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WASTE DISCHARGE REQUIREMENTS ORDER R5-2012-0103 - 12 - <br />CONSTELLATION BRANDS U.S. OPERATIONS, INC. dba WOODBRIDGE WINERY <br />WOODBRIDGE WINERY <br />SAN JOAQUIN COUNTY <br /> <br />d. Crop uptake of salt ions was less than the amount of FDS applied. Uptake rates of <br />up to 1,100 lbs/ac/year were achieved. Crop uptake of FDS has been and will <br />continue to be less than the total FDS mass applied. This includes an estimated <br />165 pounds of wastewater supplied nitrogen. <br />30. Crops will be periodically cut and removed from the LAAs, which will remove the <br />nitrogen, potassium, and other dissolved solids that are taken up by the plants. <br />31. TDS is composed of both Volatile Dissolved Solids (VDS) and FDS. The proportion of <br />VDS to FDS in wastewater varies with the source, but 50-percent of the TDS in winery <br />wastewater may be in the volatile form. The VDS can be biologically treated by soil <br />microorganisms in a well-managed wastewater treatment and land application system, <br />when wastewater is not over-applied. The forecast flow-weighted average FDS <br />concentration of the blended wastewater, storm water and supplemental irrigation <br />water is about 775 mg/L. Based on the anticipated average annual wastewater flow <br />rate of 100 Mgal at full build-out, approximately 834,000 pounds/year of wastewater <br />FDS will be applied (8,257 lbs/ac/year). <br />32. The Discharger has estimated the average total nitrogen concentration in wastewater <br />to be 20 mg/L. Based on the anticipated average annual wastewater flow rate (100 <br />Mgal), approximately 16,680 pounds/year of total nitrogen will be applied (165 <br />lbs/ac/year). The Crop Uptake and Assimilative Capacity report indicated that for LAA <br />acreage, doubled cropped with alfalfa, Sudan grass, and/or triticale grass, nitrogen <br />uptake rates were determined to be approximately 360 lbs/ac/year. Therefore, <br />proposed nitrogen loading rate is unlikely to degrade groundwater quality. Because <br />the Crop Uptake and Assimilative Capacity did not consider potassium, which is now a <br />key waste constituent due to sodium reduction efforts, it is appropriate to require the <br />Discharger to develop and implement a Nutrient Management Plan that considers all <br />macronutrients (i.e., nitrogen, phosphorus, and potassium). <br />33. Because treated wastewater will not provide adequate water to meet the crop demand, <br />supplemental irrigation water will be required to maintain crop health in the summer <br />months (generally May through September) during normal precipitation years. During <br />100-year return annual precipitation years, supplemental irrigation water may be <br />required from July through September. Supplemental irrigation water will be provided <br />by the on-site irrigation wells and Mokelumne River water (for which the Discharger <br />has riparian rights). The agricultural irrigation wells produce water that varies in TDS <br />concentration from 250 mg/L to 433 mg/L and averages 343 mg/L. Mokelumne River <br />water averages approximately 60 mg/L TDS. The FDS loading that occurs from the <br />supplemental irrigation water is in addition to that derived from wastewater. Therefore, <br />it is appropriate to require that the Discharger maximize the use of high quality surface <br />water for supplemental irrigation to minimize the salinity of the LAA percolate. <br />34. The RWD summarized a soil investigation and cropping study the Discharger <br />performed. The investigation included collection of soil samples at various depths to <br />assess changes in soil chemistry. The study period extended from October 2007 <br />through January 2010 over four crop growth cycles. Soil moisture, climate, irrigation <br />volume, irrigation water quality, crop harvest/uptake, and soil chemistry were