Vascular Plant and Vertebrate Inventory of Saguaro ... - USGS
Vascular Plant and Vertebrate Inventory of Saguaro ... - USGS
Vascular Plant and Vertebrate Inventory of Saguaro ... - USGS
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Table 6.5. Number <strong>of</strong> photographs <strong>of</strong> mammals from infrared-triggered photography by elevation strata,<br />
<strong>Saguaro</strong> National Park, Rincon Mountain District, 1999–2005. “Abundance” equals the number <strong>of</strong> photographs<br />
<strong>of</strong> that species per estimated number <strong>of</strong> working camera‑nights. Does not include individuals that could be<br />
identified to genus but not species (e.g., some photos <strong>of</strong> deer, skunks, rabbits, <strong>and</strong> squirrels).<br />
Relative<br />
Relative<br />
Relative<br />
No. photos abundance No. photos abundance No. photos abundance<br />
Virginia opossum 2 0.1<br />
American black bear 2 0.1 21 2.9 10 2.0<br />
white‑nosed coati 17 0.6 8 1.1 3 0.6<br />
ringtail 142 5.3 78 10.8 9 1.8<br />
common raccoon 5 0.2<br />
striped skunk 134 5.0 21 2.9 7 1.4<br />
hooded skunk 160 6.0 20 2.8 2 0.4<br />
white‑backed hog‑nosed skunk 20 0.7 4 0.6 3 0.6<br />
western spotted skunk 3 0.1 3 0.4<br />
coyote 97 3.6<br />
domestic dog 2 0.1<br />
common gray fox 602 22.6 283 39.3 133 27.0<br />
mountain lion 46 1.7 16 2.2 11 2.2<br />
bobcat 50 1.9 2 0.3 4 0.8<br />
round‑tailed ground squirrel 1 0.0<br />
rock squirrel 13 0.5 3 0.4<br />
Harris’ antelope squirrel 7 0.3<br />
Abert’s squirrel 8 1.6<br />
Arizona gray squirrel 2 0.3 1 0.2<br />
antelope jackrabbit 7 0.3<br />
black‑tailed jackrabbit 10 0.4<br />
desert cottontail 48 1.8 3 0.4<br />
eastern cottontail 3 0.6<br />
domestic cattle 3 0.1<br />
collared peccary 561 21.0 27 3.8<br />
mule deer 28 1.0<br />
white‑tailed deer 104 3.9 23 3.2 63 12.8<br />
Total photographs 2064 0.81 514 0.73 257 0.53<br />
Species richness 24 15 13<br />
species <strong>and</strong> not Cockrum’s desert shrew; both<br />
species potentially occur in the Rincon Mountains<br />
(Baker et al. 2003b).<br />
<strong>Inventory</strong> Completeness<br />
We confirmed a total <strong>of</strong> 59 species <strong>of</strong> mammals<br />
in the Rincon Mountain District <strong>and</strong> failed to<br />
confirm 11 species that have been previously<br />
documented for the Rincon Mountains. Of these<br />
11, four species (grizzly bear, jaguar, Mexican<br />
gray wolf, <strong>and</strong> bighorn sheep) are certainly<br />
extirpated from the district <strong>and</strong> two others<br />
(deer mice, North American porcupine, <strong>and</strong><br />
banner-tailed kangaroo rat) may be extirpated.<br />
We believe that three species <strong>of</strong> bats <strong>and</strong> one<br />
Low Middle High<br />
81<br />
rodent that were documented in the past are still<br />
present <strong>and</strong> would be confirmed with additional<br />
effort. Based on these records, if we assume that<br />
four species still present went undetected, our<br />
inventory confirmed 93% <strong>of</strong> mammals known for<br />
the district. The species accumulation curves for<br />
small mammal trapping (Fig. 6.9) <strong>and</strong> bats (Fig.<br />
6.10) as well as for infrared-triggered cameras<br />
(Fig. 6.11) also suggest that our inventory was<br />
fairly complete. These results make this effort<br />
one <strong>of</strong> the most comprehensive <strong>of</strong> its kind in<br />
the region for mammals. The infrared-triggered<br />
effort, in particular, is unprecedented.<br />
The three “new” species reported during<br />
this study may not have been observed before<br />
simply due to lack <strong>of</strong> survey effort. This situation