Table 5 Summary of model statistics^a from regression analysis of fire severity effects^b on chipmunks (Neotamias spp.) abundance in Yosemite National Park, California, 2004 and 2005 (n = 10). Models are listed from best to poorest fit.

Abundance{oak cover + patch perimeter}

4

45.84

0.00

0.42

Abundance{oak cover}

3

46.83

0.99

0.26

Abundance{oak cover + patch squareness}

4

47.98

2.14

0.14

Abundance{canopy cover}

3

50.87

5.03

0.03

Abundance{patch perimeter}

3

51.00

5.16

0.03

Abundance{patch squareness}

3

51.86

6.02

0.02

Abundance{edge distance + oak cover}

4

51.98

6.14

0.02

Abundance{fire severity}

3

52.23

6.39

0.02

Abundance{shrub cover}

3

53.10

7.26

0.01

Abundance{trap week}

3

53.58

7.74

0.01

Abundance{edge distance}

3

54.08

8.24

0.01

Abundance{trap year}

3

54.16

8.33

0.01

Abundance{canopy cover + patch perimeter}

4

55.14

9.31

0.00

Abundance{canopy cover + patch squareness}

4

56.05

10.21

0.00

Abundance{edge distance + patch perimeter}

4

56.51

10.67

0.00

Abundance{shrub cover + patch perimeter}

4

56.78

10.94

0.00

Abundance{canopy cover + edge distance}

4

56.80

10.96

0.00

Abundance{fire severity + patch perimeter}

4

56.96

11.12

0.00

Abundance{shrub cover + patch squareness}

4

57.09

11.25

0.00

Abundance{edge distance + fire severity}

4

57.56

11.72

0.00

Abundance{fire severity + patch squareness}

4

57.56

11.72

0.00

Abundance{edge distance + patch squareness}

4

57.67

11.83

0.00

Abundance{shrub cover + edge distance}

4

58.72

12.88

0.00