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<br />APPENDIX B <br /> <br />WATER EFFECTS ON WIND EROSION 8USCEPTIBILITY OF <br />THREE EASTERN MONTANA GRASSLANDS <br /> <br />by <br /> <br />Brent M. Haglund <br /> <br />Introduction <br /> <br />Both society in general and the agriculturists who depend upon the land's <br />productivity are concerned with the environmental consequences of grassland <br />management as well as its economic aspects. Episodes of severe wind erosion <br />have produced action for soil conservation in North America (Sheridan, 1981). <br /> <br />The northern Great Plains of this continent, including much of Montana, is <br />one of several geographic areas where soil productive potential has been <br />greatly lowered by wind erosion. Both wind and water erosion increase sharply <br />during dry weather (Soil Conservation Service, 1982). Diminished protective <br />plant cover exposes more ground, and increasing surface wind speeds add to the <br />transport of dry clay and silt particles (Fuchs, 1979). <br /> <br />The potential for wind erosion is affected by soil moisture (the most <br />ecologically important result of precipitation) and community types of <br />grasslands established by land management practices of ecosystem succession <br />(Buckhouse et al., 1980). Land management practices can alter wind erosion <br />potential (Troeh et al., 1980). <br /> <br />Cultivation is the major factor in soil moisture, because it exposes soil <br />to the wind, producirLg susceptibility to wind erosion. Range p10wi.ng and <br />reseeding to establish tame pastures for spring grazing have not bE!en assessed <br />for wind erosion potentials, but might increase it by producing mOI'e bare <br />ground, destroying cryptogam mats, and introducing species with less resistance <br />to wind movement (Fuchs 1979; Marshall 1971). <br /> <br />Climax or more mature communities are believed to be more resistant to <br />nutrient losses than early seral stage communities (Odum 1969; Vitousek et al. <br />1979), and so may be less susceptible to wind erosion. Native northern Great <br />Plains grasslands tend to include both relatively high-yielding C3 <br />photosynthetic pathway species (e.g., Agropvron, smithii and St1pa ~!.) and <br />more water-use efficient, but perhaps lower-yielding C4 type species such as <br />Bouteloua gracilis and BUch10e dactv10ides (KUchler, 1964). <br /> <br />Site Descriptions <br /> <br />The experiments were done in 1979 at three sites within 15 km of Miles <br />City, Montana, on the USDA Livestock and Range Research Station. A.t Miles City <br />the past 30-year average annual precipitation is 355 mm. More detailed weather <br /> <br />61 <br />