Centre for Research into Ecological and Environmental Modelling University of St Andrews
Modified
November 2024
Covariate analysis of point transects: Savannah sparrow
Further investigation of a single covariate (pasture) upon detectability of the Savannah Sparrow data set. The analysis is done in R, but the understanding of the covariates is relevant whatever software is used.
Recall, these are data from Colorado, described by Knopf et al. (1988). The question here was whether to include pasture as a covariate in the detection function. The biological question being, “does detectability of Savannah sparrows differ between the pastures in which the survey was conducted.”
Region.Label Area Sample.Label Effort object distance Study.Area
1 PASTURE 1 1 POINT 1 1 NA NA SASP 1980
2 PASTURE 1 1 POINT 2 1 NA NA SASP 1980
3 PASTURE 1 1 POINT 3 1 NA NA SASP 1980
A truncation distance of 55m was chosen. The half normal and hazard rate functions were tried in turn, allowing AIC selection of cosine adjustment terms, then pasture was included as a covariate in the detection function.
The half normal model with pasture as a covariate had a marginally smaller AIC than the half normal model without pasture. The plots and estimates are shown below.
For 1981, there was a clear preference for including pasture as a covariate in the detection function but little to choose from between the half normal and hazard rate key function. For comparability with 1980, the plots and results below are for the half normal model although AIC showed a slight preference for the hazard rate model. The differences in detection between pastures can easily be seen and this is reflected in the estimated densities (birds per hectare).
Summary for distance analysis
Number of observations : 162
Distance range : 0 - 55
Model : Half-normal key function
AIC : 1261.684
Optimisation: mrds (nlminb)
Detection function parameters
Scale coefficient(s):
estimate se
(Intercept) 2.9440471 0.1110272
Region.LabelPASTURE 1 0.7362681 0.3726357
Region.LabelPASTURE 2 0.1660949 0.1524426
Region.LabelPASTURE 3 0.2703034 0.1790810
Estimate SE CV
Average p 0.3435487 0.03715842 0.1081606
N in covered region 471.5489313 59.62606186 0.1264472
Summary statistics:
Region Area CoveredArea Effort n k ER se.ER cv.ER
1 PASTURE 0 1 95.03318 100 31 100 0.310 0.05448566 0.17576019
2 PASTURE 1 1 95.03318 100 32 100 0.320 0.06175874 0.19299605
3 PASTURE 2 1 95.03318 100 51 100 0.510 0.08225975 0.16129363
4 PASTURE 3 1 95.03318 100 48 100 0.480 0.07174590 0.14947063
5 Total 4 380.13271 400 162 400 0.405 0.03418422 0.08440547
Abundance:
Label Estimate se cv lcl ucl df
1 PASTURE 0 1.3887466 0.3779428 0.2721467 0.8203808 2.350880 255.9017
2 PASTURE 1 0.5241867 0.1817587 0.3467442 0.2699503 1.017861 250.9726
3 PASTURE 2 1.6980708 0.4057104 0.2389243 1.0676527 2.700732 251.7139
4 PASTURE 3 1.3509360 0.3544528 0.2623757 0.8127396 2.245526 253.0658
5 Total 4.9619401 0.6827259 0.1375925 3.7903971 6.495586 357.0057
Density:
Label Estimate se cv lcl ucl df
1 PASTURE 0 1.3887466 0.3779428 0.2721467 0.8203808 2.350880 255.9017
2 PASTURE 1 0.5241867 0.1817587 0.3467442 0.2699503 1.017861 250.9726
3 PASTURE 2 1.6980708 0.4057104 0.2389243 1.0676527 2.700732 251.7139
4 PASTURE 3 1.3509360 0.3544528 0.2623757 0.8127396 2.245526 253.0658
5 Total 1.2404850 0.1706815 0.1375925 0.9475993 1.623896 357.0057
In these models, the detection functions have been fitted to all the detections within the study region (for each year). An alternative would be to fit separate detection functions within each pasture (specified in Region.Label), provided there are enough detections. This would allow different shape detection functions to be fitted in each pasture (providing this is a reasonable thing to do).
References
Knopf, F. L., Sedgwick, J. A., & Cannon, R. W. (1988). Guild structure of a riparian avifauna relative to seasonal cattle grazing. The Journal of Wildlife Management, 52(2), 280–290. https://doi.org/10.2307/3801235