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<br />Rule 2.06.8(S)(b) of the Colorado Regulations specifically refers to <br />potential increases in electro-conductivity of water supplying AVFe to <br />levels above threshold value at which crop yields decrease as <br />constituting material damage. The rule further cites a specific paper <br />by E.V. Maas and G.J. Hoffman of the U.S. Salinity Laboratory <br />published in the Journal of the Irrigation and Drainage Diversion, <br />ASCE., June, 1977. <br />In their paper, Maas and Hoffman list research derived salinity <br />threshold levels and response rates for selected agricultural species <br />and group those species as well as a number of additional crops into <br />four categories based on relative tolerance to salinity (sensitive, <br />moderately sensitive, moderately tolerant and tolerant). <br />The Division has taken the approach that a positive material damage <br />finding would be made if projected salinity increases resulting from <br />mining would result in significant decreases in production or shifts <br />in species composition based on the Maas and Hoffman paper. <br />On the Trout Creek AVF, the applicant sampled vegetative cover within <br />a number of farmed fields as denoted on Supplemental Map No. 1. <br />Vegetative production, as well as cover was sampled in one field, <br />Pasture 11. A majority of the species on the AVF would be considered <br />moderately tolerant, and on an acreage weighted basis only 18.48 of <br />the cover was made up of moderately sensitive species (salinity <br />threshold reached at root zone soil saturated paste extract <br />electro-conductivity of 1.5 mmhos/cm). A number of the species <br />encountered have not been ranked by Maas and Hoffman, and other <br />references were consulted. In general, Aveneae tribe grasses and <br />Trifolium species were considered to be moderately sensitive, while <br />Triticeae, Stipeae, and Poeae tribe grasses (with the exception of <br />Dactylis) were considered to be moderately tolerant. Carex and Juncus <br />species were also considered to be moderately tolerant. <br />As shown in TABLE 17 of this document, projected Trout Creek water <br />quality for flood irrigation is approximately .5 mmhos/an. Assuming <br />that a root zone saturated extract soil salinity of .75 mmhos/cm would <br />result from flood irrigation water with a specific conductance of .5 <br />mmhos/cm, no decrease in crop production would occur. The assumed <br />relationship between irrigation water salinity and root zone soil <br />salinity is within the typical range reported in USDA Handbook 60. <br />Based on leaching calculations included in the application and soil <br />sampling conducted on the Fish Creek AVF by the Division, the 1.5:1 <br />relationship is considered conservative. No decrease in production of <br />any of the species currently grown on the Trout Creek AVF would be <br />expected unless the conductivity of the irrigation water were to <br />exceed 1 mmhos/cm. Based on species composition data submitted, <br />significant production decreases (>38 for a farm unit) would not occur <br />unless irrigation water salinity were to exceed 1.5 mmhos/an. In <br />summary, projected flood irrigation water quality is .5 mmhoe/cm and <br />material damage would not occur unless water quality were to exceed <br />1.5 mmhos/csn. <br />Given the minor effect of mine discharge on Trout Creek surface water <br />quality, a specific projection of alluvial ground water impact was not <br />made. Since alluvial recharge would occur in late spring and early <br />summer when dilution due to snowmelt runoff is at its peak, it follows <br />that alluvial waters (and thus subirrigation) would be less affected <br />by mine discharge than Trout Creek surface water (and flood <br />irrigation). <br />The proposed operation would preserve the essential hydrologic <br />functions of the alluvial valley floor. <br />21 <br />