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'K�)-- <br /> Technical Revision,$12016) Monitoring Reductions <br /> Additional reductions of the monitoring plans were requested. Table 1, Current Hydrologic Monitoring <br /> Program (starting on page 15-3a-4), has been revised to reflect these changes. The details of the <br /> changes are provided below. <br /> 1 - Remove continuous flow recording requirements at all six NPDES outfalls and surface water site <br /> WSHF1 (lower Hubberson Gulch). Continuous flow recording is not required in the NPDES permit (SCC <br /> was performing this function voluntarily). Continuous flow recording at Site WSHF1 was initially <br /> performed to gather baseline data for the mine permit application, but was never dropped after the <br /> application. Again, continuous recording at this site was voluntary, it was not required by any other <br /> permit. This recording is time-consuming and expensive to maintain. Continuous flow data is not <br /> required for final bond release. <br /> 2 - Remove all monitoring requirements for alluvial Well WHALE-2 located on Hubberson Gulch. This <br /> well was plugged with a wooden fence post (by the landowner) in late 2014 or early 2015. Data from <br /> Hubberson Gulch alluvial Well WHAL7-2, located about a mile downstream of Well WHALE-2, will be <br /> used for the final bond release application. <br /> 3 - Remove all monitoring requirements for Trout Creek Sandstone Well WTC201. This well was the <br /> shop water supply well. It is currently not in use, and cannot be sampled when the power is off. Power <br /> is no longer available at the shop facilities, and the transformer has been removed. This well is 760 feet <br /> deep, and should be unaffected by mining as confining layers of shale separate it from the coal seams <br /> mined. The table presented on the following page gives a statistical summary of the water quality of <br /> this well for the last ten years (2006 thru 2015). Water quality data at this well for the last ten years <br /> was compared to CDPHE drinking water standards found in their Regulation 41. No Table 1 (human <br /> health) standards were exceeded. Three Table 2 (secondary) standards were exceeded. The iron <br /> standard, 0.3 mg/I, was exceeded in ten out of twelve samples, with values of 0.35 to 7.86 mg/1. The <br /> manganese standard, 0.05 mg/I, was exceeded in eleven out of twelve samples, with values of 0.051 <br /> to 0.181 mg/l. The sulfate standard, 250 mg/l, was exceeded once, with a value of 260 mg/l. <br /> However, a 1988 sample had an iron value of 1.31 mg/1 and a manganese value of 0.22 mg/I. A 1991 <br /> sample had an iron value of 9.58 mg/1, a manganese value of 0.22 mg/I and a sulfate value of 241 <br /> mg/1. Mining began at Seneca IIW in 1990. <br /> TR-82 15-3a-22 Revised 7/16 <br />