HomeMy WebLinkAboutCT 99-13; Steiner Property; Tentative Map (CT) (24)BIOLOGICAL RESOURCES REPORT
AND IMPACT ANALYSIS
EOR THE STEINER PROPERTY
CITY Or CARLSBAD
SAN DIEGO COUNTY, CALIFORNIA
Prepared for:
WESTERN PACIEIC HOUSING
2385 Camino Vida Roble, Suite 107
Carlsbad, CA 92009
Contact: Scot Sandstrom
(760) 929-1600
Prepared by:
DUDER
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Professional Teams for Complex Projects
605 Third Street
Encinitas, California 92024
Contact: Anita M. Hayworth, Ph.D.
(760) 942-5147
June 1999
Biological Resources Report at Impact Analysis
Steiner Property/ Carlsbad, County of San Diego, California
TABLE Of CONTENTS
Section Page No.
SUMMARY OF FINDINGS iii
1.0 INTRODUCTION 1
2.0 METHODS AND SURVEY LIMITATIONS 1
2.1 Literature Review 1
2.2 Field Reconnaissance 1
2.2.1 Resource Mapping 2
2.2.2 Flora 2
2.2.3 Fauna 2
2.2.4 Sensitive Biological Resources ". 2
3.0 PHYSICAL CHARACTERISTICS 3
3.1 Site Description 3
4.0 RESULTS OF SURVEY 6
4.1 Botany - Plant Communities And Floral Diversity 6
4.1.1 Annual (Non-native] Grassland 6
4.1.2 Disturbed/Developed Habitat 6
4.1.3 Floral Diversity 8
4.2 Zoology - Wildlife Diversity 8
4.2.1 Birds 8
4.2.2 Reptiles and Amphibians 8
4.2.3 Mammals 8
4.3 Sensitive Biological Resources 8
4.3.1 Sensitive Plant Species 9
4.3.2 Sensitive Wildlife Species 9
4.3.3 Sensitive Habitats 10
4.3.4 Wildlife Corridors and Habitat Linkages 10
4.4 Regional Resource Planning Context 11
5.0 ANTICIPATED PROJECT IMPACTS 11
5.1 Explanation of Determination of Significance 13
5.2 Impacts to Plant Communities 13
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TABLE Or CONTENTS (Continued)
Section Page No.
5.3 Impacts to Sensitive Plants 14
5.4 Impacts to Sensitive Animals 14
6.0 RECOMMENDED MITIGATION MEASURES 14
6.1 Subregional Planning Context 14
7.0 ACKNOWLEDGMENTS 15
8.0 LITERATURE CITED 15
LIST OE EIGLRES
Figure 1 Regional Map 4
Figure 2 Vicinity Map 5
Figure 3 Biological Resources Map 7
Figure 4 Biological Resources Map with Limits of Grading 12
LIST OE TABLES
Table 1 Acreages by Habitat Type - Steiner Property 6
Table 2 Impact and Open Space Acreage for the Steiner Property 19
LIST OE APPENDICES
A. Vascular Plant Species Observed on the Project Site
B. Wildlife Species Observed or Detected on the Project Site
C. Species Sensitivity Categories
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SUMMARY OF FINDINGS
The Steiner property is an approximately 2.9-acre parcel situated within Zone 21 of the City of
Carlsbad in the western portion of San Diego County, California. The property is located west of
El Camino Real, south of Camino Vida Roble, east of the Aviara development and north of Aviara
Parkway. The property is surrounded by agriculture, open space/native habitat and some areas of
residential development. Topographically, most of the site is relatively flat and has been in
agricultural use and contains one residence. Thus the habitats onsite are composed of disturbed and
non-native vegetation types. The eastern portion of the property, a 0.8-acre area, is slated for
placement of Poinsettia Lane, a City of Carlsbad circulation element roadway, and is thus considered
"not a part." The elevations onsite vary from about 250 to 290 feet above mean sea level.
No species of plants listed as rare, threatened, endangered, or sensitive by the resource agencies are
located onsite. No animal species listed as rare, threatened, or endangered by the USFWS or CDFG
were observed onsite.
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1.0 INTRODUCTION
The Steiner property is an approximately 2.9-acre parcel situated within Zone 21 of the City of
Carlsbad in the western portion of San Diego County, California. The property is located west of
El Camino Real, south of Camino Vida Roble, east of the Aviara development and north of Aviara
Parkway. The eastern portion of the property, a 0.8-acre area, is slated for placement of Poinsettia
Lane, a City of Carlsbad circulation element roadway, and is thus considered "not a part". The
property is surrounded by agriculture, open space/native habitat and some areas of residential
development. Biological surveys of the property were conducted in May 1999, to assess the existing
conditions of the biological resources. The surveys augmented the existing data base accumulated
through previous survey work (e.g., SANDAG 1994). The purposes of this report are to describe the
biological character of the site in terms of vegetation, flora, wildlife, and wildlife habitats; and
analyze the biological significance of the site in view of federal, state, and local laws and policies.
