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Canopy hits are then classified into<br />

vertical profile bins above the ground. Camp<br />

Ripley data was binned into 1 meter vertical<br />

profiles (Figure 8-for illustration purposes<br />

this image shows binning into 10 3m bins).<br />

The number of hits were then tallied for<br />

each bin, including the ground hits, to<br />

derive the proportion of hits falling within<br />

each vertical height bin. These are then<br />

expressed as proportions of the total hits<br />

within a designated cell size (canopy<br />

closure was defined in both 10m <strong>and</strong> 50m<br />

cells). The information in these vertical bars<br />

were then used as explanatory variables to<br />

model <strong>and</strong> estimate forest metrics. For more<br />

information on the statistical models used refer to Restani <strong>and</strong> Newton (2009).<br />

Canopy cover results can be displayed as a vertical canopy profile (histogram), where the<br />

sum of the bars equals 100%, including the ground hits (Figure 9). By examining these bars <strong>and</strong> their<br />

magnitudes we can visualize what the forest st<strong>and</strong> within a cell will look like.<br />

Figure 9.<br />

Figure 8.<br />

In addition to the binned canopy closure values,<br />

the canopy cover data set contains X <strong>and</strong> Y coordinates<br />

for the center of each cell. With these centroids a raster<br />

layer with the appropriate cell size can be generated <strong>and</strong><br />

the cells can be populated with the associated canopy<br />

cover values. This provides another method for<br />

displaying results. Figure 10 shows total canopy cover,<br />

however individual vertical profiles, or a combination of<br />

profiles, could also be displayed. These raster layers can<br />

then be used for spatial analysis within a GIS.<br />

In the spring/summer 2009, an assessment was<br />

conducted on 40 bird plots <strong>and</strong> 40 r<strong>and</strong>om points across<br />

multiple l<strong>and</strong> cover types to evaluate the accuracy of forest metric estimates. A w<strong>and</strong>ering quarter<br />

method was used to select trees r<strong>and</strong>omly in each of four quadrants (NE, NW, SW, <strong>and</strong> SE)<br />

beginning from the plot center. Trees were defined as stems ≥ 10 cm dbh with saplings defined as<br />

stems < 10 cm dbh. Trees <strong>and</strong> saplings were sampled separately for dbh (m), canopy height (m), <strong>and</strong><br />

ground-to-live canopy height (m) (trees only), as well as distance to nearest neighbor (m), which will<br />

allow for estimation of stem densities within each plot.<br />

Page 19<br />

2009 Conservation Program Report

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