HomeMy WebLinkAbout3190; La Costa Oaks & Ridge Projects; La Costa Oaks & Ridge Projects; 1999-07-07The La Costa Oaks and Ridge Projects
DRAFT BIOLOGICAL TECHNICAL REPORT
July 7, 1999
Prepared for:
VIIIAGES OF LA COSTA
2300 Alga Road
Carlsbad, California 92009
Prepared by:
HEUX ENVIRONMENTAL PLANNING, INC.
8100 La Mesa Boulevard, Suite 150
La Mesa, California 91941-6452
DRAFT BIOLOGICAL TECHNICAL REPORT FOR THE
LA COSTA OAKS AND RIDGE PROJECTS
TABLE OF CONTENTS
INTRODUCTION 1
METHODS 3
EXISTING CONDITIONS 4
REGULATORY CONTEXT 10
IMPACT ANALYSIS AND MTTIGATION MEASURES 11
LITERATURE CTTED 19
APPENDIX A SURVEY INFORMATION A-l
APPENDIX B OAKS/RIDGE PLANT SPECIES LIST B-1
APPENDIX C OAKS/RIDGE ANIMAL SPEQES LIST C-1
APPENDIX D SENSITIVrTY CODES D-1
LIST OF FIGURES
Follows
No. Title Page
1 Regional Locatioii Map 2
2 Project Vicmity Map 2
3 HMP Preserve Planning Area 11
4a-b Vegetation, Sensitive Resources^ Impacts and HCP Preserve 12
LIST OF TABLES
No. Title Page
1 Summary of Vegetation Communities for the La Costa Oaks and Ridge 4
2 Vernal Pool Characteristics 5
3 Sensitive Plant Species Occurring or with Potential to Occur on the La Costa
Oaks/Ridge Project Sites 8
4 Sensitive Animal Species Occurring or with Potential to Occur on the La Costa
Oaks/Ridge Project Sites 9
5 Vegetation Impacts 12
6 Sensitive Plant Impacts 14
7 Impacts and Conservation Levels for tiie La Costa Oaks/Ridge * 15
DRAFT
INTRODUCTION
This report describes existing biological conditions within the proposed Oaks and Ridge projects of the
Villages of La Costa Master Plan (VLCMP), and provides the City of Carlsbad (City), U.S. Fish and
Wildlife Service (USFWS), Califomia Department of Fish and Game (CDFG), and the public with
information necessary to assess impacts to biological resources under fhe Califonua Environmental
Quality Act (CEQA), the City's Draft Habitat Management Plan (HMP), Draft North County Multiple
Habitat Coiwervation Program (MHCP), state and federal Endangered Species Acts (ESAs), and the
federal Clean Water Act.
The following discussion compares the proposed project's biological impacts and mitigation measures to
those reported for the Southeast n (Oaks) and Rancheros (Ridge) components of the Fieldstone La Costa
Master Plan (LCMP) as outhned in the City's Habitat Conservation Plan/Ongoing Multi-Species Plan
(HCP/OMSP) (City of Carlsbad 1995). The HCP/OMSP provides specific requirements for the
implementation of the LCMP tiiat, if implemented, would ensure that biological impacts would be
mitigated. The Southeast n project also had an EIR approved for the re-alignment of Rancho Santa Fe
Road project and mass grading. In this report, re-ahgnment construction impacts of Rancho Santa Fe
Road are kept separate from the overall project discussion.
The HCP/OMSP establishes a preserve design consistent with the Gty's HMP, MHCP, and State Natural
Communities Conservation Program (NCCP). The HCP/OMSP further provides the primary guidance
for long-term management of the site and a basis for fuIfilUng permitting requirements with the City and
both state and federal agencies. A section 10(a) incidental take perinit under the federal ESA has been
issued for species covered under the HCP/OMSP. As proposed, the Oaks/Ridge projects meet or exceed
the mitigation measures outiined for the projects in the HCP/OMSP.
PROJECT DESCRIPTION
The Oaks/Ridge projects would provide approximately 1,140 residential homes, a 5.7-acre commercial
site, a common recreation area at least 20 acres in size, a 9.6-acre SDG&E utihty corridor, necessary
circulation roads, bicycle and pedestrian trails, and approximately 525.3 acres of natural open space. An
additional 85 acres of proposed open space has been added to the overall project area in the eastern
portion of the Ridge project. The re-aHgnment of Rancho Santa Fe Road is also part of the project but is
discussed separately in tius document.
PROJECT HISTORY
The La Costa Master Plan (LCMP [Master Plan 149]) was finalized in 1972, prior to many of the current
environmental regulations. The LCMP encompassed a larger study area, some of which has since been
developed. The current VLCMP covers the two remaining undeveloped blocks of land, including La
Costa Oaks and Ridge (subject of this report) and the La Costa Greens projects.
The Oaks project, previously known as Southeast II, had an EIR approved for the re-ahgnment of Rancho
Santa Fe Road project and mass grading.
The HCP/OMSP is the result of a three-year public plarming process involving the USFWS, CDFG, the
City, local and national envirorunental groups, and Fieldstone/La Costa Associates (FLCA). The
HCP/OMSP is regional in scope, designed to be consistent with both local and regional planning efforts.
The primary purpose of the HCP/OMSP is to conserve wildlife habitat and linkages, ensuring long-term
survival of 62 sensitive plant and animal species while achieving objectives of tiie resource agendes, the
City, landowners, and other HCP/OMSP participants. The biological basis for the HCP/OMSP includes
results of biological studies conducted over a two-year period.
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The VLCMP includes modifications to tiie preserve design that allow a net increase to the preserve area
over that reported in the HCP/OMSP. The combined open space among the Oaks, Ridge, and Greens in
the HCP/OMSP totaled approximately 703 acres. Under the VLCMP, the total open space in tiie
HCP/OMSP is increased by 153.5 acres for a total of 856.5 acres. Additionally, 10 acres of disturbed
habitat in the central portion of the Oaks project has been used as a Diegan coastal sage scrub restoration
site as partial mitigation for the La Costa Valley project.
The HCP/ OMSP provides the legal framework for the Greens, Oaks and Ridge projects to meet City,
CDFG, and USFWS requirements. Several biological studies, conducted in 1991 and 1992, comprise the
biological basis for the HCP/OMSP. The data presented in this report dupUcate the data in the
HCP/OMSP wifh some additions and/or revisions. The primary data additions in this report include
quino checkerspot butterfly {Euphydryas editha quino) survey results, wetiand delineation results, and
updates to the status of sensitive species. The impacts under the VLCMP have been reduced in
comparison witti the HCP/ OMSP. Additionally it should be noted that a majority of the project area was
bumed in 1996. It is assumed that the burned areas will eventually re-establish themselves and that
sensitive species present prior to the fire will re-occupy the site in pre-fire densities.
Proposed development impacts under for the Oaks and Ridge Projects have been reduced by a net of 119
acres. Mitigation, however, would include all measures developed as part of the HCP/OMSP
conservation program. The HCP/OMSP stipulates conveyance of a total of 525.2 acres of open space on
site. In addition, tiiere are habitat management measures and other impacts minimization and mitigation
measures to be implemented.
PHYSICAL SITE CHARACTERISTICS
The Oaks and Ridge projects consist of undeveloped, natural areas divided by San Marcos Creek. San
Maicos Creek is a major drainage feature on site that provides for wildlife movement and high quaUty
habitat.
The Oaks and Ridge projects are in the City in northwestem San Diego County, Califomia (Figures 1 and
2). The Oaks and Ridge sites are approximately 741 and 465 acres, respectively. On-site elevations range
from approximately 240 feet to 740 feet above mean sea level.
SOILS
Soil types present on site include clays of the Salinas and Altamont series and various sandy loams of tiie
Excequer, Huerhuero, San Miguel, and Cieneba series (Bowman 1973).
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! RIVERSIDE COUNTY
PROJECT
LOCATION
NOTTOSCALE
IIEIIX
Regional Location Map
THE OAKS AND RIDGE PROPERTIES Fiyure
.Source: USGS 7.5 min Quadrangles: Encinitas and Rancho Santa Fei,
um
Project Vicinity Map
THE OAKS AND RIDGE PROPERTIES Figure ?
DRAFT
m
METHODS
m Nine types of surveys were conducted on site between 1990 and 1998: vegetation mapping, rare plant
surveys, coastal California gnatcatcher {Polioptila califomica califomica) surveys, coastal California
gnatcatcher banding, sensitive reptile siu^eys, sensitive butterfly surveys, quino checkerspot butterfly
surveys, small manunal trapping, and wetiand delineation. Fieldwork was conducted by Sweetwater
Environmental Biologists, hic. (SEB) and HELIX Environmental Planning, Inc (HELIX).
Vegetation was mapped on a topographic map of 1"=200' scale. An aerial photograph was used as a
reference for both site work and mapping in the office. Vemal pools were surveyed in by Htmsaker and
Associates. Focused rare plant surveys were conducted during Spring 1991 and Summer/Fall 1992 as
well as opportunistically during other surveys.
The coastal California gnatcatcher surveys followed suggested guidelines for surveys in use in 1991 (ERC
Environmental and Energy Services, Inc. 1990) because no official (USFWS) protocol was available.
However, the surveys complied with the protocol implemented later in 1992 for the NCCP (Scientific
Review Panel 1992). Surveys were conducted durmg the morning before 11:00 a.m. at a rate of 25 acres
per person-hour. Durmg the gnatcatcher surveys, a tape of coastal Cahfomia gnatcatcher vocalizations
was used to elicit gnatcatcher responses. Tape playing was minimized to avoid unnecessary harassment
of gnatcatchers. In August and September 1991, SEB banded the gnatcatchers on site. Banding was
consistent with guidelines estabhshed by the USFWS, U.S. Bu-d Banding Laboratory under the direct
supervision of Barry L. Jones (master permitee). Gnacatchers were banded and subsequentiy monitored
to determine their dispersal patterns.
Prior to the listing of the qumo checkerspot butterfly, a sensitive butterfly survey was conducted on site in
June. Because the quino checkerspot butterfly has since become federally listed as endangered (January
1997), quino presence/absence surveys were conducted that compUed with USFWS interim general
survey protocol (USFWS 1997). Surveys were conducted weekly during the 1998 flight season (March
through late April). The site was also assessed for adequate habitat and the presence of the two larval
foodplants: dwarf plantain {Plantago erecta) and owl's-clover {Castilleja exserta) and other quino habitat
features. Quino checkerspot surveys were repeated in 1999, based on the new standard protocol (USFWS
1999). Surveys in 1999 were completed weekly from March to May and covered all suitable habitat on
site at a rate of 12.5 acres or less per hour. Habitat components, such as the larval foodplants mentioned
above, were surveyed and mapped.
Wildhfe signs and observations were noted during all surveys. Survey techniques included searching all
habitats for anticipated wildlife species that could occur on site. All habitat types were searched for
wildlife presence or sign. The potential for other sensitive species to occur on site was determined by a
habitat-based analysis and by consulting the known distribution of sensitive species in tiie City. A
sensitive reptile survey and small mammal trappmg was conducted to amplify the general wildlife
information.
The wetiand delineation followed methods prescribed by the U.S. Army Corps of Engineers (ACOE)
(Envirorunental Laboratory 1987). Complete details of the wetiand dehneation methods and results are
provided in a separate wetiand delineation report.
Nomenclature for tiiis report is from Hickman, ed. (1993) for plants; Holland (1986) for vegetation
communities; Emmel and Emmel (1973) for butterflies; CoUins (1997) for reptiles and amphibians; the
American Ornithologist's Union (1983, as updated) for birds; and Jones et al. (1997) for mammals.
Sensitive animal and plant status is taken from CDFG (1994a) and CDFG (1994b), respectively (as
updated).
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DRAFT
EXISTING CONDITIONS
VEGETATION COMMUNITIES/HABITATS
The Oaks and Ridge Projects support nine vegetation communities or habitats: vemal pool, Diegan
coastal sage scrub, native grassland, riparian scrub and woodland, southem mixed chaparral, non-native
grassland, open water, eucalyptus woodland, and disturbed habitat (Table 1). As noted earUer, a fire
bumed the entire site in 1996. This report uses habitat and sensitive resource data collected before the
fire.
Table 1
SUMMARY OF VEGETATION COMMUNITIES
FOR THE LA COSTA OAKS AND RIDGE
Vegetation Communitv Acres*
Diegan coastal sage scmb 806.9
Native grassland 31.6
Riparian scrub and woodland 27.3
Southem mixed chaparral 182.8
Non-native grassland 35.6
Open water 0.4
Vemal pool 0.05
Eucalyptus woodland 0.7
Disturbed habitat 120.4
Total 1,205.8
* Areas are given in approximate acreage
Vernal pool
Vemal pool habitat on site is characterized by depressions in the disturbed habitat areas, dominated by
vemal pool vegetation. Plants observed in the pools include long-stalk water-starwort {Callitriche
marginata), stonecrop {Crassuia aquatica), spike-rush {Eleocharis sp.), and grass poly {Lythrum hyssopifolia).
Vemal pools are considered sensitive by the City of Carlsbad (1999) and the CDFG (Holland 1986), as
weU as by the USFWS because they support sensitive species, are limited in distribution, and are
declining in area. One of the vemal pools is located within non-native grassland habitat, while the rest
are entirely within disturbed areas. Approximately 1,960 square feet (0.05 acre) of vemal pool habitat (4
pools) occurs on site. The watershed, for each of the pools was also measured and is included with tiie
acreage in Table 2. Note that vemal pools 1 and 2 share a single watershed.
