Filters: Tags: Other Conifer (X)
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A 10 km moving window was used on the Other Conifer conservation element to determine the relative density of Other Conifer within the moving window.
The FSim burn probability was used to determine the burn probability of the other conifer vegetation communities. This layer was used in the intactness management question and the results weren't rolled up to an analysis unit.
The FSim burn probability was used to determine the majority (most common) burn probability within a 4km analysis unit in areas with other conifer vegetation communities withing the ecoregion.
Other Conifer Locations within the Ecoregion. These data are provided by Bureau of Land Management (BLM) "as is" and may contain errors or omissions. The User assumes the entire risk associated with its use of these data and bears all responsibility in determining whether these data are fit for the User's intended use. These data may not have the accuracy, resolution, completeness, timeliness, or other characteristics appropriate for applications that potential users of the data may contemplate. The User is encouraged to carefully consider the content of the metadata file associated with these data. The BLM should be cited as the data source in any products derived from these data.
Other Coniferwas analyzed against Disease Change Agents by computing the euclidean distance from disease other conifer stands. The resulting dataset was used in the intactness calculation.
Other Conifer was analyzed against Disease Change Agents by computing the euclidean distance from diseased other conifer stands and then calculating the average value within the 4km analysis unit.
Other Conifer vegetation communities were extracted from state ReGAP and Landfire Exisitng Vegetation (California only). The individual rasters were mosaiced to create a single raster than represent aspen with the NGB ecoregion.
Development change agents were mosaiced together and the euclidean distance was calculated. Other Conifer communiities were used to extract the distances. The resulting layer was used in the intactness calculation.
Development change agents were mosaiced together and the euclidean distance was calculated. Other Conifer communiities were used to extract the distances then zonal statistics calculated the average within the 4km analysis unit.
Other Conifer cummulative score was based on ranking burn probability, distance to disease and distance to development into three categories (1 lowest quality - 3 highest quality). The layers were added together to yield scores ranging from 3 (lowest quality in all three layers) - 9 (highest quality in all three layers).
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