2.0 METHODS AND SURVEY LIMITATIONS
Data regarding biological resources present on the project site were obtained through a review of
pertinent literature and through field reconnaissance; both are described in detail below.
2.1 Literature Review
Sensitive biological resources present or potentially present onsite were identified through a literature
search using the following sources: U.S. Fish and Wildlife Service (1989,1990,1991,1993), California
Department of Fish and Game (1980,1986,1987), California Native Plant Society's Inventory of Rare
and Endangered Vascular Plants (Skinner and Pavlik 1994), Murphy (1990), and the vegetation and
sensitive species mapping performed for the North County Wildlife Forum's Multiple Habitat
Conservation Program (SANDAG 1994). General information regarding wildlife species present in the
region was obtained from Unitt (1984) for birds, Bond (1977) for mammals, and Stebbins (1985) for
reptiles and amphibians.
2.2 Field Reconnaissance
Biological surveys of the property were conducted by Dudek & Associates, Inc., biologists Anita M.
Hayworth, Ph.D. and Darren Smith, during May 1999. All surveys were conducted by foot; the
entire property was surveyed and inventoried for biotic components.
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2.2.1 Resource Mapping
Plant communities were mapped in the field directly onto a clear acetate on a 200-scale (1"=200')
aerial photograph of the area from Aerial Fotobank, flown 18 January 1997. Vegetation boundaries
and locations of sensitive species were transferred onto a 200-scale topographic map of the site from
Hunsaker and Associates. These boundaries and locations were digitized by DUDEK GIS technician
Martie demons using the ArcCadd system at DUDEK.
Plant community classifications used in this report follow Holland (1986), with modifications to
accommodate the lack of conformity of the observed communities to those of Holland. Locations
of rare or sensitive plant and wildlife species also were mapped, and the numbers present were
estimated.
2.2.2 Flora
All plant species encountered during the field surveys were identified and recorded. Those species
that could not be identified immediately were brought into the laboratory for further investigation.
Latin and common names of plants follow the Jepson Manual (Hickman 1993). Where not listed in
Hickman (1993), common names are taken from Beauchamp (1986) or Abrams (1923). A list of plant
species observed on the property is presented in APPENDIX A.
2.2.3 Fauna
Wildlife species detected during field surveys by sight, calls, tracks, scat, or other sign were recorded.
Binoculars (10 x 50 power) were used to aid in the identification of observed animals. Records from
previous biological studies and accounts from local residents also were consulted. In addition to
species actually observed, expected wildlife use of the site was determined by known habitat
preferences of local species and knowledge of their relative distributions in the area. A list of wildlife
species observed or detected onsite is presented in APPENDIX B.
Latin and common names of animals follow Stebbins (1985) for reptiles and amphibians, American
Ornithologists' Union (1983, 1989) for birds, Jones et al. (1992) for mammals.
2.2.4 Sensitive Biological Resources
Sensitive biological resources are those defined as follows: (1) species that have been given special
recognition by federal, state, or local conservation agencies and organizations due to limited,
declining, or threatened population sizes; (2) species and habitat types recognized by local and
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regional resource agencies as sensitive; (3) habitat areas or plant communities that are unique, are of
relatively limited distribution, or are of particular value to wildlife; and 4) wildlife corridors and
habitat linkages.
Assessment of the property to support the quino checkerspot butterfly (Euphydryas editha quino}, a
federally listed endangered species, were conducted currently with the biological mapping and
inventory of the property. Biological mapping and species inventory were conducted by a biologist
who possesses a valid section 10(a)(l)(A) recovery permit for the California gnatcatcher (PoHoytila
californica) and quino checkerspot butterfly.
3.0 PHYSICAL CHARACTERISTICS
3.1 Site Description
The Steiner property is a 2.9-acre property situated within Zone 21 of the City of Carlsbad in western
San Diego County, California (Figure -/). It is bordered to the south and west by the Lohf property,
and to the north and east by undeveloped areas, most of which contain native vegetation. The
property lies approximately 3 miles east of Interstate Highway 5 and about 1.3 miles north of La
Costa Avenue, and 0.2 mile west of El Camino Real. It is in the northeastern corner of the USGS 7.5
minute Encinitas quadrangle, Section 26, T.12S., R.4W. (Figure 2).
