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Biological Assessment <br /> Federal Coal Lease Modification(COC-62920)and Federal Mine Permit(CO-0106A)Revision and Renewal <br /> Juan River Basin. A complete discussion of the baseline water quality conditions that exist in the <br /> San Juan River are detailed in the FCPP/NMEP BO (USFWS 2015) and incorporated in this BA <br /> by reference. <br /> Middle Rio Grande <br /> In 2016, the Middle Rio Grande Endangered Species Act Collaborative Program (MRGESACP) <br /> contracted with the New Mexico Environment Department Surface Water Quality Bureau <br /> (SWQB)to conduct water-quality monitoring and assessment to determine if poor water quality <br /> is contributing to the decline of Rio Grande silvery minnow populations in the Middle Rio <br /> Grande (MRG). <br /> SWQB conducted quarterly sampling of water and sediment, toxicity tests, and annual fish tissue <br /> collection and analysis at ten stations in the MRG selected by the MRGESACP. The survey <br /> extended from Bosque del Apache (downstream of San Antonio), north to the Angostura <br /> Diversion (upstream of Bernalillo), covering approximately 180 miles of river. In addition to the <br /> sampling conducted, SWQB compiled water chemistry data for sites on the MRG within the <br /> study area from other sources and earlier SWQB studies conducted from 2000 through 2008. <br /> SWQB assessed the data against water quality standards criteria contained within the State of <br /> New Mexico Standards for Interstate and Intrastate Surface Waters (20.6.4 New Mexico <br /> Administrative Code). Analysis of the data indicated dissolved oxygen levels were below the <br /> water quality criteria in the"Rio Grande (non-pueblo Alameda Bridge to Angostura Div)" and <br /> "Rio Grande (Isleta Pueblo to Alameda Bridge), aluminum concentrations were above the <br /> chronic aquatic life criteria in several locations, and water quality criteria for bacteria(E. coli) <br /> were exceeded in most of the area. A 2005 microbial tracking study indicated the bacteria are <br /> primarily from dogs and wildlife. <br /> Sediment chemistry, fish tissue contaminant concentrations, and sediment toxicity data were <br /> summarized to provide additional information on chemical pollutants in the MRG that may <br /> affect the Rio Grande silvery minnow. In general, the results of the extensive water, sediment, <br /> and fish tissue analyses performed for this study identified few water quality issues—notably <br /> elevated E coli; one sample with an ammonia concentration of 9.12 milligrams per liter(mg/L), <br /> five times the acute criteria; low dissolved oxygen during brief periods of time; and some <br /> samples elevated in metals such as aluminum, copper, and chromium. <br /> New Mexico has adopted only one fish tissue-based criterion (methylmercury)in its water <br /> quality standards. The Rio Grande silvery minnow's average adult body burden of mercury is <br /> about 0.05 microgram per gram (µg/g)wet weight mercury (Lusk et al. 2012). <br /> The concentration of mercury in all but a few small, often ephemeral, streams in New Mexico is <br /> minute, averaging less than 2.5 nanograms per liter(ng/L) (NMED 2001). At this level, there is <br /> virtually no threat to humans or wildlife from direct contact with, ingestion of, most of the state's <br /> July 2017 <br /> 14 <br />