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Last modified
7/14/2009 5:02:34 PM
Creation date
5/22/2009 12:54:55 PM
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UCREFRP
UCREFRP Catalog Number
9307
Author
Germaine, S. S.
Title
Relationships of Birds, Lizards, and Nocturnal Rodents to Their Habitat in the Greater Tucson Area, Arizona.
USFW Year
1995.
USFW - Doc Type
Phoenix, AZ.
Copyright Material
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RELATIONSHIPS OF BIItDS, LIZARDS, AND NOCTURNAL RODENTS TO THEIR I IABITAT IN TUCSON, ARIZONA <br />Lizards. Lower Sonoran vegetation correlated <br />negatively with tree lizards, and positively with <br />whiptail lizards (Fig. 5, Table 5). Upper Sonoran <br />vegetation, percent undisturbed riparian, and <br />distance from patch each correlated with 1 of the <br />4 lizard species. Distance from patch correlated <br />positively with tree lizards, and upper Sonoran <br />vegetation correlated negatively with them. <br />Percent undisturbed riparian correlated positively <br />with zebra-tailed lizards. House density did not <br />correlate with any lizard species. <br />Nocturnal Rodents. All 4 house mice were <br />captured in alleys in the high housing density <br />sites, none were captured in any of the other <br />density levels (Fig. 6). None of the 4 native <br />species of rodents were captured in high housing <br />density sites. <br />A total of 19 Bailey's pocket mice <br />(Chaetodipus baileyi) were captured. Bailey's <br />pocket mice were absent from both high density <br />housing and the high density control. Therefore, <br />I did not test them in a contingency table. They <br />were evenly distributed between the low density <br />control (n = 9) and the low housing density sites <br />(n = 10). <br />White-throated wood rats were not <br />encountered in the high housing density sites, but <br />36 individuals occurred in the other 3 areas. The <br />distribution of individuals between high housing <br />density and the other areas differed (2 tailed P = <br />0.006). A follow up test revealed no difference in <br />frequency of occurrence between the remaining 3 <br />areas (XZ = 12.67, P = 0.779). <br />Merriam's kangaroo rats were also absent <br />from high density housing. Forty individuals <br />were captured in the other 3 areas. Merriam's <br />kangaroo rats differed in abundance between all <br />areas (two-tailed P, = 0.030). Merriam's kangaroo <br />rats were also less abundant in the high density <br />control than in either the low density housing or <br />its control (XZ = 21.40, P = 0.048}. There was no <br />difference in number of Merriam's kangaroo rats <br />captured between the low density treatment and <br />control (n = 13 in both cases). <br />The desert pocket mouse was represented by <br />45 individuals, none of which occurred in high <br />housing density. The distribution of desert pocket <br />mice differed (2 tailed P <0.001), but there was <br />no difference in frequency of occurrence between <br />the 3 remaining sites (XL = 0.53, P = 0.766). <br />Nocturnal rodent species richness did not <br />differ between any of the 4 sites (2 tailed P = <br />0.576). However, total abundance was lower in <br />both the high housing density (Xz = 45.83, P <br /><0.001) and the high density control (XZ = 6.10, <br />P = 0.047) than in either of the low density sites. <br />Wildlife Community Descriptors. <br />Non-native bird species richness and total <br />abundance were positively correlated to house <br />density, percent paved or graded, and percent <br />urban-open exotic, and negatively correlated with <br />upper Sonoran vegetation (Table 6; see Table 1 for <br />full variable names). Evenness correlated <br />positively with house density. Non-native species <br />richness, total abundance, and evenness were all <br />positively correlated. <br />Native breeding bird species richness <br />correlated positively with upper Sonoran <br />vegetation and negatively with distance from <br />riparian. Total abundance of native birds <br />correlated positively with plot heterogeneity. <br />Evenness did not correlate with any variables. <br />Native breeding bird species richness was not <br />correlated with abundance or evenness, but <br />abundance was negatively correlated with <br />evenness. <br />Species richness and abundance for the <br />breeding bird indicator guild correlated negatively <br />with house density and percent urban-open exotic, <br />and positively with upper Sonoran vegetation. <br />Evenness correlated negatively with house density. <br />Species richness, abundance, and evenness were all <br />positively correlated. <br />The correlations between the 3 breeding bird <br />groups and habitat variables disappeared during <br />winter time. Bird species richness, abundance, and <br />evenness for both wintering non-native and native <br />bird groups were- not correlated with any habitat <br />descriptor. For non-native birds, the community <br />descriptors were all positively correlated. For <br />native birds, species richness and abundance were <br />positively correlated, but not evenness. <br />Lizard richness, abundance, and evenness were <br />not correlated with any habitat descriptors. All 3 <br />lizard community descriptors were correlated. <br />Predictive Models <br />Breeding Birds. House density correlated with <br />species richness for all 3 groups of birds (Table 6). <br />The correlations with house density were negative <br />for both native birds (r = -0.47) and the native <br />indicator guild (r = -0.69), and positive for the <br />non-native group (r = 0.80). Species richness in <br />STEPHEN S. GERMAINE 1995 ARIZONA GAME fr FISH DEPARTMENT, TECH. REP. 20 23 <br />
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