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-35- <br /> The ,effect of increasing soluble salts is short-termed over the <br /> life-of-mine. Upon completion of mining, there will be no discharge from <br /> the mines and upon successful rev tion, the preparations plant ponds <br /> will be removed. Thus, upon nit n, the soluble salt content of the <br /> surface water should return t . <br /> The mine discharge has not had an effect on the ion balance in the <br /> stream. The baseline information indicates that the surface and ground <br /> water is dominated by calcium bicarbonate. The mine discharge water and <br /> the receivin Creams are likewise dominated by calcium bicarbonate. <br /> On <br /> impacts of the Coal Basin mining activities on surface <br /> water is an increase in the sediment load carried in the stream from the <br /> road s tem. Mid-Continent has monitored two streams, Bear Creek and <br /> Braderic'C, Creek which have drainages that are not affecte by the mini <br /> operations he Division used the average total suspended solids co nt <br /> as the base 'ne val,ue for determining increased sediment yields fr the <br /> roads. All t roads are within the Coal Creek and-Dutch Cre k <br /> drainages. a ore, ona sediment above the aver a for Bear <br /> r`ad ich Cre ks was attributed to the roads. Using th' method of <br /> comparison of the to for Bear and Braderich Creeks as Tent levels <br /> with data for Coal a d Dutch Creeks as disturbed sampl and the water <br /> quality data submitte by the applicant, the Divisio determined that <br /> the road to Mine No. 5 ontributes a roximatel 6 tons of sediment pex4 <br /> r)c� year to Coal reek an the Mines 1 , 2, 3, and 4 hdul roads contribute r,d <br /> 2.778 tons of sediment per�yrear to Dutcn rYoa� There are 154 acres of <br /> roads within the permit area; thus, the average sediment yield from the r V9 <br /> road system would be approxima ly 18 tons o This figure is <br /> most likely higher than the sedi n actually generated from the roads. vtF� ' <br /> b ;Dutcn <br /> e Bear and Braderich Creek water eds'are smaller than the Coal and <br /> ` Creek watersheds. Likewise, <br /> t e flows in Coal and Outch Creeks are <br /> gher than in Braderich and Bear,,Cre s and sediment loads are greater <br /> r unit volume. As flows increase in treams, the velocity alsocreases, thus, the capacity ,of the wate to carry sediment is increased. <br /> agricultural areas, an.,erosion rate of 22 ons/acre/year would be <br /> excessive. However, iry teep mountain terrain ith�lfrge amount of <br /> Mancos shale, this er6sion rate is of excessive. A rosion rates in <br /> excess of 200 tons ,per acre are quite common see ater Quality Data in <br /> Volume 5) . Therefore, the sediment yield from the ads is not excessive <br /> and should not -significantly affect water quality. <br /> The applicant submitted a plan to monitor runoff from tj road system to <br /> refine the estimate of sediment generated by the road sys em. This plan <br /> should be adaptable in determining the effects of downgrade g the roads <br /> from haul roads to access roads «pon completion of the rock nnel <br /> project. I,-.�11 <br />