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43 <br />short periods and removes soil frcm these rhannalS to depths of one foot or <br />more), these areas will be filled with soil, reseeded and mulled. In addition, <br />straw bale ~;m~,t traps will be caistructed when the gullies are first observed <br />to detain rtanff aryl trap sti~,~d ~i~++P*~*. <br />Alternative sed;mo„r control mea_~ efficietxy cannot be measiued on a <br />storm-specific basis. Zhe lack of per+e_*+*+; a~ surface water as ~*rea+*~ ow, <br />precludes water quality sampling. Further, the effectiveness of the reclamation <br />practices, catpled with slope length limits will decrease soil erosion (hence <br />s ;~++P^* movement) to the point that physical m~a,remn.,rc of soil erosion wwld <br />be aoas~lished only with elaborate aryl detailed physical apas**p~•+~- systems, a <br />viable option only as a researr3r effort. <br />Water ouality St<vxi?**j~ <br />Rhe existing s i~*r+~ detention basins on the Bourg Mine are properly <br />~*'+'+; tted with NPDES (National Fbint Dis[37arge Elimination S~stan) ~+~+~; is <br />because of their ;*++a**~;ttent basin discharge being recognized as a point sauce <br />of "water pollution." The proposed alternative sediment control mcac~,roc for the <br />Bourg Mine are not designed to have specific discharges of water, indeed no <br />channel design is anticipated. ~1e slope length and slope shape modifications <br />are meant to m;n;m;~e 'lohr gp,~rg~ycn, If overlaid flows occurs, it would <br />be considered rxm-point in origination. <br />Non-point source water quality ~*a*~~**ae are usually evaluated by sampling <br />above and below the lard use activity. `!he above sample representing sane <br />measure of baGogrotud water quality and the below sample aaeP~aing lard use <br />activity ~ water quality. 'Dle stream power aryl sediment supply has already been <br />described for Mann Draw (see Streamflow Generation) . `Rie reon-point so~uoe <br />~*pa*+fl ow frsml the reclaimed Hourg Properly wand have little impact on water <br /> <br />