Topographically, most of the site is relatively flat, has been in agricultural, and contains a residence.
The elevations onsite vary from about 250 to 290 feet above mean sea level. A 0.8-acre area in the
eastern portion of the property is slated for development with Poinsettia Lane, a major circulation
element roadway. Thus the remaining area available for development is 2.1 acres.
According to Bowman (1973), the following soils are present onsite: Huerhuero loam (HrD2), and
Loamy alluvial land-Huerhuero complex (LvF3).
Soils of the Huerhuero series consist of moderately well drained loams that have a clay subsoil. These
soils developed in sandy marine sediments. Huerhuero loam (HrD2) occurs on 9 to 15 percent slopes.
Because of moderate sheet erosion, the soil has an effective rooting depth of 20 to 40 inches. Loamy
alluvial land consists of somewhat poorly drained, very deep, very dark brown to black silt loams and
sandy loams. Areas of this land were formerly wet meadows that were subsequently drained by head
cutting of gullies. The gullies eventually formed drainage ditches and thus lowered the water table.
The loamy alluvial land-Huerhuero complex occurs on 9 to 50 percent slopes and occurs on old
coastal ridges. The landscape is one of strongly sloping to steep, severely eroded soils and alluvial fill
along drainage ways.
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Steiner Property - Biological Resources Report & impact Analysis
Regional Map
BASE MAP SOURCE: USGS 7.5 Minute Series, Encinitas Quadrangle r -zooo'
Steiner Property • Biological Resources Report & Impact Analysis
Vicinity Map
Biological Resources Report sc Impact Analysis
Steiner Property/ Carlsbad/ County of San Diego/ California
4.0 RESULTS OF SURVEY
4.1 Botany - Plant Communities And Floral Diversity
Based on species composition and general physiognomy, two plant communities or habitat types
were identified onsite: non-native annual grassland (0.3 acre) and disturbed/developed habitat (1.8
acres). These habitat types are described below, their acreages are presented in Table 1, and their
spatial distribution is presented in Figure 3.
TABLE 1
ACREAGES BY HABITAT TYPE - STEINER PROPERTY
Non-native Annual Grassland 0.3 acres
Disturbed/developed Habitat 1.8 acres
TOTAL 2.1 acres
4.1.1 Annual (Non-nativel Grassland
Where the native habitat has been disturbed frequently or intensively by grazing, fire, agriculture,
or other activities, the native community usually is incapable of recovering. These areas are
characterized by weedy, introduced annuals, primarily grasses, including especially slender wild oat
(Avena barbata), bromes (Bromus diandms, B. madritensis, B. hordeaceus), black mustard (Brassica nigra)
and red-stemmed filaree (Erodium cicutarium). Within the project site, most of the present-day annual
grassland evidently is the result of past land uses, including mechanical disturbances. The annual
grassland onsite consists of large areas with high cover of non-native grasses including slender-oat,
English ryegrass (Lolium muhiflorum), ripgut grass, soft chess, rattail fescue (Vulpia myuros). This
vegetation type covers approximately 0.3 acre.
4.1.2 Disturbed/Developed Habitat
Disturbed habitat refers to areas that lack vegetation entirely or are dominated by landscape,
ornamental, or agriculture-related plant species. These areas generally are the result of severe or
repeated mechanical perturbation. Developed land refers to areas that include homes, yards,
ornamental landscaping, corrals, and other highly modified lands that support structures, land use,
or vegetation associated with dwellings. Within the property, disturbed/developed habitat includes
dirt roads, trails, plowed land, open land containing remnants of past agricultural useage, residential
Figure 3 Biological Resources Map
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fitttififiiififififiiiiitifiiiiiiitifi
VEGETATION TYPES:
I AGL| Annual Non-native Grassland
DH I Disturbed Habitat
BASE TOPO/GRADING SOURCE: Hunsaker & Associates, May 1999
100
Scale in Feet
Steiner Property • Biological Resources Report & impact Analysis
Biological Resources Map
FIGURE
Biological Resources Report SC Impact Analysis
Steiner Property/ Carlsbad/ County of San Diego/ California
dwellings and outbuildings, and ornamental landscape. A total of 1.8 acres of disturbed/developed
habitat is present onsite.
4.1.3 Floral Diversity
A total of 67 species of vascular plants was recorded from the site (APPENDIX A).
