Palm Springs pocket mouse
Perognathus longimembris
bangsi
USFWS: No status
CDFG: California Species of Special Concern
Background
Distribution, Abundance and
Trends. The Palm Springs pocket mouse is one of seven
subspecies of Perognathus longimembris, the "silky pocket
mice" that occur in southern California. The species is the
smallest of the Heteromyidae family which also includes kangaroo
rats, kangaroo mice, and spiny pocket mice. The Palm Springs
pocket mouse was originally described by Mearns (1898) with the
type locality in Palm Springs. This subspecies occurs in the
lower Sonoran life zone from the San Gorgonio Pass area east to
the Little San Bernardino Mountains and south along the eastern
edge of the Peninsular Range to Borrego Valley and the east side
of San Felipe Narrows (Hall 1981). There is no evidence that
this subspecies' range is different than what has been described
in the past (Dodd 1996), although its habitat has been greatly
reduced by urbanization and agriculture in the Coachella Valley.
The Palm Springs pocket mouse
is known to hybridize with the Los Angeles pocket mouse (P.l.
brevinasus) along its western boundary. Hybridization also
occurs, although the extent is not known, with other subspecies,
the Jacumba pocket mouse (P. l. internationalis) to the south,
and little pocket mouse (P. l. longimembris) to the north.
Generally, their habitat is
described as having level to gently sloping topography, sparse
to moderate vegetative cover, and loosely packed or sandy soils.
The species was found broadly distributed in the Plan area on
slopes ranging from 0% to approximately 15%. The Plan area
contains the major portion of the range of this species,
including the western, northern, and eastern limits of the
species' range. The southern boundary of the range extends out
of the Plan area into Imperial, and San Diego counties. The
species occurs on three existing preserves: the Coachella Valley
Preserve, the Whitewater River Floodplain Preserve, and the
Willow Hole-Edom Hill Preserve/ACEC. It occurs at the highest
reported densities for the Plan area in the Snow Creek area.
Three individuals were captured in a small mammal trapping grid
(Tierra Madre Consultants 1999) in the blowsand habitat
adjoining the San Gorgonio River wash just north of One Horse
Spring; this location is approximately 3 miles west of Snow
Creek Road. Surveys completed for this plan (Dodd 1999)
confirmed that the species also occurs at Dos Palmas Preserve/ACEC
and in the Cottonwood Canyon area of Joshua Tree National Park.
Tests to determine that the subspecies captured in these areas
is bangsi and not longimembris have not been finalized.
According to the survey results
of Shana Dodd in 1995 and 1999 (Dodd 1996, 1999) the highest
densities of this pocket mouse occur at the western end of the
Plan area, with lower densities occurring further east. Her live
trapping data, which are summarized in the table below, indicate
that this species is most abundant throughout the Snow Creek to
Windy Point area. She describes the Palm Springs pocket mouse as
moderately abundant in the Highway 62/Mission Creek area, where
the species is not currently protected. Considerable unprotected
habitat also occurs adjacent to the Willow Hole Preserve; Dodd
(1996) describes the density of this species at Willow Hole as
moderate. Additional density estimates were made for the Palm
Springs pocket mouse, based on live trapping on two 0.5 ha grids
located west or Snow Creek Road, approximately ½-mile north of
Snow Creek Village in the Snow Creek area (Spencer et al. 2000).
The minimum density was 81.6 individuals/ha and 63.3
individuals/ha, on two adjacent grids.
Our understanding of the
ecology of the Palm Springs pocket mouse arises largely from the
observations of mammalogists studying other species. Pocket mice
of the P. longimembris group are nocturnal, solitary, and
generally exhibit strong intraspecific aggression (Dodd 1996).
They spend the day in burrows they construct, comprised of a
system of tunnels and resting areas, with the entrance plugged.
This species generally breeds from January to August, with a
peak of activity from March to May (Dodd 1996). Several studies
suggest that reproduction in heteromyids may be dependent on
availability of annual vegetation. The little pocket mice
hibernate in winter and are active above ground in spring,
summer, and fall (Bartholomew and Cade 1957).
Estimates of home range size
are not available for the Palm Springs pocket mouse. In Joshua
Tree National Park, home ranges of P. longimembris range from
38.7 to 84.4 meters (Chew and Butterworth 1964); in this study
densities ranged from 0.85 to 1.74 individuals/ha. In Nevada,
home ranges of males ranged from 12.4 to 31.6 meters and home
ranges of females from 13.7 to 40.5 meters (Maza et al. 1973).
O'Farrell (1978) determined that home range for both sexes
varied from 0.28 ha in early spring to 0.80 ha in late fall.
TABLE 2.27
RESULTS OF LIVE TRAPPING FOR PALM SPRINGS POCKET MOUSE 1
|
LOCATION
|
Number
of Transects/Trap Nights
|
Number
of P.l. bangsi trapped
|
Number
of Individuals/trap night
|
Density
Estimate 2
|
|
|
|
|
|
| SNOW CREEK
TO WINDY POINT (1995) |
7/775
|
75
|
0.10
|
73.1/ha;
43.9/ha
|
WHITEWATER
FLOODPLAIN PRESERVE (1995)
(West valley) |
2/275
|
11
|
0.04
|
NA
|
| W. OF
HIGHWAY 62 (1995) |
6/1548
|
8
|
0.005
|
36.4/ha
|
| MISSION
CREEK (1999) |
4/180
|
30
|
0.17
|
NA
|
| WILLOW HOLE
- EDOM HILL (1995) |
6/1440
|
18
|
0.01
|
(5)
|
| INDIO HILLS
TO JOSHUA TREE N.P. CORRIDOR (1995) |
10/2000
|
5
|
0.003
|
(5)
|
| COACHELLA
VALLEY PRESERVE (1995) |
5/1150
|
10
|
0.009
|
(8)
|
| THOUSAND
PALMS - CVP SAND SOURCE AREA (1999) |
3/180
|
4
|
0.02
|
NA
|
| EAST END
INDIO HILLS (1999) |
5/435
|
4
|
0.009
|
NA
|
| MARTINEZ
CANYON - EAST END OF SANTA ROSA MOUNTAINS (1999) |
9/890
|
0
|
–
|
NA
|
| SHAVERS
VALLEY - S. OF JOSHUA TREE N.P. |
6/875
|
4
|
0.005
|
NA
|
| DOS PALMAS |
2/1070
|
2
|
0.002
|
NA
|
| 1
Results are from Dodd (1996 and 1999) based on live
trapping surveys from March to July 1995 and between 8
April and 28 May 1999. |
| 2
In 1995, density plots were sampled; P.l bangsi
numbers were sufficient to calculate density on 3 of the
6 density plots (two plots at Snow Creek and 1 plot W.
of Hwy 62). Numbers in parentheses under Density
Estimate are the number of P.l bangsi captured
where accurate density estimates could not be
calculated. No density plots were sampled in 1999. |
Threats and Limiting Factors.
Threats to this species and its habitat within the Coachella
Valley include agricultural development, urban development,
construction of roads, railroads, airports and other structures,
off-highway vehicle use, illegal trash dumping, and domestic
animal predators.
Special Considerations.
This species is generally associated with sandy soils. Thus,
long-term viability of populations will require the continued
functioning of the sand source and transport systems that
sustain the habitat.
|