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Web Soil Survey `b" ` <br />others and in• s the development of the others. The plant community on an ecological site, plant association, or habitat type is typified an association of species that differs from <br /> that of other ecological sites, plant associations, or habitat types in the kind andgortion of <br />uence <br />species or in total production. Descriptions of ecological sites are provided in the Field Office Technical Guide, which is available in local offices of the Natural Resources Conservation <br /> Service (NRCS). Descriptions of plant associations or habitat types are available from local U.S. Forest <br />Service offices. <br />Iota/dry-weight production is the amount of vegetation that can be expected to grow annually in a well managed area that is supporting the potential natural plant community. It includes <br /> all vegetation, whether or not it is palatable to grazing animals. It includes the current year's <br />growth of leaves, twigs, and fruits of woody plants. It does not include the increase in stem diameter of trees and shrubs. It is expressed in pounds per acre of air-dry vegetation for <br /> favorable, normal, and unfavorable years. In a favorable year, the amount and distribution of <br />precipitation and the temperatures make growing conditions substantially better than average. In a normal year, growing conditions are about average. In an unfavorable year, growing <br /> conditions are well below average, generally because of low available soli moisture. Yields are <br />adjusted to a common percent of air-dry moisture content. <br />Characteristic vegetation (the grasses, forts, shrubs, and understory trees that make up most of the potential natural plant community on each soil) is listed by common name. Under range/and <br /> composition and forest understory, the expected percentage of the total annual <br />production is given for each species making up the characteristic vegetation. The percentages are by dry weight for rangeland. Percentages for forest understory are by either dry weight <br /> or canopy cover. The amount that can be used as forage depends on the kinds of grazing animals <br />and on the grazing season. <br />Range management requires knowledge of the kinds of soil and of the potential natural plant community. It also requires an evaluation of the present range similarity index and rangeland <br /> trend. Range similarity index is determined by comparing the present plant community with the <br />potential natural plant community on a particular rangeland ecological site. The more closely the existing community resembles the potential community, the higher the range similarity <br /> index. Rangeland trend is defined as the direction of change in an existing plant community <br />relative to the potential natural plant community. Further information about the range similarity index and rangeland trend is available in the "National Range and Pasture Handbook," <br /> which is available in local offices of NRCS or on the Internet. <br />The objective in range management is to control grazing so that the plants growing on a site are about the same in kind and amount as the potential natural plant community for that site. <br /> Such management generally results in the optimum production of vegetation, control of <br />undesirable brush species, conservation of water, and control of erosion. Sometimes, however, an area with a range similarity index somewhat below the potential meets grazing needs, <br /> provides wildlife habitat, and protects soil and water resources. <br />Reference; <br />United States Department of Agriculture, Natural Resources Conservation Service, National range and pasture handbook. <br />l?ttp: / /websoil survey. arcs. usda. gov/app/WebSoilSurvey.aspx 2/24/2010