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The dry matter values for standing crops, net production, litterfall etc. of both undisturbed and disturbed stands were converted to C (Figs. 3 and 4).
The largest BCP biases were found in recently disturbed stands and the largest SCP biases were seen in locations where moss necro-masses were abundant.
Less disturbed stands were characterized by lower levels of local autocorrelation for canopy height and higher levels of vertical diversity of LiDAR returns.
We compared forest structure and regeneration patterns between undisturbed and disturbed stands 30 years after a typhoon event in the treeline ecotone of the Changbai Mountains, Northeastern China.
Therefore, our results showed that the ecological distance from naturally disturbed stands was lower after CLAAG than after the other silviculture scenarios.
After cutting abundance of 5 of 10 species was smaller in disturbed stands and only 2 species had increased abundance with aggregate retention.
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Regeneration of harvested or otherwise severely disturbed forest stands typically occurs in four stages: (1) stand initiation and regeneration stage, (2) thinning or stem exclusion stage, (3) transition or understory regeneration stage, and (4) steady-state or old-growth stage.
Disturbed deciduous stands were larger C-sinks (NEP2004 = 150 gC m−2 yr−1) than undisturbed coniferous stands (e.g. NEP2004 = 8 gC m−2 yr−1).
Hartmann, M., Lee, S., Hallam, S. J. & Mohn, W. W. Bacterial, archaeal and eukaryal community structures throughout soil horizons of harvested and naturally disturbed forest stands.
Severely disturbed wildfire stands had a higher proportion of colonizing native species as well as non-native species than other structural types, and areas protected from grazing produced greater standing crop of native forbs compared to grazed unmanaged stands.
Various types and sequences of silvicultural treatments are applied to harvested or disturbed forest stands both to assist natural regeneration and to improve yields.
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