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DRAFT
m
Table 2
Vemal Pool Characteristics
Vemal Pool Surface Area Watershed
1 760 sq. ft. 20,480 sq. ft. / 0.47 acre 2 270 sq.ft 20,480 sq. ft. / 0.47 acre
3 590 sq. ft 3,070 sq.ft./0.07 acre
4 340 sq. ft 2,670 sq. ft. / 0.06 acre
Total 1,960 sq ft. 26,220 sq ft / 0.6 acre
Diegan Coastal Sage Scrub
Coastal sage scmb is one of the major shrub communities that occur in California. Coastal sage scmb is
dominated by shmbs whose leaves die back during hot and dry periods. Coastal sage scmb is an open
plant community, allowing for the occurrence of a substantial herbaceous component. There are many
coastal sage scrub subtypes, differing in their dominant plants and overall species composition. Much of
the coastal sage scrub on the Ridge property is dominated by semi-pure stands of black sage while on the
Oaks property Califomia sagebrush is more dominant. Additional plant species m the coastal sage scmb
include laurel sumac {Malosma laurina), Mexican elderberry {Sambucus mexicana), California buckwheat
{Eriogonum fasciculatum), Califomia adolphia {Adolphia califomica), and Califomia enceUa {Encelia
califomica). Coastal sage scmb is considered a sensitive resource by several resource agencies, including
the City of Carlsbad (1999), CDFG (HoUand 1986), and USFWS, because it supports many sensitive plants
and animals. As mentioned previously, a 10-acre coastal sage scmb revegetation area has been
estabUshed on the Oaks property. Approximately 806.9 acres of Diegan coastal sage scmb (including the
revegetation) occurs on tiie Oaks and Ridge Projects.
Native Grassland
Native grassland is a community dominated by native perermial bunchgrasses such as purple needle
grass {Nasella pulchra) and foothiU needlegrass {Nasella lepida) with native forbs such as common golden
stars {Bloomeria crocea ssp. crocea) and Califomia blue-eyed grass {Sisyrinchium helium). Native grasslands
generaUy occur on fine-textured soils that generaUy exclude the annual, exotic grasses. Native grasslands
are considered sensitive by the CDFG (HoUand 1986), City of Carlsbad (1999), and USFWS because of
their limited distribution and because they support sensitive plant and animal species. Within the Oaks
and Ridge Projects native grassland is restricted to several patches within the non-native grassland.
Approximately 31.6 acres of native grassland occurs on site.
Riparian Scmb and Woodland
Riparian scrub and woodland is a generic term for plant communities occurring along drainages or river
corridors. This habitat occurs on loose, sandy or fine graveUy aUuvium deposited near stream charmels
during flood flows. Riparian habitat types are considered sensitive by the CDFG (HoUand 1986), City of
Carlsbad (1999), and USFWS due to their overaU importance to wUdlife as corridors and water sources
and because they are a declining resource. The riparian plant communities on the Oaks and Ridge
Projects are represented by two main habitat types: southem wiUow scmb and southem coast Uve oak
riparian woodland.
Southem wiUow scmb consists of dense, broadleaved, winter-deciduous stands of trees dominated by
shrubby wiUows {Salix sp.) in association with mulefat (Baccharis salicifolia). The herbaceous understory
consists of: Curly dock {Rumex crispus), cocklebur {Xanthium stmmarium var. canadense) and western
ragweed. Periodic flooding maintains this early serai community, preventing succession to a riparian
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DRAFT
m woodland or forest (HoUand 1986). In the absence of periodic flooding, competition between the wiUows
wiU intensify as these individuals grow and compete. A smaU percentage of these individuals wiU
survive and form the tree stratum, whUe most wUl die or exist as suppressed juvenUes in the lower
^ sttatum. Trees within the creek include wiUows and a few sycamores {Platanus racemosa).
Southern willow scmb occurs within the San Marcos Creek corridor.
Southem coast Uve oak riparian woodland is an open to dense riparian community that is dominated by
*• coast Uve oak {Quercus agrifolia). This community occurs Eilong large stteam courses where the water table
^ is at or near the surface for most of the year. Southem coast live oak riparian woodland thrives in the
absence of frequent flood disturbances, aUowing the ttee component to attam a sizable height Riparian
m oak woodland occurs on the south border of the Oaks property in two north-south trending drainages.
Approximately 27.3 acres of combined southern wiUow scrub and southern coast Uve oak woodland
^ vegetation occur on the Oaks and Ridge Projects.
Southern Mixed Chaparral
Southem mixed chaparral is composed of broad- and thick-leaved shrubs that grow to about six to ten
^ feet taU and form dense often nearly impenettable stands. Plant components of southem mixed chaparral
on site include chamise {Adenostoma fasciculatum), lemonadeberry {Rhus integrifolia), poison oak
i-i {Toxicodendron diversilobum), mission manzanita {Xylococcus bicolor), scrub oak {Quercus sp.), fuchsia-
flowered gooseberry {Ribes speciosum), and wUd Ulac {Ceanothus sp.). The southem mixed chaparral
occurs primarUy in four patches on nortii-facing slopes along tiie northem boundaries of both sites.
^ Approximately 182.8 acres of southem mixed chaparral occur on the Oaks and Ridge Projects.
™ Non-native Grassland
Non-native grassland consists mostiy of aimual rather than perermial grasses that are characteristicaUy
^ associated with flowering forbs. The dominant species in non-native grasslands are mediterranean,
inttoduced species. Like the native grasslands, non-native grasslands occur on fine-textured soUs. Non-
— native grassland occurs on the Oaks project site, in several patches on the main south-facing hillside.
Approximately 35.6 acres of non-native grassland occurs on site.
^ Open Water
Open water habitat is foimd in a man-made pond in one of the canyons in the northem haU of the site.'
Approximately 0.4 acre of open water occm-s in a pond at the northem end of the Ridge project site within
San Marcos Creek.
Eucalvptus Woodland
IB*
Eucalyptus woodland is dominated by eucalyptus {Eucalyptus sp.). In most instances, eucalyptus have
" been planted for a variety of cultural reasons. If sufficient moisture is available, eucalyptus become
^ naturaUzed and are able to reproduce and expand theU range which has happened in many riparian
areas. Approximately 0.7 acre of eucalyptus woodland occurs on site adjacent to San Marcos Creek m the
" northem portions of the Ridge project site.
Disttirbed
Disturbed habitats lack vegetation, are developed, or support mostiy weedy species. Disturbed areas
occur as a result of agriculture, development dumping, off-highway vehicle activity, and so on.
^ Approximately 120.4 acres of disturbed habitat occurs on the Oaks and Ridge Projects.
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DRAFT
Turisdictional Areas
ACOE jurisdictional areas include landforms such as: channels, flood plains and springs. The wetiand
areas on site are dominated by hydrophytic vegetation, hydrology, and soUs. Witiiin the proposed
development area of the Ridge property, there were no areas where wetiand vegetation, hydrology, and
soils criteria were met. On the Oaks property wetlands occur in the four vemal pools on site, at two
springs, and in several of the drainages on-site, often as ttansitional areas between or adjacent to non-
vegetated Waters of the U.S. Wetiand features on the Ridge project site occur primarUy in San Marcos
Creek. Non-vegetated Waters of the U.S. occur on both sites as ephemeral stteams, some of which
ttansition into wetiand areas. The jurisdictional widths in these drainages are determined by the OHWM
and bed and bank topography. CDFG jurisdictional areas include aU ACOE jurisdictional areas and areas
with riparian vegetation that may not meet federal jurisdictional wetland criteria (no such areas were
found on site). Details of the wetland delineation and results are reported in separate dociunents for the
Oaks and Ridge properties.
Plants
Appendix A provides a complete Ust of plant species observed on the project site. None of the sensitive
plants observed are state or federal listed species. A total of nine sensitive plant species were observed
that are not listed at federal or state levels, including ashy spike-moss {Selaginella cinerascens), Califomia
adolphia {Adolphia califomica), San Diego marsh elder {Iva hayesiana), soutiiwestem spiny rush [Juncus
acutus ssp. Sphaerocarphus), Califomia adder's tongue {Ophioglossum californicum), San Diego County
viguiera {Viguiera laciniata). Sticky-leaved Uve-forever {Dudleya viscida), Orcutfs brodiaea {Brodiaea
orcuttii), and San Diego goldenstar {Muilla clevelandii). AdditionaUy, 12 sensitive plant species were not
observed but have the potential to occur on site, These species would have been observed during fhe rare
plant surveys if present. Table 3 summarizes the species observed and potentiaUy-occurring on the Oaks
and Ridge projects site.
Animals
Appendix B provides a list of animal species found duruig project surveys. Thirteen sensitive animal
species were observed on site. Of the sensitive species observed on site, the coastsil Califomia
gnateatcher is the only federal listed as threatened species and an HMP Group 1 species. The Cooper's
hawk {Accipiter cooperii) observed on site is an HMP Group 2 species. The westem spadefoot {Spea
hammondii), San Diego homed lizard {Phrynosoma coronatum blainvillei), BeU's sage sparrow {Amphispiza
belli belli), southem California rufous-crowned sparrow {Aimophila riificeps canescens), northwestem pocket
mouse {Chaetodipus fallax fallax), and San Diego black-taUed jackrabbit {Lepus califomicus bennettii) are
HMP Group 4 species. The coastal whiptaU {Cnemidophorus tigris multiscutatus), coastal rosy boa
{Lichanura trivirgata roseofusca), Northem red-diamond rattiesnake {Crotalus mber mber), loggerhead shrike
{Lanius ludovicianus), and desert woodrat {Neotoma lepida) are not included within the HMP groupings but
are considered sensitive by the resource agencies. AdditionaUy, 26 sensitive animal species have the
potential to occur on site, including three that are federaUy listed as endangered. Table 4 summarizes the
animal species observed or potentiaUy-occurring on the Oaks and Ridge project sites.
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I I I I I I i I i I itilll
TABLE 3
SENSITIVE PLANT SPECIES OCCURRING OR WITH POTENTIAL TO OCCUR ON THE LA COSTA OAKS/RIDGE PROJECT SITES
Species Name Status Distribution Habitat(s) Oaks/Ridge OccurFence/Potentlal
Plant Species Observed On Site
California adolphia (Adolphia
califomica)
CNPS List 2; R-E-D 1-2-1 Below 1,000 feet in elevation in
westem San Diego County and
northwestem Baja Califomia,
Mexico.
Clay soils in dry canyons
and washes in coastal
sage scrub and chaparral.
Approximately 6,500 individuals observed across the
site in many drfferent stands. Most of the stands are
associated with coastal sage scrub.
Orcutt's brodiaea (Brodiaea orcuttii) Regionally Sensitive/CNPS List
IB; R-E-D 1-3-2; HMP Group 4
Riverside and San Bemardino
counties south to Baja California,
Mexico.
Vemal pools and
ephemeral streams and
seeps.
Two populations of five individuals each.
Sticky-leaved liveforever (Dudleya
viscida)
USFWS C1/CNPS List IB; R-E-D
3-2-3; HMP Group 2
Coastal areas in northern San
Diego County and in Orange '
County below 1200 feet in
elevation.
Dry, rocky cliffs and
coastal bluffs.
Several large populations observed in San Marcos
Creek canyon.
San Diego marsh-elder (Iva
ftayesiana)
Regionaliy Sensitive/CNPS List 2;
R-E-D 2-2-1; HMP Group 2
San Diego County and Baja
Califomia, Mexico.
Low-lying, moist or alkaline
places along the coast.
Has been reported along
intermittent streams
A large population (numbering in the thousands) occurs
in San Marcos Creek.
Spiny rush {Juncus acutus ssp.
leopoldii)
CNPS List 4; R-E-D 1-2-1 Los Angeles, San Bemardino,
San Luis Obispo, Ventura and
San Diego counties as well as
Baja Califomia, Mexico.
Moist, saline, or alkaline
soils.
A number of stands numbering in the thousands occur
within San Marcos Creek.
San Diego goldenstar (Muilla
clevelandii)
Regionally Sensitive/CNPS List
IB; R-E-D 2-2-2; HMP Group 4
Southwestern San Diego County
and northwestern Baja Califomia,
Mexico.
Clay soils on dry mesas
and hillsides in coastal
sage scmb or chaparral.
Approximately 1,950 individuals obsen/ed in Rancho
Santa Fe Road alignment.
California adder's-tongue
(Ophioglossum californicum)
Regionally Sensitive/CNPS List 4;
R-E-D 1-2-2
Discontinuous distn~bution from
central Calrfomia to San Diego
County and northern Baja
Califomia, Mexico.
Grassy, open areas where
it is generally associated
with short grasses and
other herbs. Although
often found near vemal
pools, the species can also
occur in relatively dry,
stony areas.
Approximately 100 individuals obsen/ed within SDG&E
easement east of Rancho Santa Fe Road.
llllllllllll i j IIIIIIII
SENSITIVE PLANT SPECIES OCCURRING OR WITH POTENTIAL TO OCCUR ON THE LA COSTA OAKS/RIDGE PROJECT SITES
Species Name Status Distribution Habitat(s) Oaks/Ridge Occurrence/Potential
Ashy Spike-moss (Selaginella
cinerascens)
CNPS List 4; R-E-D 1-2-1 San Diego County and northwest
Baja California
Flat mesas in open coastal
sage scrub or chapan'al.
