mudflats are also colonized by infaunal and epifaunal community of marine invertebrates which
are used as food sources by shorebirds. Common epifaunal species observed at the site include
the horn snail (Cerithidea californica) and crabs (Hemigrapsus oregonensis). Estimates of horn
snail density on the mudflats along the periphery of Lower Shellmaker in April 2003 ranged from
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256 to 586 Individuals per square meter, the majority of which fronts the main channel and the
tidal channel south of the project site.
Higher elevation mudflats (salt pannes) at elevations about +6 to +8 ft MLLW occur both within
open areas in the central part of the salt marsh and near the UCI Rowing Center.
Open Water and Shallow Subtidal Bottom Habitat. The open water and subtidal bottom
habitat in Upper Bay channels extends from depths of between 2 ft to -15 ft MLLW. Sediments
In the channel are unconsolidated silts with some outcrops of clay material. Open water habitat
surrounds Lower Newport Bay, In the UCI Rowing Center Access Channel, the Dunes Marina
Launch Ramp Access Channel, and the Main Channel of Upper Newport Bay.
Tidal creeks bisect the salt marsh of Lower Shellmaker Island. These small, meandering
channels are Important features of natural marsh habitats.
2. Blota of the Project Area
Invertebrates. Mudflats and open sandy areas are colonized by tiger beetles, several of which
were observed on mudflats and higher salt pans during field surveys conducted in August 1992.
They resembled CIncidela oregona and Ciclndela punctuta, but could not be positively identified.
they are however, not likely to be sensitive species (Fuller 1992). Other species which are
considered sensitive, due to loss of their habitat, are discussed In the following section.
The mudflats and shallow subtidal sediments support a food base of infaunal and epifaunal
invertebrates that are preyed upon by both shorebirds and bottom foraging fishes. The shallow
benthic and mudflat habitats in the vicinity of Shellmaker Island support at least 94 species of
benthic Invertebrates, dominated in richness and abundance by capitellid and spionid polychaete
worms, oligochaete worms, and amphipod crustaceans (MBC & SCCWRP 1980).
Fishes. At least 75 species of fish are known to occur in the Upper Bay between the Coast
Highway and Jamboree bridges (Michael Brandman Associates 1991). At high tide, submerged
mudflats become Important fish foraging habitat. The shallow subtldal habitat of Upper Newport
Bay Is an important nursery habitat for halibut and other fishes such as gobies [family Gobiidae],
topsmelt (Atherinops afBnls), anchovies (family Engraulidae), croakers (family Sclaenidae),
diamond turbot (Hypsopsetta guttu/ate), and sand bass (Paralabrax nebulifer). Others which
commonly occur in the main channel near the project site are shiner perch (Cymatogaster
aggregate), striped mullet (Mugll cephalus), round sting ray (Urolophus hallet�, and staghorn
sculpin (Leptocottus armatus).
California halibut are consistently found in the shallow waters between the Coast Highway Bridge
and the dike. Allen (1988) reported most individuals captured between Shellmaker Island and the
dike were young of the year YOTY (less than 80 mm in length) and second -year individuals (80
mm to about 160 mm). Halibut abundances were positively correlated to Increasing salinities
(Allen 1988). The waters in the vicinity of Shellmaker Island are generally well mixed and
salinities are within ranges that support YOTY and juvenile halibut (Orange County Department of
Public Health 1978, MBC and SCCWRP 1980).
Reptiles. A survey was conducted in August of 1992 on Upper Shellmaker to determine the
potential for reptiles, including sensitive species, to be present within the proposed mitigation area
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(Fuller 1992). Two species of reptiles were found; the side -blotched lizard (Ufa stanburiana) and
the western fence lizard (Sceloporus occidentalis). These commonly occur in the region.
Avian Resources. Bird surveys were conducted in the vicinity of the project area on August 19,
1991 (Coastal Resources Management 1992) and more recently between April 2002 and April
2003 (Keane Biological Consulting 2002). A variety of birds were observed along the channels
and banks, over the open water, and roosting on mudflats and in the low and middle salt marsh.
Among the water birds, the marbled godwit (Limosa fedoa), elegant tern (Sterna elegans), and
Forester's tern (Stema forsten) were the most numerous, especially on the mudflats in the vicinity
of the CDF&G tidal channel that bisects Shellmaker Island. Other common species seen included
snowy egret (Egretta thula), killdeer (Charadrius vociferus), willet (Catoptrophorus
semipalmatus), whimbrel (Numenius phaeopus), and caspian tern (Stema caspia). Pied -billed
grebe (Podilymbus podiceps), great blue heron (Ardea herodias), black -bellied plover (Pluvialis
squatarola), greater yellowlegs (Tiinga melanoleucus), long -billed curlew (Numenius americanus),
long -billed dowitcher (Limnodromus scolopaceus), ring -billed gull (Lanus delawarensis), California
gull (Larus californicus), and western gull (Lanus occidentalis) were also observed. Others that
are expected to be present at other times of the year include various ducks, semipalmated plover
(Charadrius semipalmatus), short -billed dowitcher (Limnodromus griesus), and common tern
(Stema hirundo). Two endangered species of birds, the California light-footed clapper rail "(Rallus
longirostris Wipes) and Beldings savannah sparrow (Passercu/us sandwichensis beldingi) are
also resident on Shellmaker Island. On Lower Shellmaker, one pair of breeding Belding
savannah sparrows was observed during 2002. Individual savannah sparrows were heard, but
not seen in the April 2003 surveys (Kathy Keane, pers. com., April 2003).
Substantially higher abundances and a greater diversity of shorebirds species are expected
during the late fall through spring overwintering period of transients and winter residents. The
types of birds and numbers of birds are also expected to vary depending on the time of day and
tidal conditions.
The site supports very poor habitat for land birds based on bird observations during 2002 and
2003; only the mourning dove (Zenaida macroura) was observed in large numbers. The doves
were feeding on the dredge spoil among the ruderal (weedy) vegetation in front of the CDF&G
buildings. In addition to mourning doves, the American crow (Corvus brachyrhychos), northern
mockingbird (Mimus polyglottos), European starling (Sturnus vulgaris), and house sparrows
(Passer domesticus) were present. A number of barn swallows (Hirundo rustica) were observed
hawking insects over the island in 1991, but were also foraging over nearby marshes and over the
open water. Several turkey vultures (Cathartes aura) were seen 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 black phoebe (Sayornis nigricans) and house finch (Carpodacus
mexicanaus) are expected to be occasionally present. There is no record of any nesting species
on Shellmaker Island. The presence of sensitive species of birds on Shellmaker Island is
discussed below. A complete list of bird species present in the entire Upper Newport Bay
Ecological Reserve is found in Appendix 2.
Mammals. Thompson (1978) listed a total of 17 species of mammals which have been recorded
in the Reserve, of which 7 occurred on Shellmaker Island. These include house mouse (Mus
' musculus), raccoon (Procyon lotor), Mexican opossum (Didelphis marsupialis), striped skunk
(Mephitis mephitis), house cat (Fells domesticus), California ground squirrel (Spermophilus
beecheyi), and cottontail rabbit Sylvilagus audubonii.
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3. Sensitive Species.
Plants. The distribution of the federal- and state -listed salt -marsh bird's beak (Cordylanthus
maritimus spp. maritlma) was mapped In 1991 by Fred Roberts for the CDF&G. Additional site
surveys conducted on Upper Shellmaker Island by Coastal Resources Management in May and
July 1992 corroborated the 1991 data. Brian Shelton, of CDFG mapped this species on Lower
Shellmaker Island (and other areas of Upper Newport Bay) in 2002. Generally, salt marsh bird's
beak is found in the high salt marsh meadows and transitional habitats on Shellmaker Island.
Large patches of this species are found on Lower Shellmaker Island, In the marsh at the southern
end of the island.
Invertebrates. While no sensitive insects are currently known from Lower Shellmaker Island,
potentially suitable habitat is present on dredge material "dune" habitat and mudflats surrounding
the marsh. Sensitive Insects that have a potential to be found here Include the wandering skipper
butterfly (Panoquina panoqulnoides errans), globose dune beetle (Coelus g/obosus), Gabb's tiger
beetle (Cincindela gabbi), sandy beach tiger beetle (C. hirticollis gravida), and the sand dune tiger
beetle (C. latesignata). The most likely species to occur on Shellmaker are the wandering
skipper, 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 California brackish water snail (Tryonla Imitator) is a federal species of concern. It occurs in
Upper Newport Bay and prefers shallow, coarse sediments in low salinity (brackish) areas at the
mouth of the Santa Ana -Delhi channel and the San Diego Creek. It Is also recorded from the
main channel near Shellmaker Island, but in significantly lower densities and mostly during winter
and spring when storm water run-off reduces the salinity in the main channel (MSC and SCCWRP
1980).
Fishes. No listed species of fish occur in Newport Bay. However, California halibut is considered
a locally important species because of it is commercially valuable and its nursery habitat in coastal
bays and wetlands have been reduced. California halibut spawn at sea and the larval stages are
planktonic. After several months, the larval fish settle to the bottom, and migrate into shallow
coastal waters, including embayments such as Alamitos Bay, Anaheim Bay, Outer Bolsa Chico,
and Newport Bay. Halibut are distributed throughout Lower and Upper Newport Bay; however,
the YOTY prefer shallow waters between about -1.5 feet and -3.5 feet MLLW, whereas Juveniles
prefer deeper channel bottoms. After nearly nine months in Newport Bay, Juveniles will move out
Into the open coastal environment.
Birds. Several species of birds are considered to be sensitive because of the loss of habitat
and/or a reduction in their populations.
The state endangered Belding's savannah sparrow (Passercu/us sandwichensis beldingi) is a
year-round resident and breeder in Upper Newport Bay. Its preferred nesting habitat is
pickleweed-dominated mid to high salt marsh. In 1996, the population In Upper Newport bay
was 252 pairs (Chambers Group 2000). This species is found throughout Upper Newport Bay.
The state and federal endangered light-footed clapper rail (Rallus longlrostris Wipes) is found
throughout Upper Newport Bay, utilizing cord grass marsh for nesting at several sites.
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Observed nesting areas includ Shellmaker Island (northwest section), Middle Island, Upper
Island, and in the saltmarsh above the main dike. The resident population of light footed
clapper rails represents about 65% of the California population of this species. In 1999, 104
pairs were observed in Upper Newport Bay (Chambers Group 2000).
The state and federal endangered California least tern (Sterna antillarum Brownii) is a seasonal
resident in Upper Newport Bay from April to early September. They nest on the "hot dog"
shaped island in the uppermost basin. In 1999, 40 pairs of least terns nested on this island
(Chambers Group 2000). In 2000, 60 least tern pair nested in Upper Newport Bay and fledged
12 young (Keane 2001).
The federal threatened coastal California gnatcatcher nests in coastal sage scrub along the
margins of Upper Newport Bay, but none have been seen on or near Shellmaker Island.. There
are at least 10 pairs breeding in upland habitat surrounding Upper Newport Bay (Gallagher
1997).
Other listed bird species or species of special concern that occur in Upper Newport Bay on a
seasonal basis but do not breed there include the state and federal endangered California
brown pelican, the federal threatened and California Species of Secial Concern western snowy
plover, and the state endangered American peregrine falcon. None of these species utilize
Shellmaker Island.
The state and federal endangered plant salt marsh bird's beak occurs at several sites in high
salt marsh habitat in Upper Newport Bay (Chambers Group 2000). It is the only listed plant
species confirmed to occur in Upper Newport Bay Ecological Reserve.
The California brackish water snail, a species categorized as a Federal Species of Concern, is
common around freshwater discharges to the Upper Bay.
4. Project Impacts
Thresholds of Significance. The threshold for significance of impacts to Shellmaker Island
biological resources is determined by professional judgment of scientists, and in consideration
of the relative importance of the habitat and/or species populations affected by project
implementation. For the purposes of this analysis, the project's effects on biological resources
are considered to be significant if the project would:
• Substantially affect a rare, threatened, endangered, or candidate plant or animal species, or the
habitat of any such species;
• Substantially diminish or degrade State of California Ecological Reserve habitat or City of
Newport Beach Environmentally Sensitive Habitat Area (ESHA)
• Substantially diminish or degrade habitat for wetland plants and animals;
• Result in notable net loss of a biotic community that is subject to local, state, and/or federal
regulations or that is otherwise of very limited occurrence in the region;
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• Interfere substantially with the movement of any resident or migratory fish or wildlife species, or
persistence of a native plant population; or
Conflict with adopted environmental policies, general plans, or regulatory policies of the
community and State of California.
Relevant Environmental Policies and Laws. The following laws provide guidance for the
evaluation of Impacts to biological resources.
Section 30231 of the California Coastal Act:
"The biological productivity and the quality of coastal waters, streams, wetlands, estuaries, and
lakes appropriate to maintain optimum populations of marine organisms and for the protection of
human health shall be maintained and, where feasible, restored through among other means,
minimizing adverse effects of wastewater discharges and entrainment, controlling runoff,
preventing depletion of ground water supplies and substantial Interference with groundwater flow,
encouraging waste water reclamation, maintaining natural vegetation buffer areas that protect
riparian habitats, and minimizing alteration of natural streams.
Section 30105.5 of the California Coastal Act.
Environmentally sensitive areas are "any area In which plan or animal life or their habitats are
either rare or especially valuable because of their special nature or role in an ecosystem and which
could be easily or degraded by human activities and developments"
Section 30240 of the California Coastal Act:
(a) Environmentally sensitive habitat areas shall be protected against any significant disruption of
habitat values, and only uses dependent on those resources shall be allowed within those areas.
(b) Development In areas adjacent to environmentally sensitive habitat areas and parks and
recreation areas shall be sited and designed to prevent Impacts Which would significantly degrade
these areas, and shall be compatible with the continuance of those habitats and recreational areas.
Section 30230 of the California Coastal Act.
