HomeMy WebLinkAboutGPA 2017-0003; OAKMONT OF CARLSBAD; BIOLOGICAL RESOURCES ASSESSMENT; 2017-09-17FIRSTCARBON~iOLUTIO~~~).
Biological Resources Assessment
Oakmont of Carlsbad
Carlsbad, San Diego County, California
San Luis Rey, California, USGS 7 .5-minute Topographic Quadrangle Map
Township 12S Range 04W
NORTH AMERICA I EUROPE I AFRICA I AUSTRALIA I ASIA
WWW.FIRSTCARBONSOLUTIONS.COM
Prepared for:
Oakmont Senior Living
9240 Old Redwood Hwy, Suite 200
Windsor, CA 95492
Contact: Hannah Daugherty, Project Manager
Prepared by:
FirstCarbon Solutions
250 Commerce, Suite 250
Irvine, California 92602
714.508.4100
Contact: Kim Boydstun, Senior Project Manager
Korey Klutz, Senior Biologist
Report Date: September 7, 2017
NCV O 2 1017
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Exhibit 4: Soils .............................. .
Exhibit 5: Vegetation Communities ... .
Oakmont S"nlor Living-Oakmont a/ Carlsbad
Biologkol R"sources Assessment
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Exhibit 6: Project Impacts ........................................................................................ . .. ....... 23
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Oakmont Senior Living-Oakmont of Carlsbad
Bialagical Resources Assessment
SECTION 1: SUMMARY
Summary
A biological resources assessment was conducted to document the existing biological conditions for
the Oakmont of Carlsbad Project, located on an approximately 6.4 acre site, designated by Assessor's
Parcel Number (APN) 20912001. The project site is located at the intersection of Faraday Avenue
and El Fuerte Street within the City of Carlsbad, California.
The biological resources assessment is required to determine the extent of sensitive biological
resources present within the project site and adjacent to the project site. The project site has been
previously improved/graded and contains landscape plantings along the southern and western
boundaries of the parcel. The previous site improvements also include site recontouring of the
surface hydrology to transport water to the eastern portion of the site where a drain has been
installed. Disturbed lands occur throughout the rest of the site. The disturbed lands are
characterized by bare ground and weedy plant species. Within the Disturbed Lands landcover
category vegetative cover is dominated by several plant species including yellow star thistle
(Centaurea melitensis), filaree (Erodium botrys), fascicled tar plant (Deinandra fascicu/atum), vulpia
(Vulpia myuros) and red brome (Bromus madritensis). In addition, coastal sage-chaparral scrub
occurs adjacent to the northern, western and eastern boundary of the project site. This habitat is
dominated by California sagebrush (Artemisia californica), California buckwheat (Eriogonum
fascicu/atum), toyon (Heteromeles arbutifolia), mission manzanita (Xylococcus bico/or) and coyote
bush (Baccharis pilularis). This habitat is part of the Carlsbad Multiple Habitat Conservation Program
(MHCP) Preserve area and is identified within the Carlsbad Oaks preserve designation. The project
site does not contain any jurisdictional waters or wetland habitats.
The entire project site will be impacted by the proposed development. This includes 5.1 acres of
disturbed habitat, and 1.3 acres of landscaped/ornamental vegetation. Impacts to these landcover
types are not sensitive and will not require mitigation. However, the project site does contain bare
ground and low growing vegetation, which provide suitable nesting habitat for migratory birds.
Ground disturbance and vegetation removal should be conducted outside of the nesting season
(February 1 to September 1) because of the likelihood that the site will be used for nesting. If these
activities must occur during the nesting season, a pre-construction nesting bird survey should be
conducted prior to any ground-disturbing activities or vegetation removal.
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Oakmont Senior Living-Oakmont of Carlsbad
Biological Resources Assessment Introduction
SECTION 2: INTRODUCTION
At the request of Oakmont of Carlsbad, First Carbon Solutions (FCS} conducted a biological resources
assessment to document the existing conditions within the 6.4-acre vacant project site, located in
Carlsbad, San Diego County, California. This report provides a detailed description of existing
conditions. The information contained herein includes a literature review and general biological site
assessment that identify the potential biological constraints related to the proposed development of
the property. This report provides a baseline for review under the California Environmental Quality
Act (CEQA), the Clean Water Act (CWA), the Federal Endangered Species Act (FESA}, and the
California Endangered Species Act (CESA). The report has also been prepared to be consistent with
the North County Multiple Habitat Conservation Program (MHCP).
2.1-Project Site Location
The 6.4-acre site is located north at the intersection of Faraday Avenue and El Fuerte Street within
the eastern portion of Carlsbad, Ca lifornia (Exhibit 1). The project site is situated in Township 12
South, and Range 4 West of the San Luis Rey, California, United States Geological Survey (USGS} 7.5-
minute topographic map (Exhibit 2).
2.2 -Regulatory Framework
Potential impacts to biological resources as a result of the proposed project were analyzed based
upon the environmental policies and regulations discussed in Appendix C. These include regulations
set forth by the United States Fish and Wildlife Service (USFWS}, U.S. Army Corps of Engineers
(USACE), and the California Department of Fish and Wildlife (CDFW}. Regulations include the Clean
Water Act (CWA), FESA, CESA, and CEQA. In addition, this project is also subject to City's approved
MHCP. The project site is located adjacent to the Carlsbad Oaks North Preserve area and will be
subject to MHCP adjacency guidelines (Exhibit 3).
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Oakmont Senior Living-Oakmont of Carlsbad
Biologicol Resources Assessment Methodology
SECTION 3: METHODOLOGY
Analysis of the biological resources for the project site began with a thorough review of relevant
literature, followed by a reconnaissance-level survey. The primary objective of the survey was to
document the existing site conditions and determine the potential presence of sensitive biological
resources.
For the purpose of this report, sensitive species refers to all species formally listed as threatened
and/or endangered under the FESA and CESA, California Species of Special Concern, those
designated as Fully Protected by CDFW; given a status of California Rare Plant Rank (CRPR} lA, 18, 2,
3 or 4 by the California Native Plant Society (CNPS); or designated as sensitive by city, county, or
other regional planning documents. Federal and state listed threatened and/or endangered species
are legally protected under the ESA. Species listed as California Species of Special Concern or given a
status by the CNPS have no direct legal protection under FESA or CESA, but they require a
significance analysis under the CEQA guidelines.
