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Tree and shrub biomass were estimated using a regression model on the most dominant woody species while herbaceous biomass was determined using destructive sampling.
The preliminary SLA for top and branches and belowground biomass were estimated using qualitative descriptions from the FIA field guide [14] and other studies documenting structural loss by decay class and tree component [5, 10, 16, 17].
Spatiotemporal (sites, seasons and tidal levels) variations in isotopic ratios of basal food sources and macrobenthic consumers, and also the contribution of sources to the diet of representative species and the whole macrobenthic biomass were estimated using Isosource mixing model.
Fish numerical abundance and biomass were estimated using a modified, Bohnsack stationary point count (SPC), with a radius of 7.5 m [52].
The preliminary SLA for top and branches and belowground biomass were estimated using qualitative descriptions from the FIA field guide [ 14] and other studies documenting structural loss by decay class and tree component [ 5, 10, 16, 17].
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Biomass was estimated using TLS-derived volume, then compared with destructive samples to assess the estimation accuracy.
Tree biomass was estimated using current biomass allometric equations for Australia.
Aboveground live wood biomass was estimated using allometric equations developed from 113 felled trees.
Biomass was estimated using methodology recommended by FAO and soil erosion was estimated using the universal soil loss equation (USLE).
Anchovy biomass was estimated using NASC values, the fish target strength by size and the dimension of the surveyed area.
In the field survey, physiognomic and structural aspects of primary forest and regrowth were collected and afterwards the biomass was estimated using allometric equations based on dendrometric parameters.
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