Marine resources shall be maintained, enhanced, and where feasible, restored. Special protection
shall be given to areas and species of special biological or economical significance. Use of the
marine environment shall be carried out In a manner that will sustain the biological productivity of
coastal waters and that will maintain healthy populations of all species of marine organisms
adequate for long-term commercial, recreational, sclentiric, and educational purposes.
Section 1580 et seq. of the Fish & Game Code
1580. The Legislature hereby declares that the policy of the state is to protect threatened or
endangered native plants, wildlife, oraquatic organisms or specialized habitat types, both
terrestrial and nonmadne aquatic, or large heterogeneous natural gene pools for the future use
of mankind through the establishment of ecological reserves. For the purpose of establishing
those ecological reserves, the department, with the approval of the commission, may obtain,
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accept on behalf of the state, acquire, or control, by purchase, lease, easement, gift, rental,
memorandum of understanding, or otherwise, and occupy, develop, maintain, use, and
administer land, or land and nonmarine water, or land and nonmarine water rights, suitable for
the purpose of establishing ecological reserves. Any property obtained, accepted, acquired, or
controlled by the department pursuant to this article may be designated by the commission as
an ecological reserve. The commission may adopt regulations for the occupation, utilization,
operation, protection, enhancement, maintenance, and administration of ecological reserves.
The ecological reserves shall not be classified as wildlife management areas pursuant to
Section 1504 and shall be exempt from Section 1504.
1581. Any property acquired in fee for ecological reserves shall be acquired in the name of the
state, and shall, at all times, be subject to such rules and regulations as may be prescribed from
time to time.by the commission for the occupation, use, operation, protection, and administration
of such property as ecological reserves.
1582. The department shall do all things necessary to secure a valid title in the state to the
property acquired in fee for ecological reserves but no payment shall be made therefor until the
title is vested in and satisfactory to the state. No such land will be acquired by eminent domain.
1583. Except in accordance with the regulations of the commission it is unlawful to enter upon
any ecological reserves established under the provisions of this article, or to take therein any
bird or the nest or eggs thereof, or any mammal, fish, mollusks, crustaceans, amphibia, reptiles
or any other form of plant or animal life.
1584. As used in this article, "ecological reserve" means land or land and water areas that are
designated as an ecological reserve by the commission pursuant to Section 1580 and that are
to be preserved in a natural condition, or which are to be provided some level of protection as
determined by the commission, for the benefit of the general public to observe native flora and
fauna and for scientific study or research.
1585. Notwithstanding Section 1580, which sets forth the primary purposes of ecological
reserves, the department may construct facilities and conduct programs in ecological reserves it
selects to provide natural history education and recreation if those facilities and. programs are
compatible with the protection of the biological resources of the reserve. As provided in
Sections 1764 and 1765, the department may control access, use, and collect fees for selected
ecological reserves.
1586. The Upper Newport Bay Ecological Reserve Maintenance and Preservation Fund is
hereby created in the State Treasury. Notwithstanding Section 13340 of the Government Code,
the money in the fund is continuously appropriated, without regard to fiscal years, to the
department for purposes related to the maintenance and preservation of the Upper Newport Bay
Ecological Reserve.
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Section 630, Title 14, California Code of Regulations
Chapter 11.
Ecological Reserves
§630. Ecological Reserves.
The areas specified In this chapter have been declared by the Fish and Game Commission to
be ecological reserves. A legal description of the boundaries of each ecological reserve is on file
atthe department's headquarters, 1416 Ninth Street, Sacramento. Ecological reserves are
established to provide protection for rare, threatened or endangered native plants, wildlife,
aquatic organism and specialized terrestrial or aquatic habitat types. Public entry and use of
ecological reserves shall be compatible with the primary purposes of such reserves, and subject
to the following applicable general rules and regulations, except as otherwise provided for in the
special area regulations.
(a) General Rules and Regulations:
(1) Protection of Resources. No person shall mine or disturb geological formations or
archeological artifacts or take or disturb any bird or nest, or eggs thereof, or any plant, mammal,
fish, mollusk, crustacean, amphibian, reptile, or any other form of plant or animal life In an
ecological reserve except as provided In subsections 630(a)(2) and (a)(8). The department may
implement enhancement and protective measures to assure proper utilization and maintenance
of ecological reserves.
(2) Fishing. Fishing shall be allowed In accordance with the general fishing regulations of the
commission except that the method of taking fish shall be limited to angling from shore. No
person shall take fish for commercial purposes In any ecological reserve except by permit from
the commission.
(3) Collecting. No collecting shall be done in an ecological reserve except by permit issued
pursuant to section 650 of these regulations. Any person applying fora permit must have a valid
scientific collecting permit issued pursuant to part 3 of this title.
(4) Motor Vehicles. No person shall drive, operate, leave, or stop any motor vehicle, bicycle,
tractor, or other type of vehicle in an ecological reserve except on designated access roads and
parking areas.
(5) Swimming. No person shall swim, wade, dive, or use any diving equipment within an
ecological reserve except as authorized under the terms of a permit Issued pursuant to
subsection (3).
(6) Boating. No person shall launch or operate a boat or other floating device within an
ecological reserve except by permit from the commission.
(7) Trails. The department may designate areas within an ecological reserve where added
protection of plant or animal life Is desirable, and may establish equestrian or walking trails or
paths within such designated areas. No person shall walk or ride horseback in such areas
except upon the established trails or paths.
(8) Firearms. No person shall fire or discharge any firearm, bow and arrow, air or gas gun, spear
gun, or any other weapon of any kind within or into an ecological reserve or possess such
weapons within an ecological reserve, except law enforcement personnel and as provided for in
individual area regulations that allowfor hunting.
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(9) Ejection. Employees of the department may eject any person from an ecological reserve for
violation of any of these rules or regulations or for any reason when it appears that the general
safety or welfare of the ecological reserve or persons thereon is endangered.
(10) Public Entry. Public entry may be restricted on any area at the discretion of the department
to protect the wildlife, aquatic life, or habitat. No person, except state and local law enforcement
officers, fire suppression agencies and employees of the department in the performance of their
official duties or persons possessing written permission from the department, may enter any
ecological reserve, or portion thereof, which is closed to public entry. No person may enter any
Ecological Reserve between sunset and sunrise except with written permission from the
Department, which may be granted for purposes including night fishing in accordance with
subsection (a)(2) from designated shore areas only.
A $2.00 day use pass or a valid $10.00 annual wildlife pass is required of all users of Elkhorn
Slough and Upper Newport Bay ecological reserves excepffor users that possess a valid
California sport fishing license hunting license or trapping license, or users that are under 16
years of age or users that are part of an organized youth or school group and having free
permits issued by the appropriate regional office. Refer to subsection 550(b)(16)(B), Title 14,
CCR, for regulations for fee requirements for wildlife areas.
(11) Introduction of Species. Unless authorized by the commission, the.release of any fish or
wildlife species, including domestic or domesticated species, or the introduction of any plant
species, is prohibited. The department may reintroduce endemic species on ecological reserves
for management purposes.
(12) Feeding of Wildlife. The feeding of wildlife is prohibited.
(13) Pesticides. The use of pesticides is prohibited on any ecological reserve unless authorized
by the commission with the exception that the department may use pesticides for management
purposes and for public safety.
(14) Litter. No person shall deposit, drop, or scatter any debris on any ecological reserve except
in a receptacle or area designated for that purpose. Where no designated receptacles are
provided, any refuse resulting from a person's use of an area must be removed from that area
by such person.
(15) Grazing. The grazing of livestock is prohibited on any ecological reserve.
(16) Falconry. Falconry is prohibited.
(17) Aircraft. No person shall operate any aircraft or hovercraft within a reserve, except as
authorized by a permit from the commission.
(18) Pets. Pets, including dogs and cats, are prohibited from entering reserves unless they are
retained on a leash of less than ten feet or are inside a motor vehicle, except as provided for in
individual area regulations that allow for hunting or training activities.
(19) Fires. No person shall light fireworks or other explosive or incendiary devices, or start or
maintain any fire on or in any reserve, except for management purposes as provided in
subsection (a)(1).
(20) Camping. No person shall camp onrn any ecological reserve.
(21) Vandalism. No person shall tamper with, damage or remove any property not his own when
such property is located within an ecological reserve.
(b) Areas and Special Regulations for Use:
115 Upper Newport Bay Ecological Reserve, Orange County.
(A) Fishing shall be permitted from boats. Fishing is also permitted from shore in designated
areas. Clamming or wading is not permitted.
(B) Swimming is permitted only in that area bayward from North Star Beach to mid -channel.
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(C) Boating Is limited to non -motorized craft, with the exception of law enforcement, emergency,
and department vessels and authorized operators under permit from the regional manager.
Boating shall occur in designated areas only and is limited to five miles per hour.
(D) No person shall walk, or ride horseback except on established trails, paths, or other
designated areas.
(E) The County of Orange may carry out management activities for fish and wildlife, flood
control and vector control. Authorized operation and maintenance activities shall Include, but
shall not be limited to, use of chemicals, vegetation control, dater control and use of associated
equipment.
Existing Habitats and Wildlife. The proposed facility improvements on Shellmaker Island
would be located on non -tidal, disturbed dredge spoils at elevations between approximately +9
to +17 ft MLLW and include temporary State and County facilities, the UCI Rowing Facility and
discarded materials from buildings removed from the site. There are no sensitive species of
plants within these areas and the flora consists of Invasive and ruderal (i.e., weedy) plants
communities and ornamental shrubs and trees.
Salt marsh and mudflats at elevations between —2 and +7 ft MLLW surround the proposed
construction site on the east (behind the UCI Rowing Facility), the south (on the Dunes Marina
Access Channel), and the west (Main Channel of Upper Newport Bay). Cordgrass (Spartina
foliose) and pickleweed (Salicornla spp.) are the dominant species occurring within the marsh.
These habitats encompass approximately 5.6 acres of wetland habitat.
Endangered Species. Two endangered species are known to occur within these peripheral
wetland habitats -- the state and federally listed Salt marsh bird's beak (Cordylanthus maritimus
sub species maritimus) and the state -listed Belding's savannah sparrow (Passerculus
sandwichensis beldingl). During focused surveys conducted in 2002 only one pair of potentially
breeding Belding's savannah sparrows was observed in the Lower Shellmaker Island salt marsh
bordering the Dunes Marina Access Channel. No savannah sparrows were observed during
2003 (Keane Biological Consulting, 2002 and 2003, Brian Shelton, pars. com with K. Keane,
Keane Biological Consulting). No light-footed clapper rail (Rallus longirostris lev/pes) were
observed within the project area. They are present however, in the salt marsh north east of the
project area on Shellmaker Island and along the shoreline of Back Bay Drive.
The distribution of salt marsh bird's beak nearby the project area In Lower Shellmaker Marsh
habitat as of summer 2002 is shown in Exhibit C4V.2. It also is found extensively north of the
proposed BBSC construction site on Lower and Upper Shelimaker Island at higher wetland and
transitional elevations. Keane Biological Consulting's Belding savannah sparrow focused
survey report is Included in Appendix 1.
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EXHIBIT C-IV.2
LOCATION OF GELDING'S SAVANNAH SPARROW SIGHTING AND SALT MARSH BIRD'S
BEAK NEARBY THE PROPOSED BACK BAY SCIENCE CENTER'
a
Facility Location and Infrastructure. The proposed project would removed existing temporary
structures, grade pads for the facilities, renovate existing educational areas, amphitheatre, and
native plant nursery sites, and construct new facilities, a parking lot, and, site infrastructure.
Trucks, dozers, and graders will be used for this effort. Currently, there are approximately 2.3
acres of disturbed, non -tidal habitat on the site that will be renovated. No direct impacts to
natural habitats, sensitive resources, or endangered species within the footprint of the proposed
facilities.
The proposed widening of the access road' to 20 feet will potentially result in a loss of
transitional vegetation at elevations between +7 and +9 ft MLLW between the access road and
the edge of the wetland located north of the access road. The proposed access road may
encroach three feet into the habitat area, resulting in the loss of 780 square feet of transitional
and disturbed high marsh habitat consisting of salt grass, alkali heath, and non-native grasses
such as red brome. If not mitigated, the loss of this habitat would be a localized significant
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impact to biological resources. To compensate for the loss of this habitat, a salt marsh
mitigation site will be established in the area currently used as a bike storage area near the
entrance gate (Exhibit 2) and the bike storage area will be relocated. Approximately 1,000
square feet of area will be revegetated with high salt marsh plants to compensate for the
potential loss of 780 square feet of transitional and disturbed high marsh habitat (4 to 1
mitigation ratio). The remaining 2,120 square feet will be mitigated within the proposed salt
marsh demonstration area (see Table IV-1).
Table IV-1
Impact and Mitigation Summary
Impact area
Mitigation area @ 4:1 ratio
780 s .ft (Entry road
1,000 s .ft. Bike rack area
2,120 s .ft. Demonstration marsh
3,120 s .ft. Total
area
Construction Impacts. Short-term construction Impacts include increased noise, dust, and
human disturbances on the project site, and to nearby sensitive wetland habitats and resources.
These Impacts are potentially significant, short-term Impacts but will be reduced to less than
significant by implementing the following Best Management Practices (BMPs).
Construction activities will avoid salt marsh bird's beak. All precautions will be taken to protect
the plants from disturbances and any Incidental take of this endangered species, including, but
not limited to signage and physical barriers.
An on -site storm and gray water runoff system from the building and parking area to a
freshwater pond with filtering plants will be constructed. The locations of the filtration ponds are
shown in Exhibit A: 1.1. The locations of the proposed ponds are currently at non -tidal
elevations and are not within areas where the endangered salt marsh bird's beak is located.
Best Management Practices will be Implemented to ensure that secondary construction -related
Impacts to biological resources of the wetlands are minimized during construction. Therefore,
there will be no significant adverse Impacts on Shellmaker Island biological resources due to
construction of the filtration ponds..