3.1-Literature Review
The literature review provides a baseline from which to evaluate the biological resources potentially
occurring on the project site, as wel l as the surrounding area.
3.1.1 -Topographic Maps and Aerial Photographs
FCS reviewed current USGS 7.5-minute topographic quadrangle map(s) and aerial photographs (see
Exhibit 2) as a preliminary analysis of the existing conditions within the project site and immediate
vicinity. Information obtained from the review of the topographic maps included elevation, general
watershed information, and potential drainage feature locations. Aerial photographs provide an
aerial perspective of the most current site conditions with regard to on-site and off-site land-use,
plant community location, and potential location of wildlife movement corridors.
3.1.2 -Soil Surveys
Many sensitive plant species have a limited distribution based exclusively on soil type. The United
States Department of Agriculture (USDA) has published soil surveys that describe the soil series
occurring within a particular area. A soil series is a group of soils with similar profiles. These profiles
include major horizons with similar thickness, arrangement, and other important characteristics.
These series are further subdivided into soil mapping units, which provide specific information
regarding soil characteristics. Pertinent USDA soil survey maps were reviewed to determine the
existing soil mapping units within the project site and to establish if soil conditions on-site are
suitable for any sensitive plant or wildlife species.
3.1.3 -Sensitive Species Database Search
FCS compiled a list of threatened, endangered, and otherwise sensitive species previously recorded
within the general area of the site. For the purpose of this report, "sensitive species" are defined as
those protected by FESA or CESA, designated as a California Species of Special Concern, designated
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Methodology
Oakmont Senior Living-Oakmont of Carlsbad
Biological Resources Assessment
as Protected or Fully Protected by CDFW; given a status by the CNPS; or designated as sensitive by
city, county, or regional planning documents. A compilation of sensitive plant and wildlife species
recorded in the vicinity of the site was derived from the CDFW's California Natural Diversity Database
(CNDDB 2017). Additional recorded occurrences of plant species found on or near the site were
obtained in the CNPS Electronic Inventory of Rare and Endangered Vascular Plants of California
database. The CNDDB GIS database was utilized, together with ArcGIS software, to determine
sensitive species located within a 5-mile radius of the project site. Federal Register listings,
protocols, and species data provided by the USFWS and CDFW were reviewed in conjunction with
anticipated federal and state listed species potentially occurring in the vicinity. These and other
documents are listed in Section 8, References.
3.2 -Reconnaissance-Level Survey
FCS Biologist Korey Klutz conducted the reconnaissance-level field survey on May 10th, 2017. Special
attention was paid to sensitive habitats or those areas potentially supporting sensitive floral and
fauna I species, as well as potential jurisdictional features. In addition, a follow-up survey to update
and confirm the original survey results was conducted by Mr. Klutz on July i h, 2017.
Both surveys were reconnaissance-level surveys and were conducted on foot during daylight hours.
The object of the surveys was not to extensively search for every species occurring within the project
site, but to ascertain general site condit ions and identify potentially suitable habitat areas for various
sensitive plant and wildlife species.
3.2.1 -Plant Community Mapping
Plant communities were mapped using 7.5-minute USGS topographic base maps and recent aerial
photography. Sensitive or unusual biological resources identified during the literature review were
ground-truthed during the reconnaissance-level survey for mapping accuracy. The plant
communities within the project site were classified according to The Vegetation Communities of San
Diego County (Oberbauer, 2010).
3.2.2 -Plant Species
Common plant species observed during the reconnaissance-level survey were identified by visual
characteristics and morphology in the field and recorded in a field notebook. Uncommon and less
familiar plants were identified off-site using taxonomical guides. A list of all species observed on the
project site was compiled from the survey data, shown in Appendix A. Taxonomic nomenclature
used in this study follows The Jepson Manual Second Edition {2012). Common plant names, when
not available, were taken from other regionally specific references. In this report, scientific names
are provided immediately following common names of plant species for the first reference only.
3.2.3 - Wildlife Species
Wildlife species detected during the reconnaissance-level survey by sight, calls, tracks, scat, or other
signs were recorded in a field notebook. Notations were made regarding suitable habitat for those
sensitive species determined to potentially occur within the project site. Appropriate field guides
were used to assist with species identification during surveys. Common names of wildlife species
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are standard; however, scientific names are provided immediately following common names for the
first reference only. Appendix A lists all wildlife species observed or detected on the site during the
survey.
3.2.4 -Jurisdictional Waters and Wetlands
Prior to conducting the site visit, FCS's biologist reviewed USGS topographic maps and aerial
photography to identify any potential natural drainage features and water bodies that may fall within
the jurisdiction of the USACE, RWQCB, and/or CDFW. In general, all surface drainage features
indicated as blue-line streams on USGS maps and linear patches of vegetation expected to exhibit
evidence of flows are considered potentially subject to state and federal regulatory authorities as
"waters of the U.S. and/or State." The assessment was not intended as a formal delineation of
waters of the U.S. or State, but rather to identify areas that may require a formal delineation.
3.2.5 -Wildlife Movement Corridors
Wildlife movement corridors link areas of suitable wildlife habitat that are otherwise separated by
rugged terrain, changes in vegetation, or human disturbance. The fragmentation of open space
areas by urbanization creates isolated "islands" of wildlife habitat, separating different populations
of a single species. Corridors effectively act as links between these populations.
The project site was evaluated for evidence of a wildlife movement corridor. The scope of the
biological resources survey did not include a formal wildlife movement corridor study such as the
use of track plates, camera stations, scent stations, or snares. However, the focus of this study was
to determine if the alteration of current land use on the project site would have significant impacts
on the regional movement of wildlife. These conclusions are based on the information compiled
from the literature review, including aerial photographs, USGS topographic maps, and resource maps
for the vicinity, the reconnaissance-level survey, and knowledge of desired topography and resource
requirements for wildlife potentially utilizing the project site and vicinity.