Widespread in the southern mixed chaparral and
coastal sage scmb.
Plant Species Not Observed On site
San Diego thornmint
(Acanthomintha ilicifolia)
USFWS C1/CDFG SE/CNPS List
IB; R-E-D 2-3-2; HMP Group 4
San Diego County and Baja
California, Mexico.
Heavy clay soils near
vemal pools, in grasslands,
and in chaparral and
coastal sage scrub.
Not obsen/ed. Low potential; would have been
observed if present.
San Diego ambrosia (Ambrosia
pumila)
CNPS List 1B; R-E-D 3-3-2; HMP
Group 4
San Diego County, Riverside
County, Baja Califomia, Mexico.
Chaparral coastal sage
scrub, valley and foothill
grasslands, vemal pools.
Often in disturbed areas.
Not observed. Low potential; would have been
observed if present.
Del Mar manzanita (Arctostaphylos
glandulosa ssp. crassifolia)
USFWS FE/CNPS List 1B; R-E-D
3-3-2; HMP Group 1
Coastal San Diego County. Southem maritime
chaparral on sandy mesas
and bluffs.
Not observed or expected on site. Habitat not suitable.
San Diego sagewort (Artemisia
palmeri)
CNPS List 2; R-E-D 2-2-1 San Diego County and Baja
California, Mexico.
Stream courses, often
within coastal sage scrub
and southern mixed
chaparral.
Not obsen/ed. Low potential; would have t>een
observed if present.
Encinitas baccharis {Baccharis
vanessae)
USFWS FT/CDFG SE/CNPS List
IB; R-E-D 2-3-3; HMP Group 1
San Diego County endemic. Southern maritime and
southem mixed chaparral.
Not obsen/ed. Low potential; would have been
observed if present.
Thread-leaved brodiaea (Brodiaea
filifolia)
USFWS PT/CDFG SE/CNPS List
IB; R-E-D 3-3-3; HMP Group 1
Interior valley regions of Riverside
and San Diego counties.
Clay lens soils in annual
grasslands and vernal
pools.
Not observed. Low potential. Would have been
observed if present.
Wart-stemmed ceanothus
(CeanoUtus verrucosus)
Regionally Sensitive/CNPS List 4;
R-E-D 1-2-1; HCP Group 2
Central coastal San Diego County
to Baja Califomia, Mexico.
Chaparral, coastal sage
scrub, or southem oak
woodland.
Not observed. Lew potential. Would have been
observed if present.
i ] i I I i I I llli llll
SENSITIVE PLANT SPECIES OCCURRING OR WITH POTENTIAL TO OCCUR ON THE LA COSTA OAKS/RIDGE PROJECT SITES
Species Name Status Distribution Habitat{s} Oaks/Ridge Occurrence/Potential
Orcutfs spineflower (Chorizanthe
orcuttiana)
USFWS FE/CDFG SE/CNPS List
1B; R-E-D 3-3-3; HMP Group 4;
Not a covered species under the
HCP/OMSP.
Endemic to San Diego County.
Last seen in 1967.
Found only in sandy areas
on mesas in the coastal
region. Generally
associated with coastal
sage scrub or chaparral.
Not obsen/ed. Low potential; would have been
observed rf present. This species is known from only
one location in southern maritime chapan'al 6 miles
southwest of the site.
Summer holly (Comarostaphylis
diversifolia ssp. diversifolia)
Regionally Sensitive/CNPS List
IB; R-E-D 2-2-2
Scattered locations below
approximately 2,300 feet in
elevation from the foothills to the
coast in Orange and San Diego
counties and south into Baja
Califomia, Mexico.
North-facing slopes and
drainages in chaparral.
Not obsen/ed or expected on site. Habitat not suitable.
Del Mar sand aster (Corethrogyne
filaginifolia var. linifolia)
Regionally Sensitive (formerly
USFWS PT but is now
considered protected under the
MSCP of southern San Diego
County)/CNPS List 1B; R-E-D 3-2
3; HMP Group 4
San Diego County from Carlsbad
to Fort Rosecrans.
Sandy and disturbed areas
within southern maritime
chaparral.
Not observed. Low potential; would have been
obsen/ed if present.
Westem dichondra (Dichondra
occidentalis)
Regionally Sensitive/CNPS List 4;
R-E-D 1-2-1
Santa Barbara County to Baja
California, Mexico and on San
Miguel Island.
Dry, sandy banks in
coastal sage scrub,
chaparral, or southem oak
woodland; often
proliferates on recently
burned stopes.
Not obsen/ed. Low potential; would have been
obsen/ed if present.
Blochman's dudleya (Dudleya
blochmaniae ssp. blochmaniae)
Regionally Sensitive/CNPS List
IB; R-E-D 1-2-2; HMP Group 2
Near the coast from San Luis
Obispo County south to northem
Baja Califomia, Mexico below
1,500 feet in elevation.
Dry, stony places
associated with coastal
sage scrub.
Not observed. Low potential; would have been
observed if present.
San Diego button-celery (Eryngium
aristulatum var. parishii)
USFWS FE/CDFG SE/CNPS List
IB, 1-3-2
San Diego and Riverside
Counties and Baja Califomia,
Mexico.
Vernal pools Not obsen/ed. Low potential due to the disturbed
nature of vernal pools on site. Would have been
observed if present.
Cliff spurge {Euphorbia misera) CNPS List 2; R-E-D 2-2-1; HMP
Group 4
Corona Del Mar to Baja
California, Mexico.
Sea bluffs in coastal sage
scmb.
Not obsen/ed. Low potential; would have been
observed rf present.
i I lili i 4
SENSITIVE PLANT SPECIES OCCURRING OR WITH POTENTIAL TO OCCUR ON THE LA COSTA OAKS/RIDGE PROJECT SITES
Species Name Status Distribution Habitat(s) Oaks/Rrdge Occurrence/Potential
San Diego barrel cactus
{Ferocactus viridescens)
Regionally Sensitive/CNPS List 2;
R-E-D 1-3-1: HMP Group 4
San Diego County and Baja
Calrfomia, Mexico.
Dry slopes in coastal sage
scrub.
Not observed. Low potential; would have been
obsen/ed if present.
Palrrrer's grappling hook
{Harpagonella palmeri)
Regionally Sensitive/CNPS List 2;
R-E-D 1-2-1
Below approximately 3,300 feet in
elevation in Los Angeles, Orange,
Riverside, and San Diego
counties, on San Clemente
Island, in Arizona, Baja California
and Sonora, Mexico.
Clay soils in annual
grasslands and coastal
sage scmb.
Not obsen/ed or expected on site. Habitat not suitable.
Orcutt's hazardia (Hazardia orcuttii) Regionally Sensitive/CNPS List
IB; R-E-D 3-3-2; HMP Group 4
San Diego County and Baja
Califomia, Mexico. The only
United States occunence is in
Encinitas.
Chaparral of ail types. Not observed. Low potential; would have been
observed if present.
Little mousetail (Myosurus minimus) Regionally sensitive/CNPS List 3,
R-E-D 2-3-2
Coastal San Diego County and
elsewhere north to Butte County,
California.
Vernal pool Not observed. Low potential due to dlsturised nature of
vernal pools on site. Would have been observed if
presenL
Spreading navarretia (Navarretia
fossalis)
USFWS PT/CNPS List IB R-E-D
3-2-1
San Diego County Vernal pools and vemal
swales
Not observed. Low potential due to disturbed nature of
vernal pools on site. Would have been observed if
present.
Califomia orcutt grass {Orcuttia
califomica)
USFWS FE/CDFG SE/CNPS IB
R-E-D 3-3-2
San Diego County Vernal pools Not obsen/ed. Low potential due to disturbed nature of
vernal pools on site. Would have been observed if
present.
Engelmann oak (Quercus
engelmannii)
CNPS List 4; R-E-D 1-2-2; HMP
Group 2
Cismontane foothills of southem
Califomia, primarily from the
Santa Ana Mountains to Baja
California Norte, Mexico within an
upper elevational limit of
approximately 4,200 feet.
Between dry coastal plains
and cold, montane areas
with a minimum
precipitation level of 15
inches per year (Scott
1990).
Not observed. Low potential. Would have been
observed if presenL
San Diego County viguiera
(Viguiera laciniata)
CNPS Ust4; R-E-D 1-2-1 San Diego County and Baja
Calrfomia, Mexico.
Diegan coastal sage scmb. Not observed. Low potential; would have been
obsen/ed if present
1 j 1 i I liiilJtiiiiiii
TABLE 4
SENSITIVE ANIMAL SPECIES OCCURRING OR WITH POTENTIAL TO OCCUR ON THE LA COSTA OAKS/RIDGE PROJECT SITES
Species Name Status Distiibution Habitat(s) Oaks/Ridge Occurrence/Potential
Animal Species Observed On Site
AK11:'H1BIANS
Westem spadefoot (Spea
liammondii)
Regionally Sensitive/
CDFG CSC; HMP
Group 4
Central Valley and surrounding foothills in San
Francisco and the bay areas south along coast to
northwestem Baja Califomia.
Various habitats are used, inculding coastal sage
scmb, chaparral, and grassland, but the most
important factor is the presence of ephemeral
pools. Pools need proximity to friable soils for
burrowing by young spadefoots in the dry
summer and fall periods.
Tadpoles observed in ephemeral
ponded water areas in coastal sage
scrub and grassland east and west of
Rancho Santa Fe Road.
REPTILES
Coastal whiptail
(Cnemidopliorus tigris
multiscutatus)
Regionally Sensitive Ventura Coimty south, in cismontane CaHfomia,
to soufli-central Baja Califomia, Mexico.
Open coastal sage scmb, chaparraL and
woodlands. Frequently found along the edges of
dirt roads traversing its habitats. Important
habitat components include open, sunny areas,
shrub cover with accumulated leaf litter, and an
abundance of invertebrate prey, particularly
termites (Reticulitermes sp.).
Several individuals observed in coastal
sage scrub and chaparral.
Red diamond rattlesnake
(Crotalus exsul)
Regionally
Sensitive/CDFG CSC
Extreme southeastem Los Angeles County
(Diamond Bar) into southem San Bemardino
County, and south into southem Baja Califomia,
Mexico.
Favors rocky outcrops in coastal sage scrub,
chaparral creosote bush scrub, and areas
dominated by cactus. Also encountered along
rocky canyon bottoms and on the flats adjacent to
Tocky, desert foothills.
One observed in rocky areas of coastal
sage scrub.
Coastal rosy boa (Lichanura
trivirgata roseofusca)
Regionally Sensitive Treinsverse Ranges in Los Angeles and San
Bemardino counties soutti into northwestem Baja
CaHfomia, Mexico. Also east to the lower desert
slope and is most often found below 4,500 feet in
elevation.
Usually in or near rocky areas in coastal sage
scrub, chaparral, and desert scmb.
One observed in rocky areas of coastal
sage scmb.
San Diego homed lizard
(Phrynosoma coronatum
blainvillei)
Regionally
Sensitive/CDFG CSC;
HMP Group 4
Southem California, west of ttie deserts, and south
into northem Baja Califomia, Mexico.
Coastal sage scrub, chaparraL open oak
woodlands and open coniferous forests.
Important habitat components include basking
sites, adequate scrab cover, areas of loose soil, and
an abundance of harvester ants (Pogonomyrmex
sp.), a primary prey item.
One individual observed in coastal sage
scrab near San marcos Creek canyon.
BIRDS
Cooper's hawk (Accipiter
cooperii)
Nesting-CDFG CSC;
HMP Group 2
Throughout the continental U.S. excluding Alaska,
parts of Montana, and pcu-ts of the Dakotas.
Winters south to Mexico and Honduras.
In San E>iego County tends to inhabit lowland
riparian areas and oak woodlands in proximity to
suitable foraging areas such as scmblands or
fields.
Observed hunting in oak riparian areas
during several surveys, potentially
breeding on site.
i j t J t i I llllllllll
Species Name Status Distribution Habltat{s) Oaks/RIdge Occurrence/Potential
Southem Califomia rufous-
crowned sparrow (Aimophila
ruficeps canescens)
Regionally
Sensitive/CDFG CSC;
HMP Group 4
Ventura County southeast through Los Angeles,
Orange, Riverside and San Diego counties to
northwestem Baja Califonua, Mexico.
Coastal sage scrab where it occurs on rocky
hillsides and in canyons but also may be found in
open sage scrab/ grassy areas of successional
growth for example, after a fire.
Individuals common in coastal sage
scrab prior to the 1996 fire.
Bell's sage sparrow
(Amphispiza belli belli)
Regionally
Sensitive/CDFG CSC;
HMP Group 4
Lower slopes of the Califomia and northem Baja
Cahfomia, Mexico coast ranges; on the eastem
slopes bordering the Central Valley from the San
Francisco Bay Area to Trinity County; and on the
westem slopes of the Sierra Nevada from
Calaveras to Madera counties.
Sunny, dry stands of coastal sage scrab and
chaparral. May occasionally be found in other
cirid habitats such as cismontane jtmiper
woodland and alluvial fan scrab.
Estimated 13 to 20 pairs on site prior to
the 1996 fire.
Loggerhead shrike {Lanius
ludaoicianus)
CDFG CSC Widespread, but declining, throughout North
America. Winters south to Central America.