There will be no significant long-term adverse effects of the siting of the facilities and the
associated infrastructure on the adjacent sensitive biological habitats and resources. No
sensitive bird species have been documented to breed within the project area. Additionally,
there Is no waterside construction activity proposed, therefore no temporal construction
limitations or mitigation measures are required. Shading effects from structures have been
addressed in the building designs and there will be no Increase in shading of wetland plants or
coastal sage scrub habitat that would result in a decrease in plant productivity.
The long-term Implementation of the proposed storm water and gray water biofiltration system
will have a beneficial Impact on Upper Newport Bay wetland resources because it will result In a
higher quality of storm water runoff to the waters of Upper Newport Bay compared to current
storm water quality.
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Marsh Demonstration Project. A salt marsh demonstration project is proposed as part of the
science and educational program. The purpose is to provide students with a hands-on
educational opportunity to observe and take part in restoring marsh habitat to Upper Newport
Bay.
The location of the salt marsh demonstration project is shown in Exhibit A-2.1. Currently, the
site is located on dredge spoil material at non -tidal elevations and is colonized by invasive and
ornamental plants, shrubs and trees. The footprint of the proposed marsh demonstration area
is approximately 10,000 square feet.
Construction impacts will include (1) removal of non-native shrubs, trees, bushes, and disturbed
habitat, and (2) regrading supra -tidal elevations to tidal elevations between 0.0 and +7 ft MLLW.
Trucks, dozers, graders, and hand -methods will be used for this effort. Approximately 1/4 of the
site will be left alone to be colonized naturally by marsh plants. The other half will be replanted
with native marsh plants by students and used as an outdoor science laboratory under
supervision of the Department of Fish and Game with a Department of Fish and Game
approved design.
Short-term construction impacts include increased noise levels, emissions, dust, and human
disturbances to nearby sensitive wetland habitats and resources on the south side of
Shellmaker Island. These impacts are potentially significant, short-term impacts but will be
reduced to insignificant levels by implementing BMPs. A net gain of wetlands will occur with the
marsh demonstration project. The long term benefit of additional, created habitat and the
educational experience it will provide will outweigh the short-term construction impacts.
There is also a potential to physically degrade existing salt marsh habitat on the seaward and
west side of the proposed marsh demonstration site. Appropriate precautions will be taken to
protect salt marsh habitat from disturbances and the incidental take of the salt marsh bird's beak
including, but not limited to, signage and physical barriers and routing construction equipment
away from sensitive habitats. Damage to salt marsh habitat during construction will also be
avoided by having biological monitors on site to assist construction crews in identifying sensitive
habitats and avoiding them. Any degradation to existing salt marsh habitat will be restored as
part of the project. In addition, the project will provide an excess of 8,000 sq. ft. of created
marsh habitat.
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The construction of the marsh demonstration area will have a long-term beneficial impact on
wetland resources. It will create approximately 10,000 square feet of wetland habitat vegetated
by natural and transplanting methods and will result in the removal of Invasive and ornamental
species of plants, shrubs, and trees.
Trails. The existing trail system will be formalized with marked, designated trails that will link
educational activities to the wetlands and restoration activities. There will be several spur trails
leading to small observation/teaching areas that will be placed around the perimeter of the
wetlands at which students will participate in focused activities. The designated trail areas will
not encroach on salt marsh habitat or sensitive species, but will be strategically located for
student science activities. Both DFG and the coastal Commission are developing curricula that
will be used on site. Trails will lead down to mudflats. The renovation of existing trails and the
construction of the teaching pods will not require large construction equipment that could
potentially cause short-term or long-term construction impacts on wetlands and terrestrial
vegetation in the vicinity of where trails and/or pods will be constructed. Impacts to habitats in
the vicinity of existing trails will be minimized by using hand methods or other suitable means of
clearing and trail building. The observational areas will not be placed within wetland habitats.
This will avoid potential short-term and long-term construction impacts to wetland resources.
Buffers. Buffers will be used to assist in minimizing potential long-term, direct and indirect
disturbances to wetland vegetation and wildlife. Historically, there has not been any distinct
buffer between the buildings and the wetlands. Despite this, wetland habitat has expanded, as
have endangered plant populations. Given the environmental and educational goals of the
program, the width of setbacks and buffers to wetlands will vary depending upon type of use.
Widest buffers (50 feet) will be set around the perimeters that separate buildings and
service/delivery areas from wetland area. Sand dune buffers consisting of elevated, sandy soils
will be constructed and then revegetated with dune plants. These berms will be used to buffer
highly sensitive salt marsh bird's beak stands from public Intrusion along the southern perimeter
of the buildings. The berms however, would not impede the views of students or other visitors
using the educational trails. The proposed elevation of the undulating dune berm would vary
between 3 and 5 feet high and the footprint of the berm would be approximately 15 ft wide.
Narrower buffers will be placed around less sensitive areas and will be used as educational
trails. Trails and walkways are acceptable uses of buffer habitat under Coastal Commission
guidelines. The proposed educational trail is consistent with the purpose for which the Reserve
was acquired. Signage will also be used to Identify restricted areas to visitors.
The construction of buffer areas will not result in a reduction or loss of wetland or upland habitat
on Shellmaker Island. Potential secondary Impacts to wetland resources during the
construction will be mitigated through the implementation of BMPs. In the long-term, the
creation of buffer habitat at the project site will be a beneficial Impact to project area's wetland
and wildlife resources.
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Project Design Features and Standard Conditions
PDF IV-1
New buildings and infrastructure would be located in order to minimize impacts on
sensitive biological resources. The entry road has been designed at the minimum width
necessary to provide safe vehicular access to the site while minimizing impacts to
habitat.
PDF IV-2
To compensate for the loss of this habitat caused by widening of the access road, the
site plan has been designed to include a salt marsh mitigation site in the area currently
used as a bike storage area near the entrance gate. Approximately 3, 120 square feet
of area will be revegetated with high salt marsh plants to compensate for the potential
loss of 780 square feet of transitional and high marsh habitat (4 to 1 mitigation ratio).
Prior to issuance of a grading permit, the access road and salt marsh mitigation plans
shall be submitted to the California Department of Fish and Game and USFWS for
approval.
PDF 1V--3
The trail system has been designed so as to avoid encroaching on salt marsh habitat or
sensitive species, but will be strategically located for student science activities.
PDF IV-4
Berms and buffer zones up to 50 feet wide have been designed in the site plan to protect
sensitive habitat areas and wildlife from human activity areas.
Mitigation Measures
MM IV-1
Trail improvements shall be conducted using the least environmentally damaging
methods. A qualified botanist shall be present to ensure that any trail construction
activity does not result in the degradation of wetland habitat or vegetation.
MM IV-2
A pre -construction focused survey for Beldings savannah sparrows shall be conducted
during the breeding season to determine if breeding activity is occurring. If it is
determined that any Belding savannah sparrows are exhibiting breeding behavior within
100 feet of the project site then the biological monitor, in consultation with California
Department of Fish and Game and the U.S Fish and Wildlife Service, shall determine if
construction activity should be halted until the breeding season (March to September)
has been completed.
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MM IV-3
A qualified biologist shall be onsite during grading and trenching activities. The biologist
will ensure that sensitive biological resources, Including rare, threatened, and
endangered species, are not adversely affected by the project construction activities.
Vehicular and construction personnel foot traffic shall not Impinge on coastal sage scrub,
salt marsh, mudflat, or bay environments. "No Entrance" signage and barriers will be
erected to prohibit Intrusions Into sensitive habitats.
MM IV-4
Losses of salt marsh vegetation shall be mitigated on site. A mitigation plan for any
losses of salt marsh habitat shall be prepared and approved by the Department of Fish
and Game and USFWS prior to Issuance of a grading or building permit. The mitigation
plan shall identify the site to be restored, a palette of species to be replanted, planting
techniques, and a rive year monitoring plan to ensure that losses of salt marsh habitat
are fully mitigated. The loss of salt marsh habitat shall be mitigated at a ratio of not less
than 4 to 1.
These design features and mitigation measures would reduce potential impacts to a level that Is
less than significant.
b) Have a substantial adverse effect on any riparian habitat or other sensitive natural
community identified in local or regional plans, policies, regulations, or by the California
Department of Fish and Game or U.S. Fish and Wildlife Service?
Less Than Significant With Mitigation. See Section IV.a. above. No additional mitigation
Is necessary.
c) Have a substantial adverse effect on federally protected wetlands as defined by
Section 404 of the Clean Water Act (including, but not limited to, marsh, vernal pool,
coastal, etc.) through direct removal, filling, hydrological interruption, or other means?
Less Than Significant With Mitigation. See Section IV.a. above. No additional mitigation
Is necessary.
d) Interfere substantially with the movement of any native resident or migratory fish
or wildlife species or with established native resident or migratory wildlife corridors, or
Impede the use of native wildlife nursery sites?
No Impact. See Section IV.a. above. No additional mitigation is necessary.
e) Conflict with any local policies or ordinances protecting biological resources,
such as a tree preservation policy or ordinance?
No Impact. There are no applicable local biological ordinances or policies. No
mitigation measures are necessary.
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f) Conflict with the provisions of an adopted Habitat Conservation Plan, Natural
Community Conservation Plan, or other approved local, regional, or state habitat
conservation plan?
Less Than Significant Impact. A Natural Community Conservation Planning/Habitat
Conservation Plan (NCCP/HCP) for the Central/Coastal Orange County area was approved by
the Orange County Board of Supervisors on April 16, 1996 and by the California Department of
Fish and Game and the US Fish and Wildlife Service on July 17, 1996. The project site is
included within the NCCP area but is not located within the Reserve Area. Orange County's
NCCP Program is now administered by the Nature Reserve of Orange County. Since the site is
not within the Reserve Area, the Nature Reserve has no approval authority over the project.
The educational aspects of the proposed project will support the goals of the NCCP program.
No mitigation measures are required.
V. CULTURAL RESOURCES
Would the project:
a) Cause a substantial adverse change in the significance of a historical resource as
defined in §15064.5?
No Impact. Neither the site nor any of the current structures are considered to be a
historically sensitive resource. No mitigation measures are necessary.
b) Cause a substantial adverse change in the significance of an archaeological
resource pursuant to § 15064.57
No Impact. Since Shellmaker Island is comprised of dredge material and bay sands,
there is virtually no potential for archaeological resources to be disturbed by the project. No
mitigation measures are necessary.
c) Directly or indirectly destroy a unique paleontological resource or site or unique
geologic feature?
No Impact. Since Shellmaker Island is comprised of dredge material and bay sands,
there is virtually no potential for paleontological resources to be disturbed by the project. No
mitigation measures are necessary.
d) Disturb any human remains, including those interred outside of formal
cemeteries?
No Impact. Since Shellmaker Island is comprised of dredge material and bay sands,
there is virtually no potential for human remains to be disturbed by the project. No mitigation
measures are necessary.
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VI. GEOLOGY AND SOILS
The following discussion is based on the Geotechnical Report for the Proposed Shelimaker
Island Development. City of Newport Beach, California, June 25, 2002 prepared by Leighton
and Associates. A complete copy of the report is available for review at the City of Newport
Beach Public Works Department.
Would the project:
a) Expose people or structures to potential substantial adverse effects, Including the
risk of loss, injury, or death involving:
1) Rupture of a known earthquake fault, as delineated on the most recent
Alquist-Prfolo Earthquake Fault Zoning map, Issued by the State Geologist
for the area or based on other substantial evidence of a known fault? Refer
to Division of Mines and Geology Special Publication 42.
Less Than Significant Impact With Mitigation. According to the geotechnical
report, there are no known major or active earthquake faults mapped at the site,
and the site is not located in an Alquist-Prlolo zone. The closest active mapped
segment of the Newport -Inglewood Fault is located approximately 4.9 km
westtnorthwest of the site.
Like many areas of Southern California, the site would experience groundshaking
during a seismic event in the area. The following mitigation measures would
reduce this Impact to a level that is less than significant.
Mitigation Measures
MM Vl-1
A. Prior to Issuance of a grading permit, the applicant or successor In
Interest shall demonstrate to the Department of Fish and Game or its
designee that all facilities will be designed and constructed as specified in
the Uniform Building Code.
B. Development of the site shall be subject to a grading permit to be
approved by the Department of Fish and Game or its designee. The
application for grading permit shall be accompanied by a grading plan
and specifications and supporting data consisting of solid engineering and
engineering geology reports or other reports required by the building
offlcial.
C. Prior to the issuance of any building permits a specific soils and
foundation study shall be prepared and approved by the Department of
Fish and Game or Its designee.
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ii) Strong seismic ground shaking?
Less Than Significant Impact With Mitigation. See item VI.a.i, above.
III) Seismic related ground failure, including liquefaction?
Less Than Significant Impact With Mitigation. Liquefaction is a phenomenon in
which earthquake -induced cyclic stresses generate excess pore water pressure
in low density, saturated, sandy soils and soft silts below the water table. This
causes a loss of shear strength and, in many cases, ground settlement.
Liquefaction is generally considered to be a problem in earthquake -prone areas
where conditions that promote liquefaction are present in the upper 50 feet of
earth.
Existing groundwater at the project site was measured at a depth of 5-7 feet
below ground surface (bgs). The site is indicated as potentially liquefiable on the
Seismic Hazards Zone Maps (Greenwood and Pridmore, 2001). Based on these
conditions, the liquefaction potential of the site is considered to be very high. if
not mitigated, these conditions could result in major damage to the structure
during a strong earthquake. Appropriate design of the building foundations and
structural systems as required by Mitigation Measure VIA would reduce potential
impacts to a level that is less than significant.
IV) Landslides?
Less Than Significant Impact. The project site contains no significant slope
areas. The standard requirements identified in Section VI.a, above, will ensure
that grading and construction will be done in a manner that reduces this potential
impact to a level that is less than significant. No further mitigation is necessary.
b) Result in substantial soil erosion or the loss of topsoil?
