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2020-10-27_PERMIT FILE - C1981035 (20)
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2020-10-27_PERMIT FILE - C1981035 (20)
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Last modified
1/9/2025 5:13:41 AM
Creation date
12/1/2020 12:23:52 PM
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Template:
DRMS Permit Index
Permit No
C1981035
IBM Index Class Name
Permit File
Doc Date
10/27/2020
Doc Name
Page 251-303
Section_Exhibit Name
KII Appendix 18 Lease Modification Final EA (Page 251-303)
Media Type
D
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Biological Assessment <br /> Federal Coal Lease Modification(COC-62920)and Federal Mine Permit(CO-0106A)Revision and Renewal <br /> Measured concentrations of mercury in MRG fish tissue ranged from 0.012 to 0.093 mg/kg wet <br /> weight(NMED 2008). When compared to concentrations detected from the 1997-98 BEST <br /> study, mercury showed decreases in concentrations in the MRG over time. In addition, these <br /> baseline Hg concentrations do not exceed adult fish body burden benchmarks of 0.20 mg/kg wet <br /> weight(Beckvar et al. 2005 as cited in USFWS 2014) and 0.8 mg/kg wet weight(AECOM 2013 <br /> as cited in USFWS 2014). These adult fish body burden benchmarks are intended to represent <br /> tissue burdens below which adverse effects in fish are unlikely (USFWS 2014). <br /> The average adult body burden for mercury for the Rio Grande silvery minnow is about <br /> 0.05 µg/g wet weight mercury (Lusk et al. 2012). The Tij eras plant mercury emissions would not <br /> likely increase those average concentrations above the 0.2 µg/g wet weight that is intended to be <br /> indicative of potential fish injury (Beckvar et al. 2005). <br /> Numerous studies have shown that within a species the older and larger fish have higher <br /> concentrations of mercury than younger and smaller fish(Huckabee et al 1979; Eisler 1987). <br /> In addition, studies suggest that predatory fish tend to have higher mercury levels than <br /> omnivorous or herbivorous species (ATSDR 1999; Eisler 1987). Hence, the likelihood of <br /> bioaccumulation of mercury in silvery minnow is further limited by their small size and short life <br /> span, and that they are non-piscivorous. Therefore, the determination of effect for the Proposed <br /> Action is may affect, not likely to adversely affect the Rio Grande silvery minnow. <br /> There would be no impacts to critical habitat constituent elements for the Rio Grande silvery <br /> minnow in the Rio Grande due to coal combustion from the Tij eras cement plant. Constituent <br /> elements of critical habitat for this species pertain to hydrologic flow, the seasonality of flow, <br /> water temperature, and substrate materials. Small releases of mercury via cement plant emissions <br /> 15 miles to the east would not change any these constituent elements; consequently, there would <br /> be no impacts to designated critical habitat of the Rio Grande silvery minnow. <br /> 6.2.2 Greenback Cutthroat Trout <br /> The Western Airborne Contaminants Assessment Project was completed by the National Park <br /> Service in 2008 (Landers et al. 2008). From 2002 to 2007, researchers analyzed the <br /> concentrations and biological effects of airborne contaminants in air, snow, water, sediments, <br /> lichens, pine needles, and fish in eight national parks, including Rocky Mountain National Park <br /> in Colorado. The study found that mercury levels in fish samples were low, although mercury <br /> levels increased with increasing age of fish. Poorly developed testes and or intersex trout were <br /> found in five of the nine lakes tested, indicating that endocrine and reproductive disruption was <br /> occurring (Landers et al. 2008). As part of this study, a sample from a male greenback cutthroat <br /> trout collected in Twin Lakes in the 1800s was also examined and found to be an intersex fish, <br /> showing that this is not a new phenomenon and likely does not pose a significant threat to <br /> greenback recovery. <br /> July 2017 <br /> 32 <br />
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