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REP36426
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REP36426
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Entry Properties
Last modified
8/25/2016 12:14:13 AM
Creation date
11/27/2007 7:27:56 AM
Metadata
Fields
Template:
DRMS Permit Index
Permit No
C1982055
IBM Index Class Name
Report
Doc Date
4/29/1999
Doc Name
INTEROFFICE MEMORANDUM RATON CREEK MINE C-82-055
From
JANET BINNS
To
KENT GORHAM
Permit Index Doc Type
ANNUAL RECLAMATION REPORT
Media Type
D
Archive
No
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<br /> <br />The ARR reports that patches of Canada thistle were sprayed with herbicide. Please <br />define when and with what specific herbicide spraying was conducted with. <br />The post-mining land use is rangeland. The revegetation success standards are 25% <br />vegetative cover. Perennial grass species shall comprise greater than or equal to 60% of <br />the cover, a minimum of 10% cover should be provided by perennial forb species, and at <br />lease 5% of the cover shall be attributable to shrub species. Grass species will need to <br />make up a minimum of 15% total cover in order for that portion of the diversity standard <br />to be achieved. <br />The 1998 vegetation sampling data indicates that on both the topsoiled and non-topsoiled <br />areas [he cover standard has been exceeded. The non-topsoiled area measured 32.67% <br />vegetative cover. The topsoiled azea was measured at 33.53% vegetative cover. <br />Distribution of the plants makes a definitive impact on the two areas. The topsoiled azea <br />has a greater percentage of grass species (16% relative cover) and a more even <br />distribution of the established plants. Few erosion rills are observed are observed on the <br />topsoiled area. The vegetation on the non-topsoiled area is dominated (90% relative <br />cover) by one species, Cicer milkvetch. Bare ground measured in the non-topsoiled area <br />exceeds that of the topsoiled azea by 19 % relative difference (43.2% vs. 36.33% <br />respectively.) Standazd deviation calculations were not submitted with the ARR <br />submittal. <br />The growth habit of Cicer milkvetch is clumped, tap-rooted deciduous species. <br />Considerable space exists between each Cicer plant. The non-topsoiled area tends to <br />form numerous rills throughout the azea. This rilling is not noted to the same extent on <br />the topsoiled slopes. On the non-topsoiled areas vegetation is not established suitable to <br />control erosion. <br />The Division is concerned that although Cicer milkvetch is a desirable reclamation <br />species, it also tends to be a short lived perennial. It's deciduous nature provides little <br />ground cover once the leaves have fallen during late fall, winter and early spring months. <br />The tap-rooted habit provides little soil cohesion compared to the mat forming fibrous <br />root systems of sod forming grass species. Review of the success standards indicates that <br />the desired vegetation will be grass dominated. Review of the sampling data does not <br />indicate that perennial grass species are establishing on the non-topsoiled area (2.2% total <br />vegetation cover is attributable to perennial grasses on the non-topsoiled area.) <br />The Division questions why Energy Fuels states that "the predominance of grass cover on <br />the topsoiled sites has been extensively criticized in numerous regulatory settings, as <br />precluding realizing goals of achieving a diverse and shrub dominated plant cover." The <br />revegetation success standard at this site has been drafred to heavily favor a grass <br />dominated community with perennial forbs and shrubs as minor components. The post- <br />mining land-use and success standazds do not encourage a diverse or shrub dominated <br />vegetation community. While the operator's statement may apply to other areas of the <br />state where heavy grass dominated rangeland has not been the desired post-mining <br />community, the opposite is the goal for successful reclamation at the Raton Creek Mine. <br />,i ',. <br />
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