Less Than Significant Impact With Mitigation. Soil erosion can occur naturally, and may
be accelerated during grading and construction when vegetation cover is removed and
bare soil is disturbed. The following mitigation measures would reduce this impact to a
level that is less than significant:
Mitigation Measures
MM V1-2
Prior to issuance of a grading permit an Erosion Control Plan shall be prepared
and submitted to the Department of Fish and Game or its designee for approval.
The plan shall identify methods to prevent and control potential grading -
associated erosion from discharging into Newport Bay. Proposed actions should
include erosion control methods to reduce the potential for windblown topsoil or
waterborne sediments to reach the Bay including sand bags, wind screens,
watering down of dry soils, and implementing other accepted Best Management
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Practices (BMPs) during the grading process. implementation and compliance
shall be monitored by the project construction monitor.
c) Be located on a geologic unit or soil that Is unstable, or that would become
unstable as a result of the project, and potentially result in on- or off -site landslide,
lateral spreading, subsidence, liquefaction or collapse?
Less Than Significant Impact With. Mitigation. The site is considered to have a very high
liquefaction potential. The mitigation measures described in Section VI.a, above, will ensure
that this project complies with applicable engineering standards and that potential impacts are
reduced to a level that is less than significant. No additional mitigation measures are required.
d) Be located on expansive soil, as defined in Table 18.1.8 of the Uniform Building
Code (1994), creating substantial risks to life or property?
Less Than Significant Impact. Expansive soils are generally high in clay content.
According to the Leighton report, soils in the project area are considered to have a low
expansion potential. No mitigation measures are required.
e) Have soils incapable of adequately supporting the use of septic tanks or
alternative waste water disposal systems where sewers are not available for the disposal
of waste water?
No Impact. The project would not involve the use of septic tanks. All wastewater is
proposed to be conveyed off -site via connections to the public sanitary sewer system. No
mitigation measures are necessary.
"VII. HAZARDS AND HAZARDOUS MATERIALS
Would the project:
a) Create a significant hazard to the public or the environment through the routine
transport, use or disposal of hazardous materials?
No Impact. No routine use, transport or disposal of hazardous materials Is proposed in
connection with the operation of the project. No mitigation measures are necessary.
b) Create a significant hazard to the public or the environment through reasonable
foreseeable upset and accident conditions involving the release of hazardous materials
Into the environment?
Less Than Sicnlflcant Impact. During construction, gasoline- and dlesel-powered
equipment would be used. In the event of an accident, gasoline or diesel fuel could be spilled.
Standard construction contract provisions would require that the contractor follow site
maintenance and spill cleanup procedures as described in the Standard Specifications for
Public Works Construction (the "Greenbook"). No additional mitigation measures are
necessary.
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c) Emit hazardous emissions or handle hazardous or acutely hazardous materials,
substances, or waste within one -quarter mile of an existing or proposed school?
No Impact. The project is not located within 1/4 mile of a school. The nearest schools
are Newport Harbor High School (approximately 1 mile west) and Corona del Mar High School
(approximately 1 mile north). No mitigation measures are necessary.
d) Be located on a site which is 'included on a list of hazardous materials sites
compiled pursuant to Government Code Section 65962.5 and, as a result, would it create
a significant hazard to the public or the environment?
No Impact. The project site is not included on any list of hazardous materials sites. No
mitigation measures are necessary.
e) For a project located within an airport land use plan or, where such a plan has not
been adopted, within two miles or a public airport or public use airport, would the project
result in a safety hazard for people residing or working in the project area?
No Impact. The project site is not located within 2 miles of an airport. The nearest
airport (John Wayne) is approximately 3 miles north of the site. The project site is near the flight
corridor of John Wayne Airport but is not within any hazard zone. No mitigation measures are
necessary.
f) For a project within the vicinity of a private airstrip, would the project result in a
safety hazard for people residing or working in the project area?
No Impact. There are no private airstrips within the project vicinity. No mitigation
measures are necessary.
g) Impair implementation of or physically interfere with an adopted emergency
response plan or emergency evacuation plan?
Less Than Significant Impact With Mitigation. The proposed project would have no
effect on any emergency response or emergency evacuation plan or procedures. Emergency
evacuation routes could be affected during construction, however, due to temporary street or
lane closures. The following mitigation measure would reduce this impact to a level that is less
than significant.
Mitigation Measures
MM Vll-1
Prior to award of a construction contract or issuance of a grading permit, a traffic
control plan meeting the approval of the Department of Fish and Game or its
designee shall be prepared. The plan shall specify what measures shall be
taken to minimize travel disruptions and safety hazards, including safety of
pedestrians and bicyclists, minimize inconveniences to residents and
businesses, minimize the loss of parking, and ensure adequate emergency
access at all times. The plan shall include haul routes and restrictions for soil
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export, if required. The traffic control plan shall be incorporated Into the contract
specifications and shall be enforced by the construction Inspector.
h) Expose people or structures to a significant risk of loss, Injury or death involving
wildiand fires, including where wildlands are adjacent to urbanized areas or where
residences are intermixed with wildlands?
No Impact. The project site is surrounded by urban development, and no wildland
Interface exists. No mitigation measures are necessary.
Vill, HYDROLOGY AND WATER QUALITY
As part of the educational interpretive program, a wetland demonstration project will be
designed and implemented for Shellmaker Island. This demonstration project will serve as a
teaching and research tool to: (1) introduce students to wetland biology and ecological
principals, (2) provide an opportunity for students and researchers to conduct research on the
short-term and long-term restoration potential of Newport Bay wetlands, and (3) increase the
public's awareness of the value of Southern California wetlands.
In addition, the wetland demonstration project will integrate state-of-the-art water quality best
management practices for the management of onsite stormwater and dry weather runoff from
impervious areas of the building site.
As a method to Improve the quality of stormwater and dry weather runoff from the grounds of
the Back Bay Science Center, drainage from Impervious areas on the grounds, facilities, and
parking lot will be filtered through a series of blofilters and sediment basins and discharged
around the perimeters of Lower Shellmaker Island. The purposes of this feature are to (1)
Improve site water quality runoff at the Back Bay Center site, (2) integrate the design of the
demonstration marsh with water quality enhancement features, and (3) aid in the teaching of
water quality management principals with real -world wetland enhancement programs.
Features included in the design include:
• Catch basins and bioretention planting strips that will filter site runoff from facilities,
parking lots and roadways. Catch basins will remove some of the sediments and
oil/grease constituents prior to entering bioretention strips. The bioretention planting
strips filters will enhance the removal of macronutrients such as phosphorous and
can also in reducing irrigation requirements.
Stormwater detention basin(s) or "water quality enhancement ponds" that can be
used around the perimeter of the natural marsh and the demonstration salt marsh,
where appropriate, to (1) serve as a method to provide additional filtering of site
runoff and (2) provide additional wetland demonstration activities In the use of
retaining ponds as seasonal freshwater wetlands. The site runoff, once filtered, can
also be used to provide fresh -water required for salt marsh plant seed germination.
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' Would the project:
' a) Violate any water quality standards or waste discharge requirements?
Less Than Significant Impact With Mitigation. The project site is located within Upper
' Newport Bay Ecological Reserve and is adjacent to sensitive areas. Contaminants such as oil
and grease, fertilizers, pesticides, and animal waste typically accumulate on ground surfaces
and are then washed into storm drains and waterways by irrigation or rainfall. Construction
activities could also temporarily increase the amount of soil erosion and siltation in the bay. In
order to reduce the level of contaminants leaving the property, the project has been designed to
include a stormwater detention basin and water filtration system. The purpose of this detention
' basin is to hold the initial flush of stormwater, which typically contains the highest level of
contaminants, so that these pollutants can be trapped and filtered as the water percolates into
the ground. This project design feature will substantially reduce the amount of contaminants
' leaving the site. In addition, preparation and implementation of an erosion control plan will be
required to minimize runoff of contaminants into the bay during construction.
Long-term effects on water quality are anticipated to be beneficial with the operation of the
' proposed storm water and gray water filtration system. Currently, there is no filtration or treatment
of runoff from the site. The proposed system will discharge low volumes of less toxic waters to
Newport Bay compared to existing conditions on Shellmaker Island.
Project Design Features and Standard Conditions
' PDF V111-1
The site plan has been designed to include a stormwater retention basin and filtration
system to minimize the release of pollutants into Upper Newport Bay. Prior to the
issuance of grading permits, the Department of Fish and Game or its designee shall
' verify that the proposed stormwater retention basin and filtration system have been
incorporated into the project plans.
Mitigation Measures
MM Vlll-1
Prior to issuance of any grading permit, an erosion, siltation and dust control plan shall
be submitted and be subject to the approval of the Department of Fish and Game or its
designee.
' MM V111-2
1
U
n
Prior to issuance of a grading or building permit, a Storm Water Management Plan shall be
prepared in coordination with the Erosion Control Plan to identify methods to reduce
construction period storm water runoff to Upper Newport Bay. The project construction
monitor will ensure that the BMPs contained within the SWMP are fully implemented and
complied with. Accumulated debris shall be removed following major storm events.
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MM Vlll-3
Construction debris and trash shall not be discharged to Newport gay. Plans and
specifications shall Include requirements for all construction debris to be removed form the
site and disposed of at an approved landfill.
These mitigation measures would reduce potential impacts to a level that is less than significant.
b) Substantially deplete groundwater supplies or interfere substantially with
groundwater recharge, such that there would be a net deficit In aquifer volume or a
lowering of the local groundwater table level (e.g., the production rate of pre-existing
nearby wells would drop to a level which would not support existing land uses or
planned uses for which permits have been granted)?
No impact. The project would have no effect on groundwater supplies or recharge.
Runoff from the project area currently flows into Upper Newport Bay or Newport Harbor via
storm drains or surface drainage. No mitigation measures are necessary.
c) Substantially alter the existing drainage pattern of the site or area, Including
through the alteration of the course of a stream or river, in a manner which would result
In substantial erosion or siltation on- or off -site?
Less Than Significant Impact. See Section Vlll.a. No stream courses are located on the
site. No additional mitigation measures are necessary.
d) Substantially alter the existing drainage pattern of the site or area, Including
through the alteration of the course of a stream or river, or substantially Increase the rate
or amount of surface runoff in a manner, which would result in flooding on. or off -site?
Less Than Significant Impact. No increase in runoff would be expected from the project
site. Surface runoff would be expected to decrease due to the incorporation of a stormwater
retention basin and filtration system. As discussed in Section Vlli.a, above, the detention basin
Incorporated In the project design would substantially reduce the amount of runoff leaving the
site. No additional mitigation measures are necessary.
e) Create or contribute runoff water which would exceed the capacity of existing or
planned stormwater drainage systems or provide substantial additional sources of
polluted runoff?
Less Than Significant Impact With Mitigation. See Sections Vlll.a and VIIIA, above. No
additional mitigation measures are necessary.
f) Otherwise substantially degrade water quality?
Less Than Significant Impact With Mitigation. See Sections Vili.a and VIIIA, above.
There are no other known impacts to water quality. No additional mitigation measures are
necessary.
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'1
g) Place housing within a 100-year flood hazard area as mapped on a federal Flood
Hazard Boundary of Flood Insurance Rate Map or other flood hazard delineation map?
No Impact. The site is not within a 100-year flood hazard area and no housing is
proposed as part of the project. No mitigation measures are necessary.
h) Place within a 100-year flood hazard area structures, which would impede or
redirect flood flows?
No Impact. The site is not within a 100-year flood hazard area. No mitigation measures
are necessary.
i) Expose people or structures to a significant risk of loss, injury or death involving
flooding, including flooding as a result of the failure of a levee or dam?
No Impact. The project is not located in a flood hazard area, is not near a levee or dam
and would not expose additional people or structures to flood hazards. No mitigation measures
are necessary.
j) Inundation by seiche, tsunami, or mudflow?
No Impact. The site is not located in an area that is subject to seiche or tsunami.
(CIOSA EIR p. 293). No mitigation measures are necessary.
IX. LAND USE AND PLANNING
Would the project:
a) Physically divide an established community?
No Impact. The site is currently used for the same general purpose as the proposed
project. The project would have no effect on the established community. No mitigation
measures are necessary.
b) Conflict with any applicable land use plan, policy, or regulation of an agency with
jurisdiction over the project (including, but not limited to the general plan, specific plan,
local coastal program, or zoning ordinance) adopted for the purpose of avoiding or
mitigating an environmental effect?
No Impact. The proposed project is consistent with the existing General Plan land use
designation, zoning, and Local Coastal Program Land Use Plan. The General Plan and
LCP/Land Use Plan designate the Shelimaker Island site for Recreational and Environmental
Open Space. The proposed facilities are consistent with this designation.
No mitigation measures are necessary.
c) Conflict with any applicable habitat conservation plan or natural community
conservation plan?
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Less Than Significant Impact. The site is located within the Central/Coastal Orange
County NCCP area. The projeefs proposed habitat restoration component (see Section IV.f) is
consistent with NCCP policies. No mitigation measures are necessary.
X. MINERAL RESOURCES
Would the project:
a) Result in the loss of availability of a known mineral resource that would be a value
to the region and the residents of the state?
No Impact. There are no known mineral resources on the site. No mitigation measures
are necessary.
b) Result in the loss of availability of a locally Important mineral resource recovery
site delineated on a local general plan, specific plan or other land use plan?
No Impact. There are no locally Important mineral resource recovery areas located in
the project area. No mitigation measures are necessary.
XI. NOISE
Would the project result in:
a) Exposure of persons to or generation of noise levels in excess of standards
established in the local general plan or noise ordinance, or applicable standards of other
agencies?
Less Than Significant Impact. There are two potential sources of noise: 1) noise
generated during construction, and 2) noise generated from the ongoing operation of the facility.
Since the proposed project would replace existing facilities and no substantial change in
operational characteristics would occur, there should be no substantial increase in traffic that
would contribute to a significant long-term noise increase on roadways in the vicinity. There are
also no proposed on -site activities that would generate loud noises. A short-term noise Increase
during construction would occur, however, from the Use and transport of heavy equipment. The
following standard condition would reduce construction noise to a level that is less than
significant:
Standard Conditions
SC XI-1
Pursuant to the City of Newport Beach Noise Ordinance Section 10,28.040, construction
adjacent to existing residential development shall be limited to the hours of 7:00 a.m. to
6:30 p.m. Monday through Friday and 6:00 a.m. through 6:00 p.m. on Saturday.
