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Runoff from the Loadout area that is not diverted around the area of <br /> disturbance is retained in sedimentation ponds for a maximum of 36 hours. <br /> Water retained in the two sedimentation ponds experiences some losses <br /> through evaporation and seepage. The Dry Creek diversion downstream <br /> could potentially be impacted by loses of water due to storage in the sediment <br /> ponds. <br /> The acreage served by the two sediment ponds accounts for less than one- <br /> thousandth of the acreage drained by Dry Creek. Since the area to be <br /> affected is a fraction of the total watershed, the watershed will not be <br /> significantly affected and runoff from the permit area will continue to reach <br /> Dry Creek. <br /> All waters utilized for dust suppression and other operations at the Loadout <br /> were piped in from a well in the Yampa River alluvium (H-G Shallow Well <br /> No. 1), located two miles north of the Loadout. H-G Shallow Well No. 1 was <br /> sealed in 2011. HGL owns an additional 90 acre-feet of water rights in the <br /> downstream Walker Ditch,which are not currently being utilized. Facilities <br /> have been dismantled in 2011, and the remaining office trailers were <br /> removed from the site in 2013. Plumbing to the trailer was dismantled <br /> during the removal of the office trailers. <br /> These water rights were to be utilized to compensate any downstream users <br /> for loss of water due to consumption at the Loadout. In addition, HGL has an <br /> agreement with the United States Fish and Wildlife Service (USFWS)to <br /> mitigate against losses of water to the Yampa River as a result of water <br /> consumption at the Loadout. Please refer to Volume 3, Tab 21 of the <br /> PAPand Item XII of this document. <br /> 2. Ground Water Impacts <br /> The Lewis shale has low conductivity values and is generally considered to <br /> be an aquitard that retards transmission of surface water to the Twentymile <br /> Sandstone, the underlying regional aquifer. This low conductivity unit <br /> results in low well yields that preclude the use of waters from the Lewis shale <br /> for other than stock watering (See Seneca II-W Permit, C-1982-057, Tab 7 of <br /> the PAP). Water samples from the two existing alluvial wells at the Loadout, <br /> which are completed in part in the underlying Lewis shale, often exceed <br /> water quality standards for stock watering. Operations at the Loadout should <br /> not impact this ground water. <br /> Alluvial waters are of poor quality and may be unsuitable for use in <br /> irrigation. Leachate from coal stockpiled at the Loadout could have <br /> potentially infiltrated the alluvium and added dissolved chemical loads to the <br /> Dry Creek alluvial aquifer; however,impacts to Dry Creek alluvial water <br /> quality have been minimal due to the size of the operation and the <br /> 22 <br />