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Low risk of SAD equals current aspen distribution coincident with the 2030 SAD climatic envelope classes, Potential aspen climatic envelope expansion, or No expected change in aspen climatic envelope.
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Geospatial data sets for the Wyoming Basin REA spatially quantify explicit cumulative effects and provide a broad-scale ecological context for decision-making and planning that cannot be determined using local-level information.
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The potential effect of development on patch size was used as an index of fragmentation. Patch size was quantified for relatively undeveloped patches (Terrestrial Development Index scores less than or equal to 1 percent) of sagebrush steppe. Because TDI is calculated for a 2.25 km radius moving window, relatively undeveloped patches are defined at this analysis scale. Patch sizes for relatively undeveloped areas can then be compared to baseline conditions.
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Some of the CYR rasters intentionally do not align or have the same extent. These rasters were not snapped to a common raster per the authors' discretion. Please review selected rasters prior to use. These varying alignments are a result of the use of differing source data sets and all products derived from them. We recommend that users snap or align rasters as best suits their own projects. - The Relative Flammability raster is a spatial representation of the total number of times each pixel within the Central Yukon REA boundary burned in 1,000 simulations of the Alaska Frame-Based Ecosystem Code (ALFRESCO) model. Pixel counts of simulated burns from 200 runs each of five downscaled Global Climate Models (cccma_cgcm3_1,...
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Average percent of land cover accounted for by herbaceous cover in the Wyoming Basins Ecoregional Assessment area (5 km scale), a summary of the percent cover of herbaceous cover produced by Homer and others, 2012 (Homer, C. G., C. L. Aldridge, D. K. Meyer, and S. J. Schell. 2012. Multi scale remote sensing sagebrush characterization with regression trees over Wyoming, USA: laying a foundation for monitoring. International Journal of Applied Earth Observation and Geoinformation. 14: 233 to 244.), by running the focalsum command in ArcGIS Spatial Analyst
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Some of the YKL rasters intentionally do not align or have the same extent. These rasters were not snapped to a common raster per the authors' discretion. Please review selected rasters prior to use. These varying alignments are a result of the use of differing source data sets and all products derived from them. We recommend that users snap or align rasters as best suits their own projects. - This file includes a downscaled projection of decadal mean Day of Thaw (in ordinal dates) for the decade 2060-2069 at 771x771 meter spatial resolution. Day of Thaw approximates when the running mean rises above 0°C. Although raster values represent ordinal dates, the values 0 and 365 are special classes. A value of 0 indicates...
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Current (2015), Medium (2040), and High Scenario (2040) landscape condition and Current (2015), Medium (2040), and High Scenario (2040) landscape condition at 5th-level HUC resolution. 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...
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Core area risk is classified by the percent of aspen that is core area, summarized by township. Core area was defined as aspen greater than 60 m from nonforest edges and roads or railroads.
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Ranks of landscape level ecological risks for pygmy rabbit, summarized by township, in the Wyoming Basin Rapid Ecoregional Assessment project area. Landscape level risk based on Terrestrial Development Index (TDI). Risk classes based on mean TDI score by township. Lowest risk corresponds to TDI less than 1, medium risk corresponds to TDI 1 to 3, Highest risk corresponds TDI greater than 3. See table 27.3 and appendix in the Wyoming Basin REA report at http://pubs.er.usgs.gov/publication/ofr20151155 for additional details.
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The potential effect of development on patch size was used as an index of fragmentation. Patch size was quantified for baseline conditions for pygmy rabbit. This provides a reference for comparing patch size for relatively undeveloped patches (Terrestrial Development Index scores less than or equal to 1 percent) of pygmy rabbit.
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This polygon feature class describes areas used for subsistence harvesting of moose in 2011 by surveyed households in Takotna, Alaska. This is a partial representation of areas used for resource harvesting in 2011.
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This feature class describes areas used for subsistence harvesting of sheefish by surveyed households in Ruby, Alaska. This is a partial representation of areas used for resource harvesting.
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Some of the YKL rasters intentionally do not align or have the same extent. These rasters were not snapped to a common raster per the authors' discretion. Please review selected rasters prior to use. These varying alignments are a result of the use of differing source data sets and all products derived from them. We recommend that users snap or align rasters as best suits their own projects. - This file includes a downscaled projection of decadal Active Layer Thickness and Seasonally Frozen Layer Thickness (m) for the decade 2020-2029 at 2km spatial resolution, using the A2 emissions scenario. The raster contains both negative and positive values. Positive values relate to the active layer thickness, or depth of...
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This polygon feature class describes areas used for subsistence harvesting of brown bear in 2011 by surveyed households in McGrath, Alaska. This is a partial representation of areas used for resource harvesting in 2011.
