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7.1. SR 09-19-1994
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7.1. SR 09-19-1994
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9/19/1994
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<br />-- <br /> <br />"' <br /> <br />indicated on the attached figure. <br /> <br />. <br /> <br />Each of the monitoring wells should be installed on the innermost fringe of the buffer zone <br />nearest to the Shiely well as possible, and be constructed by a licensed well contractor per <br />Minnesota Department of Health (MDH) regulations. In addition each well should be <br />surveyed for the top of casing elevation so that all water levels can be converted to <br />elevation. <br /> <br />WATER LEVEL MONITORING RECOMMENDATIONS <br /> <br />Water level data, along with accurate pumping rate data, should be collected for <br />documenting the effect of pumping on groundwater levels, and as an aid in identifying the <br />need for, or effectiveness of mitigative measures. Pumping rate information should be <br />collected from the Shiely well. At a minimum water level data should be collected from <br />the Shiely well, the monitoring wells and any other available observation points according <br />to the following schedule: <br /> <br />. <br /> <br />- immediately prior to initiation of seasonal pumping; <br />- at the pumping well 24 hours after pump start-up; <br />- at all wells I week after initiation of pumping; <br />- monthly at all wells throughout the duration of the pumping season; <br />- immediately prior to seasonal shut - down; <br />- at the pumping well 24 hours after shut - down; <br />- at all wells I week after shut down, and <br />- at all wells I month after shut down. <br /> <br />WATER QUALITY MONITORING RECOMMENDATIONS <br /> <br />Section 3.3 of the EIS indicates that potential groundwater quality impacts attributable to <br />the mining operations are primarily associated with use of above-ground fuel storage tanks. <br />Implementation of the required spill prevention plans and secondary containment minimizes <br />the potential for groundwater impacts. Should any groundwater impacts from the mining <br />operations, or other unrelated occurrence, occur in the vicinity of the well, it is likely that <br />the impacts would be drawn toward the pumping well. Operation of the Shiely well would, <br />therefore, reduce the potential that impacts would occur in residential wells. Therefore, <br />an extensive water quality monitoring program does not appear warranted. A limited <br />monitoring program, as recommended below, will provide background water quality. <br /> <br />Background Monitoring: Sample and analyze the monitoring wells and one or two <br />residential wells each along the western and southern boundaries. The recommended <br />monitoring parameters include MDH volatile organic compounds (VOCs), and diesel <br />range organics (DRO). The monitoring wells should also be tested for general <br />background chemistry parameters including nitrate + nitrite, alkalinity, chloride, <br />sulfate, sodium, potassium and dissolved metals. <br /> <br />. <br />
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