From: Ecosystem type and species’ traits help explain bird responses to spatial patterns of fire
Category | Variable | Mean (range) of values | Description | Scale | |
---|---|---|---|---|---|
Mallee woodlands | Foothill forests | ||||
Fire regime | Time since fire (years) | 34 (0–106) | 37 (0–107) | Number of years between the date of the bird survey and the most recent mapped fire at the site that preceded the survey | Site |
Amount early (ha) | 15 (0–81) | 35 (0–81) | The amount (ha) of vegetation classified as “early-successional” [0–10 years since fire (MW), 0–3 years since fire (FF)] within a 900 × 900 m window, centered on the bird survey site | Landscape | |
Amount late (ha) | 31 (0–81) | 16 (0–81) | The amount (ha) of vegetation classified as ‘late-successional’ [> 35 years since fire (MW), > 40 years since fire (FF)] within a 900 × 900 m window, centered on the bird survey site | Landscape | |
Spatial diversity of successional vegetation (index) | 0.38 (0–1.13) | 0.30 (0–1.33) | Shannon’s diversity index of post-fire successional states within a 900 × 900 m window, centered on the bird survey site. Successional states were: Mallee woodlands: 0–10, 11–35, > 35 years since fire. Foothill forests: 0–3, 4–10, 11–40, > 40 years since fire | Landscape | |
Environmental conditions | Temperature (℃) | 16.6 (15.4–17.4) | 23.7 (19.4–28.5) | MW: annual average daily temperature; FF: average daily maximum temperature for January (hottest month) | Site |
Elevation (m) | 66 (32–104) | 397 (33–954) | Meters above sea level based on digital elevation model (DEM) | Site | |
Vegetation type (categorical) | Triodia Mallee Chenopod Mallee Heathy Mallee | Driest Dry Mesic | Groups of vegetation classes with similar floristic and structural characteristics | Site |