4.2 Zoology - Wildlife Diversity
4.2.1 Birds
Twelve (12) species of birds were observed during the recent survey work (see APPENDIX B). The
avifauna is comprised of a moderately diverse assemblage of species associated with coastal sage scrub
and chaparral. The most commonly observed species include mourning dove (Zenaida. macroura),
Anna's hummingbird (Calypte anna), common raven (Corvus corax), and European starling (Sturnus
vulgaris).
4.2.2 Reptiles and Amphibians
No species of reptiles were observed onsite. Reptiles common in the area and likely to occur onsite
include side-blotched lizard (Uta stansburiana), Great Basin fence lizard (Sceloporus occidentalis),
southern alligator lizard (Gerrhonotus multicarinatus webHi), and gopher snake (Pituophis melanoleucus).
No amphibians were observed onsite.
4.2.3 Mammals
Three species of mammals were recorded from the site, including cottontail rabbit (Sylvilagus sp.),
California ground squirrel (Spermophilus beecheyt), and coyote (Canis latrans). Other mammal species
likely to be present include striped skunk (Mephitis mephitis), Virginia opossum (Didelphis virginica),
and raccoon (Procyon lotor).
4.3 Sensitive Biological Resources
The following resources are discussed in this section: (1) plant and animal species present in the
project vicinity that are given special recognition by federal, state, or local conservation agencies and
organizations owing to declining, limited, or threatened populations, that are the results, in most
cases, of habitat reduction; and (2) habitat areas that are unique, are of relatively limited distribution,
or are of particular value to wildlife. Sources used for determination of sensitive biological resources
are as follows: wildlife - U.S. Fish and Wildlife Service (USFWS 1989,1991), California Department
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Biological Resources Report & Impact Analysis
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of Fish and Game (CDFG 1980,1986), Remsen (1978), Everett (1979), McGurty (1980), and Murphy
(1990); plants -- USFWS (1990,1993), CDFG (1987), and Skinner and Pavlik (1994); and habitats -
Holland (1986).
4.3.1 Sensitive Plant Species
No sensitive plant species were observed onsite and none are likely to occur.
4.3.2 Sensitive Wildlife Species
No sensitive wildlife species were observed onsite and none are likely to occur. One other species
currently under great concern by the resources agencies is the quino checkerspot butterfly. Currently
almost every property undergoing consideration for development requires addressing the likelihood
of presence of the butterfly. This species is discussed below. The listing authorities and explanation
of listing categories are presented in APPENDIX C.
Euyhydryas editha quino - quino checkerspot butterfly
USFWS: Endangered
CDFG: None
The quino checkerspot is the southernmost subspecies of the wide ranging, polytypic species known
as Edith's checkerspot (£. editha). It formerly occurred throughout southern California from Orange
(Orsak 1977) and western Riverside counties south to Baja California, Mexico (Brown, Real &
Faulkner 1992). By 1977, Orsak (1977) reported that it was locally extinct in Orange County; and
by 1990 it appeared to be extinct in coastal San Diego County. Many of the former localities of this
species still support high quality, undisturbed vegetation; hence, the reasons for its precipitous decline
are unknown. It is likely that the unique metapopulation dynamics of this species combined with
habitat fragmentation as the result of development and the drought years of the mid-1980s
effectively eliminated it from the western portion of San Diego County.
The habitat assessment of the property determines whether the project site contains habitat
components and features appropriate to support the quino checkerspot. The butterfly is associated
with low elevation meadow habitats or clearings characterized by clay soils or cryptogamic plants
and may occur in sparsely vegetated chaparral, coastal sage scrub, or oak woodlands. Other habitat
features include the presence of host plants [dwarf plantain (Plantago erecta) or owls-clover (Castillefa
exserta}], nectar plants [popcorn flower (Cryptantha sp.), goldfields (Lasthenia sp.), fiddleneck
(Amsinckia intermedia'), chia (Salvia columbariae), or other spring annuals] located in sparsely vegetated
areas, and hilltops and ridgelines.
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The Steiner property is characterized by disturbed habitat in the form of agriculture usage and
existing residence. In addition, there are no hilltops or ridges present on the site; the property is
relatively level. No clay soils are present; the soils are dominated by sandstone based formations.
No food plant or nectar source is available. Based on the lack of any of the habitat features or
components required to support the quino checkerspot butterfly, no survey during the flight period
would be required.
4.3.3 Sensitive Habitats
Sensitive habitats are those that are considered rare within the region, support sensitive plant and/or
wildlife species, or function as corridors for wildlife movement. No habitat types that are considered
sensitive occur onsite.