Construction shall not be allowed outside of these hours Monday through Saturday and
at any time on Sundays and federal holidays.
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' b) Exposure of persons to or generation of excessive groundborne vibration or
groundborne noise levels?
Less Than Significant Impact. A short-term increase in groundborne vibration and noise
' would be expected to occur during excavation and construction. Limitations on allowable hours
of construction found in Standard Condition XI-1 would reduce this impact to a level that is less
than significant.
' c) A substantial permanent increase in ambient noise levels in the project vicinity
above levels existing without the project?
' No Impact. The project would not result in significant long-term noise impacts. No
mitigation is necessary.
' d) A substantial temporary or periodic increase in ambient noise levels in the project
vicinity above levels existing without the project?
Less Than Siqnificant Impact. See Section XI.a, above.
e) For a project located within an airport land use plan or, where such a plan has not
' been adopted, within two miles of a public airport or public use airport, would the project
expose people residing or working in the project area to excessive noise levels?
Less Than Significant Impact. The site is located near the flight path from John Wayne
Airport; therefore construction workers, employees and visitors would be subject to minor noise
impacts due to aircraft overflight. These impacts are not considered significant, however, since
the site is approximately 3.3 miles from John Wayne airport and is outside the 65 d6 CNEL
noise contour. No mitigation measures are necessary.
f) For a project within the vicinity of a private airstrip, would the project expose
people residing or working in the project area to excessive noise levels?
No Impact. There are no private airstrips within the vicinity of the site. No mitigation
measures are necessary.
XII. POPULATION AND HOUSING
Would the project:
a) Induce substantial population growth in an area, either directly (for example, by
proposing new homes and businesses) or indirectly (for example, through extension of
roads or other infrastructure)?
No Impact. Since the operation of the proposed project would be substantially similar to
the existing facility, no increase in population would be induced. No mitigation measures are
necessary.
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b) Displace substantial numbers of existing housing, necessitating the construction '
of replacement housing elsewhere?
No impect. There is no existing housing that would be displaced by the proposed
development. No mitigation measures are necessary.
c) Displace substantial numbers of people, necessitating the construction of
replacement housing elsewhere?
No Impact. No people or existing housing would be displaced by the proposed
development. No mitigation measures are necessary.
Xill. PUBLIC SERVICES
Would the project result in substantial adverse physical impacts associated with the '
provision of new or physically altered governmental facilities, need for new or physically
altered governmental facilities, the construction of which could cause significant '
environmental impacts, in order to maintain acceptable service ratios, response times or
other performance objectives for any of these public services:
a) Fire protection?
Less Than Significant Impact. The proposed project would not cause a substantial
increase in demand for fire protection and paramedic service since the project would replace
existing facilities, No mitigation measures are necessary.
b) Police protection?
Less Than Significant Impact With Mitigation. The proposed project would not cause a
substantial Increase in demand for police protection since the project would replace existing
facilities. Traffic control during construction will be provided by the contractor in a manner
meeting the approval of the City Traffic Engineer (see Mitigation Measure VII-1). No additional
mitigation measures are necessary.
c) Schools?
No Impact. The proposed project would have no effect on student generation or school
operations since it is not a residential use. No mitigation measures are necessary.
d) Parks?
No Impact. The proposed project would provide recreational opportunities for bird
watching and other educational activities. It would have no effect on the demand or usage of
parks or recreation facilities. No mitigation measures are necessary.
li
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e) Other public facilities?
No Impact. The proposed project would
mitigation measures are necessary.
XIV. RECREATION
have no effect on any other public. facilities. No
a) Would the project increase the use of existing neighborhood and regional parks
or other recreational facilities, such that substantial physical deterioration of the facility
would occur or be accelerated?
Less Than Significant Impact. Back Bay Drive, which is adjacent to Shellmaker Island,
is a popular recreational trail. Publicity associated with the new facilities could potentially make
more people aware of this trail, and result in a minor increase in its use. This increase would
not be expected to be significant, however. No mitigation measures are necessary.
b) Does the project include recreational facilities or require the construction or
expansion of recreational facilities, which might have an adverse physical effect on the
environment?
No Impact. The project includes tidepools and trails, which are recreational amenities.
There are no additional impacts associated with those facilities that are not addressed in this
Initial Study.
XV. TRANSPORTATIONITRAFFIC
Would the project:
a) Cause an increase in traffic, which is substantial in relation to the existing traffic
load and capacity of the street system (i.e., result in a substantial increase in either the
number of vehicle trips, the volume to capacity ratio on roads, or congestion at
intersections)?
Less Than SignificantImpact With Mitigation. Since the project would replace existing
facilities with substantially the same operational characteristics, no significant increase in traffic
would result. No mitigation is required for long-term traffic Impacts.
Short-term impacts would occur due to construction traffic. Mitigation Measure VII-1 would
require that a traffic control plan be prepared to specify measures to minimize travel disruptions
and safety hazards. This mitigation measure would reduce potential short-term construction
traffic impacts to a level that is less than significant.
b) Exceed, either individually or cumulatively, a level of service standard established
by the county congestion management agency for designated roads or highways?
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Less Than Significant Impact. Please see Section XV.a. Since the project would
replace existing facilities, it would not generate a substantial Increase in traffic and would not
exceed any level of service standard. No mitigation is necessary.
c) Result in a change in air traffic patterns, including either an increase In traffic
levels or a change in location that results In substantial safety risks?
No Impact. The project would have no effect on air traffic patterns. No mitigation
measures are necessary.
d) Substantially increase hazards due to a design feature (e.g., sharp curves or
dangerous intersections) or incompatible uses (e.g., farm equipment)?
Less Than Significant Impact With Mitigation. The project would replace existing
facilities and would not create traffic hazards due to design features. No mitigation is
necessary.
e) Result in inadequate emergency access?
Less Than Significant Impact. See Section XV.d, above.
f) Result in inadequate parking capacity?
Less Than Significant Impact With Mitigatioh. Parking demand estimates for the new
facilities are shown in Table XV-1. The table shows that peak parking demand of 54 cars
occurs between 5 and 8 am. The on -site parking area provides spaces for 66 cars and one bus,
therefore adequate parking will be provided. No mitigation Is necessary.
Table XV•1
Parking Demand — Shellmaker Island
Mon
Tues
Wed
Thurs
Fri
Sat
I Sun
5-8 am
54
54
54
54
54
54
1 54
8 am -noon
28
48
50
48
50
40
40
Noon-4 m
34
51
53
53
53
41
41
4-6 13M
25
41
41
41
41
38
32
6-9 m
4
4
4
4
16
4
4
9 m-5 am
0
0
0
0
16
0
0
Source: City of Newport Beach
Temporary demand for additional parking would be created by workers during construction.
Mitigation Measure VII-1 would reduce this Impact to a level that is less than significant.
g) Conflict with adopted policies, plans, or programs supporting alternative
transportation (e.g., bus turnouts, bicycle racks)?
Less Than Significant Impact With Mitigation. The proposed project would include a
bicycle rack, which would support alternative transportation goals. Potential disruption of bus
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n
travel and bicycle lanes could occur during construction, however. Mitigation Measure VII-1
would reduce this impact to a level that is less than significant.
XVI. UTILITIES AND SERVICE SYSTEMS
Would the project:
a) Exceed wastewater treatment requirements of the applicable Regional Water
Quality Control Board?
Less Than Significant Impact. Since the project would replace an existing facility with
substantially the same operational characteristics, it would not generate a substantial increase
in wastewater flows or unusual treatment requirements. No mitigation measures are necessary.
b) Require or result in the construction of new water or wastewater treatment
facilities or expansion of existing facilities, the construction of which could cause
significant environmental effects?
Less Than Significant Impact. See Section XVI.a. No mitigation measures are
necessary.
c) Require or result in the construction of new storm water drainage facilities or
expansion of existing facilities, the construction of which could cause significant
environmental effects?
Less Than Significant Impact. The project design includes a stormwater retention basin
and filtration system. This would reduce the potential impact to a level that is less than
significant. No additional mitigation measures are necessary.
d) Have sufficient water supplies available to. serve the project from existing
entitlements and resources, or are new or expanded entitlements needed?
Less Than Significant Impact. The project would replace existing facilities with
I' substantially the same operational characteristics, and would not result in a significant increase
in demand for water. No mitigation measures are necessary.
e) Result in a determination by the wastewater treatment provider, which serves or
may serve the project that it has adequate capacity to serve the project's projected
demand in addition to the provider's existing commitments?
Less Than Significant Impact. See Section XVI.b, above. No mitigation measures are
necessary.
f) Be served by a landfill with sufficient permitted capacity to accommodate the
project's solid waste disposal needs?
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Less Than Significant Impact. The project would replace existing facilities with
substantially the same operational characteristics, and would not result in a significant increase
in solid waste generation. No mitigation measures are necessary.
g) Comply with federal, state, and local statutes and regulations related to solid
waste?
Less Than Significant Impact. The project could generate solid waste during
construction. Standard contract specifications requiring the contractor to remove and dispose of
waste in accordance with applicable statutes and regulations Would reduce this impact to a level
that is less than significant. No mitigation measures are necessary.
MANDATORY FINDINGS OF SIGNIFICANCE
a) Does the project have the potential to degrade the quality of the environment,
substantially reduce the habitat of a fish or wildlife species, cause a fish or wildlife
population to drop below self-sustaining levels, threaten to eliminate a plant or animal
community, reduce the number or restrict the range of a rare or endangered plant or
animal or eliminate Important examples of the major periods of California history or
prehistory?
Less Than Significant With Mitigation Incorporated. The project has the potential to
degrade the quality of the environment, but project design features, standard conditions, and
mitigation measures would reduce these potential Impacts to a level that is less than significant.
b) Does the project have impacts that are individually limited, but cumulatively
considerable? ("Cumulatively considerable" means that the incremental effects of a
project are considerable when viewed in connection with the effects of past projects, the
effects of other current projects, and the effects of probable future projects.)
Less Than Significant With Mitigation incorporated. The project would contribute to
short-term cumulative impacts in the areas of air quality, noise and traffic during the construction
period. The projects contribution to these cumulative Impacts would be substantially reduced
by the standard conditions and mitigation measures, however, and the incremental impacts of
the project Would be so small that they would make only a de minimis contribution to the
cumulative impacts caused by other projects.
c) Does the project have environmental effects, which will cause substantial adverse
effects on human beings, either directly or indirectly?
Less Than Significant With Mitigation Incorporated. The project design features, '
standard conditions, and mitigation measures would substantially reduce the potentlat impacts
of the project to a level that is less than significant. '
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D. REFERENCES
Building News Publications, Standard Specifications for Public Works Construction, 1997 (the
"Greenbook")
California Coastal Act (Public Resources Code Division 20, Section 30000 at seq.)
California Code of Regulations. Title 14 Natural Resources
California Fish and Game Code
City of Newport Beach, Circulation Improvement and Open Space Agreement Final EIR, 1992
City of Newport Beach, Newport Beach General Plan.
City of Newport Beach, Newport Beach Municipal Code.
Coastal Resources Management, Shellmaker Island Estuarine Studies Center Biological Impact
Assessment, June 2003
County of Orange, Central and Coastal NCCP Program Map, 1996
Keane Biological Consulting, Results of 2002 and 2003 Focused Surveys at Shellmaker Island
for Belding's Savannah Sparrow, June 2003
Leighton and Associates, Geotechnical Report for the Proposed Shellmaker Island
Development City of Newport Beach, California, June 25, 2002
Shelton, Brian, Department of Fish and Game, Personal Communication, May 2002
South Coast Air Quality Management District, CEQA Air Quality Handbook, 1993
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E. LIST OF PREPARERS
Lead Agency:
California Department of Fish Theresa Stewart Supervisor, Land
and Game Management and Monitoring
Program, South Coast
Region
Karl Lewis Senior Wildlife Biologist
Lands and Facilities Branch
Sacramento, CA
Brian Shelton Wildlife Biologist,
Upper Newport Bay
Ecological Reserve Manager
John Scholl Environmental Scientist,
Upper Newport Bay
Ecological Reserve
Responsible Agencies:
California Coastal
Kristine Finstad
Restoration and Education
Commission
Project Coordinator
City of Newport Beach
Lloyd Dalton, P.E.
Principal Engineer
Gail Pickart, P.E.
Consulting Engineer
Dave Kiff
Assistant City Manager
County of Orange
Mike Hansen
Facilities Operations Mgr,
Health Care Agency
Environmental Consultants:
Civic Solutions, Inc. John Douglas, AICP Director of Planning Projects
Coastal Resources Rick Ware Wetlands Consultant
Management
Keane Biological Consultants Kathy Keane Biologist
Leighton and Associates Ali Bastani, GE Senior Project Engineer
Organizations and Persons Consulted
Ron Yeo, FAIA, Architect, Inc. Ron Yeo, FAIA
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Project Architect
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APPENDICES
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APPENDIX 1
RESULTS OF 2002 AND 2003 FOCUSED SURVEYS AT SHELLMAKER ISLAND FOR
BELDING'S SAVANNAH SPARROW
Prepared By:
Kathy Keane, Keane Biological Consultants
For:
Rick Ware, Coastal Resources Management
Introduction and Purpose
Keane Biological Consulting (KBC) conducted focused surveys on Shellmaker Island, Upper
Newport Bay during 2002 and 2003. The purpose of the surveys was to determine the status
and distribution of this State of California endangered species within salt marsh habitat that is in
the vicinity of the proposed Estuarine Studies Center. This report summarizes the results of
surveys conducted in Spring 2002 and 2003 and also reports on the presence of other bird
species observed during the surveys.
