Table 2 Covariate coefficients (β) from top single-species occupancy model for the Northern saw-whet Owl landscape use (ψ) and detection likelihood (p) ranked by akaike’s information criterion for small sample sizes, including standard error (SE) the lower and upper 95% confidence intervals (LCL; UCL). All variables were scaled to have a mean of 0 and standard deviation of 1 prior to analysis.

From: Sensory interference shapes habitat suitability for an acoustically specialized predator

Parameter

Variable a

β

SE

LCL

UCL

p

Intercept

−1.67

0.04

−1.74

−1.592

p

PRECIP

−0.10

0.03

−0.16

−0.03

p

DATE

−0.63

0.04

−0.71

−0.56

p

LOWFREQNOISE

−0.40

0.04

−0.48

−0.32

ψ

Intercept

0.44

0.14

0.17

0.71

ψ

BRDLF400

−0.52

0.17

−0.85

−0.19

ψ

ELEV

−0.42

0.16

−0.73

−0.12

ψ

STRMDIST

0.38

0.18

0.02

0.74

ψ

RAILROAD

−0.36

0.18

−0.70

−0.01

ψ

OWLFREQ

−0.30

0.14

−0.58

−0.02

ψ

SMCON200

0.37

0.15

0.07

0.67

  1. a SMCON200 = proportion of small conifer within 200 m, BRDLF400 = proportion of broadleaf trees within 400 m, RAILROAD = distance to nearest railroad (km), STRMDIST = distance to nearest stream (m), OWLFREQ = mean noise values within the range of 1.6–7.6. l kHz. ELEV = elevation (m), DATE = Julian date, LOWFREQNOISE = mean nightly noise values calculated from 250–1000 Hz (dBFS), PRECIP = amount of daily precipitation (mm).