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Table 9 Fixed effects and associated hypotheses (HA from Table 5) in top models of adult buprestid activity across 11 burned sites sampled in the greater Sierra Nevada region of California, USA, during the summers of 2015 and 2016. QAICc = quasi-Akaike’s information criterion, corrected for small sample size; DOY = day of year; Neg = negative; Pos = positive; BA = basal area

From: Patterns of woodboring beetle activity following fires and bark beetle outbreaks in montane forests of California, USA

Response

Model rank

Predictor

Effecta

ΔQAICc

ΔNull

HA

Adult buprestid activity

1

Ignition date (DOY)

Negns

0.00

11.96

P

DOY × DOY

Neg***

P

Fire age

Neg***

A

DOY × DOY × Fire age

Pos***

P, A

2

Snag BA

Pos**

6.17

5.79

M, S

Fire age

Neg**

A

Snag BA x Fire age

Posns

M, S, A

3

Snag BA

Pos***

6.32

5.64

M, S

4

Char height

Pos**

7.57

4.39

S

5

Char height

Pos**

7.66

4.30

S

Fire age

Neg**

A

Char height × Fire age

Negns

S, A

Adult Cypriacis aurulenta activityb

1

Host tree taxon = pine

Pos**

0.00

0.39

H

Adult

Melanophila consputa

activity

1

Fire age

Neg***

0.00

20.19

A

Char height

Posns

S

Live tree BA

Neg**

M, S

Ignition date

Neg***

P

2

Fire age

Neg***

2.33

17.86

A

Burn severity = low

Neg***

S

Burn severity = moderate

Neg***

S

Ignition date (DOY)

Neg*

P

DOY × DOY

Neg*

P

3

Fire age

Neg***

3.84

16.35

A

Char height

Pos***

S

Ignition date (DOY)

Neg*

P

DOY × DOY

Neg*

P

4

Fire age

Neg***

4.46

15.73

A

Burn severity = low

Neg***

S

Burn severity = moderate

Neg**

S

5

Live tree BA

Neg***

7.55

12.64

M, S

  1. ans (P > 0.05), * (P < 0.05), ** (P < 0.01), *** (P < 0.001)
  2. bOnly one model of adult Cypriacis aurulenta activity was supported relative to the null model