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13.2 Wind Speed <br />Wind speed data was not available at the Uravan meteorological station. Longer term <br />wind speed records are available from the BLM and the Boise Interagency Fire Center <br />Remote Automatic Weather Station (RAWS) in Nucla, Colorado (NUCC2), elevation <br />5860 ft. Based on the available data from the Nucla station from 2002 through 2012, the <br />average annual wind speed is 5.0 mph. Winds are primarily westerly winds. <br />As indicated in the climate data, precipitation for the Uravan site is 12.57 inches per year, <br />whereas the evaporation is approximately 47 inches per year. The evapotranspiration <br />rates (evaporation plus transpiration rates from area vegetation) in this semi -arid location <br />would be higher than simple pan evaporation rates. Therefore, all rain and snow melt <br />will infiltrate the porous dump material with very little percolating completely through <br />the pile, the rest being returned to the atmosphere via evaporation or transpiration, or <br />being absorbed by the dry but porous rock, leaving very little water for recharge. <br />(14) Geochemical Data and Analysis <br />This section discusses the results of the SPLP tests to measure the concentration of <br />uranium related constituents leaching from waste rock and ore stockpiles. Besides <br />uranium and vanadium, there are several constituents that are commonly associated with <br />these types of mineral deposits. These constituents include arsenic, molybdenum, <br />selenium, and at some sites radium. While most of these constituents occur naturally in <br />the environment, their association with mining operations and potential for migration in <br />the environment are examined. <br />Analytical results from the SPLP tests are compared with the appropriate federal and <br />state water quality regulations and guidelines. These regulations include the Safe <br />Drinking Water Act, National Secondary Drinking Water Standards (not federally <br />enforceable), State of Colorado Basic Standards for Groundwater (5 CCR 1002 -41), and <br />Colorado Agricultural Standards. <br />14.1 Results of SPLP Tests <br />Laboratory SPLP results for chemical constituents of interest are presented in Table 5 <br />along with applicable water quality standards and guidelines. Both the ore and waste <br />rock samples contain constituents above Federal or State standards or guidelines. Since <br />the ore will be placed on a clay liner and only temporarily stored onsite and removed on a <br />first -in first -out basis, only constituents associated with waste rock pile that will <br />permanently remain on site will be discussed. Aluminum, arsenic, uranium and <br />vanadium exist in concentrations that exceed Federal and State standards or guidelines. <br />The main environmental issue concerning aluminum is potential toxicity to aquatic <br />organisms. The EPA guidelines are for the pH range of 6.5 to 9.0 while the EPP sample <br />at JD -9 has a pH of 9.5. In general, the more sensitive an organism is to a low pH, the <br />stronger the toxic response to Al concentrations to falling pH levels (Baker and Schofield, <br />1982). Based on the site distance to the nearest water body, it is highly unlikely, even <br />under the most extreme conditions, that aluminum could be transported such a large <br />O'Connor Design Group Inc. U - 23 <br />