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Each 10 m × 10 m quadrat provided a single sample.
We found a delay effect that the increase rate of the species richness and cumulative species richness peaked earlier in landslide scale than that in 2 m × 2 m quadrat scale.
In the second experiment, we monitored small mammals over eight consecutive weeks in a 160 m×170 m quadrat enclosing a 20 m-thinned forest strip and a clear-cut to investigate some aspects of the role of riparian strips at the landscape scale.
We designated ten 1 m × 1 m quadrat plots at each of the 15 sites (Figure 2).
Forest floor was determined by gathering all organic material lying on the forest floor within 0.52 m × 0.52 m quadrat followed by the clipping of understory biomass.
We counted all individuals visible within each 2.5×2.5 m quadrat (subplot).
Similar(49)
Vegetation data were collected in 5 × 1 m quadrats along transect lines perpendicular to the riverbank between 172 m and 178 m elevation.
Randomly selected 10 × 10 m quadrats within the larger, 1 km2 study areas were completely surveyed for seagrass cover by divers at 0.625 m2 resolution (fine scale).
A nested sampling design of 20 × 20 m, 10 × 10 m, 5 × 5 m and 1 × 1 m quadrats was employed to study species richness of three categories of plants: herbaceous plants, shrubs and trees.
The effect of spatial scale on the processes that influence habitat selection was investigated using GIS as a tool to create and test models at a hierarchical range of scales from 200 m grid-sites level to 20 m quadrats.
The leading species in the 2 m × 2 m quadrats became more and more diversified in both herb and shrub layer, and substitution of leading species was obviously observed.
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