4.3.4 Wildlife Corridors and Habitat Linkages
Wildlife corridors are linear features that connect large patches of natural open space and provide
avenues for the immigration and emigration of animals. Wildlife corridors contribute to population
viability in several ways: (1) they assure the continual exchange of genes between populations which
helps maintain genetic diversity; (2) they provide access to adjacent habitat areas representing
additional territory for foraging and mating; (3) they allow for a greater carrying capacity; and (4)
they provide routes for colonization of habitat lands following local populations extinctions or
habitat recovery from ecological catastrophes (e.g., fires).
Habitat linkages are patches of native habitat that function to join two larger patches of habitat.
They serve as connections between habitat patches and help reduce the adverse affects of habitat
fragmentation. Although individual animals may not move through a habitat linkage, the linkage
does represent a potential route for gene flow and long-term dispersal. Habitat linkages may serve
as both habitat and avenues of gene flow for small animals such as reptiles and amphibians. Habitat
linkages may be represented by continuous patches of habitat or by nearby habitat "islands" that
function as "stepping stones" for dispersal.
No habitat linkages/wildlife corridors have been identified for the site, however, due to the location
of the property within areas of extensive open space, wildlife species probably use the property in
general movements through the area. Due to the small size of the property and overall lack of
vegetative cover, the wildlife usage is probably relatively small.
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4.4 Regional Resource Planning Context
In San Diego County, three major, coordinated conservation planning efforts currently are in progress
with the long-term goal of identifying a system of preserves that will protect native habitat lands and
their associated biota. The three efforts are (1) the City of San Diego's Multiple Species Conservation
Program (MSCP), administered by the Metropolitan Wastewater Department, focused on biological
resource planning for the southwestern one-fourth of the County; (2) the San Diego Association of
Government's (SANDAC) Multiple Habitat Conservation Program (MHCP), funded by a consortium
of jurisdictions in northern San Diego County known as the North County Wildlife Forum, focusing
on the northwestern one-fourth of the County; and (3) the County of San Diego Open Space Plan,
which focuses on the portion of the County east of the MSCP and MHCP study areas. The ultimate
goal of these plans is the establishment of biological reserve areas in conformance with the State of
California's Natural Community Conservation Program (NCCP). These programs are moving
forward under the regulatory influence of the 4(d) Rule pursuant to the Endangered Species Act,
which allows for the interim loss of 5% of existing coastal sage scrub until the preserves (NCCPs) are
formalized.
In this context, the Steiner property lies within the City of Carlsbad Focus Planning Area of the
MHCP and is within Preserve Planning Area 4 of the Carlsbad Habitat Management Plan (HMP).
The property is located within a Standards Area that has been designated to receive some level of
conservation. Typically, the standards areas identify that the development should be restricted to
25% of the property with development focused on the disturbed/agricultural useage areas. Due to
the extremely small size of the Steiner property, this standard is inappropriate for use. The entire
site, excepting that identified for the Poinsettia Lane alignment, is formerly agriculture useage or is
currently residential use.
5.0 ANTICIPATED PROJECT IMPACTS
This section addresses potential impacts to biological resources that would result from
implementation of the proposed project, and provides analyses of significance for each potential
impact. Impacts were quantified by overlaying the limits of project grading on the biological
resources map of the site (Figure 4)- For purposes of this assessment, all biological resources within
the limits of grading for development are considered 100 percent lost.
Impacts to biological resources can be direct - resulting from the permanent removal of habitat, or
indirect - resulting from changes in land use adjacent to natural habitat (e.g., increased light, noise,
and urban runoff, interruption of wildlife movement, etc.). Both of these types of impacts and their
levels of significance are discussed in this section.
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i i i i i i i i i r i i i i i \ i s i i f i r i i i i i i i i i
Proposed Limits of Grading
BASE TOPO/GRADING SOURCE: Hunsaker & Associates, May 1999
VEGETATION TYPES:
| AGL | Annual Non-native Grassland
"DH"l Disturbed Habitat
Scale in Feet
Steiner Property - Biological Resources Report & Impact Analysis
Biological Resources Map With Proposed Grading Limits
Biological Resources Report 6C Impact Analysis
Steiner Property/ Carlsbad/ County of San Diego/ California
5.1 Explanation of Determination of Significance
For this section, the following criteria are used to determine the significance of an impact:
• Substantial effect on a rare or endangered species plant or animal or habitat of that
species is considered a significant impact.
• Substantial interference with the movement of any resident or migratory fish or
wildlife species is considered a significant impact.
• Substantial reduction of habitat for fish, wildlife, or plants is considered a significant
impact.