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Oakmont Senior Uving-Oakmont of Carlsbad
Biological Resources Assessment Existing Conditions
SECTION 4: EXISTING CONDITIONS
4.1-Weather Conditions
Weather conditions during the May 10th, 2017 survey consisted of overcast skies, with an average
temperature of 65 degrees Fahrenheit. Weather conditions during the second survey (July 7th, 2017)
consisted of clear skies, with an average temperature of 85 degrees Fahrenheit.
4.2 -Environmental Setting
The project site is located in the eastern portion of Carlsbad, north of Faraday Avenue and at the
northern terminus of El Fuerte Street. The site is located on a relatively flat, previously graded pad
at an elevation of approximately 260 feet above mean sea level (AMSL).
The sout hern portion of the site is bounded by Faraday Avenue and includes a linear strip of existing
landscaped vegetation. The landscaping buffer extends along the western boundary of the site but at
the parcel boundary coastal sage-chaparral scrub occurs. This native habitat also is adjacent to the
northern and eastern portion of the site. Vegetation present throughout the project site has been
disturbed and can be generally classified as poor quality. The plant communities lack native soil
structure and appear to be maintained/cleared periodically for fuel management purposes. It should
be noted that the native habitat adjacent to the project site is within the City's Carlsbad Oaks Preserve.
4.3 -Soils
Based on the USDA-Natural Resources Conservation Service, two soil types occur on-site including
Huerhuero loam, 9 to 15 percent slopes, and Cieneba coarse sandy loam, 30 to 65 percent slopes
(Exhibit 4). However, as previously stated, the entire project site has been previously disturbed by
site recontouring. The existing soil profiles have been disturbed and it is likely that additional fill
material has been imported to the site.
4.4 -Plant Communities
The project site contains two landcover types including landscaped/ornamental vegetation and
disturbed habitat (Exhibit 5). Overall, the plant communities on-site have been disturbed due to
prior site grading. There are very few native understory species and bare ground is abundant.
Adjacent to the site both developed lands and mature coastal sage-chaparral scrub occur. This
section provides a description of the plant communities that occur on-site and immediately adjacent
to the project site. A complete list of plants observed on-site and immediately adjacent to the
project site is provided in Appendix B.
4.4.1 -Disturbed Habitat (5.1 acres)
Disturbed habitat is any land on which the native vegetation has been significantly altered by
agriculture, construction, or other land-clearing activities, and the species composition and site
conditions are not characteristic of the disturbed phase of a plant association (e.g. disturbed Diegan
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Existing Conditiom
Oakmont Senior Living-Oakmont of Carlsbad
Biologlcol Resources Assessment
Coastal Sage Scrub). On-site this landcover is primarily dominated by bare ground and scattered
vegetation including filaree, red brome, vulpia and fascicled tarplant. This landcover type appears to
be routinely cleared/disturbed for fuel management purposes. Approximately 5.1 acres of disturbed
habitat were mapped within the development parcel.
4.4.2 -Landscaped/Ornamental Vegetation (1.3 acres)
Landscaped/ornamental vegetation occurs along the southern and western boundaries of the
project site. The southern portion consists of an approximately 700-foot long by SO-foot wide patch
of landscaped vegetation adjacent to Faraday Avenue. The western landscaped area occurs on an
irrigated cut slope and is dominated by acacia (Acaccia longiflora), Plumbago (Plumbago sp) and
lemonade berry (Rhus integrifolia). Several coast live oak trees (Quercus agrifolia) were also planted
in this area but are now dead. Due to the proximity of the adjacent habitats and the fact that little
maintenance has occurred in this area, an understory of non-native grasses and native shrubs also
occur. Non-native grasses observed included red brome, vulpia and rip-gut (Bromus diandrus).
Native shrubs observed included golden bush (lsocoma menziesii), California buckwheat, coyote
bush and deerweed (Acmispon scoparious). Approximately 1.3 acres of landscaped/ornamental
vegetation occurs within the property.
4.4.3 -Coastal Sage-Chaparral Scrub (off-site)
Diegan coastal sage/chaparral scrub is a "hybrid" of two common vegetation types and usually
indicates either an area of sage scrub growing on disturbed substrates, converting into a mature
chaparral vegetation; or a mature ecotone in which ecological conditions for each of these two
vegetation types does not allow one habitat type to out-compete the other. This plant community is
characterized by aromatic shrubs and subshrubs characteristically dominated by drought-deciduous
species. Dominant species observed included California sagebrush (Artemisia californica), toyon
(Heteromoles arbutifolia), mission manzanita (Xylococcus bicolor), California buckwheat (Eriogonum
fasciculatum), black sage (Salvia mel/ifera), and laurel sumac (Malosma laurina). Nuttall's scrub, a
sensitive plant, was observed off-site within this plant community. This habitat type does not occur
on-site but is abundant off-site along the western and northern boundaries of the project site.
4.5 -Wildlife
Most of the wildlife activity on the project site was represented by avian species. The habitats on
the project site provide minimal foraging, cover, and nesting habitat for year-round residents,
seasonal residents, and migrating songbird species. Common species observed include California
towhee (Pipilo crissalis), Bewick's wren (Thryomanes bewickii), bushtit (Psaltriparus minimus),
western scrub jay (Aphelocoma californica), California quail (Cal/ipepla californica), common raven
(Corvus corax), and killdeer (Charadrius vociferous)
Common mammal species observed during the surveys included California ground squirrel
(Sphermophilus beecheyi), coyote scat (Canis latrans), and mule deer scat (Odocoileus hemionus).
Only one reptile species was observed during the survey and it was a western fence lizard (Sceloporus
occidentalis). A list of all flora and fauna observed during the survey is included in Appendix B.
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Oakmont Sen/or Living-Oakmont of Carlsbad
Biological Resources Assessment
SECTION 5: SENSITIVE BIOLOGICAL RESOURCES
5.1 -Critical Habitat
Sensitive Biological Resources
The project site does not occur within any USFWS designated Critical Habitat. However, the western
boundary is immediately adjacent to designated coastal California gnatcatcher (Polioptilo ca/ifornica
colifornico) Critical Habitat.