Habitat: Open habitats including grasslands,
scrablands, and mderal areas witti adequate
perching locations.
Two pair observed, possibly breeding.
Coastal Califomia gnatcatcher
(Polioptila californica califomica)
USFWS FT/CDFG
CSC; HMP Group 1
Southem Los Angeles, Orange, westem Riverside,
and San Diego counties soutti into Baja Califomia,
Mexico.
Coastal sage scrub. 35 pairs observed in coastal sage scrab
on site prior to 1996 fire.
Northwestern San Diego
pocket mouse (Chaetodipus
fallax follax)
Regionally
Sensitive/CDFG CSC;
HMP Group 4
Los Angeles County and southem San Bemardino
County south into west-cential Baja California,
Mexico.
Open areas of coastal sage scrub and weedy
growth, often on sandy substrates.
Trapped in southem mixed chaparral
and coastal sage scrub along dirt roads
and open areas on site.
San Diego black-tailed
jackrabbit (Lepus californicus
bennettii)
Regionally
Sensitive/CDFG CSC;
HMP Group 4
Southem Santa Barbara County, south on ttie
coastal slope to the vicinity of San Quintin, Baja
Califomia, Mexico, Localities on the eastem edge
of its range include Jacumba and San FeUpe Valley
in San Diego County,
Occurs primarily in open habitats including
coastal sage scrab, chaparral, grasslands,
croplands, and open, disturbed areas if there is at
least some scrab cover present.
Obseived in coastal sage scrab and non-
native grassland.
San Diego desert woodrat
(Neotoma lepida intermedia)
Regionally
Sensitive/CDFG CSC
•
Coastal slope of souttiem Califomia from San Luis
Obispo County south into coastal northwestem
Baja California, Mexico.
Open chaparral and coastal sage scrab, often
building large, stick nests in rock outcrops or
around clumps of cactus or yucca.
Several individuals trapped in coastal
sage scmb and chaparral.
Animal Species Not Observed On Site
INVERTEBRATES
San Diego fairy shrimp
(Branchinecta sandiegoensis)
USFWS FE; HMP
Group 4; Not a
covered spedes under
the HCP/OMSP.
Populations of this shrimp are known from vemal
pool habitat throughout much of San Diego
County.
Vemal pool Not observed. Moderate potential
wittiin the four vemal pools on site.
I I I I I i I I I E I I i t I I I & i
Species Name Status Distribution Habitat(s) Oaks/Ridge Occurrence/Potential
Quino checkerspot butterfly
(Euphydryas editim quino)
USFWS FE; HMP
Group 4; Not a
covered species under
the HCP/OMSP.
Current papulations are known to exist as several,
probably isolated, colonies in southwestem
Riverside County, southem San Diego Counly,
and northem Baja California, Mexico.
The principal larval host plants in San Diego are
dot-seed plaintain (Plantago erecta) owl's clover
(Castilleja exserta). Potential habitat in the region
includes vegetation communities with relatively
open areas that typically include the host and
nectaring plants; habitats include vemal pools,
lake margins, non-native grassland, perennial
grassland, disturbed habitat, disturljed wetlands,
and open areas within shrab communities.
Not observed during focused surveys in
1998 or 1999. Low potential; larval host
plants present on site but butterfly not
known historically from site.
Harbison's dun skipper
(Euphyes vestris liarbisoni)
Regionally Sensitive;
HMP Group 4
Southem Orange County to the Mexican border. Riparian habitats and chaparral where perennial
sources of water provide adequate habitat for the
larval foodplant, San Diego sedge (Carex spissa).
Not observed. Moderate potential;
Habitat abundant in San marcos Creek
and larval food plants present
However ttie site may be too close to
the coast for this species.
Hermes copper (Lycaena
liermes)
Regionally Sensitive;
HMP Group 4
San Diego County, south of Fallbrook to northem
Baja Califomia, Mexico.
Southem mixed chaparral and coastal sage scrab. Not observed. Moderate potential;
larval food plants presenL
Riverside fairy shrimp
(Streptocepluilus wootoni)
USFWS FE; HMP
Group 4; Not a
covered species under
the HCP/OMSP.
Populations of this shrimp are known from one
vemal pool in Carlsbad, some pools in Otay Mesa,
a few pools in Orange County, and Riverside
County.
Vemal pool Not observed. Low potential within the
four vemal pools observed on site. Pool
depth not appropriate.
VERTEBRATES
AMIHI^IANS.;;;- V
Califomia red-legged frog
(Rana aurora draytonii)
USFWS PE/CDFG
CSC; HMP Group 4
Northem Califomia along westem slopes of Sierra
Nevada through coast ranges to norttiwestem Baja
Califomia.
Occurs in ponds, marshes, and pools in creeks and
streams.
Not observed. Low potential; not
known from San Diego County since
the early 1970s.
REf^i|s-v,
Silvery legless lizard (Anniella
nigra argentea)
CDFG CSC East of San Francisco Bay south to norttiwestem
Baja California, Mexico. Primarily west of the
major mountain ranges, but there are scattered
populations along the westem edges of the
Califomia deserts.
Washes, beaches, alluvial fans, scrablands, and
oak woodlands. Important habitat components
include loose soil and leaf-litter, adequate sott
moisture, warmth, and an abundance of
invertebrate prey.
Not observed. Low potential because
appropriate habitat (sandy soils) occurs
on site.
Southwestem pond turtte
(Clemmys marmorata pallida)
Regionally
Sensitive/CDFG CSC;
HMP Group 4
Vicinity of Monterey in central Califomia south
into northwestem Baja Califomia, Mexico.
Primarily west of the major moimtain ranges in
southem Califomia, but there is a population
along ttie Mojave River in San Bemardino County,
Variety of wetland habitats including freshwater
marshes, creeks, ponds, and reservoirs. Adequate
basking sites, deep water retreats, and egg laying
areas are important components of habitat.
Not observed. Moderate potential;
would likely have been observed if
present However the species could
emigrate to the site via upstream
habitat into San Marcos Creek canyon
because appropriate habitat (ponds in
stream habitats) occurs.
I I I I
Species Name Status Distribution Habitat(s) Oaks/Ridge Occurrence/Potential
Orange-throated whiptail
(Cnemidophorus hyperythrus
beldingi)
Regionally
Sensitive/CDFG CSC;
HMP Group 2
Southem Orange County and southem San
Bemardino County (Colton), south to ttie cape of
Baja Califomia, Mexico.
Coastal sage scrab, chaparral, edges of riparian
woodlands, and washes. Also found in weedy,
disturbed areas adjacent to these habitats.
Important habitat requirements include open,
sunny areas, shaded areas, and abundant
invertebrate prey base, particularly termites
(ReticuUtermes sp.).
Not observed. High to moderate
potential because habitat on site is
appropriate.
San Diego banded gecko
(Coleonyx variegatus abbotti)
Regionally Sensitive Southem slopes of the San Gabriel Mountains of
Los Angeles County, south ttiroughout cismontane
and coastal souttiem Califomia into northwestem
Baja California, Mexico. Also found on Cedros
Island off the Pacific coast of Baja CaHfomia,
Mexico.
Chaparral and coastal sage scrab in areas with
rock outcrops.
Not observed. Low potential because
appropriate habitats (rocky outcrops)
do not occur on site.
San Diego ringneck snake
(Diadophis punctatus similis)
Regionally Sensitive Southwestem San Bemardino County south along
the coastal slope into northwestem Baja California,
Mexico.
Generally occurs in moist habitats such as oak
woodlands and canyon bottoms, but is also
sometimes encountered in grassland, chaparral,
and coastal sage scrab.
Not observed. Moderate potential
because appropriate habitat (chaparral)
occur on site.
Coronado Island s]smk
(Eumeces skiltonianus
interparietalis)
Regionally
Sensitive/CDFG CSC
Distribution: Southwestern Czdifomia from Los
Angeles County south into northwestem Baja
Califomia, Mexico. Also occurs on several islands
off the Pacific coast including Los Coronados
Islands.
Grasslands, coastal sage scrab, open chaparral,
pine oak woodland, and coniferous forests.
Prefers areas where there is abundant leaf Utter or
low, herbaceous growth.
Not observed. Moderate potential
because appropriate habitats (coastal
sage scrab and grasslands) occur on
site.
Coast patch-nosed snake
(Salvadora liexalepis virgultea)
Regionally
Sensitive/CDFG CSC;
HCP Group 5
Santa Barbara County south into northwestem
Baja Califomia, Mexico,
Primarily f otmd in chaparral but also inhabits
coastal sage scrab and areas of grassland mixed
with scrub.
Not observed. Moderate potential
because favored food source (whiptails)
occur on site.
Two-striped garter snake
(Tliamnophis liammondii)
Regionally Sensitive Distribution: Monterey County south through the
coastal ranges into northwestem Baja Califomia,
Mexico.
Primarily along permanent creeks and streams lmt
also around vemal pools and along intermittent
streams. Occasionally fotmd in chaparral or ofher
habitats relatively far from permanent water.
Not observed. Moderate potential;
would Hkely have been observed if
present However, like the pond turtle,
the species could emigrate to the site.
BIRDS •
Tricolored blackbird {A^laius
tricolor)
Regionally
Sensitive/CDFG CSC;
HMP Group 2
Califomia's Central VaUey and tfiroughout the
lowlemd regions west of ttie Sierra Nevada
Moimtains from San Diego County north to Lake
County. There are also breeding populations in
Califomia in Siskiyou and Modoc Counties and,
more recentty, in southem Oregon,
Forages in pastures, croplands, lakeshores, and
irrigated grassy areas. Breeds in freshwater
emergent wetlands, mostly marshes composed of
cattails (Typha spp.), wittows (Salix spp.), mulefat
(Baccharis sahcifolia), and tamarisk (Tamarix
spp.).
Not observed or expected on site.
Habitat not suitable.
Burrowing owl (Atliene
cunicularia)
Burrow sites-CDFG
CSC; HMP Group 4
Distribution:. Lower British Columbia to
Manitoba, Canada and ttie coitral and westem
U.S. south to northem Mexico and Baja Califomia,
Mexico.
Generally restricted to grasslands and agricultural
lands. Uses burrows of Califomia ground squirrel
(Spermophilus beecheyi) for nest sites.
Not observed or expected on site.
Habitat not suitable.
liil till I I I I I I I I I I i j
Species Name Status Distribution Habitat(s) Oaks/Ridge Occurrence/Potential
Cactus wren {Campylorhynchus
brunneicapillus)
Regionally
Sensitive/CDFG CSC;
HMP Group 4
Southem Orange County (San Juan Creek) soutti
through San Diego County into northwestem Baja
California, Mexico.
Restricted to clumps of prickly-pear (Opuntia
Uttoralis and O. oricola) or cholla (O. prolifera)
growing in coastal sage scrab or along washes.
Not observed. Low potential because
appropriate habitat (cactus patches)
does not occur on site.
Northem hamer (Circus
cyaneus)
Nesting-CDFG CSC;
HMP Group 4
Widespread throughout the temperate regions of
North America and Eurasia. Winters and migrates
throughout Califomia from below sea level in
Deatti Valley to an elevation of 9,800 feet. Known
breeding areas in San Diego County include
Torrey Pines, ttie Tijuana River Valley, and Camp
Pendleton,
CoastaL salt and freshwater marshlands;
grasslands; and prairies.
Not observed. Moderate potentizil to
forage on site but for breeding the site is
not appropriate.
Yellow warbler (Dendroica
petechia brewsteri)
CDFG CSC Throughout North America. A spring and
summer breeding resident in southem California.
Riparian areas throughout Califomia. Primarily
restricted to riparian woodland and ripsirian scrab
habitats in souttiem Califomia,
Not observed. Some potential for this
species to occur within San Marcos
Creek.
Southwestem willow
flycatcher {Empidonax traillii
extimus)
USFWS FE/CDFG SE;
HMP Group 1
Within the U,S., breeding range is restricted to
souttiem Califomia, Arizona, Utah, Nevada, New
Mexico, and Texas. Largest remaining population
in southem Califomia is at The Nature
Conservancy's Kem River Preserve. Other
significant remaining populations occur in San
Diego County along the Santa Margarita and San
Luis Rey Rivers. Intennittent sightings have
occurred at the south end of Lake Cuyamaca, at
the upper end of the Sweetwater Reservoir, at the
east end of Lower Otay Lake, and in the Tijuana
River Valley (Unitt 1987).
Breeds within thickets of willows or other riparian
understory, usuaUy along streams, ponds or lakes,
or in canyon drainage bottoms. Migrant birds
may be located among any of the larger trees or
shrabs in the Coimty of San Diego, but even
migrants seem to prefer damp areas.
Not observed. Moderate potential
because appropriate habitats (mature
riparian woodlands and streamside
riparian haliitats) are within San Marcos
Creek.
Califomia homed lark
(Eremophila alpestris actia)
Regionally
Sensitive/CDFG CSC
Coastal slopes and lowlands from Sonoma County
to northem Baja Califomia, Mexico,
Sandy beaches, agricultural fields, grasslands, and
open areas.
Not observed. Moderate potential for
occurrence because species is rather
common and appropriate habitat
(grassland) is present on site.
YeUow-breasted chat (Icteria
virens)
CDFG CSC; HMP
Group 2
Most of North America. Breeds in southem
Califomia during the spring and summer.