Distribution and Regional Status
The savannah sparrow (Passerculus sandwichensis) is a widespread and abundant species of
North American open habitats south to northern El Salvador and Honduras. Seventeen
subspecies are recognized, most of which are migratory. Several species, however, are residents
of coastal salt marshes of the southwestern United States and Mexico, including the large -billed
savannah sparrow (Passerculus sandwichensis rostratus), which occurs along the east and west
shores of the Gulf of California, and the Belding's savannah sparrow (Passerculus sandwichensis
beldingi)l , which is found from Morro Bay south to El Rosario, Baja California (Wheelwright and
Rising 1993).
Legal Status
The Belding's savannah sparrow was listed by the California Department of Fish and Game
(CDFG) as endangered in January 1974. It is not currently listed as endangered or threatened by
the United States Fish and Wildlife Service (USFWS).
General Biology
Ecology
Belding's savannah sparrows occupy coastal salt marshes and coastal estuaries where
pickleweed, sea-blite (Suaeda sp.), salt bush (Atriplex sp.), and salt grass are dominant plant
species. Although other subspecies subsist on a diet of insects during the summer and seeds
during the winter, Belding's savannah sparrows eat a variety of crustaceans as well as seeds of
pickleweed. They may forage in other nearby habitats including along rock jetties (Garrett and
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Dunn 1981) and are capable of drinking salt water. Nests are built low in pickleweed in middle
to upper portions of salt marshes, or in non -tidal seepage areas dominated by pickleweed
(Massey 1977). Predators include several raptor species, clapper rail (Rallus longirostris
levlpes), red fox (Vulpes vulpes), striped skunk (Mephites mephites), raccoon (Procyon lotor),
and domestic cat (Wheelwright and Rising 1993).
Conservation
Savannah sparrows of other subspecies have likely benefited from human activity because of their
preference for breeding in open habitats such as agricultural fields and grazing lands (Wheelwright
and Rising 1993). However, the Belding's savannah sparrow population has declined over the
past century due to destruction of suitable salt marsh habitat by filling for housing, industrial use
and marina development (Garrett and Dunn 1981).
Attempts to estimate the population of Belding's savannah sparrow during the last 20 years have
been proven difficult because of the large foraging range maintained by each pair as well as the
reclusive nature of the bird. A census of the state's population in 1986 counted 2,274 pairs (R.
Jurek, pers. comm.). Point Mugu Naval Air Station in Ventura County supported the largest
population, with 446 pairs (Zembal et al. 1988). Upper Newport Bay and Bolsa Chica in Orange
County also supported high•quality habitat and relatively stable populations (Zembal at al. 1988). A
statewide survey in 1991 estimated 1,844 pairs north of Mexico, although this included only a
partial count for Point Mugu. Another statewide census was conducted in 1996 and estimated
2,350 breeding pairs (R. Zembal, pers. comm.), indicating the population may be somewhat
increasing, though surveys since that time indicate a general decline. Current threats to the
population are continued degradation of coastal saltmarsh habitats due to freshwater diversion,
siltation and water pollution, and further habitat losses to residential development (Zembal at al.
1988).
Survey Methods
Saltmarsh habitat dominated by pickleweed (Sailcomla vlrginfca) noted to be suitable for
Belding's savannah sparrow was identified on Shellmaker Island all along the western shore,
extending from the UCI crew boat facility to the northwestern corner of the island. These areas
were surveyed for the presence of savannah sparrows on April 25, 2002 and May 13, 2002.
Surveys on April 25 were conducted from 0740 to 0920; surveys on May 13 were conducted
from 0712 to 0830. During 2003, the surveys were conducted on April 16 and April 23, 2003
between the hours of 0714 to 0945.
No standard protocol exist for survey methods; however, Dick Zembal, an expert on this
subspecies, recommends that surveys be conducted during early morning hours of the breeding
season and that surveys not be conducted during inclement weather. In addition, personal
observations Indicate that detection of Belding's savannah sparrows is higher during sunny
rather than overcast weather.
Surveys detected and recorded the location and number of birds and behaviors such as
vocalizations (call notes and songs), courting and nesting activities, perching, chasing, and
fleeing. The presence of potential predators was also noted. From these breeding and territorial
behaviors, the number and approximate locations of individuals, paired birds, and territories
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' were estimated. Individuals were determined to be a member of a pair based on behavior (if
they were observed in close proximity or were otherwise interacting as a pair, not demonstrating
territorial defensive behavior to one another). Each pair as well as individual birds displaying
territorial behavior (chasing other individuals, perched vocalizing and warning [full song and/or
warning "chip" notes], or carrying food or nesting material, or present with fledglings) were
considered to be an active territory.
Survey Results
2002 Surveys. One pair of Belding's savannah sparrows was observed during both April and
May surveys. The pair was feeding, and the male was singing, throughout the patch of
pickleweed in the northwestern corner of the "island." No nest -building behavior was noted, and
no nest was located, but observed behavior suggested the pair was both feeding and nesting in
the area. No Belding's savannah sparrows were seen or heard in the pickleweed habitat
located near the UCI crew boat facility on the southwestern corner of the "island" during either
survey. Several other species of birds were detected on and in the vicinity of the "island" during
the survey, including the endangered California least tern (Sterna antillarum browns) foraging in
nearby shallow waters.
2003 Surveys. No Belding's savannah sparrows were observed during the surveys. Brian
Shelton, manager of the Upper Newport Bay Ecological Reserve for the California Department
of Fish and Game, states that he has not seen or heard Belding's savannah sparrows at the site
this year. No Belding's savannah sparrows were seen or heard in the pickleweed habitat
located near the UCI crew boat facility on the southwestern corner of the "island" during either
survey. Several other species of birds were detected on and in the vicinity of the "island" during
the survey (Table 1 and 2).
References
Garrett, K. and J. Dunn. 1981. Birds of Southern California: Status and Distribution. Los Angeles
Audubon Society, California.
' Massey, B.W. 1977. A census of the breeding population of the Belding's savannah sparrow in
California, 1977. Unpublished report, ,Department of Fish and Game, The Resources
Agency, Sacramento.
t Wheelwright, N.T., and J.D. Rising. 1993. Savannah Sparrow (Passerculus sandwichensis). In
The Birds of North America, No. 45 (A. Poole and F. Gill, Eds.). Philadelphia: The
Academy of Natural Sciences; Washington, D.C.
Zembal, R.L., K.J. Kramer, R.J. Bransfield, and N. Gilbert. 1988. A survey of Belding's
savannah sparrows in California. American Birds: 42(5), pp. 1233-1236.
' Back Bay Science Center Initial Study/Mitigated Negative Declaration
July 16, 2003 Page 83
I
Civic Solutions, Inc.
Table 1.
Birds Observed During April 16 and 23 Surveys
American goldfinch
Anna's hummingbird
Barn swallow
Common yellowthroat
European starling
great blue heron
House finch
Least sandpiper
Mallard
Marsh wren
mourning dove
northern harrier (preying on shorebirds)
northern rough -winged swallow
Snowy egret
song sparrow
western sandpiper
Willet
Table 2.
Birds Observed During April 16 and 23 Surveys Hear Shelimaker island
California gnatcatcher (east, on the slope of Bay Back)
Belding's savannah sparrow (north of the access road)
Caspian tern, eleganttern, Forster's tern (foraging in nearby waters)
California least tern (foraging in nearby waters)
American crow (flying overhead)
white -throated swift (flying overhead)
black -crowned night heron (flying overhead)
Back Bay Science Center Initial Study/Mitigated Negative Declaration
July 16, 2003 Page 84
Civic Solutions,
APPENDIX 2
Biological Resources Inventory
Property Name
UPPER NEWPORT BAY ER
Bird List - Common and Scientific Names
ALLEN'S HUMMINGBIRD
AMERICAN AVOCET
AMERICAN BITTERN
AMERICAN COOT
AMERICAN CROW
AMERICAN FLAMINGO
AMERICAN GOLDEN -PLOVER
AMERICAN GOLDFINCH
AMERICAN KESTREL
AMERICAN PIPIT
AMERICAN REDSTART
AMERICAN ROBIN
AMERICAN WHITE PELICAN
AMERICAN WIGEON
ANNA'S HUMMINGBIRD
ARCTIC LOON
ARCTIC TERN
ASH -THROATED FLYCATCHER
BAIRD'S SANDPIPER
BALD EAGLE
BANK SWALLOW
BARN OWL
BARN SWALLOW
BELTED KINGFISHER
BEWICK'S WREN
Thursday, October 25, 2001 Page 1 of 20
Back Bay Science Center
July 16, 2003
Property #
00361
Selasphoms sasin
Recurvirostm americana
Botaums lentiginosus
Fuliea americana
Corvusbmchyrhynchos
Phoenicoptems ruber
Pluvialis dominica
Carduelis tristis
Falco sparverius
Anthusrubescens
Setophaga mticilla
Turdus migratorius
Pelecanus erythrorhynchos
Anas americana
Calypte anna
'Gavia arctica
Stoma pamdisaea
Myiarchus cinerascens
Calidds bairdii
Haliaeetus leucocephalus
Riparia riparia
Tyto alba
Hirundo rustica
Ceryle alcyon
Thryomanes bewickii
Initial Study/Mitigated Negative Declaration
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Civic Solutions, Inc.
Property Name
Property #
UPPER NEWPORT BAY ER
00361
BLACK PHOEBE
Sayomis nigricans
BLACK RAIL
Laterallus jamaiccnsis
BLACK SCOTER
Mclanitta nigm
BLACK SKIMMER
Rynchops nigcr
BLACK TERN
Chlidonias nigcr
BLACK TURNSTONE
Arcnada mclanocephata
BLACK -BELLIED PLOVER
Pluvialis squatarola
BLACK -CHINNED HUMMINGBIRD
Archilochus alexandri
BLACK -CROWNED NIGHT HERON
Nycticomx nyoticorax
BLACK -HEADED GROSBEAK
pircucticus melanocepholus
BLACK -LEGGED KITTIWAKE
Rissa tridactyla
BLACK -NECKED STILT
Hlmantopus mexicanus
BLACK -TAILED GNATCATCHER
Polioplila mclanum
BLACK -THROATED GRAY WARBLER
Dendroica nigrescens
BLUE -GRAY GNATCATCHER
Polioptila cacrulca
BLUE -WINGED TEAL
Anas discars
BONAPARTE'S GULL
Larusphiladelphia
BRAND14S CORMORANT
Phalacrocorox pcnicillams
BRANT
Brantabcmicla
BREWER'S BLACKBIRD
Euphagas cyanocephalus
BROWN PELICAN
Pelecanus occidentalis
BROWN -HEADED COWBIRD
Molothrus atcr
BUFFLEHEAD
Buccphala albeola
BULLOCKS ORIOLE
Icterus bullockii
BURROWING OWL
Athene cunicularia
BUSHTIT
Psaltripams minhnus
CACTUS WREN
Campylorhynclms brunncicapillus
Thursday, October 25, 2001 Page 2 of 20
Back Bay Science Center Initial Study/Mltigated Negative Declaration
July 16, 2003 Page 86
Civic Solutions, Inc.
Property Name
Property #
UPPER NEWPORT BAY ER
00361
CALIFORNIA GULL
Lams califomicus
CALIFORNIA QUAIL
Callipepla californica
CALIFORNIA THRASHER
Toxostoma redivivum
CALIFORNIA TOWHEE
Pipilo crissalis
CANADA GOOSE
Branta canadensis
CANVASBACK
Aythya valisineria
CASPIAN TERN
Stema caspia
CASSIN'S KINGBIRD
Tyrannus vociferans
CATTLE EGRET
Bubulcus ibis
CEDARWAXWING
Bombyeilla cedmmm
CHIPPING SPARROW
Spizella passerina
CINNAMON TEAL
Anas cyanoptera
CLAPPER RAIL
Rallus longirostris
CLARK'S GREBE
Aechmophoms clarkii
CLAY -COLORED SPARROW
Spizella pallida
CLIFF SWALLOW
Petrochelidon pyrrhonota
COMMON GOLDENEYE
Bucephala clangula
COMMON LOON
Gavia immer
COMMON MERGANSER
Mergus merganser
COMMON MOORHEN
Gallinula chloropus
COMMON RAVEN
Corvus corax
COMMON SNIPE
Gallinago gallinago
COMMON TERN
Stema himndo
COMMON YELLOWTHROAT
Geothlypis trichas
COOPER'S HAWK
Accipiter cooperii
COSTA'S HUMMINGBIRD
Calypte costae
DARK -EYED JUNCO
Junco hyemalis
Thursday, October 25, 2001 Page 3 of 20
Back Bay Science Center Initial Study/Mitigated Negative Declaration
July 16, 2003 Page 87
I'L
Civic Solutions, Inc.
Property Name
Property #
UPPER NEWPORT BAY ER
00361
DOUBLE -CRESTED CORMORANT
Phalncrocorax aurilus
DOWNY WOODPECKER
Picoides pubcscens
EARED GREBE
Podiceps nigricollis
ELEGANT TERN
Stoma clegans
EURASIAN WIGEON
Anas pcnolopo
EUROPEAN STARLING
Smmus vulgaris
FORSTER'S TERN
Stoma forslorl
PDX SPARROW
Passerelln iliaca
FRANKLIN'S GULL
Lams pipixcan
GADWALL
Anas slrepcm
GLAUCOUS GULL
Lams hyperbotcus
GLAUCOUS -WINGED GULL
Lams glauccscens
GOLDEN EAGLE
Aquila chrysactos
GOLDEN -CROWNED SPARROW
Zonotrichia atticapilla
GREAT BLUE 14ERON
Ardca herodlas
GREAT EGRET
Ardea alba
GREAT HORNED OWL
Bubo virginianus
GREATER ROADRUNNER
Gcococeyx californianus
GREATER SCAUP
Aythya marila
GREATER WHITE -FRONTED GOOSE
Anscr albifrons
GREATER YELLOWLEGS
Tringa mclanoleuca
GREAT -TAILED GRACKLE
Quiscalus moxicanus
GREEN HERON
Butorides viresccns
GREEN -TAILED TOWHEE
Pipilo chlorums
GREEN -WINGED TEAL
Anas crceca
HAMMOND'S FLYCATCHER
Empidonax hammondii
HEERMANN'S GULL
Larus hcemtanni
Thursday, October 25, 2001 Page 4 of 20
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July 16, 2003 Page 88
Civic Solutions, Inc.