5.2 -Sensitive Plant Communities
A review of the CNDDB resulted in one sensitive plant community, southern maritime chaparral, as
being reported to occur within the vicinity of the project site. This plant community was not
observed within the project site but may occur w ithin the off-site habitat north of the project site.
The entire project site will be impacted by the proposed development. Impacts to disturbed habitat
(5.1 acres) and landscape/ornamental vegetation (1.3 acres) are not considered significant and will
not require mitigation (Exhibit 6).
5.3 -Special Status Species
5.3.1 -Threatened and Endangered Wildlife Species
Tables 1 and 2 in Appendix A identify the sensitive plant and wildlife species known to occur within
the vicinity of the project site, their status, habitat requirements, and their potential to occur within
the project site. The project site does not contain suitable habitat for any threatened or endangered
plant or wildlife species. However, it should be noted that the federally threatened California
gnatcatcher is known to occur in the habitat immediately adjacent to the project site.
5.3.2 -State Fully Protected Species
State-listed fully protected species were not observed during the site visit, nor are any anticipated to
occur on the project site.
5.3.3 -Sensitive Plant Species
A review of the CNDDB resulted in eight sensitive plant species reported to occur within the vicinity
of the project site and are presented in Appendix A. The project site does not contain suitable
habitat for any sensitive plant populations. However, it should be noted that Nuttall's scrub oak was
observed within the off-site habitat north of the project site.
5.3.4 -Sensitive Wildlife Species
California Species of Special Concern (CSC) do not have legal protection under ESA or CESA but are
recognized as sensitive by CDFW and therefore, require an independent assessment under the CEQA
process to determine if project-related impacts are significant. After review of the CNDDB, no CSC
species has a moderate to high potential to occur on-site. Furthermore, no CSC species were
observed during the field surveys.
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Sensitive Biological Resources
Oakmont Senior Uving-Oakmont of Carlsbad
Biological Resources Assessment
5.4 -Jurisdictional Waters and Wetlands
The project site does not contain any jurisdictional waters or wetlands. Surface flows appear to
drain on-site into an existing storm drain located in the southeastern portion of the project site.
5.5 -Wildlife Movement Corridors
Wildlife movement corridors link areas of suitable wildlife habitat that are otherwise separated by
rugged terrain, changes in vegetation, or human disturbance. The fragmentation of open space
areas by urbanization creates isolated "islands" of wildlife habitat, separating different populations
of a single species. Corridors effectively act as links between these populations.
The project site has been previously disturbed and does not contain any regional or local wildlife
corridors. Wildlife is anticipated to migrate locally within the adjacent habitat north, west and east
of the site.
5.6 -Nesting Birds
The Migratory Bird Treaty Act (MBTA) protects all common wild birds and their nests found in the
United States (U.S.) except the house sparrow, starling, feral pigeon, and resident game birds such as
pheasant, grouse, quail, and wild turkey. The MBTA makes it unlawful for anyone to kill, capture,
collect, any migratory bird including feathers, parts, nests, or eggs.
The project site contains vegetative cover, which provides suitable nesting habitat for a variety of
avian species. The trees within the landscaped/ornamental vegetation on the project site could
provide suitable nesting habitat for raptor species. The disturbed habitat may provide suitable
nesting habitat for ground-nesting species such as western meadowlark (Sturnella neglecta) and
killdeer (Charadrius vociferus).
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Oakmont Senior Uvlng-Oakmant of Carlsbad
Blologlcol Resources A.s.sessment Impact Analysis and Recommendations
SECTION 6: IMPACT ANALYSIS AND RECOMMENDATIONS
The following discussion addresses potential impacts to sensitive biological resources resulting from
the proposed project and provides recommendations for future surveys, if needed.
6.1 -Sensitive Plant Communities
The project site does not contain any sensitive plant communities. Implementation of the project
will impact 5.1 acres of disturbed habitat and 1.3 acres of landscaped/ornamental vegetation.
Therefore, no sensitive plant communities will be impacted by the proposed project.
6.2 -Critical Habitat
As discussed in Section 5.1, above, the project site borders California gnatcatcher (Polioptila
ca/1fornica californica) designated critical habitat to the west . As a result, noise related to project
construction has the potential cause a significant indirect impact to California gnatcatcher critical
habitat during the gnatcatcher breeding season (March 1 to August 15). Construction activities
should avoid the gnatcatcher breeding season. However, if the nesting season cannot be avoided,
the following measure will be implemented:
• The off-site suitable coastal sage scrub habitat is located on private land (APN 209-050-25 &
APN 209-120-08). Authorization to access these properties to conduct nesting bird surveys
will require owner authorization. If authorization is not granted, the City of Carlsbad will
provide direction to ensure no indirect impacts occur to nesting bird species as a result of
project initiation.
• A single pre-construct ion nesting bird survey will be conducted by a qualified biologist in
appropriate habitat for all nesting MBTA covered bird species including the coastal California
gnatcatcher within a 500-ft survey buffer within three (3) days of construction.
• The USFWS will be notified immediately of any federally listed species that are located during
pre-construction surveys.
• If nests of listed birds, migratory birds, raptors, or other sensitive species are located, they will
be fenced with a protective buffer of at least 500 ft. from active nests of listed species, and
300 ft. from common bird species. All construction activity will be prohibited within this area.
• During the breeding season, construction noise will be measured regularly to maintain a
threshold at or below 60dBA hourly l,,q within 500 ft. of breeding habitat occupied by listed
species. If noise levels supersede the threshold, the construction array will be changed or
noise attenuation measures will be implemented until a qualified biologist determines that
the nestlings have successfully fledged.
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Impact Analysis and Recommendations
6.3 -Special-status Species
Oakmont Senior Uving-Oakmant of Carlsbad
Biological Resources Assessment
6.3.1 -Threatened and Endangered Species
According to the CNDDB, no endangered or threatened species have been documented as occurring
on the project site. Additionally, no endangered or threatened species were observed during the
reconnaissance-level survey. Although endangered and threatened species have been recorded
within the vicinity of the project site (e.g., California gnatcatcher), suitable habitat does not occur
on-site.
6.3.2 -State Fully Protected Species
No state fully protected species were observed on-site and none are ant icipated to occur on the
project site. Therefore, implementation of the proposed project is not expected impact State Fully
Protected species.
