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The trees grew in 9 (T cordata) or in 13 (B pendula) sampling sites of tree stands planted along roadsides in the upland part of the city of Nizhni Novgorod (Russia).
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Table 1 Description of the study sites Site Year of tree fall Elevationa (m a.s.l).l
Table 1 Description of the study sites Site Year of tree fall Location [lat (°N) long (°E)] Elevationa (m a.s.l).l
Kfs was measured at depth 0.04 0.15 m using a constant head well permeameter across four paired landcover sites of adjacent tree and intensely grazed grassland.
Table 1 Summary of the different wood density datasets that were used to develop the various models Five-ring density samples at breast-height Disc-level data collected on felled trees Ring-level densitometry data at breast-height Region Number of sites Number of trees Age (years) Number of sites Number of trees Age (years) Number of sites Number of trees Age (years) Min.
Fig. 6 Relative climatic favorability of occupied sites for tree species over 90 years of A2 climate change under suppressed, historical, and future fire regimes.
We used a hierarchical community model to examine how attributes of retention sites (number of trees and snags, distance to forest edge) were associated with the species richness of birds using the sites.
This mechanism also provides a wide range of regeneration sites for tree species that have different environmental requirements (e.g. [ 1]).
Firstly, windfalls affect not only the site of the tree knocked over itself but also neighbouring sites due to the damage caused by the tree falling over.
To analyse the effects of the study site and the age of the trees on leaf damage, we constructed another GLMM by using treatment, study site, age of trees, and sampling time as fixed effects.
There was no spatial auto-correlation between distance and die-off severity among sites, and sites with greater levels of tree mortality were associated with proxies indicating degradation.
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