5.2 Impacts to Plant Communities
Direct Impacts
Implementation of the proposed project would result in the direct loss of 1.9 acres (see Table 2),
including impacts to the following habitat types:
« 0.3 acre of non-native grassland — less than significant
• 1.6 acres of disturbed/developed land - less than significant
TABLE 2
IMPACT AND OPEN SPACE ACREAGE FOR THE STEINER PROPERTY
Direct Impact Open Space
Non-native Grassland 0.3 acre 0.0 acre
Disturbed/developed Habitat 1.6 acres 0.2 acres
TOTAL 1.9 acres 0.2 acre
In general, the proposed plan results in impacts to the bulk of the property. Although the location
of non-native grassland on a property frequently leads to usage of a site by raptors for foraging, due
to the extremely small size of the habitat and adjacency to residences, the patch would not function
as raptor foraging habitat. Impacts to the vegetation communities onsite are considered less than
significant.
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Steiner Property, Carlsbad/ County of San Diego/ California
Indirect Impacts
Indirect impacts from the proposed development include the following:
• Reduction in carrying capacity of adjacent native habitats as a result of noise and
lighting associated with development.
• Inadvertent potential increase of feral rat, cat, and other small predator populations
in native habitats adjacent to proposed development areas.
These impacts probably are most severe within the first 50 feet of development. Because the first 50
feet already is considered 100 percent impacted from the brush management zones, and indirect
impacts from these sources are minimal beyond 50 feet, these impacts are consider less than
significant.
5.3 Impacts to Sensitive Plants
No impacts to sensitive plant species would occur.
5.4 Impacts to Sensitive Animals
No impacts would occur to sensitive animal species.
6.0 RECOMMENDED MITIGATION MEASURES
Due to lack of significant impacts resulting from the development of the property, no mitigation
measures are required.
6.1 Subregional Planning Context
In a regional context, the biological resources present of the Steiner property are regionally .
The Steiner property is located within Preserve Planning Area 4 of the Carlsbad HMP andis
designated as a "Standards" area.
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Steiner Property/ Carlsbad/ County of San Diego/ California
7.0 ACKNOWLEDGMENTS
This report was prepared by DUDEK biologist Anita M. Hayworth, Ph.D. Graphics were provided
by Martie A. demons; Tonette S. Foster provided word processing assistance.
8.0 LITERATURE CITED
Abrams, L. 1923. Illustrated flora of the Pacific States. Stanford University Press, Stanford,
California.
American Ornithologists'Union. 1983. The Check-list of North American Birds, 6th edition. Allen
Press, Lawrence, Kansas.
American Ornithologists' Union. 1989. Thirty-seventh Supplement to the American Ornithologists'
Union Check-List of North American Birds. The Auk 106:532-538.
Atwood, J. L. 1990. Status review of the California gnatcatcher (Polioptila californica). Unpublished
technical report, Manomet Bird Observatory, Manomet, Massachusetts. 79 pp.
Beauchamp, R. M. 1986. A flora of San Diego County, California. Sweetwater Press, National City,
California. 241 pp.
Bond, S. I. 1977. An annotated list of the mammals of San Diego County, California. Trans. San
Diego Soc. Nat. Hist. 18: 229-248.
Bowman, R. H. 1973. Soil Survey, San Diego Area, California, Part 1. United States Department of
the Agriculture. 104 pp. + appendices.
Bury, B. 1971. Status report on California's threatened amphibians and reptiles. California
Department of Fish and Game, Inland Fisheries Administrative Report #72-2.
California Department of Fish and Game (CDFG). 1980. At the Crossroads: A Report on the Status
of California's Endangered and Rare Fish and Wildlife. State of California Resources Agency,
Sacramento. California.
California Department of Fish and Game (CDFG). 1986. Endangered, Rare, and Threatened Animals
of California. State of California Resources Agency, Sacramento, California.
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California Department of Fish and Game (CDFG). 1987. Designated Endangered or Rare Plants.
Summary list from Section 1904 Fish and Game Code (Native Plant Protection Act). State
of California Resources Agency, Sacramento, California.
Everett, W. T. 1979. Sensitive, threatened and declining bird species of San Diego County. San
Diego Audubon Society Sketches 29:2-3.
Grinnell, J. and A. Miller. 1944. The distribution of the birds of California. Pacific Coast Avifauna
27: 1-608.
Hickman, J. C. 1993. The Jepson manual: Higher plants of California. University of California
Press, Berkeley. 1400 pp.
Holland, R. F. 1986. Preliminary descriptions of the terrestrial natural communities of California.