Brushy tangles, briars, stream thickets, riparian
scrab, and riparian woodland. Breeding confined
to riparian woodlands.
Not observed. Some potential for this
species to occur within San Marcos
Creek.
Least Bell's vireo (Vireo bellii
pusillus)
USFWS FE/CDFG SE;
HMP Group 1
Formerly common and widespread in Califomia
and northwestem Baja Califomia, Mexico. Known
to winter only in southem Baja Califomia, Mexico.
Riparian woodland and is most frequent in areas
that combine an understory of dense, young
WiUows (Salix spp.) or mulefat (Baccharis
salicifolia) with a canopy of tall wiUows.
Not observed. Low to moderate
potential to occur because appropriate
iiabitat (wiUow scrab and woodland)
occurs on site in San Marcos Creek.
MAMMALS _
j t I I llllllllllll
Species Name Status Distribution Habitat(s) Oaks/Ridge Occurrence/Potential
Dulzura (Califomia) pocket
mouse (Cliaetodipus californicus
femoralis)
RegionaUy
Sensitive/CDFG CSC
Reported from the mouth of the Santa Margarita
River soutti into norttiem Baja Califomia, Mexico.
In San Diego Coimty it ranges eastward to ttie
desert transition zone. Some locaUties near the
eastem edge of its range are Banner, San FeUpe
VaUey, and Campo.
Primarily associated with mature chapanal. It
has, however, been trapped in mule-fat (Baccharis
salicifolia) scrab.
Not observed. Low potential. Habitat
occurs on site.
Califomia mastiff bat (Eumops
perotis californicus)
RegionaUy
Sensitive/CDFG CSC;
HMP Group 4
A permanent resident in southem Califomia. Chapanal and where coast Uve oaks are found.
Also occurs in arid, rocky areas.
Not observed. Low potential. Habitat
appropriate for foraging.
Southern grasshopper mouse
(Onychomys torridus ramona)
Regionally
Sensitive/CDFG CSC
Northem Los Angeles County along the coastal
slope to extreme norttiwestem Baja Califomia,
Mexico. LocaUties near the eastem edge of its
range in San Diego County include Culp VaUey
and Jacumba in the desert transition zone.
Arid habitats including various types of
scrablands.
Not observed. High to moderate
potential. Appropriate habitat
(grassland) occurs on site.
Pacific pocket mouse
(Perognathus longimemhris
pacificus)
USFWS FE/CDFG
CSC; HMP Group 4;
Not a covered species
under the
HCP/OMSP.
Between 1894 and 1972, the subspecies was
recorded from eight general locales from Los
Angeles County south to the Mexican border in
San Diego County. Only three populations are
known to be extant today: one at ttie Dana Point
Headlands in Orange County and two on Camp
Pendleton in San Diego County. The subspecies
occurs within approximately Z4 miles inland of
the Pacific Ocean and has not been reUably
recorded above 600 feet in elevation (Erickson
1993).
Fine-grained, sandy or graveUy subsfrates in
coastal strand, coastal dunes, river aUuvium, and
coastal sage scrab growing on marine terraces.
Not observed. Habitat determined to
be inappropriate.
Townsend's westem big-eared
bat (Plecotus taionsendii
taiunsendii)
RegionaUy
Sensitive/CDFG CSC;
HMP Group 4
British Columbia, along the eastem slopes of the
Cascade and Siena Nevada mountiuns, into
southem CaHfomia from Santa Barbara County
south to norttiem Baja Califomia, Mexico. In the
eastem portion of its range it is known firom Soutti
Dakota, Kansas, Oklahoma, and the westem half
of Texas, as weU as south into the Mexican states
of Sonora and Chihuahua.
A cave-dwelling spedes but is sometimes found in
attics and bams.
Not observed. Low potential. Habitat
appropriate for foraging.
DRAFT
REGULATORY CONTEXT
Biological resources are subject to regulatory review by tiie federal government, State of CaUfornia, and
City. The federal govemment administers non-marine plant and wUdlife related issues through the
USFWS, whUe wetiands and Waters of tiie U.S. issues are administered by ACOE. CaUfomia law relating
to wetiand, water-related, and wildlife issues is administered by the CDFG.
The HCP/ OMSP tteats the 62 species that occur or potentiaUy occur on site as if they were Usted at
federal and state levels, although most are not listed.
Federal Government
The federal ESA, administered by the USFWS, provides the legal framework for the Usting and protection
of spedes (and theU habitats) which are identified as l>eing endangered or threatened with extinction.
Actions that jeopardize endangered or threatened species and the habitats upon which they rely are
considered a 'take' under tiie ESA. Section 9(a) of tiie ESA defines take as: "to harass, harm, pursue,
hunt, shoot, wound, kiU, ttap, capture, or coUect, or attempt to engage in any such conduct." 'Harm' and
'harass' are further defined in federal regulations and case law to include actions that adversely impair or
disrupt a Usted species' behavioral pattems.
Sections 7 and 10(a) of fhe federal ESA regulate actions that could jeopardize endangered or threatened
species. Section 10(a) aUows issuance of permits for 'mcidental' take of endangered or threatened spedes.
The term 'incidental' appUes if the taking of a Usted species is incidental to, and not the purpose of, an
otiierwise lawful activity. The HCP\OMSP is an approved 10(a) permit and meets requirements of
Section 10(a) whUe fulfUUng goals of tiie NCCP for tiie City and tiie MHCP. A habitat conservation plan,
demonsttating how the taking wUl be minimized and what steps taken would ensure the species'
survival, must be submitted for issuance of Section 10(a) permits.
Nesting raptors, such as red-taUed hawks and burrowing owls, are protected under the Federal Migratory
Bud Treaty Act (MBTA). This law is generaUy protective of migratory birds but does not actuaUy
stipulate the type of protection required. In common practice, USFWS places resttictions on disturbances
aUowed near active raptor nests. The HCP/OMSP stipulates that constmction activities are precluded
within 200 feet of an active raptor nest.
Federal wetiand regulation (non-marine issues) is guided by the Rivers and Harbors Act of 1899 and the
Clean Water Act. The Rivers and Harbors Act deals primarUy with discharges into navigable waters,
whUe the purpose of the Clean Water Act is to restore and maintain the chemical, physical, and biological
mtegrity of aU Waters of the U.S. Permitting for projects fUUng Waters of the U.S. (induding wetiands
and vemal pools) is overseen by the ACOE under Section 404 of the Clean Water Act. Projects may be
permitted on an individual basis or may be covered under one of several approved nationwide permits.
Individual permits are assessed individuaUy and approved based on the type of action, amount of fiU, etc.
Individual permits typicaUy require substantial time for approval, whUe nationwide permils are pre-
approved if a project meets appropriate conditions. It is currentiy assumed that an Individual Section 404
permit wiU be needed for the project.
State of Califomia
The CaUfomia ESA is simUar to the federal ESA m that it contains a process for Usting of species and
regulating potential unpacts to Usted species. Section 2081 of tiie CaUfomia ESA authorizes CDFG to
enter into a memoranda of agreement for take of Usted species for scientific, educational, or management
purposes. Requuements under Section 2081 are addressed in the HCP/OMSP for the 62 species
considered as listed.
HELIX
Draft Biological Technical Report for the La Costa Oaks and Ridge projects /MDI-06 /July 7,1999
DRAFT
The California NCCP Act (Section 2835) aUows the CDFG to authorize take of species covered by plans in
agreement with NCCP guideUnes. The HCP/OMSP meets the requirements of the NCCP Act as OMSP
and provides a basis for CDFG authorization for take of state-listed species. An NCCP initiated by the
State of Califomia under Section 4(d) of the federal ESA focuses on conserving coastal sage scrub in order
to avoid the need for future federal and state listing of coastal sage scmb dependent species. The coastal
California gnafcateher is presentiy listed as threatened under the federal ESA, whUe several additional
species inhabiting coastal sage scrub are candidates for federal listing. This project is considered a
completed NCCP plan witiiin the Cit/s Draft HMP.
The Native Plant Protection Act (NPPA) enacted a process by which plants are listed as rare or
endangered. The NPPA regulates coUection, transport, and commerce in plants that are listed. The
CaUfornia ESA foUowed NPPA and covers both plants and animals that are determined to be endangered
or threatened with extinction. Plants listed as rare under NPPA were designated threatened under the
Califomia ESA. The HCP/ OMSP conserves the plant species treated as listed adequately in agreement
with tiie NPPA.
The CDFG Code (Sections 1600-1603) requires agreement with CDFG for projects affecting riparian and
wetiand habitats through issuance of a Stteambed Alteration Agreement. Stteambed Alteration
Agreements are required for impact to any riparian habitat including, in the case of the Oaks and Ridge
projects, two riparian communities. The HCP/OMSP provided for approval of a Stteambed Alteration
Agreement for the Oaks and Ridge projects.
The Califomia Environmental QuaUty Act (CEQA) and its implementing guidelines (CEQA Guidelines),
require projects that potentiaUy have significant effects (or impacts) on tiie environment to be submitted
for environmental review. Significant impacts to the environment are typicaUy mitigated through the
environmental review process, in accordance with existing laws and regulations. This report fulfills the
requirements of CEQA.
City of Carlsbad
The City HMP has been in preparation since 1990 and is currentiy in the form of an agency informal
review draft. The HMP is an NCCP subarea plan, addressing potential impacts to native spedes and
habitats whUe at the same time providing mitigation options that satisfy the federal and state ESAs. The
primary objective of the HMP is to identify and maintain a preserve system that aUows for the sustained
existence of animals and plants at both the local and regional levels. The HMP preserve is a network of
large habitat blocks with interconnecting linkages. The area covered by the HCP/OMSP is within Local
FacUity Management Zones (LFMZ) 10, 12, and a portion of 11 of the HMP (Figure 3). The Oaks and
Ridge projects Ue within LFMZ 11 and 12. Impacts and mitigation measures for the HCP\OMSP projects
are incorporated into the HMP. The HCP/OMSP is a completed component of the HMP.
The CEQA process for the Greens project is overseen by the City, This report is intended to provide the
City with an adequate basis to proceed with the CEQA approval process. The final city authorization of
the Oaks and Ridge projects wiQ depend on project consistency with the HMP.
IMPACT ANALYSIS AND MITIGATION MEASURES
This section presents an impact analysis of the Oaks and Ridge projects in the context of that approved
under the HCP/OMSP. The projecfs impacts are assessed based on the currentiy proposed projecfs
impacts to the existing environment. Impacts resulting from the re-aUgnment of Rancho Santa Fe Road
HEUX ,
Draft Biological Technical Report for the La Costa Oaks and Ridge projects /MDI-06 / July 7, 1999 11
NOTE:
FOCUSED PLANNING AREAS INCLUDE
THOSE AREAS THAT ARE PRESENTLY
VACANT AND WITH OR WITHOUT AN
APPROVED TENTATIVE TRACT MAP.
CARLSBAD CITY BOUNDARY
LEGEND
HMP PRESERVE PUVNNING AREAS
HCP PLAN AREA
Prepared By: Hofman Planning Associates
ll[LIX
HMP Preserve Planning Area
THE OAKS AND RIDGE PROPERTIES
Oaks/Ridge
Project
NTS
Fiijure 3
DRAFT
are separated from the overaU project impacts. The total project impacts (including Rancho Santa Fe
Road) are compared with impacts and mitigation measures approved under fhe HCP/OMSP and to show
consistency of the current plan with the HCP/OMSP. Impacts are dettimental effects of a project that
may be direct or indirect. Direct impacts displace habitat, such as during grading. Indirect impacts are
secondary effects of a project. Examples of indirect impacts include habitat insularization, edge effect,
exotic species invasion, vehicular noise, and increased human or pet intmsion. The magnitude of an
indirect impact can be the same as a direct impact Impacts were calculated based on the most recent
impact footprints for the project. Areas that are modified due to grading, placement of stmctures, or
alteration of existing features are considered to be directiy impacted.
DIRECT IMPACTS
Direct impacts are those that immediately alter the affected biological resources such that those resources
are not expected to recover to their pre-impacted state. An assumption of this direct impact assessment is
that aU areas outside the HMP Preserve Area on site wiU be interpreted as receiving direct impacts.
Vegetation Communitie^Habitats
Project
Direct impacts resulting from the project total 558.5 acres of tiie 1,205.8 acres on site (Figure 4a-b; Table 5).
Habitats impacted include Diegan coastal sage scrub (312.4 acres), southern mixed chaparral (120.7 acres),
non-native grassland and native grassland (47.0 acres), combined riparian habitats (1.0 acre), vemal pool
(4 pools; 0.05 acre), and disturbed habitat (77.2 acres). Impacts to vemal pools, Diegan coastal sage scmb,
and riparian habitats are considered significant.
Grading impacts to vemal pool watershed would occur in three distinct watersheds, one of which
encompasses two pools. Within aU of these watersheds, there would be a total loss of vemal pool surface
area, negating the value of remaining watershed portions. None of these impacted pools are known to
support sensitive spedes.
Table 5
VEGETATION IMPACTS
Habitat Total Impacts (%) Conserved (%)
Project Rancho Santa
Fe Road
Realignment
Diegan coastal sage scmb 809.1 268.1 (33%) 46.6(6%) 494.4 (61%)
Riparian 25.1 0.0 (0%) 1.0 (4%) 24.1 (96%)
Southem mixed chaparral 182.8 110.2 (60%) 10.5 (6%) 62.1 (34%)
Grasslands 67.2 43.6 (65%) 3.4 (5%) 20.2 (30%)
Open water 0.4 0.0 (0%) 0.0 (0%) 0.4 (100%)
Vemal pool 1,960 sq. ft.