6.3.3 -Sensitive Plant Species
No sensitive plant populations were observed on-site and none are anticipated to occur on-site.
Therefore, implementation of the proposed project is not expected impact sensitive plant species.
6.3.4 -Sensitive Wildlife Species
CSC wildlife species do not have potential to occur on-site. Therefore, implementation of the
proposed project is not expected impact CSC species.
6.4 -Jurisdictional Waters and Wetlands
The project site does not contain jurisdictional waters or wetland habitat. Therefore,
implementation of the proposed project is not expected to impact any jurisdictional resources.
6.5 -Wildlife Movement Corridors
Local or regional wildlife movement corridors do not occur on-site. Therefore, implementation of
the proposed project is not expected impact wildlife movement corridors.
6.6 -Nesting Birds
The project site contains suitable nesting habitat for a number of different avian species. The shrubs
on the project site provide nesting opportunities for several songbirds. The trees on the project site
could provide suitable nesting habitat for raptor species. Impacts to nesting birds are a violation of
the Migratory Bird Treaty Act (MBTA) and CDFW Code. If ground or vegetation disturbance occurs
during the nesting season (February 15 t hrough September 15}, nesting birds may be directly or
indirectly impacted, which is a significant impact.
Clearing and grubbing activities are generally prohibited during the bird breeding season (February
15-September 15}. However, clearing and grubbing activities can occur if a preconstruction survey is
performed. The United States Fish and Wildlife Service (USFWS) must be notified at least seven days
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Biological Resources Assessment Impact Analysis and Recommendations
before clearing and grubbing begins. During this activity, a qualified biologist will walk the area
ahead of construction equipment to flush birds away from impact areas. The biologist will
immediately report to USFWS the number and location of any federally listed birds disturbed by
clearing and grubbing.
Other construction activities will also be avoided during the breeding season if feasible. If this
cannot be avoided, the following measures will be taken:
• Surveys will be conducted by a qualified biologist in appropriate habitat for nesting raptors
and migratory birds (including, but not limited to the least Bell's vireo) and within an
additional 500-ft survey buffer within three days of construction.
• The USFWS will be notified immediately of any federally listed species that are located during
pre-construction surveys.
• If nests of listed birds, migratory birds, raptors, or other sensitive species are located, they will
be fenced with a protective buffer of at least 500 feet from active nests of listed species, and
300 feet from other sensitive bird species. All construction activity will be prohibited within
this area.
• During the breeding season, construction noise will be measured regularly to maintain a
threshold at or below 60 dBA hourly equivalent continuous noise level (Leq) within 500 feet of
breeding habitat occupied by listed species. If noise levels exceed the threshold, the
construction array will be changed or noise attenuation measures will be implemented.
6.7 -MHCP Adjacency Standards
Direct and indirect impacts may negatively affect sensitive species and sensitive habitats that are
adjacent to a property that is being or has been developed. For example, temporary impacts during
construction, such as noise and dust, could affect nearby nesting birds. Permanent impacts might
include edge effects which could result in invasion by non-native plant species. To avoid these
potential impacts, Adjacency Standards have been developed which apply to properties that are
adjacent to conserved habitat areas or undeveloped portions of a Standards Area that might be
conserved. The standards address issues of fire management, erosion control, landscaping, fencing,
signage, indirect impacts, and non-native species control. A selection of project-related Habitat
Management Plan (HMP) Adjacency Standards is provided below:
• Fuel management. Where existing Hard line Preserve areas are adjacent to existing developed
areas, the fuel management zone may continue to encroach into the preserve. However,
where new development or preservation is planned, fuel management must be incorporated
within the development boundaries and cannot encroach into the preserve.
• Positioning of fuel modification areas. Fuel reduction zones, fire breaks and access routes
should be positioned to (1) avoid sensitive biological resources, (2) be located at the top or
bottom of (not across) a slope, or (3) be located along existing fire breaks where available.
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• Erosion control measures should be implemented to avoid new surface drainage or erosion
within or near the preserve.
• The use of non-native or invasive plant species in landscaping for public projects adjacent to
preserves is prohibited.
• Native plants used for restoration or revegetation should be obtained from local genetic stock
to avoid genetic contamination of native species.
• Irrigation runoff should be prevented from entering into the preserve from adjacent
landscaping to reduce nitrogen, pesticides, and excess moisture.
• Signage and fencing should be used as necessary to prevent harmful or unauthorized use of
the adjacent preserve, and to protect animals from road kill mortality. Fences that restrict
animal movement across movement corridors and habitat linkages should be removed.
• Lighting adjacent to preserves should be reduced (low pressure sodium lighting) and/or
shielded.
• Noise. The use of noise generating equipment should be avoided during the breeding season.
Noise levels inside the preserve should not exceed 60 dBA Lew
• Public outreach should be used to educate the residents of adjacent neighborhoods about not
using invasive species in landscaping, overuse of pesticides and fertilizers, and the problem of
unleashed pets and pet waste.
As proposed, the project has been designed to incorporate the Adjacency Standards detailed above.
In addition, a 60-foot fuel management area has been established along the perimeter of the project
site. The fuel management area is located entirely within the project site and will not impact the
adjacent Carlsbad Oak North Preserve lands.
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SECTION 8: REFERENCES
Burt, W.H., and Grossenheider, R.P. 1980. Peterson Field Guides, Mammals. Houghton Mifflin
Company. New York, New York.
California Department of Fish and Wildlife (CDFW). 2003. Natural Communities List. The Resources
Agency of California, Department of Fish and Wildlife, Natural Diversity Data Base.
Sacramento, California.
California Department of Fish and Wildlife (CDFW). 2014. Special Animals List. The Resources
Agency of California, Department of Fish and Wildlife, Natural Heritage Division, Natural
Diversity Data Base. Sacramento, California.
California Department of Fish and Wildlife (CDFW). 2016. Endangered and Threatened Animals List.
The Resources Agency of California, Department of Fish and Wildlife, Natural Heritage
Division, Natural Diversity Data Base. Sacramento, California.
California Department of Fish and Wildlife (CDFW). 2016. Endangered, Threatened, and Rare
Plants. The Resources Agency of California, Department of Fish and Wildlife, Natural
Heritage Division, Natural Diversity Data Base. Sacramento, California.
