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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 /> confidence that many semi-arid areas such as the western U.S. will suffer a decrease in water <br /> resources due to climate change (IPCC 2007). Milly et al. (2005)project a 10 to 30 percent <br /> decrease in precipitation in mid-latitude western North America by the year 2050, based on an <br /> ensemble of 12 climate models. <br /> Recent studies have indicated that global warming has the potential to adversely affect river <br /> systems that support greenback cutthroat trout(Defenders of Wildlife 2002; Ficke et al. 2007). In <br /> general, threats from climate change could affect fish populations through reduction of <br /> precipitation, increase in fire, and increase in stream temperature. Higher temperatures in lentic <br /> systems (lakes) also could increase evaporation and result in lowered lake levels (Ficke et al. <br /> 2007). This threat is common to all fish considered in this impact analysis. <br /> Climatic variation associated with climate change may lead to reductions in quality of habitat for <br /> all fish species evaluated. The potential impacts from climate change that could affect these <br /> species in the AA include changes in snowpack, streamflow timing, and hydrograph evolution. <br /> Changes in the timing and magnitude of runoff include earlier runoff, warmer stream <br /> temperatures, and the spread of in-stream non-native species and diseases. Changes in <br /> streamflow intensity and timing may also affect riparian ecosystems. <br /> 6.2 Effects to Listed Species and Critical Habitats <br /> There are no direct impacts expected to any federally listed species as a result of the proposed <br /> King 11 Mine lease modification or associated with revision and renewal of the mine plan permit. <br /> There are indirect impacts to listed species associated with combustion of King 11 coal at GCC's <br /> Pueblo, Colorado and Tij eras, New Mexico cement plants. <br /> The following impact analysis for each affected species is based on the relatively small <br /> contributions of mercury to the AAs from combustion of King II Mine coal. Specifically, the <br /> release of 10 to 15 pounds per year of mercury from the GCC Pueblo plant, 25 pounds per year <br /> from the Tij eras plant, and less than 0.25 pound per year from the narrow-gauge railroads. <br /> 6.2.1 Rio Grande Silvery Minnow <br /> New Mexico has adopted only one fish tissue-based criterion (methylmercury)in its water <br /> quality standards. For other parameters, SWQB used the USGS Biomonitoring of Environmental <br /> Status and Trends (BEST)Program (Schmitt 2004) screening levels for evaluation. USGS BEST <br /> mercury concentrations that affect fish health are 0.7-5.4 mg/kg wet weight. In 2008, the New <br /> Mexico Environment Department(NMED), Surface Water Quality Bureau (SWQB) concluded a <br /> study (LAMED 2008)to provide baseline condition and trends for key water quality parameters in <br /> the Middle Rio Grande (MRG) as part of a comprehensive water quality monitoring and <br /> assessment program to elucidate relationships between water-quality and declines in silvery <br /> minnow populations. The study compiled water chemistry data for sites within the study area <br /> collected between 2000 through 2008. <br /> July 2017 <br /> 31 <br />
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