0.05 acre
1,960 sq. ft.
0.05 acre (100%)
0.0 (0%) 0 sq. ft.
0.0 acre (0%)
Eucalyptus woodland 0.7 0.2 (29%) 0.0 (0%) 0.5 (71%)
Disturbed habitat 120.4 73.5(61%) 3.7 (3%) 43.3 (36%)
Total 1,205.8 514.2 (43%) 46.6 (4%) 645.0 (53%)
HELIX
Draft Biological Technical Report for tlie La Costa Oaks and Ridge projects /MDI-06 / July 7,1999 n
FOR CONTINUATION SEE SHEET NO. 2
NOTTOSCALE
HABITAT LEQEND:
323 J ACRES ["""^ DaSTINQ HABTTAT CONSERVATION FLAN RESEFWE 1^ ^ (BOUNDARY PEfl CfTY OF CAHLSBAD DATA)
+ia3.7 ACRES
ACRES
• AREA TO K ADCED TU THE HASTTAT CONSEFWATION PLAN flESERVE TOTAL AREA: 122.B AC.
AREA TO REMOVED FTOM THE HABfTAT CONSERVATION PUN RESERVE
TOTAL AREA: 3.8 AC.
IMPACT AREA:
BM,B ACRES NET HCP AREA
VEGETATION LEGEND (on-sHe):
DE5CMPTKW HCP
AHEA
uwrrs
(4C8ES)
Dcss-a
SMC
somv
UNO
na
EW
POND oa nvs
DIEQAN CO^ALSASE BCRUB
(CUjrenNitBAaESRUSH DOMINATED)
OIEQAN C09TAL OUE SCRUB
(BL*CK SAQE DCMIMATEO]
SOUTHERN MKED CHAPARRAL
KlUTHERN COAST UVE OAK RIPARIAN
WOOOLANO
NONMATIVE GRASSLAM3
NATIVE <3RAS8LWD
EUCALinuS WOODLANO
POND
DISTURBED/nUDERAL
SOimiBW WILCM SCRUB
[BURNED AREA]
(RCMD)
1(1,11
29.1 B
I, 14
II. 96
734 *
0.4a
33.93
1B.17
-0-
-0-
907.71
ee,e7
144.32
3.4Z
33.00
24.SS
0.T*
-3-
UAS
ti7
21,48
1.03
TOTAL 3X9,27 «ei>>4a
SENSITIVE RESOURCES (on-Gits):
CO
w
Ao
M
BS
Sc
On
SfWL
ncer BCM
8C
DICHaNDHA OCCOB^AUS
VIQUERAIACINMTA
AOOIPHW CAUFORNICA
JUNCUS ACTUS
COASTAL GAQE SPARnOW
SBAQINEUA CNERASCENS
COREOPSIS MARIT1HA
BAN DEQO HORNED LIZARD
ROSY BOA
QNAT<»TCHm {iiumlmHimll
OJX
0. 03
1. TS
0.01
>1,5Z
O.OB
o.OI
0,2$
4.
39,08
B&AOtKELLA ONERASCBB OCCURS TMROUQHOLn-^EAND RUniU&CnOWNgD SPARROW IB SPREAD THROUQHOin CHAPARRAL
EnSnMG PROJECT AREA: 120B.7 ACRES
UUTTB OF PROJECT QRADINQ
ll[LIX
Vegetation, Sensitive Resources, Impacts and HCP Preserve
THE OAKS AND RIDGE PROPERTIES figure <a
FOR CONTINUATION SEE SHEET NO. 1
SHEET 2 OF 2 SHEETS
ll[LIX Vegetation, Sensitive Resources, Impacts and HCP Preserve
THE OAKS AND RIDGE PROPERTIES Figure 41)
m
DRAFT
Federal (ACOE) jurisdictional impacts within the boundaries of the proposed Oaks and Ridge
developments (induding Rancho Santa Fe Road) consist of approximately 0.58 acre of wetiands (entirely
freshwater marsh), 0.55 acres of non-vegetated Waters of the U.S., and 0.05 acre of vemal pool habitat (4
pools),. Jurisdictional non-vegetated Waters of the U.S. habitats to be impacted comprise imvegetated
streambed habitats. Wetiand areas are regulated under a "no net loss" poUcy by the ACOE, and any
impacts to ACOE jurisdictioriai wetiands areas wiU require mitigation. The permit requirements under
Section 404 for the project wiU require an individual permit due to the amoimt of wetlands being
impacted (greater than 6 acres including the La Costa Greens Project). The fmal determination for permit
requirements wiU depend upon the timing of the project and direction from the ACOE.
m A CaUfomia Regional Water QuaUty Control Board permit (401 Certification) wiU also be obtained before
any impacts to jurisdictional areas occur.
m
^ State (CDFG) jurisdictional impacts within the boundaries of the proposed Oaks and Ridge development
(including Rancho Santa Fe Road) consist of approximately 1.13 acres. The HCP/OMSP identifies
impacts and mitigation requirements for a Streambed/Lake Alteration Agreement permit for the Oaks
and Ridge projects.
Rancho Santa Fe Road
m
m Direct impacts resulting from the Rancho Santa Fe Road reaUgnment project total 46.6 acres of the 1,205.8
acres on site (Figure 4a-b; Table 5). Habitats impacted include Diegan coastal sage scmb (28.0 acres),
*• southem mixed chaparral (10.5 acres), non-native grassland and native grassland (3.4 acres), combined
^ riparian habitats (1.0 acre), and disturbed habitat (3.7 acres). Impacts to Diegan coastal sage scmb and
riparian habitats are considered significant.
Federal (ACOE) jurisdictional impacts within the Rancho Santa Fe Road reaUgnment consist of 1.0 acre of
the total ACOE jurisdictional wetiands areas. As discussed above an individual permit wiU be required
_ and mitigation wtil depend upon the timing of the project and direction from the ACOE. A Califomia
Regional Water QuaUty Control Board permit (401 CertiJfication) wiU also be obtained before any impacts
to jurisdictional areas occur. State (CDFG) jurisdictional impacts within the Rancho Santa Fe Road
reaUgnment consist of approximately 1.0 acre of the total projecfs 1.13 acres. The HCP/OMSP grants a
Stieambed/Lake Alteration Agreement permit for the Oaks and Ridge projects, induding Rancho Santa
^ Fe Road.
— Sensitive Plant Species
Project
Five sensitive plant species would be directiy impacted by tiie Project (Table 6). Impacts to Orcutfs
brodiaea are considered significant due to this species high sensitivity. PotentiaUy-occurring species are
not expected on site but if present, they likely occur in very low numbers. PotentiaUy-occurring species
were contemplated as part of the HCP/OMSP.
HELIX
Draft Biological Technical Report for the La Costa Oaks and Ridge projects /MDI-06 / July 7, 1999 13
DRAFT
m
m
M
Table 6
Sensitive Plant Impacts
Plant Species Conserved On Site (individuals) Assumed Taken (individuals)
Orcutf s brodiaea 0 10
San Diego marsh elder Nearly aU Less than 100
Califomia adolphia 2,400 4,100
Westem dichondra 2 of 5 stands 3 of 5 stands
Ashy spike-moss 460 acres* 560 acres*
*individuals not counted, acreage of habitat provided instead
Rancho Santa Fe Road
One sensitive plant spedes, San Diego golden-star, would be dUectiy impacted by the Rancho Santa Fe
Road reaUgnment. Impacts to 1,500 individuals would occur leaving approximately 400 individuals in
open space. The impacts to San Diego golden-star are considered significant due to this species high
sensitivity. PotentiaUy-occurring species are not expected in the proposed reaUgnment area. Potentially-
occurring species were contemplated as part of the HCP/OMSP.
Sensitive Animal Species
Project and Rancho Santa Fe Road
For this section, impads of the overaU project and Rancho Santa Fe Road reaUgnment are discussed
together because these areas support simUar habitats and therefore simUar species would occur.
Of the 13 sensitive animals species observed on site, only the impacts to the coastal CaUfornia gnatcatcher
and potentiaUy nestuig raptor species (Cooper's hawk and burrowing owl) are considered significant.
Impacts to the San Diego homed Uzard, coastal whiptaU, northwestern San Diego pocket mouse, San
Diego black-taUed jackrabbit, and desert woodrat are considered adverse but not sigriificant due to their
low sensitivity. Some loss of raptor foraging habitat wiU result from the project. AdditionaUy,
loggerhead shrike breeding and foraging habitat wiU be lost. These impads are considered adverse but
not sigruficant.
INDIRECT IMPACTS
Indirect impacts are impacts to the biological resources that occur over short or long periods of time due
to the project action. Although biological resources may not initiaUy be directiy impacted, over time they
may be affected indirectiy due to the relative proximity of development. Examples of indirect impacts
expected to occur as a result of the proposed project include habitat insularization, edge effect, exotic
species invasion, domestic pets, increased human intmsion, Ughting, and noise impacts.
HCP/OMSP ANALYSIS
The direct impacts within the Oaks and Ridge projects are summarized in tabular format (Table 7), then
analyzed within the context of the HCP/OMSP. Figure 4a-b depicts the impact area for the project.
HELIX
Draft Biological Technical Report for tbe La Costa Oaks and Ridge projects /MDI-06 /July 7,1999 14
DRAFT
Table 7
Habitat Total Impacts Conserved Conserved Amount added to
(VLCMP) under VLCMP under HMP preserve
-Vemal pool 0.05 0.05 0.0 Not
identified
N/A
M In HMP
•m Diegan coastal
sage scrub
809.1 314.7 494.4 423.5 +70.9
m Riparian 25.1 1.0 24.1 19.3 +4.8
-m
Southem mixed
chaparral
182.8 120.7 62.1 29.2 +32.9
M Grasslands 67.2 47 20.2 19.3 +0.9
Open water 0.4 0.0 0.4 0.4 No change
m Eucalyptus
woodland
0.7 0.2 0.5 0.0 +0.5
Disturbed habitat 120.4 77.2 43.3 33.5 +9.8
Total 1,205.8 560.8 645.0 525.2 +119.8
Vemal pool habitat was discovered on site during 1999 surveys. The project would impact aU of the
vernal pools and their respective watersheds.
Approximately 70.9 acres of coastal sage scmb are added to the HCP/OMSP preserve. This is in part
accounted for by the revegetation on site of 10 acres for the La Costa VaUey project. The other areas of
increase occur in patches throughout the site. Of the coastal sage scmb being removed from the
development footprint, the part within the San Marcos Creek corridor east of the shared boimdary of the
Oaks and Ridge projects is expected to contribute in the most meaningful manner to the functionaUty of
the preserve. WhUe many of these patches are smaUer (2.0 acres and less), they adjoin existing preserve
areas and increase the overall value of the preserve. A single 7-acre patch being added (southem part of
the site) is sufficientiy large to support several sensitive species, but is completely surrounded by
development.
Soutiiem nuxed chaparral additions to the preserve occur in the nortiiern half of the sites. Five of the
areas being added dUectiy adjoin existing preserve areas, including two patches of 5 acres or greater.
One other addition of southern mixed chaparral is approximately 10 acres but does not adjoin existing
preserve areas.
Grassland areas being added are for the most part isolated from the preserve, adjacent to off site areas
that are either developed or are not part of the Carlsbad HMP preserve. The additions iaclude
approxunately one acre of native grassland, a habitat of higher value than non-native grassland. The
native grassland being added is adjacent to the riparian area in the extreme southern haU of the sites.
Additions of riparian habitats to the preserve are significant, especiaUy within the San Marcos Creek
canyon due to its functionaUty as a wUdlife corridor. Another zone of riparian bemg added is at the
extreme southern half of the Oaks site. Although this area would be isolated from the other preserve
areas by development, regardless, preservation of this area is important because it represents tiie only oak
woodland on site.
The additions to the preserve would result in an increase in the habitat for aU sensitive plant spedes
observed on site. The additions to the preserve wUl benefit the coastal CaUfomia gnatcateher by adding
HELIX
Draft Biological Technical Report for the La Costa Oaks and Ridge projects /MDI-06 /July 7, 7999 15
m
DRAFT
65.3 acres of habitat adjacent to preserved coastal sage scrub patches. Several additional coastal sage
scrub-dependent species (orange-throated whiptail, southem CaUfornia rufous-crowned sparrow, etc.)
would benefit from additions to the preserve. Foraging habitat for raptor species such as the northern
harrier, white-taUed kite. Cooper's hawk, burrowing owl, and golden eagle wiU be increased significantly
by the overaU addition of 119.8 acres to the preserve.
MITIGATION MEASURES
Mitigation for project impacts is in the context of the HCP/OMSP, involving preservation of 521.4 acres
on the Oaks/Ridge sites. In addition, there are interim and ongoing habitat management, and project-
specific impact minimization and mitigation measures. The VLCMP implements a larger preserve area
and increases the amount of on-site open space by approximately 119.8 acres.
On site conservation would occur within the preserve areas designated in the HCP/OMSP and the areas
added under the VLCMP depicted on Figure 4a-b.
The foUowing mitigation measures apply to both the overaU project emd to the Remcho Santa Fe Road
reaUgnment, where appUcable.
