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I <br /> I <br /> I <br /> I <br /> i <br /> ! <br /> I <br /> I <br /> I <br /> I <br /> I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br /> <br />Minnesota Rules 7001.3200 B, D, E & H also address site suitability based on the site's <br />capability of groundwater protection, the feasibility of remediation of polluted <br />groundwater and the ability to meet standards for erosion and drainage. <br /> <br />Several types of evaluations are commonly used to determine site suitability. The <br />evaluation systems include: <br /> <br /> · U.S. EPA Criteria for Identifying Areas of Vulnerable Hydrogeology and <br /> RCRA-Statuary Interpretive Guidance (CIAVH); <br /> <br /> · Site Suitability Criteria Used by the MPCA; <br /> <br /> · MPCA Report on Groundwater Contamination Suscept~ility; <br /> <br /> · U.S. EPA's DRASTIC Index for Determining Groundwater Pollution <br /> Potential; and <br /> <br /> · U.S. EPA Hazard Ranking System. <br /> <br />U.S. EPA Criteria for Identifying Areas of Vulnerable Hydrogeology (CIAVH) <br /> <br />The CIAVH guidance document addresses avoiding vulnerable or sensitive environments <br />when siting solid and hazardous waste facilities. The vulnerable areas are determined <br />based on the time of travel (TOT) needed for leachate to move from a disposal unit to <br />an underlying aquifer. Locations with short TOT's, where the groundwater moves fairly <br />rapidly, are considered more vulnerable than those with long TOT's. In general, the <br />EPA uses a TOT of 100 feet in 100 years as the criterion for determining vulnerability. <br /> <br />Times of travel can be calculated from data commonly available such as hydraulic <br />conductivity. The criteria distance of 100 feet divided by hydraulic conductivity results in <br />the time of travel. The hydraulic conductivity ranges and the calculated TOT's for the <br />various hydrogeologic units at Sites Q, P, and D are presented in Table No. 1. <br /> <br />17 <br /> <br /> <br />