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All understory woody species were counted, identified, and separated by height class.
The height class distribution revealed that more than 93% of the saplings recorded were less than 400 cm tall, and fire significantly reduced the rate of change in density of saplings in the 200 400 cm height class.
Results for DBH and height class distributions indicated that recruitment for most tree species began within a few years of stand initiation.
Woody canopy height class distributions differed significantly between protected and accessible areas, with the tallest vegetation (>10 m) occurring on protected termite mounds.
In each grid cell, the forest dynamics is simulated with a multi-species, height structured forest model, based on growth, competition and death of the trees in each height class.
The smallest fertile colonies (<30 mm height class) were on an average 24.0 mm in height and 3.6 mm in basal diameter: these colonies were on an average between 7 and 10 years.
Soil C density was the largest measured C pool, containing 274.6 Mg C ha−1 to 314.1 Mg C ha−1 and accounting for 45 73% of the height class ecosystem C densities, which ranged from 373.8 Mg C ha−1 to 620.8 Mg C ha−1.
Neither height class nor the interaction between height class and treatment were significant (Table 3) indicating that changes in mortality across height classes were relatively similar between treatments.
Using this data, a mixed-effects model was used to test the effects of treatment, height class and the interaction between treatment and height class on transformed mortality.
The influence of height class and treatment on tree mortality was assessed using analysis of variance.
Note that there was no individual in the height class 4 (>20 m) in NPI.
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