California Department of Fish and Wildlife (CDFW). 2016. Special Vascular Plants, Bryophytes, and
Lichens List. The Resources Agency of California, Department of Fish and Wildlife, Natural
Heritage Division, Natural Diversity Data Base. Sacramento, California.
California Native Plant Society (CNPS). 2017. California Native Plant Society's Electronic Inventory
of Rare and Endangered Vascular Plants of Ca lifornia.
California, State of. 1989. Fish and Wildlife Code.
Hickman, J.C. 1993. The Jepson Manual: Higher Plants of California. University of California Press.
Berkeley, California.
Holland, R.F. 1986 (updated 1996). Preliminary Descriptions of the Terrestrial Natural Communities
of California. Non-game Heritage Program. California Department of Fish and Wildlife.
Sacramento, California.
Munz, P.A. 1974. A Flora of Southern California. University of California Press. Berkeley, California.
National Geographic Society. 1999. National Geographic Society Field Guide to the Birds of North
America. 3rd Edition. National Geographic Society, Washington, DC.
Sawyer, J.O. and T. Keeler-Wolf. 1995. A Manual of California Vegetation. California Native Plant
Society. Sacramento, California.
Stebbins, R. C. 2003. A Field Guide to Western Reptiles and Amphibians. 2nd Edition. Houghton-
Mifflin Company. Boston, Massachusetts.
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31
References
Oakmont Senior Living-Oakmont of Carlsbad
Biological Resources Assessment
Tibor, D. P. 2001. California Native Plant Society's Inventory of Rare and Endangered Plants of
California. California Native Plant Society. Special Publication, No. 1, 61h Edition.
U.S. Fish and Wildlife Service (USFWS). 1993 (Sep 30). Plant Taxa for Listing as Endangered or
Threatened Species; Notice of Review. Federal Register 50 CFR Part 17. U.S. Department of
the Interior. Washington, DC.
U.S. Fish and Wildlife Service (USFWS). 1994 (Nov 15). Endangered and Threatened Wildlife and
Plants; Animal Candidate Review for Listing as Endangered or Threatened Species. Federal
Register SO CFR Part 17. U.S. Department of the Interior. Washington, DC.
U.S. Fish and Wildlife Service (USFWS). 1997c {Oct. 31). Endangered and Threatened Wildlife and
Plants. Federal Register SO CFR Part 17.11 and 17.12. U.S. Department of the Interior.
Washington, DC.
U.S. Fish and Wildlife Service (USFWS). 2008 (Oct. 17). Endangered and Threatened Wildlife and
Plants; Designation of Critical Habitat for the San Bernardino Kangaroo Rat (Dipodomys
merriami parvus); Final Rule. Federal Register 50 CFR Part 17, Vol. 73, No. 202. U.S.
Department of the Interior. Washington, DC.
U.S. Geological Survey (USGS). 1967 and Photo revised 1981. la Habra, California 7.5-Minute
Topographic Map.
Udvardy, M.D. 1994. National Audubon Society Field Guide to North American Birds. Alfred A.
Knopf, Inc. New York, New York.
United States Army Corps of Engineers (USACE). 1987. Wetlands Delineation Manual, Technical
Report Y-87-1, U.S. Army Engineer Waterways Experiment Station, Vicksburg, Mississippi.
United States Department of Agriculture (USDA). 1979. Soil Survey of San Bernardino County,
Southwestern Part, California. Department of the Interior. U.S. Government Printing Office.
Washington, DC.
United States Department of Agriculture (USDA). 1989. Alluvial Scrub Vegetation of Southern
California. Ted L. Hanes, Richard D. Friesen, and Kathy Keane. USDA Forest Service Gen.
Tech. Rep. PSW-110. 1989.
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Appendix A:
Sensitive Species Tables
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Species
Table 1 {cont.): Species Status Plant Species
I Status j
Scientific Name I Common Name 1 USFWS I CDFW CNPS Preferred Habitat Potential On-site/Suitable Habitat
Code Designations
U.S. Fish and Wildlife Service-State California Native Plant Society
FE Federal Endangered CE California Endangered 1B Plants rare, t hreatened, or endangered in California and elsewhere. Plants rare,
FT Federal Threatened CT California Threatened threatened, or endangered in California, but more common elsewhere.
PE Proposed Endangered 1 Seriously endangered in California.
PT Proposed Threatened 2 Fairly endangered in California.
3 We need more information about this plant
4.2 Plants of limited distribution; fairly threatened in California
Table 2: Special Status Wildlife Species
Species Status Potential to Occur/Known T
-
Scientific Name Common Name Federal State Required Habitat Occurrence/Suitable Habitat
Reptiles and Amphibians
Aspidoscelis hyperythra orangethroat -CDFW Coastal sage scrub and chaparral habitats Not detected. Suitable habitat occurs
whiptail watch list immediately adjacent to the project site.
Phrynosoma b/ainvillii coast horned Species -This species may be found in grassland habitats containing Not detected. Suitable habitat occurs
lizard of vernal pools essential for breeding and egg-laying. immediately adjacent to the project site.
Special
Concern
Plestiodon skiltonianus Coronado Island -CDFW Coastal sage scrub and chaparral habitats Not detected. Suitable habitat occurs
interparieta/is skink watch list immediately adjacent to the project site.
Salvadora hexa/epis coast patch-Species -Inhabits semi-arid brushy areas and chaparral in canyons, Not detected. Suitable habitat occurs
virgultea nosed snake of rocky hillsides, and plains. immediately adjacent to the project site. Special
Concern
Birds
Aimophila ruficeps southern -CDFW This bird occurs in southern California coastal sage scrub Not detected. Suitable habitat occurs
canescens California rufous-watch list plant communities and require tall Opuntia cactus for immediately adjacent to the project site.
crowned sparrow nesting and roosting.
