From: Rapid changes in tree composition and biodiversity: consequences of dams on dry seasonal forests
Deciduous forest 1 | Number of individuals | Basal area | Dynamic rates T0–T2 | Dynamic rates T2–T4 | Dynamic rates T0–T4 | |||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Species | T0 | T2 | T4 | T0 | T2 | T4 | M | R | O | I | M | R | O | I | M | R | O | I |
  Acacia polyphylla | 40 | 39 | 35 | 0.25 | 0.25 | 0.28 | 19.4 | 18.4 | 19.2 | 19.9 | 5.3 | 0.0 | 3.4 | 8.5 | 13.9 | 11.0 | 12.6 | 15.3 |
  Anadenanthera colubrina | 141 | 170 | 187 | 3.18 | 4.67 | 5.14 | 1.8 | 10.9 | 2.4 | 19.5 | 4.8 | 9.0 | 4.8 | 9.2 | 4.0 | 10.5 | 5.0 | 15.7 |
  Bauhinia ungulata | 28 | 30 | 29 | 0.09 | 0.12 | 0.13 | 3.6 | 6.9 | 3.5 | 18.3 | 5.1 | 3.5 | 4.8 | 6.4 | 4.8 | 5.6 | 5.4 | 13.7 |
  Campomanesia vellutina | 92 | 89 | 86 | 1.23 | 1.19 | 1.18 | 6.2 | 4.6 | 6.3 | 4.8 | 1.7 | 0.0 | 3.2 | 2.8 | 4.0 | 2.4 | 4.9 | 4.0 |
  Casearia rupestris | 24 | 21 | 19 | 0.18 | 0.17 | 0.18 | 13.4 | 7.4 | 11.4 | 8.6 | 4.9 | 0.0 | 5.5 | 8.9 | 9.6 | 4.2 | 9.0 | 9.3 |
  Guazuma ulmifolia | 19 | 22 | 23 | 0.17 | 0.25 | 0.29 | 0.0 | 7.1 | 2.6 | 19.0 | 4.7 | 6.7 | 2.9 | 9.4 | 2.7 | 7.3 | 3.5 | 15.0 |
  Myracrodruon urundeuva | 279 | 238 | 199 | 5.33 | 5.61 | 5.44 | 8.2 | 0.6 | 3.7 | 6.1 | 9.0 | 0.5 | 4.2 | 2.7 | 8.7 | 0.6 | 4.2 | 4.7 |
  Piptadenia gonoacantha | 71 | 96 | 99 | 0.80 | 1.02 | 1.05 | 11.2 | 23.6 | 16.9 | 26.5 | 7.0 | 8.4 | 14.2 | 15.3 | 11.8 | 18.8 | 22.8 | 27.9 |
  Platypodium elegans | 21 | 21 | 20 | 0.58 | 0.65 | 0.72 | 2.4 | 2.4 | 6.4 | 11.9 | 2.4 | 0.0 | 0.5 | 5.5 | 2.5 | 1.3 | 3.6 | 8.8 |
  Tabebuia roseoalba | 246 | 237 | 231 | 2.86 | 3.05 | 3.12 | 3.9 | 2.1 | 2.4 | 5.5 | 3.0 | 1.7 | 1.9 | 3.1 | 3.5 | 2.0 | 2.3 | 4.4 |
Entire community | 1124 | 1136 | 1133 | 16.80 | 19.16 | 20.54 | 6.5 | 7.1 | 4.9 | 11.0 | 4.9 | 4.7 | 4.0 | 6.6 | 6.1 | 6.3 | 5.0 | 9.2 |