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2023-06-29_PERMIT FILE - C1981019A (2)
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2023-06-29_PERMIT FILE - C1981019A (2)
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Last modified
7/11/2024 9:41:43 AM
Creation date
9/27/2023 8:50:25 AM
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Template:
DRMS Permit Index
Permit No
C1981019A
IBM Index Class Name
Permit File
Doc Date
6/29/2023
Doc Name
Volume 1 Rule 4
Section_Exhibit Name
4.01 Through 4.30
Media Type
D
Archive
Yes
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RULE 3 PERFORMANCE BOND REQUIREMENTS <br /> <br />Rule 4 Performance Standards 4-42 Revision Date: 6/13/23 <br /> Revision No.: MR-247 <br /> <br />Native soil, collected from the locally source ecosystems on or directly adjacent to Colowyo Mine <br />exhibiting similar tall shrubs species as being implemented in the trial, will be used to inoculate <br />the test sites with beneficial mycorrhizae. Mycorrhizae are symbiotic relationships that form <br />between fungi and plants. The fungi colonize the root system of a host plant, providing increased <br />water and nutrient absorption capabilities while the plant provides the fungus with carbohydrates <br />formed from photosynthesis. Once the mounding is completed and prior to installation of weed <br />guard fabric, locally sourced soils (containing local mycorrhizae) will be scattered at random on <br />the mounded surface. Care will be taken to ensure these soils are place around where the tubling <br />will be planted and under the weed guard fabric. <br /> <br />Weed guard fabric will also be placed around the tubelings, with limited opening size in the weed <br />guard fabric to plant the tubeling. This should help assist in limiting competition from moisture <br />from other plants. The final step will be to broadcast seed the entire trial area with the seed mixture <br />presented on Table 2.05-8. No other manipulation of the trial area will occur post construction to <br />limit annuals, but if necessary noxious weeds will be controlled during the entire trial period. <br /> <br />Colowyo will monitor the survival of planted tall shrubs annually for three years following <br />planting. The primary purpose of this approach to test plots is to identify areas that already exhibit <br />favorable conditions to establish tall shrubs, rather than try to replicate those conditions. <br /> <br />4.15.7 Determining Revegetation Success: General Requirements and Standards <br /> <br />Three reference areas have been selected to represent the three major vegetative communities to <br />be disturbed, sagebrush, mountain shrub, and aspen. The locations of these reference areas are <br />shown on Map 4. Detailed vegetative sampling was performed on these reference areas as <br />described in Section 2.04.10. <br /> <br />The reference areas were sampled for herbaceous cover, herbaceous production and woody plant <br />density. Species diversity was determined utilizing herbaceous cover data from the premining <br />inventory of the sagebrush, mountain shrub, and aspen communities. The reference areas are each <br />approximately seven acres in size. <br /> <br />Statistical tests were performed on the vegetative data from the reference areas to prove that they <br />were comparable to the premined area. The parameters compared were herbaceous cover and <br />herbaceous production. Revegetation success will be determined by comparisons of weighted <br />averages between reference areas and revegetated areas in accordance with Rule 4.15.7(4) (b). <br /> <br />For demonstration of revegetation success, vegetation cover, herbaceous production, and in certain <br />circumstances woody plant density will be sampled to statistical adequacy (where necessary), and <br />compared to the revegetation metrics described in Section 4.15.8 below. Sampling methodologies <br />and statistical testing utilized for bond release evaluations are described in Section 4.15.11. <br /> <br />To summarize, there are three reference areas, the Mountain Shrub reference area, Sagebrush <br />reference area, and Collom Aspen reference area that are utilized to evaluate revegetation success
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