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05/02/2002 16:06 4716922 EILAND LAW PAGE 07 <br />adjacent to the blasting area, and subject to the "fallout" from blasting agent, will be piled up, <br />without surface cover, so that the amount of blasting agent will be concentrated in the pile. Rio <br />Grande's blasting plan contains no reference to necessary measures to stabilize and protect these <br />piles from contamination, as required by Rule 3.1.6.(3), which will ultimately contain a relatively <br />high concentration of contamination accumulated from blasting on adjacent strips (e.g., <br />protective liners underneath the piles). Almost constant wind erosion, in addition to water <br />erosion from periodic heavy rainfall, can disperse the dust from these piles beyond the site's <br />boundaries. In case of seepage from snowmelt and rain, there exists significant potential for <br />groundwater contamination. <br />Rule 3.1.7 states that Rio Grande must show that it will protect groundwater quality <br />standards. It is unclear, in the permit application, how the blasting agent will be kept from <br />seeping into groundwater. There is a reasonable potential for degradation of groundwater <br />quality, as well as of surface. To solve the problem with respect to both groundwater and surface <br />water, a less contaminative blasting agent should be used. If ammonium nitrate and diesel fuel <br />are to be used, the reclamation plan should include measures that will remove it from the soil and <br />potential entrance into ground or surface water. Testing procedures to determine if treatment has <br />successfully taken place should be included, including some criterion for determining that the <br />agent is cleaned from the soil so that it can neither filter into the groundwater nor run off into <br />surface water. <br />This case fits the criterion of "reasonability," from blasting agent alone, An adequate <br />groundwater monitoring program is not included in the permit. 3. 1.8 Wildlife. Rule 3.1.7 states <br />that points of compliance, if not established, shall be determined, and on groundwater monitoring <br />specifies that "a groundwater monitoring program shall be required . .. where are adverse impact <br />on groundwater quality may reasonably be expected." The permit does not appear to deal with <br />the potential of contamination resulting from the huge quantities of blasting agent, or establish <br />compliance points for dealing with such contamination. Contamination will not stop at the site <br />boundary because pollutants can seep into the groundwater. <br />Rule 3.1.7.6.8. III, states that the office should consider the factors of toxicity, mobility, <br />and persistence in the environment of the contaminants and " (IV) the potential of the site as an <br />aquifer recharge area." The mesa slopes downward toward the north and the St. Charles River <br />and neighboring farms in the river valley. Runoff from the site containing blasting agent could <br />negatively affect the surface water quality for these users. Exhibit D (Mining Plan), p. D-4, <br />states that impoundment of runoff water in the mining holes is designed for a 100-yr. storm <br />event. CCAP believes that is too little and should be raised to be designed for a 500-yr. event. <br />Cloud bursts happen in that area frequently, and often exceed the 100-yr. storm, event volume in <br />limited areas washing out roads and small dams. If the impoundment areas are not designed <br />correctly and such a storm hits that area, it will wash out the ponds, sending the runoff and <br />contaminants into the St. Charles River, and also let loose a volume of water that could produce <br />flooding on farms downstream. If the holding ponds do not fail, they could still allow a large <br />amount of water contaminated with blasting agent to seep into the groundwater. <br />