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Hubberson Gulch AVF impact evaluation with the Dry Creek AVF impact evaluation which <br />follows. <br />On page 129 and 130, there is an evaluation of salt loading impacts on the productivity of <br />subirrigated grass hay fields on Dry Creek (the same fields referenced in the page 53 <br />paragraph excerpt above). The narrative states that "...impacts to downstream subirrigated <br />fields from Seneca II-W South may best be characterized using surface water chemistry <br />downstream of the mining area". (This would seem to directly contradict the statement on <br />page 53, that the subirrigated fields would 'not be affected by surface flow in Dry Creek). <br />Further, the narrative states that "the postmining TDS concentration (1289 mg/p in Dry <br />Creek, at Station WSD5 (which is representative of water in Dry Creek as it flows past the <br />Olsen fields...)may represent aworst-case scenario for subsurface impacts to downgradient <br />hay fields." (The TDS value of 1289 mg/I is taken from Table 17-42a, and represents <br />projected salt loading impact to Dry Creek at Station WSD5, resu/ting from //-W South Area <br />Spoi/ Discharge. Table 17-42b presents projected salt loading impacts resulting from <br />combined spoil discharge from the //-W original permit area and the South Area extension. <br />The WSD5 projected TDS value in this table is 2451 mg/I. Since this cumulative projection <br />represents the water that would actually flow past the subirrigated fields in question, it <br />would seem that the value of 2451 mg/I should be used in the impact evaluation on page <br />129, rather than the value of 1289 mg/I, which was used.) <br />The Dry Creek AVF evaluation includes Table 17-43c (Projected Impacts to Downstream <br />subirrigated Crops). The basis for projections regarding species composition and crop salt <br />tolerance threshold and response slope values in Table 17-43c and related narrative for Dry <br />Creek AVF evaluation is not well documented. Salinity threshold value and response slope <br />(percent yield decrease per unit salinity increase) for the one species that occurs on both <br />the Hubberson AVF and Dry Creek AVF (smooth brome) are not consistent. In Table 17- <br />43b (Hubberson AVF), irrigation water salinity threshold of 1.3 and response slope value of <br />13.2°k are used and source is cited. Table 17-43c values are 1.5 and 7.0, respectively, <br />and source for the values is not cited. It appears that the response slope value may be <br />erroneously based on projected soil extract values rather than projected irrigation water <br />values, in Table 17-43c. If the Table 17-43b threshold and response slope values for <br />smooth brome are substituted into Table 17-43c, the result is that the over-all crop yield <br />reduction projection for the Dry Creek AVF field increases from 2.6% to 4.5%. Since the <br />projected yield decrease would exceed 3%, the impact would no longer be considered a <br />"negligible impact" as defined by the Divisiori's Material Damage Guidance Document, for a <br />small ranching operation. If the apparently correct TDS value of 2451 mg/I were used as <br />the basis of the evaluation rather than 1289 mg/I, the projected crop reduction would <br />obviously be significantly greater. <br />The operator will need to address and resolve the discrepancies and apparent errors <br />discussed above. Dry Creek Water quality-projections used in the page 129 evaluation will <br />need to be amended as appropriate, and field species composition and salinity response <br />projections of Table 17-43c on page 130 will also need to be documented and updated as <br />appropriate (following the process and assumptions used in Table 17-43a and b). If <br />properly amended crop yield decline projections for the Dry Creek subirrigated fields indicate <br />that yield declines would exceed 3% of the hay production for the subject ranching <br />operation, potential material damage would be indicated. As such, the operator may be <br />obligated to conduct intensive site specific surface water, alluvial water, soil; and <br />vegetation field investigations to demonstrate that continued'mining will not result in <br />material damage. <br />Another line of investigation that the operator will need to explore, is how the fields in <br />question fit into the landowner's farm/ranch operation. The only information given on this <br />