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SU0007680
Environmental Health - Public
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2600 - Land Use Program
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QX-98-0001
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SU0007680
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Last modified
5/7/2020 11:33:10 AM
Creation date
9/8/2019 12:41:03 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
RECORD_ID
SU0007680
PE
2656
FACILITY_NAME
QX-98-0001
STREET_NUMBER
15004
Direction
E
STREET_NAME
PELTIER
STREET_TYPE
RD
City
ACAMPO
APN
02107001
ENTERED_DATE
4/17/2009 12:00:00 AM
SITE_LOCATION
15004 E PELTIER RD
RECEIVED_DATE
4/17/2009 12:00:00 AM
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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SJGOV\rtan
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\MIGRATIONS\P\PELTIER\15004\QX-98-0001\SU0007680\APPL.PDF \MIGRATIONS\P\PELTIER\15004\QX-98-0001\SU0007680\CDD OK.PDF \MIGRATIONS\P\PELTIER\15004\QX-98-0001\SU0007680\EH COND.PDF \MIGRATIONS\P\PELTIER\15004\QX-98-0001\SU0007680\CORRESPOND.PDF
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EHD - Public
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Jennings and Haye- Species of Special Concern 96 <br /> California tiger salamanders, garter snakes, great blue herons, and raccoons are probably <br /> the most important predators of larval and post-metamorphic S. hammondii (Childs 1953, <br /> Feaver 1971). No data are available on the movement ecology or colonization abilities of <br /> S. hammondii. <br /> Habitat: Western spadefoots require temporary rainpools with water temperatures of <br /> >_ 9°C and < 30°C (Brown 1966, 1967) in which to reproduce and that last>_ 3 weeks <br /> (Feaver 1971) in order to metamorphose successfully. Rainpools in which western <br /> spadefoots reproduce and from which they are able to metamorphose successfully lack <br /> fishes, bullfrogs, and crayfishes; many indications exist that S. hammondii cannot recruit <br /> successfully in the presence of exotic predators, primarily introduced fishes, but also <br /> bullfrogs and crayfishes (K. Baldwin, S. Morey, B. Shaffer, pers. comm.; pers. observ.). <br /> Soil characteristics of burrow refuge sites that western spadefoots use have not been <br /> studied, but if they are similar to those of S. multiplicatrls, the soil may become fairly <br /> compact and hard during the season of summer aestivation (Ruibal et al. 1969). <br /> Status: Threatened; concern over the decline of S. hammondii is not new. Nearly 20 <br /> years ago, both Robert L. Livezey and Rudolfo Ruibal (in litt. 3 and 7 February 1972 to <br /> Leonard Fisk) believed that this taxon had sustained drastic reductions over the previous <br /> 15-20 years in the Central Valley and southern California. Current data indicate that in <br /> southern California (from the Santa Clara River Valley,Los Angeles and Ventura counties, <br /> southward), > 80% of habitat once known to be occupied by S. hammondii has been <br /> developed or converted to uses that are undoubtedly incompatible with its successful <br /> reproduction and recruitment. In northern and central California, loss of habitat has been <br /> less severe, but nevertheless significant; it is estimated that>30% of the habitat once <br /> known to be occupied by S. hammondii has been developed or converted to uses <br /> incompatible with the survival of this taxon: Regions severely affected include the lower <br /> two-thirds of the Salinas River system, and much of the areas east of Sacramento, Fresno, <br /> and Bakersfield. Moreover, in many ares of the Central Valley,remaining suitable rainpool <br /> or vernal pool habitat, which is concentrated on valley terraces along the edges of the <br /> Valley Floor,has been disappearing in a fragmented fashion, which may present a <br /> significant threat to the metapopulation structure of S.hammondii. The continued <br /> placement of mosquitofish by mosquito abatement programs in vernal pools threatens some <br /> populations (S. Morey, pers. comm.; pers. observ.). Emigration of juvenile and adult <br /> bullfrogs into rainpool breeding sites may also pose a threat to some populations (Hayes <br /> and Warner 1985; Morey and Gullin 1992; A. McCready and S. Morey, pers. comm.). <br /> Management Recommendations: Effort should be made to protect significant areas of <br /> rainpool habitat from alteration. Currently,rainpool habitats that harbor S. hammondii are <br /> protected in only a handfull of relatively small preserves,mostly under the jurisdiction of <br /> The Nature Conservancy (e.g., Santa Rosa Plateau,Riverside County; Pixley Vernal Pools <br /> Preserve, Tulare County). The biggest gap in current understanding of S. hammondii <br /> relates to its population structure and how habitat fragmentation may affect its likely <br /> metapopulation structure. Such an understanding is critical to determining the spatial <br /> population array that will allow S. hmnmondii to survive long-term. Much of the basic life <br /> history of S. hammondii remains poorly understood. In particular, variation in <br /> postmetamorphic survivorship, longevity, and movements must be understood in order to <br /> refine the direction of management. Finally, the features of suitable habitat remain poorly <br /> understood. It has often been assumed that S. hammondii requires loose soil for <br /> subterranean dormancy, but it has also been observed to occupy small mammal burrows <br /> (Stebbins 1951). Whether it uses the latter only as temporary refuges during its season of <br /> surface activity is unknown, but a better understanding of its pattern of utilization of <br /> subterranean refuges will allow refining of our current understanding of suitable habitat. <br /> Indications exist that western spadefoots can easily burrow into moist soils that would be <br />
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