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Biological Resources Report & Impact Analysis
Steiner Property/ Carlsbad/ County of San Diego/ California
Endangered Vascular Plants of California. Special Publication No. 1 (4th Edition), California
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APPENDICES
PUDER
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APPENDIX A
VASCULAR PLANTS OBSERVED WITHIN STEINER PROJECT AREA
Scientific name
1 Mesembryanthemum nodiflorum
2 Rhus integrifolia
3 Ambrosia psilostachya var. californica
4 Artemisia calif ornica
5 Baccharis pilularis
6 * Cotula australis
7 Eriophyllum confertiflorum var. confertiflorum
8 Gnaphalium stramineum
9 Hazardia squarrosa ssp. grindelioides
10 Hemizonia fasciculata
11 Heterotheca grandiflora
12 * Hypochaeris glabra
13 Isocoma menziesii ssp. veneta
14 * Silybum marianum
15 * Sonchus oleraceus
16 * Taraxacum officinale
17 Cryptantha sp.
18 * Raphanus sativus
19 * Silene gallica
20 Marah macrocarpus
21 Lotus scoparius
22 Quercus dumosa
23 Salvia mellifera
24 Chlorogalum pan/iflorum
25 * Eucalyptus sp.
26 Plantago erecta
27 * Limonium perezii
28 * Avenabarbata
29 * fl/wmw diandrus
30 * 5/0/mw madritensis ssp. rubens
31 * Cortaderia selloana
32 * Vulpiamyuros
33 Navarretia hamata
34 Eriogonum fasciculatum
common name
small-flowered ice plant
lemonadeberry
western ragweed
coastal sagebrush
coyote brush
Australian brass-buttons
cotton-batting plant
saw-toothed goldenbush
fascicled tarweed
telegraph weed
smooth car's-ear
coastal golden bush
milk thistle
common sow-thistle
common dandelion
wild radish
common catchfly
wild cucumber
deerweed
Nuttall's scrub oak
black sage
small-flowered amole
eucalyptus
dot-seed plantain
Perez rosemary
slender oat
ripgut grass
foxtail chess
pampas grass
rattail fescue
hooked navarretia
California buckwheat
FAMILY
AIZOACEAE - CARPET-WEED FAMILY
ANACARDIACEAE - SUMAC FAMILY
ASTERACEAE - SUNFLOWER FAMILY
ASTERACEAE - SUNFLOWER FAMILY
ASTERACEAE - SUNFLOWER FAMILY
ASTERACEAE - SUNFLOWER FAMILY
ASTERACEAE • SUNFLOWER FAMILY
ASTERACEAE - SUNFLOWER FAMILY
ASTERACEAE - SUNFLOWER FAMILY
ASTERACEAE - SUNFLOWER FAMILY
ASTERACEAE - SUNFLOWER FAMILY
ASTERACEAE - SUNFLOWER FAMILY
ASTERACEAE - SUNFLOWER FAMILY
ASTERACEAE - SUNFLOWER FAMILY
ASTERACEAE - SUNFLOWER FAMILY
ASTERACEAE - SUNFLOWER FAMILY
BORAGINACEAE - BORAGE FAMILY
BRASSICACEAE - MUSTARD FAMILY
CARYOPHYLLACEAE • PINK FAMILY
CUCURBITACEAE - GOURD FAMILY
FABACEAE - PEA FAMILY
FAGACEAE - BEECH FAMILY
LAMIACEAE - MINT FAMILY
LILIACEAE - LILY FAMILY
MYRTACEAE - MYRTLE FAMILY
PLANTAGINACEAE - PLANTAIN FAMILY
PLUMBAGINACEAE - LEADWORT FAMILY
POACEAE - GRASS FAMILY
POACEAE - GRASS FAMILY
POACEAE - GRASS FAMILY
POACEAE - GRASS FAMILY
POACEAE - GRASS FAMILY
POLEMONIACEAE • PHLOX FAMILY
POLYGONACEAE - BUCKWHEAT FAMILY
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APPENDIX A {Continued)
VASCULAR PLANTS OBSERVED WITHIN STEINER PROJECT AREA
Scientific name common name FAMILY
35 * Rumexcrispus curly dock POLYGONACEAE - BUCKWHEAT FAMILY
36 * Anagallis arvensis scarlet pimpernel PRIMULACEAE - PRIMROSE FAMILY
37 Adenostoma fasciculatum chamise ROSACEAE - ROSE FAMILY
38 Heteromeles arbutifolia toyon ROSACEAE - ROSE FAMILY
39 Mimulus aurantiacus bush monkeyflower SCROPHULARIACEAE - FIGWORT FAMILY
40 * Nicotiana glauca tree tobacco SOLANACEAE - NIGHTSHADE FAMILY
41 Solatiumparishii Parish's nightshade SOLANACEAE - NIGHTSHADE FAMILY
42 * Urtica urens dwarf nettle URTICACEEAE - NETTLE FAMILY
"denotes non-native species
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APPENDIX B
WILDLIFE SPECIES OBSERVED OR
DETECTED ON THE PROJECT SITE
TERRESTRIAL VERTEBRATES
BIRDS
ACCIPITRIDAE - HAWKS
Buteo jamaicensis - red-tailed hawk
COLUMBIDAE - PIGEONS & DOVES
Zenaida macroura - mourning dove
TROCHILIDAE - HUMMINGBIRDS
Calypte anna - Anna's hummingbird
TYRANNIDAE - TYRANT FLYCATCHERS
Tyrannus verticalis - western kingbird
CORVIDAE - JAYS & CROWS
Afhelocoma coemlescens - scrub jay
Corvus corax - common raven
MIMIDAE - THRASHERS
