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2002-07-08_GENERAL DOCUMENTS - M2002004 (4)
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2002-07-08_GENERAL DOCUMENTS - M2002004 (4)
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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 3
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HABITAT MGMT
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DRMS
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D
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8 COLORADO SCHOOL OF MINES RESEARCH INSTITUTE <br />dried at 70 °C for 24 hr to obtain a wet -to -dry weight conversion factor. This <br />factor was then applied to the wet weight field data to convert the individual <br />strip and row weights to a dry weight basis. <br />Cover <br />Percentage cover of the perennial grasses was quantitatively determined in <br />1981 by measuring, with a tape measure, grass occupancy for each row within a <br />strip. The measurements were made following harvesting and, in essence, measured <br />the basal area coverage for each row of grass. In certain plots, sod formation <br />by thickspike and western wheatgrass precluded quantification of cover by the <br />above method; in such areas percentage basal cover was obtained by ocular esti- <br />mate <br />Rooting Depth <br />A combination gamma- neutron probe was used to monitor moisture levels and, <br />indirectly, rooting depth at four locations in each plot. Using the previously <br />mentioned access holes, the probe was lowered down the hole and moisture data <br />were collected at the 15, 30, 50, 70, 90, and 110 cm depths. According to Cable <br />(1980), a neutron probe integrates soil water content in a sphere of soil ranging <br />from 15 to 25 cm in radius around the source point. Density measurements were <br />taken at the same time using the same probe. The moisture data were converted to <br />percentage moisture by weight and graphed to show the extent of water removal. <br />It was assumed that correlations exist between soil water depletion and the rela- <br />tive quantity of roots present in the soil; a number of studies have shown that <br />this assumption is valid for a variety of situations (Bohm, 1979). During most <br />years, moisture data were collected in May, June, August, and October. <br />Plant Establishment and Tillering <br />Small subplots (0.09m were established in the spoil and soil buffer areas <br />for the purpose of quantifying plant tillering and establishment. Using a wire <br />hoop to mark the subplot boundary, sufficient soil or spoil was removed to cover <br />the seeds with 2 cm of material. A counted number of seeds (30 pure live seed <br />equivalent) was placed on the surface and the excavated material returned. Two <br />such plots were established for each species planted, one in soil and one in <br />spoil. At the end of the first growing season after planting, the number of live <br />seedlings (plant establishment) and the number of tillers per established plant <br />were recorded for each plot. <br />Water Infiltration <br />The rate of water infiltration for spoil and for soil (where soil depth was <br />approximately 152 cm) was determined using an infiltrometer as described by <br />Bertrand (1965) and Haise et al. (1956). A double -ring infiltrometer was used <br />when there was sufficient room to accommodate both rings without damaging the <br />established grasses. In many situations, there was sufficient room to accomo- <br />date only the 30 -cm- diameter inner ring. To minimize lateral water movement <br />when one ring was used, the ring was driven 10 to 18 cm into the ground. All <br />infiltration tests were conducted for a 4 -hr period. Infiltration was measured <br />at the time of plant harvesting, and ring locations were marked on a map to <br />ensure that the same location was not used in subsequent years. Infiltration <br />tests were initiated 2 years after plot establishment; the delay was to allow <br />plot settling to be essentially complete prier to infiltration testing. <br />
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