Sensitive Habitats
Impacts to Diegan coastal sage scrub would be mitigated by on-site preservation of 494.4 acres (54
percent) of the coastal sage scmb on site within the HCP/OMSP open space. This action, in conjunction
with the measures below, would fully mitigate impacts to coastal sage scrub.
Impacts to wetiands, including aU ripariem habitats, wiU be mitigated at a 2:1 ratio and impacts to other
Waters of the U.S. wiU be mitigated at a 1:1 ratio. Figure 7 identifies areas proposed for riparian habitat
restoration. Vernal pool mitigation requirements have not yet been identified. If mitigation is initiated
prior to project impacts, mitigation ratios may be reduced but would not faU below 1:1 for wetlands and
0.5:1 for other Waters of the U.S. Alteration to or fiUing in of these areas would be subject to regulation by
the ACOE in the form of a permit pursuant to Section 404 of the federal Qean Water Act. A Section 401
waiver or certification from the Califomia Regional Water QuaUty Contiol Board is also required. The
details of the mitigation wiU be detennined as a part of the permit processes with the ACOE.
Sensitive Plant Species
Impacts to Orcutfs brodiaea and San Diego golden star are not mitigated by the project, but they are
considered covered species under the HCP/OMSP. They are covered due to theU conservation under
regional conservation plans such as the MHCP and HMP. PotentiaUy occurring species discussed earUer
are not expected to occur on site. However if these species were to occur, they would likely benefit
through the HCP/OMSP open space program cited above.
Sensitive Animal Species
Mitigation for impacts to the coastal Califomia gnatcateher would be mitigated through the coastal sage
scmb preservation on site cited above. Mitigation is not required for the other coastal sage scmb-
occupying sensitive species impacted on site (San Diego homed lizard, coastal whiptaU, northwest San
Diego pocket mouse, San Diego black-taUed jackrabbit, and desert woodrat) due to their low sensitivity
status and/or limited extent on site. Regardless, the proposed coastal sage scrub mitigation would
benefit these species.
HELIX
Draft Biological Technical Report for tlie La Costa Oaks and Ridge projects /MDI-06 / July 7, 1999 14
m
DRAFT
Impacts to burrowing owl and Cooper's hawk do not require mitigation outside that approved in tiie
HCP/OMSP because it is a completed component of the HMP. Cumulative impacts to the habitats of
these species wiU be met in conjunction with habitat preservation proposed in the HCP/ OMSP and other
regional conservation efforts.
Mitigation for impacts to loggerhead shrike habitat is being met through tiie proposed habitat
preservation on site.
Mitigation proposed in the HCP/OMSP is considered to be met for aU potentiaUy-occurring animal
species, except for the two fairy shrimp species, quino checkerspot butterfly and Pacific pocket mouse.
Surveys for Ihe checkerspot were negative and the habitat on site is inappropriate for the pocket mouse.
Since these species were determined not to be present, no mitigation is required for them. Surveys for the
fairy shrimp are ongoing. Results of fairy shrimp surveys wiU determine the need for mitigation, but if
shrimp are found they wiU be mitigated in the context of any vernal pool mitigation program.
Habitat Management and Mitigation For Indirect Impacts
Two types of habitat management are directed in the HCP/OMSP: interim and ongoing habitat
management. Interim management measures include access control, clean-up of dumped trash, and
implementation of project-specific measures outlined below. Ongoing habitat management is to be
guided by annual plans prepared by a designated entity proscribed by a management advisory
committee composed of the project proponent and agency and City representatives. The ongoing plan
would consist of monitoruig, habitat restoration and enhancement, cowbird trapping, weed contiol, fire
management, access contiol maintenance, and pubUc education.
^ Impacts would be minimized and mitigated primarUy by the proposed habitat conservation on and off
site. In addition, there are ten impact avoidance and minimization measures to be implemented. The
*• measures summarized below are described in greater detaU in the HCP/OMSP:
~" • Nest site protection;
M - No clearing or grading to be aUowed in gnateatcher-occupied habitat between February 15 and
July 31.
— - Clearing activities within 200 feet of active raptor nest sites wiU be avoided.
• ContioUed access and barriers;
- Prior to and during constmction activities, access barriers wiU be estabUshed at key entry points
to the site. The boundaries of conserved habitat areas wiU be fenced with the help of a biologist
to prevent disturbance during constmction.
^ • Noise level control;
- During grading and constmction, noise levels beyond 60 dBA leq wUl be prevented during the
gnateatcher breeding season (Febmary 15 to July 31) by use of temporary six-foot noise berms.
• • Storage and staging area placement;
- Storage and staging areas wiU be placed as far from conserved habitat areas as possible and
• these areas shaU be kept free from tiash and other waste that may attiact scavengers.
^ • Biological monitoring;
- A biologist wiU monitor constiuction activities to ensure that conserved habitat areas do not
m receive excessive amounts of dust or other disturbances. In addition, erosion contiol measures
wiU be inspected regularly.
• Contingendes for unforeseen disturbances;
^ - Where disturbance to conserved habitat areas is unavoidable, the disturbance wiU be authorized
and mitigation measures wiU ensue. Revegetation plans wUl be prepared in cooperation with the
City prior to the disturbance.
HEUX
—' Draft Biolo^cal Technical Report for the la Costa Oaks and Ridge projects /MDI-06 / July 7, 1999 17
DRAFT
• Fuel management zone composition;
- Fuel management zones wiU be designed to minimize impacts to native vegetation.
• Lighting standards;
- Lighting wiU be directed away from conserved habitat areas and shielded. Residential lighting
will be designed to not shine on conserved habitat areas.
• Landscaping directives;
- Invasive plant species shaU not be used in landscaping adjacent to conserved habitat areas. A
list of such species shaU be provided in the CC&Rs of the homeowners association.
• A pubUc information program;
- The pubUc wUl be educated as to the importance of the conserved habitat areas and ways to
avoid impacts to them. The program wiU include educational brochures.
Supplemental mitigation measures are described in the HCP/OMSP as weU including:
• Funding of $50,000 for gnatcatcher research,
• Coordination with other regional and local conservation efforts (MHCP), and
• Cooperation with other landowners.
The aforementioned measures mitigate aU project impacts to a level below significant and comply with aU
local, state, and federal regulations.
HELIX
Draft Biological Technical Report for the La Costa Oaks and Ridge projects /MDI-06 /July 7, 1999 18
DRAFT
LITERATURE CITED
American Omithologists' Union. 1983. CheckUst of Nortii American Birds (6th Edition). American
Ornithologists'Uiuon, 877 pp. Updated every two years.
Carlsbad, City of. 1995. Habitat Conservation Plan/Ongoing Multi-Species Plan for Properties in the
Southeast Quadrant of the City of Carlsbad, California. June, 1995.
Carlsbad, City of. 1999. Habitat Management Plan for Natural Communities in the City of Carlsbad.
AprU 1999.
CDFG. 1993. Natural Community Conservation Planning Process GuideUnes. Unpublished.
CDFG. 1994a. Special Animals. Califonua Department of Fish and Game, Natural Diversity Data Base,
August, 1994. Updated as new listings occur.
CDFG. 1994b. Designated Endangered, Threatened, or Rare Plants and Candidates with Official Listing Dates.
California Department of Fish and Game, Natural Diversity Data Base. January, 1994. Updated
as new Ustings occur.
Collins, J. T. 1997. Standard common and cunent scientific names for North American amphibians and
reptUes (4th Edition). Society for the Study of Amphibians and ReptUes, Herpetological Circular
No. 25,40 pp.
Envuonmental Laboratory. 1987. "Corps of Engineers Wetiands DeUneation Manual," Technical Report
Y-87-1, U.S. Army Engineer Waterways Experiment Station, Vicksburg, Mississippi. 100 pp. plus
Appendices A through D.
Hickman, J. C. (Ed.). 1993. The Jepson Manual, Higher Plants of CaUfomia. University of CaUfornia
Press, Berkeley, 1400 pp.
HoUand, R. F. 1986. Prelimmary descriptions of the terrestiial natural communities of CaUfomia.
Nongame-Heritage Program, Califomia Department of Fish & Game.
Jones, C, R. S. Hoffman, D. W. Rice, R. J. Baker, M. D. Engstiom, R. D. Bradley, D. J. Schmidly, and C. A.
Jones. 1997. Revised checkUst of North American Mammals North of Mexico, 1997. Occasional
Papers of tim Museum, Texas Tech University, 173:1-25.
Mock, P.J., B.L. Jones, and J. Konecny. 1990(7). CaUfomia Gnatcatcher Survey GuideUnes. Unpublished
SANDAG. 1997. PreUminary Biological Analysis for MHCP Priority Species. UnpubUshed draft
SANDAG Board Report.
Scientific Review Panel. 1992. Coastal Sage Scrub Survey Guidelines. Unpublished. 10 pp. plus
attachments.
Skinner, Mark W., and PavUk Bruce M. 1994. Inventory of Rare and Endangered Plants of Califomia.
CaUfomia Native Plant Society.
HELIX
Draft Biological Technical Report for tlte La Costa Oaks and Ridge projects /MDI-06 /July 7, 1999 19
DRAFT
USDA SoU Conservation Service. 1992. Hydric SoU Lists. Field Office Offidal List of Hydric SoUs Map
Units for San Diego Area, Califomia . Section II Field Office Technical Guide. Davis, California.
USFWS. 1997. Coastal Califomia gnateatcher {Polioptila califomica califomica) Presence/Absence Survey
Guidelines. Unpublished.
USFWS. 1998. Quino Checkerspot butterfly {Euphydryas editha quino) Presence/Absence Survey
Guidelines. UnpubUshed.
USFWS. 1999. Survey Protocol for the Endangered QuUio Checkerspot Butterfly {Euphydryas editha quino)
for the 1999 Field Season. January 25,1999.
HELIX
Draft Biological Technical Report for the La Costa Oaks and Ridge projects /MDI-06 / July 7,1999 20
m
APPENDIX A
SURVEY INFORMATION
Siurvey focus MontVyear
Vegetation mapping August and November 1990;
AprU, May, and October 1991;
June 1992
Rare plant surveys March 1991;
July, September, and October 1992
Coastal Califomia gnatcatcher surveys AprU, May, September, October, and December 1991;
January, March, and April, 1992
Coastal Califomia gnateatcher banding August and September 1991
Sensitive butterfly surveys June 1992
Quino checkerspot butterfly surveys AprU 1998; March to May, 1999
Sensitive reptUe surveys May and June 1992
SmaU mammal ttapping August 1992
Wetiand delineation September 1998
A-l
APPENDIX B
OAKS/RIDGE PLANT SPECIES LIST
m
m
Scientific Name
Achillea millefolium var. millefolium
Adenos toma fasciculatum
Adolphia califomica
Allium sp.
Ambrosia psilostachya
Anagallis arvensis
Animopsis califomica
Antirhinnium sp.
Apiastmm angustifolium
Artemisia califomica
Amndo donax
Astragalus sp.
Avena sp.
Baccharis salicifolia
Baccharis sarothroides
Brassica geniculata
Bromus diandms
Bromus hordaceus
Bromus madritensis ssp. mbens
Calandrinia ciliata
Callitriche marginata
Calystegia macrostegia
Chamaesyce polycarpa
Castilleja affinis
Castilleja exserta
Ceanothus sp.
Centaurea melitensis
Centaurium venustum
Chamomilla suaveolens
Chenopodium album
Chlorogalum sp.
Chrysanthemum coronarium
Cirsium sp.
Claytonia perfoliata
Clematis sp.
Cneoridium dumosum
Collinsia sp.
Crassuia aquatica
Crassuia erecta
Cryptantha sp.
Cuscuta sp.
Common Name
Common yarrow
Chamise
Califomia adolphia
WUd onion
Westem ragweed
Scarlet pimpernel
Yerba mansa
Snapdragon
WUd celery
California sagebmsh
Giant reed
Milkvetch
WUd oat
Mule fat
Broom baccharis
Mustard
Ripgut grass
Soft chess
FoxtaU chess
Red maids
Long-stalk water-starwort
Moming glory
Rattiesnake weed
Paintbrush
Purple owl's clover
LUac
Tocalote
Canchalagua
Pineapple weed
Lamb's quarters
Soap-plant
Annual garland, crown daisy
Thistle
Miner's lettuce
Virgin's bower
Spicebush
Chinese houses
Stonecrop
Stonecrop
Cryptantha
Dodder
B-1
APPENDIX B
OAKS/RIDGE PLANT SPECIES LIST (Cont.)