Property Flame
Property #
UPPER NEWPORT BAY ER
00361
HERMIT THRUSH
Catharus guttatus
HERMIT WARBLER
Dendroica oceidentalis
HERRING GULL
Larus argentatus
HOODED MERGANSER
Lophodytes cucullatus
HORNED GREBE
Podiceps auritus
HORNED LARK
Eremophila alpestris
HOUSE FINCH
Carpodacus mexicanus
HOUSE SPARROW
Passer domesticus
HOUSE WREN
Troglodytes aedon
KILLDEER
Charadrius vociferus
LARK SPARROW
Chondestes grammacus
LAUGHING GULL
Lams atricilla
LAWRENCE'S GOLDFINCH
Carduelis lawrencei
LEAST BITTERN
Ixobrychus exilis
LEAST SANDPIPER
Calidds minutilla
LEAST TERN
Sterna antillarum
LESSER GOLDFINCH
Carduelis psaltria
LESSER NIGHTHAWK
Chordeiles acutipennis
LESSER SCAUP
Aythya affinis
LESSER YELLOWLEGS
Tringa flavipes
LIGHT-FOOTED CLAPPER RAIL
Rallus longirostris levipes
LINCOLN'S SPARROW
Melospiza lincolnii
LOGGERHEAD SHRIKE
Lanius ludovicianus
LONG -BILLED CURLEW
Numenius americans
LONG -BILLED DOWITCHER
Limnodromus scolopaceus
MACGILLIVRAY'S WARBLER
Oporomis tolmiei
MALLARD
Anas platyrhynchos
Thursday, October 25, 2001 Page 5 of 20
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July 16, 2003 Page 89
Civic Sotutlons, Inc.
Property Name
Property #
UPPER NEWPORT BAY ER
00361
'
MARBLED GODWIT
Limosa fedoa
MARSH WREN
Cistathorus palustris
'
MERLIN
Falco columbarius
MEW GULL
Larus cans
'
MOUNTAIN PLOVER
Charadrius montanus
MOURNING DOVE
Zcnaida macroum
NASHVILLE WARBLER
Vennivom ruricapilla
'
NELSON'S SHARP -TAILED SPARROW
Ammodrainus nclsoni
NORTHERN FLICKER
Colaptes auratus
,
NORTHERN HARRIER
Circus cyancus
NORTHERN MOCKINGBIRD
Mimus polyglottos
'
NORTHERN PINTAIL
Arias acuta
NORTHERN ROUGH -WINGED SWALLOW
Stelgidopteryx serripennis
NORTHERN SHOVELER
Anas clypeata
t
NUTTALL'S WOODPECKER
Picoides nuttallii
OLIVE -SIDED FLYCATCHER
Contopus cooped
'
ORANGE -CROWNED WARBLER
Vcrmivom cclata
OSPREY
Pandion haliacros
'
PACIFIC LOON
Gavla Pacifica
PACIFIC -SLOPE FLYCATCHER
Empidonax difftcilis
'
PALM WARBLER
Dcndroica pahnamm
PARASITIC JAEGER
Stercorarius parasiticus
PECTORAL SANDPIPER
Calidris mclanotos
'
PEREGRINE FALCON
Falco porcgrinus
PIED -BILLED GREBE
Poditymbus podiceps
,
PINE SISKIN
Carduclis pinus
PLUMBEOUS VIREO
Virco plumbcus
,
Thursday, October 25, 2001 Page 6 of 20
Back Bay Science Center Initial Study/MlOgated Negative Declaration
July 16, 2003 Page 90
I
Clvic Solutions, Inc.
Property Name
Property #
UPPER NEWPORT BAY ER
00361
PRAIRIE FALCON
Falco mexicanus
PURPLE FINCH
Carpodacus purpureus
PURPLE MARTIN
Progne subis
RED KNOT
Calidris canutus
RED PHALAROPE
Phalaropus fulicaria
RED -BREASTED MERGANSER
Mergus serrator
RED -BREASTED SAPSUCKER
Sphyrapicus tuber
REDDISH EGRET
Egretta rufescens
REDHEAD
Aythya americana
RED -NECKED GREBE
Podiceps grisegena
RED -NECKED PHALAROPE
Phalaropus lobatus
RED -SHOULDERED HAWK
Bunco lineatus
RED-TAILED HAWK
Buteo jamaicensis
RED -THROATED LOON
Gavin stellata
RED -WINGED BLACKBIRD
Agelaius phoeniceus
RING -BILLED GULL
Lams delawarensis
RING-NECKED DUCK
Aythya collaris
RING-NECKED PHEASANT
Phasianus colchicus
ROCK DOVE
Columba livia
ROCK WREN
Salpinetes obsoletus
ROST GOOSE
Chen rossii
ROUGH -LEGGED HAWK
Buteo lagopus
ROYAL TERN
Stema maxima
RUDDY DUCK
Oxyum jamaicensis
RUDDY TURNSTONE
Arenaria interpres
RUFOUS HUMMINGBIRD
Selasphoms mfus
SANDERLING
Calidris alba
Thursday, October 25, 2001 Page 7 of 20
Back Bay Science Center Initial Study/Mitigated Negative Declaration
July 16, 2003 Page 91
Civic 5olullons, Inc.
Property Name
Property #
UPPER NEWPORT BAY ER
00361
SAVANNAH SPARROW
Passerculus sandwichcnsis
SAY'S PHOEBE
Sayornis soya
SEMIPALMATED PLOVER
Charadrius semipalmatus
SEMIPALMATCD SANDPIPER
Calidris pusilla
SHARP -SHINNED HAWK
Accipiter striatus
SHARP -TAILED SANDPIPER
Calidris acuminata
SHORT -BILLED DOWITCHER
Limnodromus griscus
SHORT -EARED OWL
Asio flammeus
SNOW GOOSE
Chen cacruicsccns
SNOWY EGRET
Egretta thula
SNOWY PLOVER
Chamdrius aicxandrinus
SOLITARY SANDPIPER
Tringasolilaria
SONG SPARROW
Mclospiza tnelodia
SORA
Potzona carolina
SPOTTED DOVE
Sucptopclia chinensis
SPOTTED SANDPIPER
Actitis mocularia
SPOTTED TOWHEE
Pipilo maculatus
STILT SANDPIPER
Calidris himantopus
SUMMER TANAGER
Pimnga rubra
SURF SCOTER
Mclanitla perspicillata
SWAINSON'S HAWK
Buteo swainsoni
SWAINSON'S THRUSH
Catharus ustulatus
SWAMP SPARROW
Mclospiza gcorgiona
THAYER'S GULL
Larus thayeri
TOWNSEND'S WARBLER
Dendroica townscndi
TREE SWALLOW
Tachycincta bicolor
TRICOLORED BLACKBIRD
Agelaius tricolor
Thursday, October 25, 2001 Page 8 of 20
Back Bay Science Center Initial Study/Mitigated Negative Declaration
July 16, 2003 Page 92
Civic Solutions, Inc.
Property Name
Property #
UPPER NEWPORT BAY ER
00361
TRICOLORED HERON
Egretta tricolor
TROPICAL KINGBIRD
Tyrannus melancholicus
TUNDRA SWAN
Cygnus columbianus
TURKEY VULTURE
Cathartes aura
VAUNS SWIFT
Chaetura vauxi
VESPER SPARROW
Pooecetes gramineus
VIOLET -GREEN SWALLOW
Tachycineta tltalassina
VIRGINIA RAIL
Rallus limicola
WARBLING VIREO
Vireo gilvus
WESTERN GREBE
Aechmophorus occidentalis
WESTERN GULL
Lams occidentalis
WESTERN KINGBIRD
Tyrannus verticalis
WESTERN MEADOWLARK
Sturnella neglecta
WESTERN SANDPIPER
Calidris maul
WESTERN SCRUB -JAY
Aphelocoma californica
WESTERN TANAGER
Piranga ludoviciana
WESTERN WOOD -PEWEE
Contopus sordidulus
WHIMBREL
Numenius phaeopus
WHITE -CROWNED SPARROW
Zonotrichia leucophrys
WHITE-FACED IBIS
Plegadis chihi
WHITE-TAILED KITE
Elanus leucums
WHITE -THROATED SWIFT
Aeronautes saxatalis
WHITE -WINGED DOVE
Zenaida asiatica
WHITE -WINGED SCOTER
Melanitta fusca
WILLET
Catoptrophorus semipalmatus
WILLOW FLYCATCHER
Empidonax traillii
WILSON'S PHALAROPE
Phalaropus tricolor
Thursday, October 25, 2001 Page 9 of 20
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July 16, 2003 Page 93
Civic Solutions, Inc.
Property Name
UPPER NEWPORT BAY ER
WILSON'S WARBLER
WOOD DUCK
WRENTIT
YELLOW RAIL
YELLOW WARBLER
YELLOW -BREASTED CHAT
YELLOW -HEADED BLACKBIRD
YELLOW -BUMPED WARBLER
Plant List - Scientific and Common Names
Abronia maritims Nutt. cx S. Wats.
Alismaplantago-aquatica L.
Amamnthus albus L.
Ambrosia chamissonis (Las.) Greene
Ambrosia psilostachya DC.
Amsinckia menzicsii (Leltm.) A. Ncls. & J.F. Macbr.
Amsinckia menzicsii var. intermcdia (Fisch & C.A. May.)
Anagallis arvensis L.
Ancmopsis califomica (Nutt.) Hook. & Am.
Apium gmvcolcns L.
Arctotis stocchadifolia Berg.
Artemisio califomica Less.
Artemisia douglasiana Bess.
Artcmisia dmcunculus L.
Amndo donax L.
Asparagus officinalis L. ssp.officinalis
Aster subulatus vac ligulalus Shinners
Atriplex lentiformis ssp. Icntifannis (Torr.) S. Wats.
Atriplex patula L.
Atriplex scmibaccata R. Br.
Atriplex serenana A. Nels.
Thursday, October 25, 2001 Page 10 of 20
Back Bay Science Center
July 16, 2003
Property #
00361
Wilsonia pusilla
Aix sponsa
Chamaca fusciata
Cotumicops novcbomccnsis
Dcndrolca pctechia
Icteria virens
Xanthocephalus xonthoccphalus
Dendroica coronota
red sand verbena
water plantain
prostrate pigweed
silver burr ragweed
cumuli ragweed
Menzies' fiddicncck
rancho's Brewccd
scarlet pimpernel
yerba mansa
wild celery
African daisy
California sagebrush
Douglas'sagewort
wormwood
giantrocd
garden asparagus
annual saltmarsh aster
big saltbush
spear saltbush
Australian saltbush
bractscale
Initial Study/Mitigated Negative Declaration
Page 94
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Property Name
Property #
UPPER NEWPORT BAY ER
00361
Atriplek subspicata (Nutt.) Rydb.
saline saltbush
Avena fatua L.
wild oat
Baccharis salicifolia (Ruiz & Pavon) Pers.
mule's fat
Batis maritima L.
turtleweed
Bela vulgaris L.
common beet
Bloomeria crocea (Tore.) Coville
common goldenstars
Brassica nigm (L.) W.D.J. Koch
black mustard
Brooms diandrus Roth
ripgutbrome
Bromus hordeaceus L,
soft brome
Brooms madritensis ssp. ntbens (L.) Husnot
£oxtail chess
Camissonia bistorta (Nutt. ex Torr. & Gray) Raven
southern suncup
Camissonia cheiranthifolia ssp. cheimnthifolia (Hornem. ex
beach primrose
Capsella bursa-pastoris (L.) Medik.
shepherd's purse
Carex spissa Bailey
San Diego sedge
Carpobroms chilensis (Molina) N.E. Br.
sea fig
Castilleja affinis Hook. & Am.
Indian paintbrush
Centaurea melitensis-L.
Maltese star thistle
Cemmnculus minimus L.
chatfweed
Chamaesyce maculata (L.) Small
spotted sandmat
Chenopodium ambrosioides L.
Mexican tea
Chenopodium murale L.
nettleleaf goosefoot
Chenopodium rubrum L.
red goosefoot
Chrysanthemum coronarium L.
crowndaisy
Cisms L.
rockrose
Cleome isomeris Greene
bladderpod spiderflower
Conium maculatum L.
poison hemlock
Convolvulus arvensis L.
field bindweed
Conyza canadensis (L.) Croaq.
Canadian horseweed
Cordylanthus maritimus ssp. maritimus Nutt. ex Benth.
saltmarsh bird's beak
Coronopus didymus (L.) Sm.
lesser swineeress
Cortaderia jubata (Lem.) Stapf
selloa pampas grass
Cotula australis (Sieber) Hook. f.
Australian waterbuttons
Thursday, October 25, 2001 Page 11 of 20
Back Bay Science Center Initial Study/Mitigated Negative Declaration
July 16, 2003 Page 95
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Property Name
Property #
UPPER NEWPORT BAY ER
00361
Cotula coronopifolia L.
common brassbultons
Cressa mmillensis Knuth
spreading alknliwced
Cuscuta salina Engclm,
salunarsh dodder
Cynrara cardunculus L.
cardoon
Cynodon dactylon (L.) Pors.
bermudograss
Diciclostemma capitation ssp, capitatum (Benth.) Wood
bluedicks
Distichlis spicala (L.) Grcenc
inland saltgrass
Drosanthemum speciosum (Haw.) Schwant.
royal dewflower
Dudleya lanccolata (Nutt.) Britt. & Rose
lanceleaf livcforever
Dudleya stolonifera Moran
Laguna Beach livcforevcr
Emex spinosa (L.) Compd.
spiny threccornerjack
Encelia califamica Nutt.