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Appendix B:
Flora Compendium
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Scientific Name Common Name Special Status Nativity Cal_lPC_Rank Family Common
-Onagraceae-Evening Clarkia purpurea Purple clarkia NATIVE -Primrose family
Cortaderia selloana Pampas grass -NATURALIZED High Poaceae-Grass family
Longbeak -Geraniaceae-Erodium botrys NATURALIZED -filaree Geranium family
Festuca myuros Rattail fescue -NATURALIZED Moderate Poaceae-Grass family
Fennel -Apiaceae-Carrot Faeniculum vu/gore NATURALIZED High family
~
Heteromeles --Rosaceae-Rose family arbutifo/ia Toyon NATIVE
'---
Heterotheca Telegraph --Asteraceae-Sunflower
grandiflora weed NATIVE family
Smooth cat's--Asteraceae-Sunflower Hypochaeris glabra NATURALIZED Limited family ear
Jsocoma menziesii Coastal --Asteraceae-Sunflower
var. menziesii goldenbush NATIVE family
Lactuca serriola Prickly lettuce --Asteraceae-Sunflower NATURALIZED family
Marsh --Plumbaginaceae-Limonium sp. NATURALIZED rosemary Leadwort family
--Fabaceae-Legume Lupinus succu/entus Arroyo lupine NATIVE family
Malosma /aurina Laurel sumac --Anacardiaceae-Sumac NATIVE Or Cashew family
Melilotus indicus Indian --Fabaceae-Legume
sweetclover NATURALIZED family
Platanus racemosa Western --Platanaceae-Plane NATIVE Tree, Sycamore family sycamore
Polypogon Rabbit foot -
monspeliensis beard grass NATURALIZED Limited Poaceae-Grass family
Quercus dumosa Nuttall's scrub
oak CRPR 18.1 -NATIVE Fagaceae-Oak family
Rhus integrifo/ia Lemonade --Anacardiaceae-Sumac
berry NATIVE Or Cashew family
-Polygonaceae-Rumex crispus Curly dock NATURALIZED Limited Buckwheat family -
Salix /aevigata Red willow --Salicaceae-Willow NATIVE family ,._
Salvia apiana White sage --Lamiaceae-Mint NATIVE family
--
Scientific Name Common Name Special Status Nativity Cal_lPC_Rank Family Common -
Sonchus asper ssp. Prickly sow --Asteraceae-Sunflower NATURALIZED asper thistle family
Indian rice --Poaceae-Grass family Stipa hymenoides NATIVE grass -
Xylococcus bicolor Mission --Ericaceae-Heath
manzanita NATIVE family
California --Gentianaceae-Gentian
Zeltnera venusta NATIVE family centaury
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Appendix C:
Regulatory Framework
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REGULATORY FRAMEWORK
Sensitive Plant and Wildlife Species
Sensitive species are native species that have been accorded special legal or management protection
because of concern for their continued existence. There are several categories of protection at both
federal and state levels, depending on the magnitude of threat to continued existence and existing
knowledge of population levels.
Federal Endangered Species Act
The United States Fish and Wildlife Service (USFWS) administers the Federal Endangered Species Act
(ESA). The ESA provides a process for listing species as either threatened or endangered, and
methods of protecting listed species. The ESA defines as "endangered" any plant or animal species
that is in danger of extinction throughout all or a significant portion of its known geographic range.
A "threatened" species is a species that is likely to become endangered. A "proposed" species is one
that has been officially proposed by the USFWS for addition to the federal threatened and
endangered species list.
ESA Section 9 prohibits "take" of threatened or endangered species. The term "take" means to
harass, harm, pursue, hunt, shoot, wound, kill, trap, capture, or collect, or to attempt to engage in
such conduct. Take can include disturbance to habitats used by a threatened or endangered species
during any portion of its life history. The presence of any federally threatened or endangered
species in a project area generally imposes severe constraints on development, particularly if
development would result in "take" of the species or its habitat. Under the regulations of the ESA,
the USFWS may authorize "take" when it is incidental to, but not the purpose of, an otherwise lawful
act.
California Endangered Species Act
The California Department of Fish and Wildlife (CDFW) administers the California Endangered
Species Act (CESA). The State of California considers an "endangered" species one whose prospects
of survival and reproduction are in immediate jeopardy. A "threatened" species is one present in
such small numbers throughout its range that it is likely to become an endangered species in the
near future in the absence of special protection or management. A "rare" species is one present in
such small numbers throughout its portion of its known geographic range that it may become
endangered if its present environment worsens. The rare species designation applies to California
native plants. State threatened and endangered species are fully protected against take, as defined
above. The term "species of special concern" is an informal designation used by CDFW for some
declining wildlife species that are not state candidates for listing. This designation does not provide
legal protection, but signifies that these species are recognized as sensitive by CDFW.
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Th e California Native Plant Society (CNPS) is a California resource conservation organization that has
developed and inventory of California's sensitive plant species. This inventory summarizes
information on the distribution, rarity, and endangerment of California's vascular plants. The
inventory is divided into four lists based on the rarity of the species. In addition, the CNPS provides
an inventory of plant communities that are considered sensitive by the state and federal resource
agencies, academic institutions, and various conservation groups. Determination of the level of
sensitivity is based on the number and size of remaining occurrences as well as recognized threats.
M igratory Bird Treaty Act
The Migratory Bird Treaty Act (MBTA) protects all common wild birds found in the United States
(U.S.) except the house sparrow, starling, feral pigeon, and resident game birds such as pheasant,
grouse, quail, and wild turkey. Resident game birds are managed separately by each state. The
MBTA makes it unlawful for anyone to kill, capture, collect, possess, buy, sell, trade, ship, import, or
export any migratory bird including feathers, parts, nests, or eggs.
California Fish and Wildlife Code-Sections 3503 and 3511
The CDFW administers the California Fish and Wildlife Code (CFG Code). There are particular
sections of the CFG Code that are applicable to natural resource management. For example, Section
3503 of the CFG Code states it is unlawful to take, possess, or needlessly destroy the nest or eggs of
any bird that is protected under t he MBTA. CFG Code Section 3503.5 further protects all birds in the
orders Falconiformes and Strigiformes, birds of prey such as hawks and owls, and their eggs and
nests from any form of take. CFG Code Section 3511 lists fully protected bird species where the
CDFW is unable to authorize the issuance of permits or licenses to take these species.
