Environmental Engineering Reference
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collected in the Modoc plateau, eastern Mojave, or Colorado Desert bioregions during
the surveillance period.
We identifi ed a total of 166 unique locations for positive rodent samples (Figure
2a). The California ground squirrel ( Spermophillus beecheyi ) was the rodent species
with the largest total number of specimens (12,546; Table 1) and number of posi-
tive specimens (559; Table 1), representing 105 of these unique geocoded locations.
Because California ground squirrels are a key indicator species for plague epizootics
[36] and human disease risk in California [10], we also ran models for this subset of
data only.
Table 1. Number of total samples and positive samples for the rodent species most commonly
collected during plague surveillance in California.
Species
Common Name
Total samples
Positive
samples
Prevalence
(proportion seropositive)
Spermophilus beecheyi
California ground squirrel
12546
559
0.045
Tomias senex
Shadow chipmunk
2701
174
0.064
Golden-mantled ground
squirrel
Spermophilus lateralis
2685
19
0.007
Peromyscus maniculatus
Deer mouse
1776
20
0.011
Neotoma fuscipes
Dusky-footed woodrat
1622
10
0.006
Yellow-pine chipmunk
1014
58
0.057
Tamias a moe nus
Tamias speciosus
Lodgepole chipmunk
658
43
0.065
Tamiasciurus douglasii
Douglas' squirrel
475
44
0.093
Spermophilus beldingi
Belding's ground squirrel
408
21
0.051
Tamias quadrimaculatus
Long-eared chipmunk
400
16
0.040
Neotoma lepida
Desert woodrat
307
2
0.007
Tamias merriami
Merriam's chipmunk
277
18
0.065
Neotoma cinerea
Bushy-tailed woodrat
186
6
0.032
Peromyscus boylii
Brush mouse
117
2
0.017
Peromyscus truei
Pinon Mouse
108
0
0.000
T amias minim us
Least chipmunk
96
2
0.021
Peromyscus crinitus
Canon mouse
82
1
0.012
Glaucomys sabrinus
Northern Flying squirrel
71
0
0.000
Total
25529
995
0.039
Only records of positive rodents were included for niche modeling, as negative
samples (Figure 2b) were frequently obtained from areas that had also yielded posi-
tive samples, or from which too few specimens had been collected to be considered
representative. The 3,788 sampling events had yielded negative samples, but 2,296 of
these were at locations where positive samples had also been collected. Of the remain-
ing 1,492 sampling events, only fi ve locations had been sampled more than 20 times,
which we estimated as the minimum number of samples that would need to be taken
to confi rm a location as a true absence.
 
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