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SU0013451
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SU0013451
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Last modified
5/17/2021 4:00:53 PM
Creation date
6/23/2020 11:17:55 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
RECORD_ID
SU0013451
PE
2600
FACILITY_NAME
WC-90-1
STREET_NUMBER
2248
Direction
W
STREET_NAME
LAKE FOREST
STREET_TYPE
RD
City
ACAMPO
APN
00306001
ENTERED_DATE
6/17/2020 12:00:00 AM
SITE_LOCATION
2248 W LAKE FOREST RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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SJGOV\dsedra
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EHD - Public
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Swainson's hawk is monogamous, and pairs remain together year after year until one dies. Nesting <br /> begins well after arrival in Central California,usually in May. Incubation lasts from 28 to 35 days, and <br /> nestlings are fledged at between four and eight weeks of age. Nest sites are solitary trees or small <br /> groves adjacent to agricultural fields or open grassland (Bloom, 1984). Many of the nesting areas are <br /> associated with riparian woodland. Schlorff and Bloom (1984) report that 82 percent of nests in their <br /> study were located within one mile of riparian forests. Estep (1989) confirms this fmding with an <br /> estimate of 78 percent nesting in riparian areas. Nests are usually located near the tops of tall trees, <br /> sometimes up to 90 feet above the ground (Mallette and Gould, 1978). Nest locations are normally <br /> within easy flying distance to agricultural fields with abundant rodent pray. <br /> Major prey items include rodents(California meadow voles,pocketgophers,California ground squirrels), <br /> birds (meadow larks, mourning doves, young ring-necked pheasants), and larger insects such as <br /> grasshoppers and Jerusalem crickets. Foraging range depends on both the abundance and availability of <br /> prey. Thus, a given piece of land could have a very high mouse population,but if the vegetative cover <br /> there was such that these rodents could not be detected from an aerial perch, then the site would be of <br /> little value to this or any other soaring hawk species. <br /> The actual home range area over which foraging occurs also varies greatly with land use. Craighead and <br /> Craighead (1956) recorded maximum foraging range in Wyoming as varying between 180 and 1,056 <br /> acres. In Central California, Estep (1989) recorded a range from 30 to 16,000 acres. Bechard (1982) <br /> found a direct correlation between foraging home range and cultivated land. Where the latter occupied <br /> more of the acreage in an area, the foraging area was consistently larger. <br /> Perhaps the most pertinent current estimate of foraging requirements are those given in the 1990 <br /> California Department of Fish and Game Mitigation Guidelines for Swainson's Hawk in the Central <br /> Valley of California. This document states that the minimum acreage needed to support a nesting pair <br /> is 1,200 acres and that all acreage within a ten mile radius of an active nest is considered potential <br /> foraging habitat. <br /> In addition to the observations made during this study, there are two additional reports which show <br /> Swainson's hawk utilization of Brovelli woods. One is the Brovelli Woods Raptor Survey(Guse, 1990) <br /> which was conducted over only one half of a full daylight period in late June, but still reports two <br /> possible nest sites in Brovelli Woods. The other source is the Habitat Conservation Plan for the <br /> Swainson's Hawk in San Joaquin County(Jones& Stokes Associates, 1990)which reports three nesting <br /> territories for the project site and places all 25 nesting territories in the Dry Creek Swainson's Hawk <br /> subpopulation within CDFG's estimated average foraging radius of 10 miles of the site (Figure 4.7-14). <br /> The project site falls within the range of this subpopulation group. <br /> One other state-listed threatened species was observed during the course of the study. This is the greater <br /> sandhill crane (Gnus canadensis tabida). Mixed flocks of both greater and lesser sandhill cranes were <br /> observed on two occasions in the pasture north of the project site and once on the project site. The latter <br /> observation was made after the early growth of annual grass and forb species had begun to grow above <br /> the previous season's dead grass mat. It is also possible that on some occasions this subspecies utilizes <br /> the Tracy Lake basins for both feeding and roosting given the fact that numerous sightings have been <br /> made on lands adjacent to the site (Gifford, 1992). Because work was temporarily halted during the <br /> major wintering period for sandhill cranes in San Joaquin Valley, no crane roosting in the shallow bay <br /> areas of Tracy Lakes was documented. Like most other large water birds, cranes are very refractory <br /> to human presence, and their use of any foraging or roosting site is predicated on the relative absence <br /> of humans. <br /> 19 <br />
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