Jurisdictional Waters and Wetlands
Impacts to natural drainage features and wetland areas are regulated by the United States Army
Corp of Engineers (USACE), Regional Water Quality Control Board {RWQCB), and CDFW based upon
the policies and regulations discussed below.
United States Army Corp of Engineers Regulations
Federal Clean Water Act-Section 404
The USACE administers Section 404 of the federal Clean Water Act (CWA). This section regulates the
discharge of dredge and fill material into waters of the U.S. USACE has established a series of
nationwide permits that authorize certain activities in waters of the U.S., if a proposed activity can
demonstrate compliance with standard conditions. Normally, USACE requires an individual permit
for an activity that will affect an area equal to or in excess of 0.5 acre of waters of the U.S. Projects
that result in impacts to less than 0.5 acre can normally be conducted pursuant to one of the
nationwide permits, if consistent with the standard permit conditions. USACE also has discretionary
authority to require an Environmental Impact Statement for projects that result in impacts to an area
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between 0.1 and 0.5 acre. Use of any nationwide permit is contingent on the activities having no
impacts to endangered species.
Waters of the United States
Waters of t he U.S., as defined in the Code of Federal Regulations (CFR) Section 328.3, include all
waters or tributaries to waters such as lakes, rivers, intermittent and perennial streams, mudflats,
sand-flats, natural ponds, wetlands, wet meadows, and other aquatic habitats. Frequently, waters of
the U.S., with at least intermittently flowing water or tidal influences, are demarcated by an ordinary
high water mark (OHWM). The OHWM is defined in CFR Section 328.3(e) as the line on the shore
established by the fluctuations of water and indicated by physical characteristics such as a clear,
natural line impressed on the bank shelving, changes in the character of soil, destruction of
terrestrial vegetation, the presence of litter and debris, or other appropriate means that consider
the characteristics of the surrounding areas. In this region, the OHWM is typically indicated by the
presence of an incised stream bed with defined bank shelving.
In June 2001 t he USACE South Pacific Division has issued Guidelines for Jurisdictional Delineations for
Waters of the United States in the Arid Southwest. The purpose of this document was to provide
background information concerning physical characteristics of dryland drainage systems. These
guidelines were reviewed and used to identify jurisdictional drainage features within the Project Site.
Wetlands
According to the USACE Wetlands Delineation Manual, Technical Report, three criteria must be
satisfied to classify an area as a jurisdictional wetland:
1. A predominance of plant life that is adapted to life in wet conditions (hydrophytic
vegetation)
2. Soils that saturate, flood, or pond long enough during the growing season to develop
anaerobic conditions in the upper part (hydric soils)
3. Permanent or periodic inundation or soils saturation, at least seasonally (wetland
hydrology)
Wetland vegetation is characterized by vegetation in which more than 50 percent of the composition
of dominant plant species are obligate wetland, facultative wetland, and/or facultative species that
occur in wetlands. As a result of the 2001 Solid Waste Agency of North Cook County (SWANCC) case,
a wetland must show connectivity to a stream course in order for such a feature to be considered
jurisdictional. Although wetland criteria was used to identify if areas were considered wetlands, the
exact limits of jurisdiction were not measured based on the standard wetland delineation protocol
as described in t he 1987 USACE manual.
United States Army Corp of Engineers Regulated Activities
The USACE regulates the discharge of dredged or fill material including, but not limited to, grading,
placing of rip-rap for erosion control, pouring concrete, laying sod, and stockpiling excavated
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material. Activities that generally do not involve a regulated discharge, if performed specifically in a
manner to avoid discharges, include driving pilings, drainage channel maintenance, temporary
mining and farm/forest roads, and excavating without stockpiling.
Regional Water Quality Control Board Regulations
Clean Water Act-Section 401
Per Section 401 of the CWA, "any applicant for a Federal permit for activities that involve a discharge to
waters of the State, shall provide the Federal permitting agency a certification from the State in which
the discharge is proposed that states that the discharge will comply with the applicable provisions
under the Federal Clean Water Act." Therefore, before the USACE will issue a Section 404 permit,
applicants must apply for and receive a Section 401 water quality certification from the RWQCB.
Porter-Cologne Water Quality Act
The RWQCB regulates actions that would involve "discharging waste, or proposing t o discharge
waste, within any region that could affect t he water of the state" (water code Sectionl3260 (a)),
pursuant to provisions of t he Porter-Cologne Water Quality Act. "Waters of the State" are defined as
"any surface water or groundwater, including saline waters,.within the boundaries of the state"
(water code Section 13050 (e)).
Regional Water Quality Control Board Regulated Activities
Under Section 401 of the CWA, t he RWQCB regulates all activities that are regulated by the USACE.
Additionally, under the Porter-Cologne Water Quality Act, the RWQCB regulates all activities,
including dredging, filling, or discharge of materials into waters of the state that are not regu lated by
the USACE due t o a lack of connectivity with a navigable water body and/or lack of an OHWM.
California Department of Fish and Wildlife Regulations
California Fish and Wildlife Code-Section 1600 to Section 16003
The CFG Code mandates that "it is unlawful for any person to substantially divert or obstruct the
natural flow or substantially change the bed, channel, or bank of any river, stream, or lake
designated by t he department, or use any material from the stream beds, without first notifying the
department of such activity." CDFW jurisdiction includes ephemeral, intermittent, and perennial
watercourses, including dry washes, characterized by the presence of hydrophytic vegetation, the
location of definable bed and banks, and the presence of existing fish or wildlife resources.
Furthermore, CDFW jurisdiction is often extended to habitats adjacent to watercourses, such as oak
woodlands in canyon bottoms or willow woodlands that function as part of the riparian system.
Historic court cases have further extended CDFW jurisdiction to include watercourses that seemingly
disappear, but re-emerge elsewhere. Under the CDFW definition, a watercourse need not exhibit
evidence of an OHWM to be claimed as jurisdiction. However, CDFW does not regulate isolated
wetlands; that is, those that are not associated with a river, stream, or lake.
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California Department of Fish and Wildlife Regulated Activities
The CDFW regu lates activities that involve diversions, obstruction, or changes to the natural flow or
bed, channel, or bank of any river, stream, or lake that supports fish or wildlife resources.
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