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2002-07-08_GENERAL DOCUMENTS - M2002004 (2)
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2002-07-08_GENERAL DOCUMENTS - M2002004 (2)
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Last modified
8/24/2016 2:18:41 PM
Creation date
3/28/2012 3:05:03 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 1
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HABITAT MGMT
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DRMS
Media Type
D
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• r r'ul'I • r1H!✓, 1 t M t i'u tivriutt'ItrV , t �vt <br />rmurs= rIU. JYJJ cve 'v (1 <br />150 <br />J U 1 . ; ,!7 ri N�!y <br />The seeded 'all -star' species (e.g., aggressive wheatgrasses and needlegrasses) will grow equally well <br />with or without a separate topsoil strata. Where spoil material is suitable for plant growth, <br />replacement depths have little effect on cone mity composition until very shallow replacement depths <br />are used, i.e., below six inches. Uncovered spoil represents the extreme case of no soil replacement. <br />Varying soil depth and landform can increase local landscape diversity. In the natural landscape near <br />Colstrip, a mixed shrub /gumbo knob type occurs. Low shrubs include shadscale saltbush, skunkbush <br />sumac, rose, and stunted big sagebrush. The species cohabit sites on or near exposed shaley <br />sedimentary beds, with topography playing a minor role. Small areas of exposed spoil could be used <br />to an advantage in reclaimed landscapes, as long as the spoil does not contain toxic substances. These <br />patches are not prune habitat for competitive cool- season gasses due to some combination of salinity, <br />sodicity, alkalinity, or extreme texture -- habitat factors to which the hardy shrubs and associated <br />forbs are well adapted. In this example, the reclaniator seeks to favor stress- tolerators over efficient <br />competitors. The same mixed shrub species along with rubber rabbitbrush have been found to <br />colonize unseeded old spoils at Colstrip. After 50 years, Sindelar (1978) found diversity on these <br />spoils to be similar to native rangeland. <br />Low ridges (linear patches) of exposed spoil could easily be established where heavier textured spoils <br />are prevalent. Slope would not need to be steep, so as to avoid potential soil erosion problems. Soil <br />replacement depth would be thinned toward the top of the south face, with a small area of exposed <br />spoil along the "ridge_" The resulting reclaimed 'oviform would resemble a native landform in both - <br />fonn and function. The thinning soil replacement depth would approximate shallow topsoils found on <br />upper slopes of native hillsides. <br />Through erosion, some spoil would inevitably end up on top of soil. This should not matter as long as <br />the spoil is nontoxic and at most moderately plant - inhibitory. Many native plant communities in coal <br />regions occur in soils that would be considered unsuitable based on regulatory criteria (see Keck and <br />Wraith these proceedings). Seeding spoils with mixed shrubs and forbs but not grasses probably has <br />the best chance of establishing something analogous to native communities. <br />One more example will be of particular interest to redamators: establishing trees in uplands. Pines in <br />southeastern Montana are associated with areas of shallow sedimentary bedrock, usually. sandstone_ <br />Stark (1982) found that pines near Colstrip are highly dependent on the presence of large platy rocks <br />that stop infiltration and concentrate water, and that soil pH of 5-6 and rapid water infifih, ation also <br />were associated with pine germination and growth rate, but deep rooting was not. Such substrates do <br />not normally occur in postmine landscapes, and we do not expect postrnine pine abundance to <br />approach premine levels. Historical factors share responsiblility for prentine pine densities. <br />Our recommendation is to create landforms with cool north aspects where evapotranspiration will be <br />less. Replaced forest topsoil in rifer reclamation areas would be six inches or less deep; any more <br />would favor competitive grasses. Functionally, the topsoil would be used as a source of native <br />propagules so replacement soil would be topsoil salvage from pine areas. Seeding might be <br />unnecessary, or a diversity mixture only might be seeded. Pines would be planted. <br />Summing up: Where spoil provides a decent plant growth medium, a two -lift soil replacement <br />strategy is probably unnecessary in uplands but might be appropriate for gentle slopes where <br />productivity is the focus. Replaced soils should be deep on gentle slopes and thin to perhaps <br />nonexistent on some ridges where alternative plant cominututies are to be established. In areas of <br />moderate slope and relatively clean spoil, a foot of replaced soil depth may suffice to establish and <br />sustain productive grasslands. Some spoil materials are not necessarily undesirable amidst sods, and <br />some "undesirable" soil materials may be desirable with a view to diversity. Sediment deposit can be <br />an opportunity for interseeding a special seed mix. These examples model natural landscape features <br />and would greatly reduce salvage and hauling costs. This does not imply that large surface areas of <br />spoil should be part of redamation or that spoil ridges should be left behind; spoil ridges are unlike <br />natural landforms and prone to severe erosion. <br />
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