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2002-07-08_GENERAL DOCUMENTS - M2002004 (3)
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2002-07-08_GENERAL DOCUMENTS - M2002004 (3)
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DRMS Permit Index
Permit No
M2002004
IBM Index Class Name
GENERAL DOCUMENTS
Doc Date
7/8/2002
Doc Name
ATTACHMENT, PART 2
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204 <br />OPER <br />t /ha, compared to 32 t /ha on bare rt #cats Yado no <br />topsoil loss was observed on reclain ea, iOE percent sropes (loamy texture) <br />with 3.36 t /ha of crimped -in straw (63). <br />In summary, organic matter applied and incorporated or in -situ reduces <br />erosion. Erosion rates on bare topsoil with high organic matter levels are 25 <br />to 75 percent lower than on bare soils with low organic matter levels. Ap- <br />plications of straw mulch in excess of about 3.0 t /ha probably will reduce <br />erosion to barely measurable levels. <br />Climate. In the mining areas of the arid and semiarid West annual <br />precipitation ranges from 15 to 46 cm. While a few mining sites in moun- <br />tainous areas or in the Northwest receive 45 to 125 cm, plant growth at most <br />western mine sites commonly is limited by water stress related to low <br />precipitation. Also, precipitation often occurs as short - duration, high - <br />intensity rainstorms or rapid snowmelt. Moderate to high infiltration and <br />percolation rates in the upper part of the soil profile, which are influenced <br />by organic matter levels and additions of mulch, are important for minimiz- <br />ing erosion and maximizing water storage and intake. <br />Again, higher organic matter levels increase infiltration rates and the <br />water- holding capacities of soils with various textures. Also, vesicular ar- <br />buscular mycorrhiza populations tend to increase the effective root surface <br />area for absorption of water and nutrients. Both of these mitigative charac- <br />teristics of organic matter tend to maximize the use of precipitation in <br />semiarid areas. <br />Effects of topsoil stockpiling on organic matter. Based on studies in <br />North Dakota and Wyoming, long -term stockpiling is detrimental to topsoil <br />in arid and semiarid mining environments (21). Four years after direct re- <br />placement, native vegetation production on topsoil that had not been stock- <br />piled was five times greater than that on a similar area covered with topsoil <br />that had been stockpiled for 2 years. The researchers attributed the differ- <br />ence to adverse changes in organic matter. <br />Several factors affect humus formation in soil, and stockpiling affects <br />many of these factors. Assuming the stripped area originally supported a <br />dynamic plant community, the following factors of organic matter forma- <br />tion are likely to be affected: soil organisms, moisture, temperature, 0 sup- <br />ply, and plant material supply. <br />The first and most obvious change occurring to buried topsoil is the loss <br />of a large seasonal addition and smaller daily additions of dead plant tissue <br />(future humus). After the initial decay of easily decomposable carbo- <br />hydrates, amino acids, and proteins, more slowly decomposable lignins, <br />tannins, fats, oils, waxes, and other substances continue to decay. Mi- <br />crobial communities in the soil directly or indirectly compete with one an- <br />other for the slowly declining supply of organic residues when moisture, <br />temperature regime, and 0 supply are decreasing. The composition of mi- <br />SOIL ORGANIC MATTER <br />crobial communities changes as a <br />(21, 40). <br />Changes in organic matter leve <br />cation within the stockpiled tops( <br />out establishing vegetation on a t <br />found the organic matter levels d <br />the stockpile compared to the inte <br />that the natural wetting and dry <br />greater availability of organic r <br />than on the interior of the stocl <br />breaks down, water - soluble orga <br />With respect to topsoil stockp <br />that vesicular - arbuscular mycorr <br />terior of the stockpile and that <br />potential of the soil (65). Simila <br />relatively few vesicular - arbuscula <br />years old. In Wyoming one scien <br />arbuscular mycorrhiza infection I <br />age (52). Thus, vesicular - arbusc <br />plant roots in the interior of the s <br />certain interval of stockpile stor; <br />In summary, the microbial po <br />arbuscular mycorrhiza growth in <br />time with reduced 0 levels, reduc <br />supply, and loss of plants and rc <br />sition of the readily decomposa <br />followed by CO organic residuf <br />responsible for this process in t <br />and not deteriorate further (4). <br />Soil sampling for organic mate <br />tions, scientists use soil color a: <br />content in soils with less than 12 <br />tion factors that influence orga' <br />soil map unit to the next, the th <br />accordingly. As a result, under <br />matter field characteristics (col <br />that determine those characteri <br />conditions. <br />A taxonomically based soil st <br />for field characterization of bas( <br />the soil taxonomic system outli <br />survey should be conducted by <br />characteristics and soil - forming <br />
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