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02/28/97 18:51 $ ~ 002 <br />• • <br />The Fish and Wildlife Plan 2.05.6(2) provides an adequate overview of impacts associated with <br />the proposed mining activities. However, rho plan fails to provide any significant mitigation <br />measures to reduce the impacts on fish and wildlife resources. A mitigation plan addressing the <br />sequencing of efforts (avoidance, rninimization, mitigation of toss) to address impacts is lacking <br />and should be included before a proper analysis of mitigation can be made. As an example, the <br />impact amlysis projects the direct loss of approximately 1,9?A linear feet of fish habitat, <br />increased sedimentation and decreased water quality, but fails to address a sequencing of <br />measures to reduce impacts. Of particular concern to CDOW is the reduction in water quality <br />resulting fmm increases in sulfates, TDS, iron, and manganese. The analysis does not mention <br />whether an increase in cadmium and zinc levels are anticipated. It is also tmcleaz whether a <br />decrease iu pH is anticipated resulting in increased toxicity of metals to aquatic life. It should be <br />noted, however, that specific mitigation plans regarding aquatic habitats and hydrologic balance <br />were not provided for our review. These specific plans need to be provided for an adequate <br />review of the proposed application. Nevertheless, the application does provide some steps for <br />reductions in sediment loads through the use of best management practices including appropriate <br />road alignment, revegetation and sediment control ponds. In addition, the plan calls for locating <br />all roads, except for crossings, out of the "chatmel" of any stream. These sups should help <br />mitigate some of Ule impacts on the aquatic environment <br />The application outlines a post surface mine land use change from rangeland/wildlife to rangeland <br />exclusively. As stated in the fish and wildlife plan 2.05.06(2), the "conversion of the surface mine <br />area from an oak/pinyon to a grassland community type will decrease mule deer, elk, black beaz, <br />and turkey usage of the area." This conversion of habitat type, in light of its importance as critical <br />winter range ,will result in a significant [ong term negative impact on wildlife. The mitigation plan <br />fails to address mitigation remedies for such habitat loss. In addition, the operation plan 2.05.2(5) <br />states that there will be a shortage of topsoil and subsoil for complete redistribution on all <br />disturbed areas. If this is the case, it seems unlikely that restoration of habitat with compazable <br />productivity can be achieved. With such impacts noted, the prescribed seeding mixtures do <br />provide an excellent mix of cool/warm season native grasses in association with beneficial browse <br />species. However, the revegetation prescription fails to provide needed mitigation for the quality <br />of habitat lost. <br />With the corollary that CROW has not reviewed the aquatic/hydrologicbnlance mitigation plan, <br />CROW encourages the adoption of the following mitigation recommendations: <br />-Maintain current surface mine land use status of wildlife habitat/rangelandnnd reclaim <br />disturbed areas using woody species that aze comparable in composition and quantity as <br />the high quality habitat (oak/pinyon) being destroyed. Replace oak/pinyon habitat with <br />oak/pinyon habitat. <br />-Maintain appropriate setbacks on all riparian habitats and reclaim/enhance all disturbed <br />riparian habitats. <br />-Monitor mining impacts on flathead chub populations and provide annual status report to <br />CDOW for review, <br />-Survey/monitor areas of disturbance for nesting raptors and provide CDOW an annual <br />report on nesting status and subsequent mitigations measures !f nescescary. <br />