Mimus polyglottos - northern mockingbird
EMBERIZIDAE - WOOD WARBLERS, TANAGERS, BUNTINGS & BLACKBIRDS
Pipilo erythwfhthalmus - rufous-sided towhee
Pifilo crissalis - California towhee
Melosfiza melodia - song sparrow
FRINGILLIDAE - FINCHES
Carpodacus mexicanus - house finch
Carduelis psaltria - lesser goldfinch
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APPENDIX B (Continued)
MAMMALS
LEPORIDAE - HARES & RABBITS
Sylvilagus sp. - cottontail rabbit
SCIURIDAE - SQUIRRELS
Spermophilus heecheyi - California ground squirrel
CANIDAE - WOLVES & FOXES
Canis latrans - coyote
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APPENDIX C
SPECIES SENSITIVITY CATEGORIES
Federal (1993)
Endangered. Taxa threatened throughout all or a significant portion of their range.
Threatened. Taxa likely to become endangered in the foreseeable future.
Category!. Taxa for which the USF WS currently has on file substantial information on biological
vulnerability and threat(s) to support the appropriateness of proposing to list them
as endangered or threatened species.
Category^. Taxa for which information now in possession of the USFWS indicates that
proposing to list them as endangered or threatened is appropriate but for which
substantial data on biological vulnerability and threat(s) are not known or on file to
support the immediate preparation of rules.
Category^. Taxa that were once considered for listing as endangered or threatened, but are
currently not receiving such consideration. These taxa are included in one of the
following three subcategories.
Subcategory 3A: Taxa presumed to be extinct.
Subcategory 3B: Taxa whose names do not meet the Endangered Species Act's legal
definition of species.
Subcategory 3C: Taxa now considered to be more widespread that originally
thought.
Note: The taxa in Categories 1 and 2 are candidates for possible addition to the list of endangered
and threatened species. The USFWS encourages their consideration in environmental
planning.
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APPENDIX C (Continued)
State of California (1990)
Endangered. Taxa which are in serious danger of becoming extinct throughout all, or a significant
portion, of their range due to one or more causes including loss of habitat, change in
habitat, over exploitation, predation, competition, or disease (Section 2062 of the Fish
and Game Code).
Threatened. Taxa which, although not presently threatened with extinction, are likely to become
endangered species in the foreseeable future (Section 2067 of the Fish and Game Code).
Rare.
Candidate.
Taxa which, although not presently threatened with extinction, are present in such
small numbers throughout their range that they may become endangered if the
present environment worsens (Section 1901 of the Fish and Game Code).
Taxa which the Fish and Game Commission has formally noticed as being under
review by the Department in addition to the list of threatened and endangered species.
California Native Plant Society (1994)
Lists
1A:
IB:
2:
3:
4:
Presumed Extinct in California
Rare or Endangered in California and Elsewhere
Rare or Endangered in California, More Common Elsewhere
Need More Information
Plants of Limited Distribution
Note: Plants on CNPS list IB meet California Department of Fish and Game Criteria for Rare
or Endangered listing.
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APPENDIX C (Continued)
R-E-D code
R (Rarity)
1- Rare, but found in sufficient numbers and distributed widely enough that the potential for
extinction or extirpation is low at this time.
2- Occurrence confined to several populations or to one extended population.
3- Occurrence limited to one or a few highly restricted populations, or present in such small
numbers that it is seldom reported.
E (Endangerment)
1- Not endangered
2- Endangered in a portion of its range
3- Endangered throughout its range
D (Distribution)
1- More or less widespread outside of California
2- Rare outside California
3- Endemic to California
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