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                  <gco:CharacterString>Entity and Attribute Overview: Ecosystem rarity was determined through the calculation of a rarity index through the following steps: 1. The USGS GAP Analysis landcover data (Version 2, 2011) was used to identify the natural terrestrial ecosystems of the United States. This means that landcover types relating to open water and human use ( i.e. urban, agriculture, or plantation forests) were removed from the landcover data set. 2. These natural ecosystems were then grouped into their corresponding spatial pattern category, of which there are four. These four patterns are each defined by set criteria and include a discussion of disturbance regimes and are derived from the work of Comer et al. 2003. Small patch forming systems are defined as those that form small, discrete areas of vegetation cover, typically limited in distribution by localized environmental features. In undisturbed conditions, typical occurrences range from 1-50 ha (2.47 - 123.5 acres). Large patch forming systems are defined as systems that form large areas of interrupted cover and typically have narrower ranges of ecological tolerances than matrix types. Individual disturbance events tend to occupy patches that can encompass a large proportion of the overall occurrence (e.g. &gt;20%). In undisturbed conditions, typical occurrences range from 50-2,000 ha (123.5 - 4940 acres). Matrix forming systems are defined as those that form extensive and contiguous cover, occur on the most extensive landforms, and typically have wide ecological tolerances. Disturbance patches typically occupy a relatively small percentage (e.g. &lt;5%) of the total occurrence. In undisturbed conditions, typical occurrences range in size from 2,000 to 100,000 ha (4940 - 247,000 acres). Linear systems are defined as systems that occur as linear strips and are often ecotonal between terrestrial and aquatic ecosystems. In undisturbed conditions, typical occurrences range in linear distance from 0.5 to 100 km (0.31 - 62 miles). 3. Within the four spatial pattern categories, the ecosystems were aggregated up a taxonomic level (within the National Vegetation Classification (NVC) hierarchy) to the macrogoup. The NVC macrogroups are defined as subcontinental or regional communities differing by mesoclimate, geology, substrate, hydrology, and disturbance regimes (Faber-Langendoen et al. 2009). Many of the ecosystems in the GAP Version 2 dataset are similar to one another. This raised the question of whether or not the ecosystem unit was the correct scale to consider for the conservation of biodiversity. For example, there are six ecosystems with titles that begin with "Southern Coastal Plain Nonriverine Basin Swamp." Each of these six systems has a unique modifier associated such as "Okefenokee Bay/Gum Modifier" or "Okefenokee Pine Modifier;" yet these six systems seem comparable enough to act as habitat substitutes for one another. To deal with the potential niche overlap of the individual ecosystems, we aggregated up a level in the NVC hierarchy to the macrogroup level. Aggregating the ecosystems into macrogroups assures adequate variability in species assemblages, both plant and animal, between ecological communities considered in calculating the rarity metric. 4. We have first sorted the ecosystems into their corresponding spatial patterns in order to rank relative rarity amongst comparable systems. Next, we aggregated the systems within each spatial pattern type up to the macrogroup level to reduce habitat niche overlap that may exist at the finer ecosystem scale. This sorting of ecosystems by spatial pattern category followed by aggregation to the macrogroup level created a unique set of ecological entities that could not be referred to as either ecosystems or macrogroups. We refer to this unique set as ecoforms, of which there are 199. We ranked each of the four spatial pattern sets of ecoforms by descending area (i.e. the ecoform with the greatest area is ranked as 1, then the ecoform with the second greatest area is ranked as 2 etc...). We then divided this rank by the total number of ecoforms in each spatial pattern set. This ratio was then normalized by multiplying by 100 and rounding to the nearest integer. This gives us an index of rarity ranging from 0 (common) to 100 (rare). 5. A threshold value of 75 was selected; thus defining ecoforms (and corresponding ecosystems) with index values &gt; 75 as rare. 6. The GAP Version 2 landcover raster was reclassified to this raster with 5 values. The 0 values represent all the GAP landcover codes that are not identified as rare by this index. The 1 values represent all the large patch forming ecosystems identified as rare. The 2 values represent all the linear ecosystems identified as rare. The 3 values represent all rare matrix forming ecosystems. The 4 values identify all the rare small patch type ecosystems. References: Comer, P., D. Faber-Langendoen, R. Evans, S. Gawler, C. Josse, G. Kittel, S. Menard, M. Pyne, M. Reid, K. Schulz, K. Snow, and J. Teague. 2003. Ecological systems of the United States: A working classification of U.S. terrestrial Systems. NatureServe, Arlington, VA. Faber-Langendoen, D., D. L. Tart, and R. H. Crawford. 2009. Contours of the revised U.S. National Vegetation Classification Standard. Bulletin of the Ecological Society of America 90:87-93. GAP, USGS. 2011a. National Landcover, Version 2. GAP, USGS. 2011b. Protected areas database of the United States (PADUS) version 1.2. Entity and Attribute Detail Citation: https://www.epa.gov/enviroatlas/enviroatlas-fact-sheets</gco:CharacterString>
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