HomeMy WebLinkAboutCUP 01-22; ZONE 19 PARK; FOCUSED CALIFORNIA GNATCATCHER SURVEY RESULTS; 2003-01-06897
P&D Environmental ¾ A Division of P&D Consultants
RIO SAN DIEGO PIAZA JAN 113 isi 8954 RIO SAN DIEGO DRIVE
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January 6, 2003
Ms. Elaine Blackburn
CITY OF CARLSBAD
1635 Faraday Avenue
Carlsbad, CA 92008
SUBJECT: ZONE 19 COMMUNITY PARK
CityOf 619/291-1475
Clrlsball 619/291-1476 FAX
www.pdconsultants.com
Focused California Gnatcatcher Survey Results
Dear Elaine,
Protocol surveys were conducted by P&D Environmental biologists for the California
gnatcatcher (Polioptila californica) at the Zone 19 Community Park site in Carlsbad, California.
The surveys conformed to general protocol established for the gnatcatcher by the U.S. Fish and
Wildlife Service (USFWS), per the latest revision of July 1997. A total of three site visits were
conducted at the site, two by Doug Willick and one by Gilberto Ruiz, on the dates of December
18 and 26, 2002, and January 2, 2003. Mr. Willick and Mr. Ruiz are individually permitted by
USFWS to conduct presence/absence surveys for the California gnatcatcher (CAGN). Surveys
employed the use of taped gnatcatcher vocalizations, consistent with survey protocol. Weather
conditions during the site visits were considered favorable for the detection of this species.
As the project site itself has been recently under agricultural production, it is currently disturbed
and does not contain coastal sage scrub habitat considered suitable for the CAGN. The survey,
therefore, focused on native scrub vegetation in areas adjacent to the site. As documented in
greater detail in previous reports, the native vegetation adjacent to the site primarily consists of
maritime chaparral. In general, the southern and eastern limits of the project site are developed
and include non-native, landscaped vegetation.
No CAGNs were detected visually or aurally on the December 18 or January 2 site visit. One
CAGN, however, was identified on the December 26 visit, in chaparral vegetation bordering the
northern edge of the site. This bird was initially detected when its calls were heard shortly after
playing CAGN vocalizations from the recorder. Soon after the vocal identification was made, a
gnatcatcher was briefly seen at this location. The observation in itself was not considered
conclusive, due to the brevity of the observation and the bird's partial concealment in vegetation.
However, the identification was based on the vocalizations that were heard, which included the
"mew" call that is distinctive to this species. The bird did not apparently remain in the area for
any length of time, as no additional CAGN vocalizations or observations were made.
During the January 2 2003 , survey, a single blue-gray gnatcatcher (Polioptila caerulea) was
foraging in dense vegetation along the northern edge of the site, approximately 200 to 300 feet
~
PINZ 19/Park/CAGN-Survey-Ltr.doc ( 175508)
AN AECOM COMPANY
Ms. Elaine Blackburn
City of Carlsbad
January 6, 2003
Page 2
east of the December 26 CAGN location. This bird was well seen and carefully identified by its
diagnostic plumage details (e.g., clean white underparts and entirely white outer rectrices) and
vocalizations.
It is the opinion of the P&D biologists conducting this survey that the vegetation surrounding the
project site, including distances out at least 500 to 750 feet from the site, would not likely
support breeding pairs of the CAGN. The vegetation in the vicinity of the December 26 CAGN
identification consists of chaparral habitat dominated by chamise, as well as several coast live
oaks. Although coastal sage scrub (CSS) plant species are occasionally present in the chaparral
surrounding the project site, these are fairly rare and generally consist of black sage. California
sagebrush and buckwheat, CSS species most preferred by CAGN, is extremely scarce to absent
in this general area. Although the structure of the chaparral plant community surrounding the
project site is occasionally not quite as arborescent as other types of chaparral, it is still taller and
much denser than CSS associations typically occupied by the CAGN. Due to the density of the
vegetation, for example, it was extremely difficult to nearly impossible in many areas to traverse
through the habitat, except in the rare instances where small game trails were present. This
vegetative structure, as well as the species composition, is not typical of habitat occupied by the
CAGN in southern California.
Based on the lack of habitat that would be considered suitable to support resident, breeding pairs
of the California gnatcatcher in the vicinity of the project site (including out at least 500 to
750 feet), it is our opinion that the CAGN recorded on December 26 represents a dispersing or
transient individual. The inability to relocate this bird on other surveys would further support
this conclusion.
Finally, there may be a low possibility that a bird could had been drawn in by the tape-recorded
vocalizations from an extreme distance. After surveying the outlying native plant communities
from the higher vantage points on the site, no suitable CAGN habitat of any extent could be seen
within at least a half mile. Small patches of vegetation dominated by CSS species were seen
about 500 to 600 feet to the west (approximately a 1/2 acre in total) and about 750 feet to the
north (1/2 to one acre in total), although these were surrounded by either dense chaparral or
developed areas.
Sincerely,
P&D ENVIRONMENTAL
~~ Betty Dehaney, CEP
Director of Environmental Services
cc: John Cahill -City of Carlsbad
John Martin -USFWS
P/NZI 9/Park/CAGN-Survey-Ltr.doc (175508)
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Habitat Types
D Coastal Sage Scrub -Disturbed
D Southern Maritime Chaparral
L] Southern Maritime Chaparral -Disturbed
Southern Maritime Chaparral/
Scrub Oak Chaparral
Oak Woodland
D Non-Native Grassland
D Agriculture
D Landscape
D Ruderal
D Disturbed
~ Del Mar Manzanita
- - - -Park Disturbance Footprint
•
■
Coastal California Gnatcatcher
(single Male May 2002)
Coastal California Gnatcatcher
(single Male Dec. 2002)
Carlsbad Zone 19 Community Park Habitat Map and Park Development Area
Appendix A.1