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This feature class describes areas used for subsistence harvesting of sheefish by surveyed households in Galena, Alaska. This is a partial representation of areas used for resource harvesting.
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This data depicts random points generated within ESRI modelbuilder. The methodology to generate these points is documented within the Current Subsistence toolbox, model: YKL_DV_B_C_Subsistence_Step1_RiverSegments.
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This data depicts pipeline locations in Alaska as digitized primarily from 1:24,000, 1:63,360, and 1:250,000 USGS quadrangles. The source document that represented the newest information and best geographic location was used to capture the data. All infrastructure from the primary source document was digitized and then supplemented with the information from other source documents for additional or updated infrastructure or attributes.
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Some of the YKL rasters intentionally do not align or have the same extent. These rasters were not snapped to a common raster per the authors' discretion. Please review selected rasters prior to use. These varying alignments are a result of the use of differing source data sets and all products derived from them. We recommend that users snap or align rasters as best suits their own projects. - This file includes a downscaled projection of decadal average of winter (December, January, February) total precipitation (in millimeters) for the decade 2050-2059 at 771x771 meter spatial resolution. The file represents a decadal mean of seasonal totals calculated from monthly totals, using the A1B emissions scenario. The...


map background search result map search result map BLM REA WYB 2011 Average percent cover of herbaceous vegetation, summarized at 5 km BLM REA WYB 2011 Invasive Species Locations in WYBREA, points BLM REA WYB 2011 WFDSS Interagency Historic FirePerimeters 20120608 v1 BLM REA WYB 2011 Sagebrush Steppe Relatively Undeveloped Patches 15m BLM REA WYB 2011 Foothills Aspen Distribution Functional Type no null values BLM REA WYB 2011 TS C ASPEN RISK Poly Ch15 Fig16a BLM REA WYB 2011 Aspen Low Risk of Sudden Aspen Decline BLM REA WYB 2011 Pygmy Rabbit Patches Baseline BLM REA WYB 2011 Pygmy Rabbit Ecological Risk BLM REA CYR 2013 Future Relative Flammability from 2000 to 2099 BLM REA YKL 2011 CL L WinterTotalPPT2050s A1B BLM REA YKL 2011 Alaska Pipelines 1:63,360 BLM REA YKL 2011 YKL Subsistence River Segment points in the Yukon River Lowlands - Kuskokwim Mountains - Lime Hills BLM REA YKL 2011 Subsistence Harvest Areas of Sheefish (polygons) in Galena, Alaska. BLM REA YKL 2011 Subsistence Harvest Areas of Brown Bear in McGrath, Alaska. BLM REA YKL 2011 PF N ActiveLayerThickness A2 BLM REA YKL 2011 Subsistence Harvest Areas of Sheefish in Ruby, Alaska. BLM REA YKL 2011 Subsistence Harvest Areas of Moose in Takotna, Alaska. BLM REA NOS 2012 Landscape Condition Figures F2 to F3 BLM REA YKL 2011 Subsistence Harvest Areas of Sheefish (polygons) in Galena, Alaska. BLM REA YKL 2011 Subsistence Harvest Areas of Sheefish in Ruby, Alaska. BLM REA YKL 2011 Subsistence Harvest Areas of Brown Bear in McGrath, Alaska. BLM REA YKL 2011 Subsistence Harvest Areas of Moose in Takotna, Alaska. BLM REA WYB 2011 Invasive Species Locations in WYBREA, points BLM REA WYB 2011 TS C ASPEN RISK Poly Ch15 Fig16a BLM REA WYB 2011 Pygmy Rabbit Ecological Risk BLM REA WYB 2011 Sagebrush Steppe Relatively Undeveloped Patches 15m BLM REA WYB 2011 Foothills Aspen Distribution Functional Type no null values BLM REA WYB 2011 Average percent cover of herbaceous vegetation, summarized at 5 km BLM REA WYB 2011 Pygmy Rabbit Patches Baseline BLM REA WYB 2011 Aspen Low Risk of Sudden Aspen Decline BLM REA YKL 2011 YKL Subsistence River Segment points in the Yukon River Lowlands - Kuskokwim Mountains - Lime Hills BLM REA YKL 2011 CL L WinterTotalPPT2050s A1B BLM REA YKL 2011 PF N ActiveLayerThickness A2 BLM REA CYR 2013 Future Relative Flammability from 2000 to 2099 BLM REA NOS 2012 Landscape Condition Figures F2 to F3 BLM REA YKL 2011 Alaska Pipelines 1:63,360 BLM REA WYB 2011 WFDSS Interagency Historic FirePerimeters 20120608 v1