•m Scientific Name Common Name
m Cynodon dactylon Bermuda grass
Ml Cyperus sp. Sedge
Datura wrightii Jimson weed
m Dichlostemma pulchellum Blue dicks
Dichondra occidentalis Westem dichondra
m Dodecatheon sp Shooting-stJu:s
m Dryopterios arguta Wood fem
Dudleya pulverenta Chalk dudleya
Eleocharis sp. Spike-msh
m Encelia califomica Califomia encelia
Eremocarpus setigems Turkey muUein
Eriogonum fasciculatum CaUfomia buckwheat
Eriophyllum confertiflomm Golden yarrow
Erodium sp. Filaree
Eschscholzia califomica Califomia poppy
Eucalyptus sp Eucalyptus
Foeniculum vulgare Sweet fermel
Galium sp. Bedstiaw
Gazenia sp. Calttans daisy
Gnaphalium sp. Everlasting
Hazardia squarrosus Goldenbush
— Helianthemum scoparium Rock rose
Hemizonia fasciculata Fascicled tarplant
Heteromeles arbutifoUa Toyon
... Heterotheca grandiflora Telegraph weed
Hordeum sp. WUd barley
Isocoma menziesii Goldenbush
Juncus acutus ssp. leopoldii Southwestem spiny rush
Juncus bufonius Toad rush
MH Juncus sp. Rush
Lasthenia califomica Goldfields
Lathms sp. Chaparral pea
Wt* Lepidium sp. Peppergreiss
Lessingia filaginifolia var. virgata Sand-aster
Linanthus dianthifloms Ground pink
Lolium perenne Perennial ryegrass
Lotus scoparius Deerweed
nm Lonicera sp. Honeysuckle
Lupinus sp. Lupine
M Lythmm hyssopifolium Grass poly
B-2
APPENDIX B
OAKS/RIDGE PLANT SPECIES LIST (Cont.)
Ml
Scientific Name
Malacothamnus fasciculatus
Malosma laurina
Malva parviflora
Marah macrocarpus
Marmbium vulgare
Matricaria matricarioides
Medicago polymorpha
Mimulus aurantiacus ssp. australis
Mirabilis califomica
Muilla clevelandi
Nasella pulchra
Navarretia sp.
Nicotiana glauca
Opuntia littoralis
Oxalis sp.
Parietaria hespera
Pennesetum sp.
Pentagramma triangularis ssp, triangularis
Phacelia sp.
Pholistoma sp.
Picris echioides
Plagiobothrys sp.
Plantago erecta
Plantago ovata
Platanus racemosa
Polypogon monspeliensis
Pterostegia drymarioides
Quercus agrifolia
Quercus dumosa
Raphanus sativus
Rhus integrifolia
Ribes speciosum
Ricinus communis
Rumex crispus
Salix lasiolepis
Salsola tragus
Salvia apiana
Salvia columbariae var. columbariae
Salvia mellifera
Sambucus mexicana
Common Name
Bush maUow
Laurel sumac
Cheeseweed
ChiUcothe
Horehound
Common pineapple-weed
Bur-clover
YeUow bush monkey-flower
Wishbone plant
Cleveland's goldenstars
Purple needlegrass
Skunkweed
Tree tobacco
Coastal prickly pear
Wood-sorrel
PelUtory
Fountain grass
Goldenback fern
PhaceUa
Fiesta flower
Bristiy ox-tongue
Popcorn flower
Dwarf plantain
Plantain
Westem sycamore
Aimual beardgrass
Califomia thread-stem
Coast Uve oak
NuttaU's scmb oak
WUd radish
Lemonadeberry
Fuchsia-flower gooseberry
Castor bean
Curly dock
Anoyo wiUow
Russian thistie
White sage
Chia
Black sage
Mexican elderberry
B-3
APPENDDC B
OAKS/RIDGE PLANT SPECIES LIST (Cont.)
Scientific Name Common Name
Sanicula sp Snakeroot
m Schinus molle Pemvian pepper-ttee
Schismus barbatus Mediterranean schismus
'•I Selaginella cinerascens Ashy spike-moss
m Silene gallica WindmiU pink
Sisyrinchium bellum Blue-eyed grass
m Solanum sp. Nightshade
m Sonchus asper Prickly sow-fhistie
Spergula arvensis Stickwort
an Stachys sp Hedge-nettie
m Stephanomeria virgata Virgate wreath-plant m Tamarix sp. Tamarisk
m Toxicodendron diversilobum Poison oak
Trifolium sp Clover
m Typha latifolia Broad-leaved cattaU
Typha sp. CattaU
Verbena sp. Verbena
m Vulpia myuros var. myuros RattaU fescue
Xanthium stmmarium Cocklebur
Xylococcus bicolor Mission manzanita
MB Yucca aloifolia* Spanish bayonet
Yucca schidigera Mohave yucca
m
m
B-4
APPENDIX C
OAKS/RIDGE ANIMAL SPECIES LIST
Common Name
Invertebrates
Butterflies and Moths
Anise swaUowtaU
Behr's metahnark
Brown elfin
Buckeye
Cabbage white
Califomia dogface
Califomia ringlet
Checkered skipper
Common white
Echo blue
Fiery skipper
Funereal duskywing
Gray hairstteak
Marine blue
Mournful dusky-wing
Painted lady
Perplexing hairstteak
Sara orangetip
Southem blue
Virginia lady
West coast lady
Westem checkered skipper
Western taUed blue
Westem tiger swaUowtaU
Tiger moth
MisceUaneous
Bumblebee
Crayfish
Crane fly
Cricket
Darkling beetie
Damsel fly
Deer fly
Earwag
Field cricket
Scientific Name
Papilio zelicaon
Apodemia mormo virguiti
Incisalia augustinus
Junonia coeia
Artogeia rapae
Zerene eurydice
Coenonympha califomica
Pyrgus albescens
Pontia protodice
Celastrina ladon echo
Hylephila phyleus
Erynnis funeralis
Strymon melinus
Leptotes marina
Erynnis tristis
Vanessa cardui
Callophrys perplexa
Anthocharis sara
Glaucopsyche lygdamus
Vanessa virginiensis
Vanessa annabella
Pyrgus albens
Everes amyntula amyntula
Papilio mtulus
Unknown
Bombus sonoms
Order Artiiropoda
Order Diptera
Eleoides sp.
Order Diptera
Order Diptera
Labidura sp.
Gryllus sp.
C-1
APPENDIX C
OAKS/RIDGE ANIMAL SPECIES LIST (Cont.)
Common Name
Grasshopper
Harvester ant
Hornet
Horsefly
Honeybee
Jemsalem cricket
Ladybird beetie
Osttacods
Scientific Name
Order Orthoptera
Pogonomyrmex sp.
Order Hymenoptera
Order Diptera
Order Hymenoptera
Stenopelmatus sp.
Hippodamia sp.
PUlbug Armadillidium sp.
m Sowbug Porcellio sp.
Tarantula hawk Pepsis sp.
m Trap-door spider Class Arachnida
•m Velvet ant DasymutiUa sp.
'm Vertebrates
Amphibians
Ml Pacific tteefrog Hyla regilla
Reptiles
AlUgator lizard Gerrhonotus multicarinatus
•™ Califomia kingsnake Lampropeltus getula
Gopher snake Pituophis catenifer
MM Granite spiny lizard Scelopoms orcuttii
Pacific rattiesnake Crotalus viridis
San Diego horned lizard Phrynosoma coronatum blainvillii
mat Side-blotched lizard Uta stansburiana
Two-sttiped garter snake Thamnophis hammondii
Westem fence lizard Scelopoms occidentalis
Mi Birds
American crow Corvus brachyrhinchos
Americim kesttel Falco sparverius
American robin Turdus migratorius
Aima's hummingbird Calypte anna
m Ash-throated flycatcher Myiarchus cinerascens
Bam swaUow Himndo mstica
MR BeU's sage sparrow Amphispiza belli belli
C-2
APPENDIX C
OAKS/RIDGE ANIMAL SPECIES LIST (Cont.)
Common Name
Belted kingfisher
Bewick's wren
Black phoebe
Black-headed grosbeak
Blue-grey gnatcatcher
Blue grosbeak
Bufflehead
BuUock's oriole
Bushtit
Califomia quaU
Califomia thrasher
Califomia towhee
Canyon wren
Cassin's kingbird
Caspain tem
CUff swaUow
Coastal Califomia gnatcatcher
Common raven
Common poorwiU
Common yeUowthroat
Cooper's hawk
Costa's hummingbird
Eared grebe
European starling
Grasshopper sparrow
Greater roadrunner
Homed lark
House finch
House wren
ICUldeer
LazuU bimting
Lesser goldfinch
Loggerhead shrike
MaUard
Mourning dove
Northem fUcker
Northem harrier
Northern mockingbird
Northern rough-winged swaUow
Northern shoveler
NuttaU's woodpecker
Orange-crowned warbler
Scientific Name
Ceryle alcyon
Thryomanes bewickii
Sayornis nigricans
Pheucticus melanocephalus
Polioptila caemlea
Guiraca caemlea
Bucephala albeola
icterus bullockii
Psaltripams minimus
Callipepla califomica
Toxostoma redivivum
Pipilo crissalis
Catherpes mexicanus
Tyrannus vociferans
Stema caspia
Himndo pyrrhonota
Polioptila califomica califomica
Corvus corax
Phalaenoptilus nuttallii
Geothlypis trichas
Accipiter cooperii
Calypte costae
Podiceps nigricollis
Sturnus vulgaris
Ammodramus savanarmm
Geococcyx califomianus
Eremophila alpestris
Carpodacus mexicanus
Troglodytes aedon
Charadrius vocifems
Passerina amoena
Carduelus psaltria
Lanius ludovicianus
Anas platyrhynchos
Zenaida macroura
Colaptes auratus
Circus cyaneus
Mimus polyglottos
Stelgidopteryx serripennis
Anas clypeata
Picoides nuttallii
Vermivora celata
C-3
APPENDIX C
OAKS/RIDGE ANIMAL SPECIES LIST (Cont.)
m
Common Name
Pacific-slope flycatcher
Phainopepla
Pied-bUled grebe
Red-shouldered hawk
Red-taUed hawk
Red-winged blackbird
Rock dove
Ruddy duck
Savannah sparrow
Say's phoebe
Scmb jay
Song sparrow
Southern CaUfomia mfous-crowned
sparrow
Spotted towhee
Tree swaUow
Turkey vulture
Vaux's swift
Violet-green swaUow
Warbling vireo
Westem kingbird
Westem meadowlark
White-crowned sparrow
White-taUed kite
White-throated swift
Wilson's warbler
Wrentit
YeUow-breasted chat
YeUow-mmped warbler
Mammals
Bobcat
Botta's pocket gopher
CaUfornia ground squirrel
Coyote
Deer mouse
Desert cottontaU
Domestic dog
Mule deer
Opossum
San Diego black-tailed jackrabbit
Woodrat
Sdentific Name
Empinonax difficilis
Phainopepla nitens
Podilymbus podiceps
Buteo lineatus
Buteo jamaicensis
Agelaius phoeniceus
Columba livia
Oxyura jamaicensis
Passerculus sandwichensis
Sayornis saya
Aphelocoma coemlescens
Melospiza melodia
Aimophila mficeps canescens
Pipilo maculatus
Tachycineta bicolor
Cathartes aura
Chaetura vauxi
Tachycineta thalassina
Vireo gilvus
Tyrannis verticalis
Sturnella neglecta
Zonotrichia leucophrys
Elanus leucums
Aeronautes saxatillis
Wilsonia pusilla
Chamaea fasciata
Icteria virens
Dendroica coronata
Lynx mfus
Thomomys bottae
Spermophilus beecheyi
Canis latrans
Peromyscus maniculatus
Sylvilagus audubonii
Canis familiaris
Odocoileus hemionus
Didelphis virginiana
Lepus califomicus bennetii
Neotoma sp.
C-4
Wl
APPENDIX D
SENSITIVITY CODES
FEDERAL SPECIES DESIGNATIONS (USFWS 1990,1991)
Category
FE Federal endangered species
• FT Federal threatened species
PE Species already proposed to be listed as endangered.
^ PT Species already proposed to be listed as threatened.
Cl &iough data on fQe to support federal listing,
RS Threat and/ or distribution data insufficient to support federal listing.
« Plants onlv
• RS* Threat and/or distribution data insufficient to support federal listing, but the plant is presumed extinct.
Previously considered for listing, but no longer under considerafion because (Skinner & Pavlik 1994):
Ca Extinct,
Cb Taxonomically invalid.
mi Cc Too widespread and/or not threatened.
• STATE SPECIES DESIGNATIONS (CDFG 1991b)
>« SE State listed as endangered (listed as "CE" in Skinner & Pavlik 1994),
ST State listed as threatened (listed as "CT" in Skirmer & Pavlik 1994).
SCE State candidate for listing as endangered (listed as "CC" in Skinner & Pavlik 1994).
SCT State candidate for Hsting as threatened (listed as "CC" in Skinner & Pavlik 1994).
m CSC CDFG "species of spedal concem,"
• Plants only
CR State-listed, rare.
CEQA CEQA consideration mandatory.
• CEQA? CEQA consideration recommended,
— CALIFORNIA NATIVE PLANT SOCIETY DESIGNATIONS (Skinner & Pavlik 1994)
mm The CNPS Ust
mm Listl Plants of highest priority.
List lA Plants presumed extinct in Califomia.
M List IB Plants rare, threatened or endangered in Califomia and elsewhere.
List 2 Plants rare, threatened or endangered in Califomia, but common elsewhere.
•m List 3 Plants about which we need more ii\formation.
List 4 Plants of limited distribution (A watch list).
m
The R-E-D Code
mt R (Rarity) 1 Rare, but found in sufficient nimibers and distributed widely enough that the potential for extinction or
extirpation is low at this time.
Mi 2 Occurrence confined to several populations or to one extended population.
3 Occurrence liinited to one or a few highly restricted populations, or present in such numbers that it is
m seldom reported.
*• E (Endangerment) 1 Not endangered.
2 Endangered in a portion of its range,
••i 3 Endangered throughout its range.
D (Distribufion) 1 More or less widespread outside Califomia.
2 Rare outside Califomia.
MM 3 Endemic to Califomia.
D-1