“…We then intersected each survey segment with the GPS locations for each white-tailed deer group detected. Segment-level spatial covariates included a bivariate smooth of geographic coordinates (Universal Transverse Mercator [UTM]) to account for spatially autocorrelated whited-tailed deer detections and land cover types known to influence deer abundance such as distance from agriculture cover (m) [40][41][42][43], distance from developed cover (m) [42][43][44][45], distance from forest cover (m) [42,46,47], distance from shrub cover (m) [43,48,49], distance from timber cuts (m) [48,50], distance from wetland cover (m) [43,51,52], distance from water (m) [51,53], elevation (m) [12,54,55], and days with snow cover [56,57]. Land cover such as agriculture, developed, forest, shrub, timber cuts, wetland, and water were identified using an updated land cover map of the Park for 2016 that combined Landsat 8 satellite imagery (30 m resolution) acquired from the USGS Global Visualization Viewer for imagery, Normalized Difference Vegetation Index, National Land Cover Dataset, the Adirondack Park Agency's wetlands data, and timber treatment data provided by regional timber companies [24].…”