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HomeMy WebLinkAboutHDP 94-04; Jefferson Street Lot 17 & 18; Hillside Development Permit (HDP)BIOLOGICAL RESOURCES OF LOTS 17 AND 18 CITY OF CARLSBAD, CALIFORNIA Prepared for: Mr. Daniel Muhe 4041 Aquila Street, #1 Carlsbad, Califomia 92008 Prepared by: Tierra Environmental Services 9903-E Businesspark Avenue San Diego, Califomia 92131 Chris Nordby Principal Biologist SEP 0 8 J^iy ^^^^ GlTfOFCi^."^ 7^7 INTRODUCTION Project Location and Description. This report addresses the biological resources of two small parcels of land, Jefferson Street Lot 17 and Jefferson Street Lot 18, located at in the City of Carlsbad (Figure 1). The lots are located on the west side of Jefferson Street, adjacent to Buena Vista Lagoon, They are bounded to the north and south by detached residential housing. Each lot is approximately 0.2 acre in size, including former easements for the widening of Jefferson Street, now abandoned (Figure 2). A single family residential development is planned for the site. Plans have been submitted to the City of Carlsbad who determined that a biological survey was necessary before the application could be considered complete. This report has been prepared in response to the City of Carlsbad's requirements. Physical Characteristics. Lots 17 and 18 are contiguous and are referred to throughout this report as the property site or subject parcel. The terrain of the property consists of a series of terraces and bluffs. The uppermost terrace is a relatively flat area adjacent to Jefferson Street. This terrace is roughly 35 m long and 20 m wide. The area closest to jefferson Street has been used for automobile parking and is mostly barren of vegetation. This terrace ends at a steep bluff that drops approximately 30 feet to the second terrace. The second terrace is approximately 35 m long and 10 m wide. The second terrace ends at another abmpt bluff that drops approximately 30-40 feet to the edge of Buena Vista Lagoon. This bluff and the fmal terrace adjacent the lagoon are not part of the subject property but are included here for descriptive purposes. Lots 17 and 18 terminate on the second terrace. FIELD SURVEY METHODS AND LIMITATIONS The subject parcels were surveyed for biological resources on July 9, 1994. The survey was conducted from 1100 hours to 1200 hours under partly cloudy skies with and average temperature of approximately 70 degrees F. The survey consisted of onsite analysis of vegetation communities, photographs of site, and a focused search for any sensitive plant or animal species. Because of the limited nature of the survey, the focus was on vegetation rather than wildlife. However, due to the disturbed condition of the site and the close proximity of residential units and associated pets, wildlife use of the site is expected to be minimal. RESULTS Vegetation. No sensitive plant species were observed during the field survey. In general, the site is dominated by non-native species; primarily Hottentot fig {Carbobrotus edulis), wild oat (Avena barbata), and brome grasses (Bromus spp.). Remnant coastal sage scrab habitat is also present including Califomia sagebrash (Artemisia californica), flat-top buckwheat {Eriogonum fasciculatum), and bladderpod (Isomeris arborea). As each terrace and bluff supports slightly different assemblage or dominant species, the vegetation is described by those physiographic features. The upper terrace is barren of vegetation for approximately 60% of its area as a result of automobile paridng. The remaining vegetation is dominated by Hottentot fig and non-native grasses including, wild oat and bromes (Figure 3). Additional species include scattered telegraph weed (Heterotheca grandiflora), sacred datura (Datura meteloides), and mustard (Brassica sp.). One lemonade berry {Rhus integrifolia) shrab with intermixed wild cucumber (Marah macrocarpus) occurs at the extreme westem edge of the terrace. The bluff consists of both bare sandstone and native and non-native vegetation. The dominant vegetation is, again, Hottentot fig and non-native grasses. In addition, the bluff supports scattered remnant coastal sage scrab elements including 4-6 individual lemonade berry shrabs, 2 individual Califomia sagebrash shrabs, 4 individual bladderpod plants, and a patch of flat-top buckwheat less than 5 m^ intermixed with Hottentot fig (Figure 4). The lower terrace supports primarily Hottentot fig and non-native grasses with a strip of Califomia sagebrash consisting of approximately 15 individuals and covering an area of approximately 17 m long and 3 m wide (Figure 5). Additional species include gum {Eucalyptus spp.) and scattered coastal isocoma (Haplopappus venetus). Wildlife. No sensitive wildlife species were observed on the property. The few wUdlife species that were observed during the survey are those that are typically found in association with human residences. These included house finch {Carpodacus mexicanus), lesser goldfinch {Carduelis psaltria), scrab jay {Aphelocoma coerulescens), and Anna's hummingbird {Calypte anrm). Because of the fragmented condition of adjacent natural communities, it is doubtful that any sensitive reptiles inhabit the site including orange-throated whiptail (Cnemidophorous hyperyhtrus) and/or San Diego coast homed lizard {Phymosoma coronatum blainvillei). HABITAT EVALUATION The study site supports one native plant community; Diegan coastal sage scrab. However; this community is highly disturbed and exists only as scattered remnant individuals or small stands with non-native vegetation dominant. The coastal sage scrab vegetation exists in isolated patches and the site is bounded by developed property on three sides. As a result, the important wildlife values often associated with this habitat type, especially regarding habitat for the threatened coastal Califomia gnatcatcher (Piloptila califonica californica), are greatly diminished. The coastal sage scrab habitat on site does not constitute habitat for the gnatcatcher. The impacts associated with the proposed project are not considered significant on a local or regional scale. The only area of biological sensitivity is Buena Vista Lagoon which wiU not be impacted by the proposed project, y 7^ 1000 2000 FIGURE 1 Vicinity Map TIERRA ENVIRONMENTAL SERVICES FIGURE 2 Assessor's Parcel Map of Lots 17 and 18 TIERRA ENVIRONMENTAL SERVICES FIGURE 3 View of upper terrace looking west FIGURE 4 View of bluff looking east TIERRA ENVIRONMENTAL SERVICES