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the I.~: I relationship (soil salinity/irrigation water salinity) is considered conservative. However, the <br />applicant previously submitted vegetation data for irrigated areas on Trout Creek (Exhibit J') that <br />demonstrate that moderately sensitive species comprise a very small portion of the total vegetative <br />production on those areas irtieated downstream of the Foidel Creek mine. The applicant also points out <br />that irrigation water is applied in excess of what is necessary for the species grown, and this excess <br />leaches the soil profile, thus making the assumed relationship between soil salinity and irrigation water <br />salinity a worst case assumption. fhe applicant proposes that no decrease in production of any of the <br />species currently grown on the Trout Creek AVF would be expected unless the conductivity of the <br />irrigation water were to exceed 1 mmhos/cm. Based on species composition data submitted, the <br />applicant predicts that significant production decreases (>3% for a farm unit) would not occur unless <br />irrigation water salinity were to exceed 2.0 mmhos/cm. <br />Given the factors involved, the Division finds it is appropriate to propose an irrigation water material <br />damage suspect level of 1.5 mmhos/cm for Trout Creek, from the confluence of Middle Creek [o the <br />Yampa River. Establishing the suspect level at l.5 mmhos/cm acknowledges the evidence submitted <br />by the applicant while maintaining a reasonable suspect level established through research and <br />application. <br />As a result of TR-32, the applicant has proposed a plan to discharge mine water only when the stream <br />has the dilution capacity to maintain waters at or below the discharge points on Fish Creek and Trout <br />Creek to I.5 mmhos/cm. In summary, projected flood irrigation water quality" is-1.230 mmhos/cm and <br />material damage in terms of productivity declines would not be expected unless water salinity were to <br />exceed l.5 mmhos/cm. <br />Given the minor effect of mine discharge on Trout Creek surface water quality, a specific projection of <br />alluvial ground water impact was not made. Since alluvial recharge would occur in late spring and <br />early summer when dilution due to snowmelt runoff is at its peak, it follows that alluvial waters (and <br />thus subirrigation) would be less affected by mine discharge than Trout Creek surface water (and flood <br />irrigation). <br />The proposed operation would preserve the essential hydrologic functions of the alluvial valley <br />floor. <br />The essential hydrologic functions of the Trout Creek alluvial valley floor have been identified as the <br />capacity to support subirrigated and flood irrigated agricultural activities. <br />The proposed plan would not result in any surface disturbance or undermining of the AVF. Also, as <br />discussed previously, no material damage would result from changes in the quality of surface and <br />ground water that supply the alluvial valley floor. Thus, the essential hydrologic functions of the <br />alluvial valley Floor would not be affected by the proposed operation. <br />Foidel Creek/Middle Creek Confluence Area <br />Map 15 of the life of mine application delineates previously designated alluvial valley floors in the <br />vicinity of the Foidel Creek/Middle Creek confluence, downstream along Middle Creek to the Trout <br />Creek confluence and downstream on Trout Creek to the Yampa River. htap 15 shows a flood <br />irrigated field at the confluence of Foidel and Middle Creek and a number of Flood irrigated fields <br />along the Trout Creek AVF downstream from the Middle Creek confluence. <br />C:U H B1C82056\RN03\RN03FI ND.doc <br />34 <br />