From: Predicting snag fall in an old-growth forest after fire
Snag population | Snag abundance | Density (snags ha−1) | Basal area (m2 ha−1) |
---|---|---|---|
Pre-fire snags DBH ≥ 10 cm | |||
 Abies concolor | 1467 | 57.3 | 7.242 |
 Pinus lambertiana | 399 | 15.6 | 7.180 |
 Quercus kelloggii | 108 | 4.2 | 0.144 |
 Calocedrus decurrens | 36 | 1.4 | 0.465 |
 Cornus nuttallii | 3 | 0.1 | 0.002 |
 Total | 2013 | 78.6 | 15.033 |
Post-fire snags DBH ≥ 10 cm | |||
 Abies concolor | 6202 | 242.3 | 11.476 |
 Pinus lambertiana | 1162 | 45.4 | 11.462 |
 Quercus kelloggii | 387 | 15.1 | 0.502 |
 Calocedrus decurrens | 282 | 11 | 0.907 |
 Cornus nuttallii | 189 | 7.4 | 0.100 |
 Total | 8222 | 321.2 | 24.447 |
Post-fire snags 1 ≤ DBH < 10 cm | |||
 Abies concolor | 10,759 | 420.3 | 0.996 |
 Pinus lambertiana | 1777 | 69.4 | 0.143 |
 Quercus kelloggii | 1411 | 55.1 | 0.073 |
 Calocedrus decurrens | 601 | 23.5 | 0.053 |
 Cornus nuttallii | 232 | 9.1 | 0.020 |
 Total | 14,780 | 577.4 | 1.285 |