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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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8/24/2016 2:18:41 PM
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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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HABITAT MGMT
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DRMS
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196 <br />the degree of organic matter decomposi fr - ` -, is- <br />ing decomposition (14). As soil reaches oil <br />organic matter level is relatively constant. <br />Regardless of soil conditions, the direct effects of organic matter are the <br />same: generally, plants respond favorably because nutrients, especially N, <br />are provided through decomposition and mineralization (43). Campbell <br />stated, "Crop yields are often directly proportional to the N released from <br />organic matter, the other nutrients are also important but N is required in <br />much larger amounts and is more likely to be deficient" (15). <br />Effects on soil. Soil organic matter directly or indirectly influences the <br />physical environment (4). As the percentage of organic matter decreases in a <br />given soil, the bulk density increases, with an associated reduction in poros- <br />ity. The combination of increased bulk density and reduced aeration <br />restricts root growth, impairs normal root absorption, and inhibits micro- <br />biological activity. <br />Soil structure greatly influences fertility (42). Organic matter is one of the <br />most important factors in soil structure development. Soils with good struc- <br />ture provide the best conditions for supplying water and nutrients to plants <br />(42). The best water and nutrient regimes occur in soils with granular struc- <br />ture in which the aggregate size is 1 -2 mm. Such soil structure is formed <br />most readily under a mixture of perennial grasses and legumes. The <br />prerequisites for the formation of good soil structure include (1) consolida- <br />tion of the soil particles under pressure from highly branched root systems <br />of grasses, (2) the formation of humin and humic acid, (3) penetration into <br />the soil crumbs of the highly dispersed solutions of humin and humic acids, <br />and (4) conversion of these acids into a cohesive soil aggregate by means of <br />Ca supplied by the legume roots (42). <br />Also critical is the fact that conversion of humus substances into a soil <br />aggregate is irreversible under natural processes (42). After plowing or disk- <br />ing, formation of humus substances that bind soil crumbs is slow and re- <br />quires a specific environmental condition (42). Similarly, increased stability <br />of aggregates usually accompanies an increase in organic matter (15). Thus, <br />to maintain good soil structure there must be an absence of continued plow- <br />ing and a source for newly formed humus substances on a regular basis. <br />Incorporation of manure into soil influences microorganism activity. <br />Organic material itself, without biological transformation, has little effect <br />on soil structure. Microorganisms, without organic materials as a source of <br />energy, are ineffective in producing soil aggregation. Fungi and actinomy- <br />cetes produce mycelia and have metabolic processes that synthesize complex <br />organic molecules. Decomposition products remain in the soil. The sum of <br />these effects is the production of stable soil aggregates. This stability, <br />therefore, can result from the mechanical binding action of the cells and <br />filaments of the organisms; cementation effects of the products of micro- <br />SOIL ORGANIC MATTER <br />bial synthesis; and the stabilizint <br />Organic matter usually impro <br />proves drainage in fine - textured <br />deeper root systems. Collectively <br />ability and the water use efficie <br />plant species, soil type, and clim <br />effects of organic matter may in <br />matter in general increases plant <br />Organic matter increases infilti <br />surface long enough for it to en <br />condition of the soil. Organic n <br />increases the rate of infiltration. <br />soil, eventually improving soil <br />increases. Contrary to this gene; <br />increasing infiltration, some fo <br />because of the presence of hydro <br />One of the most important ch <br />tain and exchange positively <br />primary controlling factors of c: <br />clay and the quantity of organic <br />in most mineral soils accounts fc <br />exchange capacity (15). In sandy <br />the cation exchange capacity is <br />A buffer solution is one that <br />acid or base. Soils behave like be <br />colloidal properties associated • <br />hold H, Al, and other cations (, <br />soils with lower organic matter 1 <br />matter levels. <br />There is a wide range of chemi <br />ing metal cations into weakly ioi <br />ing agents —occur naturally in <br />organic fraction as well as soli, <br />Organic matter can hold meta <br />chelation (15). In soils having n <br />plants, chelation may hinder ad <br />the metallic ion. <br />Soil organic matter and re <br />Because virgin organic matt <br />within a particular mine site, t <br />levels for organic matter to rat( <br />The same is true of surface soil 1 <br />
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