California brittlebush
Epilobium brachycarpum K. Presl
autumn willowwccd
Eriophyllum confortiflorum (DC.) Gray
yellow yarrow
Erodium botrys (Cay.) Bertol.
longbeak stork's bill
Erodium cicutarium (L.) VHcr. ex Ait.
redstcm stork's bill
Eucalyptus globulus Labili.
Tasmanian blucgum
Foeniculutn vulgare P. Mill.
sweet fennel
Frankcnia salina (Molina) I.M. Johnston
alkali scalrcath
Gilia angelensis V. Grant
chaparral gilia
Gnaphalium califoMieum DC,
everlasting
Gnaphalium palusue Nutt.
western marsh cudwecd
Hemizoniapungens (Hook. & Am.) Tore & Gray
common spikewced
14eteromeles arbutifolia (Lindl.) M. Rocmer
loyon
Heicrotheca grondiflom Nutt
tcicgraphwccd
Hirschfeldia incana (L.) Lagreze-Fossat
shortpod mustard
Hordcum deptessum (Scribn. & J.G. Sm.) Rydb.
dwarf barley
liordeum mudnum ssp. lcporinum (Link) Atcmtg.
Icporinum barley
Isocoma menziesli var. vemonioidcs (Nutt.) Nesom
Mcnzics'jimtnywecd
Jaumca camosa (Less.) Gray
marsh jaumca
Juncus balticus Willd.
Baltic rush,
Lepidium virginhcum L.
Virginiapepperweed
Thursday, October 25, 2001 Page 12 of 20
Back Bay Science Center Initial Study/Mitigated Negative Declaration
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Civic Solutions, Inc.
Property Name
Property #
UPPER NEWPORT BAY ER
00361
Leptochloa uninervia (J. Presl) A.S. Iiitche. & Chase
Mexican sprangletop
Limonium califomicum (Boiss.) Heller
California sealavender
Lotus scoparius (Nutt.) Ottley
common deerweed
Lupinus bicolor Lind].
bicolor lupine
Lupinus succulentus Dougl, ex K. Koch
hollowleaf annual lupine
Lupinus tmncatus Nutt. ex Hook. & Am.
collared annual lupine
Lycium califomicum Nutt. ex Gray
California desertthorn
Malva parviflom L.
cheeseweed mallow
Malva sylvestris L.
high mallow
Malvella leprosa (Ortega) Krapov.
alkali mallow
Matrubium vu]gare L.
horehound
Medicago polymorpha L.
burclover
Melilotus indica (L.) All.
annual yellow sweetclover
Melilotus offlcinalis (L.) Lam.
yellow sweetclover
Mesembryanthemum crystallinum L.
common iceplant
Mesembryanthemum nodiflorum L.
slenderleaf iceplant
Monanthochloe littomlis Engelm.
shoregrass
Myoporum laetum G. Forst.
ngaio tree
Nicotiana glauca Graham
tree tobacco
Oenanthe sarmentosa K. Presl ex DC.
water parsely
Opuntia ficus-indica (L.) P. Mill,
tuna cactus
Opuntia prolifera Engelm.
coastal cholla
Oxalis pes-caprae L.
African woodsorrel
Phacelia distans Benth.
distant phacelia
Phalaris aquatics L.
hardinggrass
Phalaris minor Retz,
littleseed canarygrass
Picris echioides L.
bristly oxtongue
Plantago subnuda Pilger
tall coastal plantain
Poe annua L.
annual bluegrass
Polypogon rnonspeliensis (L.) Desf
annual mbbitsfoot grass
Polypogon viridis (Gouan) Breistr.
beardless rabbitsfoot grass
Potamogeton nodosus Poir.
longleaf pondweed
Thursday, October 25, 2001 Page 13 of 20
Back Bay Science Center
July 16, 2003
Initial Study/Mitigated Negative -Declaration
Page 97
Civic Solutions, Inc.
Property Name Property #
UPPER NEWPORT BAY ER 00361
Potentilla anserina ssp. Pacifica (Howell) Rousi
Rophanus sativus L.
Rhus imcgrifotia (Nutt.) Death. & Hook. f. ex Brewer & S. Wats.
Ricinus commmtis L.
Rorippa nasturtium-aqualicum (L.) Hayek
Rum" crispus L.
Salicomia bigelovii Ton•.
Salicomia sublerminalis Parish
Salicomia virginica L.
Salix exigua Nutt.
SaIN laevigata Hcbb
Salix lucida ssp. lasiandm (Benth.) 8. Murr.
Salsola L.
Sambucus mexicana K. Presl ex DC.
Schismus barbatus (Loell. ex L.) Thellung
Schpus.umericanus Pers.
Scirpus califomicus (C.A. Mey.) Steud.
Scirpus robustus Pursh
Scnccio vulgaris L.
Silybum marianum (L.) Gacrin.
Sisymbrium irio L.
Solanum douglasii Dunal
Solanum sarrachoidcs Scndincr
Sonchus asperssp. asper(L.) Hill
Sonchus oleraccus L.
Spartina foliosa Trin.
Sporgularia media (All.) Chiov.
Suaeda califomica S. Wats.
Toxicodendron divcrsilobum (Tory. & Gray) Greene
Triglochin maritimum L.
Typha domingensis Pers.
Typha latifolia L.
Thursday, October 25, 2001 Page 14 of 20
Back Bay Science Center
July 16, 2003
cinquefoil
wild radish
lemonade sumac
castorbenn
watercress
curly dock
dwarf saltwort
pickloweed
Virginia glasswort
sandbar willow
willow
Pacific willow
Russian Ihistle
blue elderberry
common Mediterranean grass
American bulrush
California bulrush
bulrush
common groundsel
blessed milkthistle
Londonrocket
grecnspotnightshade
nightshade
spiny sowthistle
common sowdiistlo
California cordgmss
mediasandspurry
California seablitc
Pacific poison oak
seaside arrowgrass
southern cattail
broadleaf cattail
Initial Study/Mitigated Negative Declaration
Page 98
Civic Solutions, Inc.
Property Name
UPPER NEWPORT BAY ER
Urtica urens L.
Xanthium slrumarium L.
Mammal List - Common and Scientific Names
BLACK -TAILED JACKRABBIT
BOBCAT
BOTTA'S POCKET GOPHER
BROAD -FOOTED MOLE
CALIFORNIA GROUND SQUIRREL
CALIFORNIA VOLE
COMMON MUSKRAT
COYOTE
DEER MOUSE
DESERT COTTONTAIL
DESERT. SHREW
FERAL CAT
GRAY FOX
HOUSE MOUSE
LONG-TAILED WEASEL
MULE DEER
NORWAY RAT
RACCOON
STRIPED SKUNK
VIRGINIA OPOSSUM
WESTERN HARVEST MOUSE
WESTERN SPOTTED SKUNK
Thursday, October 25, 2001 Page 15 of 20
Back Bay Science Center
July 16, 2003
Property #
00361
dwarf nettle
rough cockleburs
Lepus californicus
Lynx rufus
Thomomysbottae
Scapanus latimanus
Spermophilus beecheyi
Microms californicus
Ondatra zibethicus
Canis latrans
Peromyscus maniculatus
Sylvilagus audubonii
Notiosorex crawfordi
Felis Carus
Urocyon cinereoargenteus
Mus musculus
Mustela frenata
Odocoileus hemionus
Rattus norvegicus
Procyon later
Mephitis mephitis
Didelphis virginiana
Reithrodontomys megalotis
Spilogale gracilis
Initial Study/Mitigated Negative Declaration
Page 99
Civic Solutlons, Inc.
Property Name
Property #
UPPER NEWPORT BAY ER
00361
Amphibian List - Common and Scientific Names
AFRICAN CLAWED FROG
Xenopus Nevis
BULLFROG
Rana catesbeiana
CALIFORNIA NEWT
Taricha torosa
CALIFORNIA SLENDER SALAMANDER
Batmchoseps auenuatus
PACIFIC CHORUS FROG
Pscudacris regilla
WESTERN TOAD
Bufo borcas
Reptiles List - Common and Scientific Names
CALIFORNIA LEGLESS LIZARD
COACHWHIP
COAST HORNED LIZARD
COMMON KINGSNAKE
GOPHER SNAKE
SIDE -BLOTCHED LIZARD
SLIDER
SOUTHERN ALLIGATOR LIZARD
STRIPED RACER
WESTERN FENCE LIZARD
WESTERN POND TURTLE
WESTERN RATTLESNAKE
WESTERN WHIPTAIL
Thursday, October 25, 2001 Page 16 of 20
Anniolla pulchm
Masticophis flagellum
Phrynosoma comnatum
Latnpropcltis getula
Pituophis mclanolcucus
Um stansburiana
Tmchemys scripts
Elgadamulticarinata
Masticophis latemlis
Scclopotus occidentalis
Clemmys marmorata
Crotalus Addis
Cnemidophorus Tigris
Back Bay Science Center Initial Study/Mitigated Negative Declaration
July 16, 2003 Page 100
Civic Solutions, Inc.
Property Name
UPPER NEWPORT BAY ER
Fish List - Common and Scientific Names
arrow goby
barred sand bass
barred surfperch
betray
black bullhead
black croaker
bluegill
bonefish
brown smoothhound shark
butterfly stingray
60 turbot
California clingfish
California corbina
California halibut
California killifish
California tonguefish
checkspotgoby
deepbody anchovy
diamond stingray
diamond turbot
fathead minnow
gray smoothhound shark
green sunfish
homyhead turbot
kelp bass
leopard shark
Thursday, October 25, 2001 Page 17 of 20
Back Bay Science Center
July 16, 2003
Property #
00361
Clevelandia ins
Paralabrax nebulifer
Amphistichus argentus
Rhinoloatos productus
Ameiums melas
Cheilotrem saturnum
Lepomis macrochirus
Dorosoma petenensis
Mustelus henlei
Platyrhnoidis triseriata
Pleuronichthys coenosus
Gobiesox rhessodon
Menlicirrhus undulatus
Paralichthys californicus
Fundulus parvipinnis
Symphurus atricauda
llypnus gilberti
Anchoa compressa
Mvliobams califoramca
Hypsopsetta guttulata
Pimephales promelas
Mustelus califomicus
Lepomis cyanellus
Pleuronichthys verticalis
Pamlabmx clattmtus
Triakis semifasciata
Initial Study/Mitigated Negative Declaration
Page 101
11
Civic Solutlons, Inc.
Property Name
Property #
UPPER NEWPORT BAY ER
00361
longjaw mudsucker
Gilliclithys mimilis
mosquitofish
Gabusia nttinis
northern anchovy
Bngmulis mordax
opaloye
Girella nigricahs
Pacific Butterfish
Peprilus simillimus
Pacific mackerel
Scombor japonicus
Pacific sardine
Sardinops caerulea
pile surfperoh
Ithacobilus vacua
red shiner
Notropis lutrcnsis
rockfish spp
Sebaslodes sp.
round stingray
Gvmnum mamtomta
Salcma
Xcnislius califomiensus
satgo
Anisoircmus davidsoui
shadow goby
Yongcich(hys nebulosus
shiner surfperch
Cymalogaster aggregate
shovelnosc guitarfish
Dasymis dipleupa
silver goldfish
Carassius auratus
slough anchovy
Anchoa delieatissima
specklefin midshipman
Porichthys myriaste
spotfin croaker
Roncador steatnsi
spotted sand bass
Pamlabrax maculatofascinalus
spotted turbot
Pleuronichdrys ritterl
staghom sculpin
Collus mniams
thomback
Urolopus ballcrld
thrcadfin shad
Dorosoma pclenense
tilapia sp
Tilapia spp,
walleye surfperch
Ityperprosopon argenleum
Thursday, October 25, 2001 Page 18 of 20
Back Bay Science Center Initial Study/Mitigated Negative Declaration
July 16, 2003 Page 102
Civic Solutions, Inc.
Property Name
UPPER NEWPORT BAY ER
white croaker
white seabass
white surfnirch
yellowfin croaker
zebraperch
Property #
00361
Genyonemus lincatus
Cynoscion nobilis
Heterostichus restrains
Umbrina toreador
Hermosilla azurea
Invertebrate List - Common and Scientific Names
Pacific lilticneck clam
Protothaca staminea laciniam
Pacific littleneck clam
Protothaca staminea
Pink hearted hydroid
Tubilaria crocea
Thin -shelled littleneck
Protothaca tenerrima
Vegetation Communities List
30.000.00
SCRUB AND CHAPARRAL
32.000.00
Coastal Scrub
40.000.00
GRASS & HERB DOMINATED COMMUNITIES
41.000.00
Native Grassland
41.070.00
Cordgrass Saline/Alkaline Grassland
41.070.01
California Cordgrass
50.000.00
BOG AND MARSH
52.000.00
Marsh
52.100.00
Fresh - Brackish Water Marsh
52.101.00
Bulrush
52.102.00
Bulrush - Cattail Wetland
52.103.00
Cattail Wetland
52.200.00
Salt- Alkali Marsh
52.201.00
Pickleweed Wetland
60.000.00
RIPARIAN AND BOTTOMLAND HABITAT
Thursday, October 25, 2001 Page19 of20
Back Bay Science Center
July 16, 2003
Initial Study/Mitigated Negative Declaration
Page 103
Clylc Solutions, Inc.
Property Name Property #
UPPER NEWPORT BAY ER 00361
61.000.00 Riparian lorestand Woodland
61.20o.00 Willow Riparian Forosts and Woodlands
Wildlife Habitat types
COASTALSCRUE
ESTUARINE
FRESH EMERGENT WETLAND
MARINE
SALINE EMERGENT WETLAND
VALLEY FOOTHILL RIPARIAN
Data Sources - Document Name, Date, Author and Comments
UPPER NEWPORT DAY ER MANAGEMENT PLAN I/l/89 DAUGHERTY (1978), HARDY
Thursday, October 25, 2001 Page 20 of 20
Back Bay Science Center Initial Study/Mitigated Negative Declaration
July 16, 2003 Page 104