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Nitrate Loading Study 1 rerr�con <br /> Landavazo Property Tracy, CA <br /> December 15, 2017 < Terracon Project No. NA177067 <br /> term effect (i.e., over years)on groundwater quality, and is not intended for prediction of seasonal <br /> changes" (Hantzsche and Finnemore, 1992). <br /> The method takes into account the development area, soil denitrification factor, rainfall volume, <br /> rainfall nitrate concentration, waste effluent quantity, and waste effluent nitrate concentration. The <br /> formula, assumptions and calculations used for the analysis are shown in Appendix B. The units <br /> of nitrate used in the mass balance equation are nitrate-N, whose maximum drinking water <br /> contaminant level (MCL) is 10 mg/L. <br /> 1.0 CHEMICAL AND PHYSICAL SOIL PROPERTIES <br /> 1.1 Chemical and Physical Soil Properties <br /> Terracon reviewed the United States Department of Agriculture (USDA) Natural Resources <br /> Conversation Service (NRCS) Web Soil Survey (https://websoilsurvey.sc.egov.usda.gov), for <br /> information regarding soil properties. Based on information obtained from the website, onsite <br /> soils consist of Stomar clay loam which consist of well drained soils with 0 to 2 percent slopes. <br /> Parent materials consist of alluvium derived from sedimentary rock. Typical soil profiles consist <br /> of 0 to 17 inches fine clay loam, 17 to 47 inches clay, and 47 to 60 inches clay loam. <br /> 1.2 Mass Transport Soil Properties <br /> Based on a review of the USDA Soil Survey of San Joaquin County California (Issued 1992), <br /> Stomar clay loam soils, have slow permeability, and high shrink swell potential. Water in-take in <br /> irrigated areas is anticipated at 0.5 inches per hour. The slow permeability is a limitation and can <br /> be mitigated by increasing the leachfield size, backfilling trenches with sand, and/or increasing <br /> the length of the leach lines. <br /> The longer the effluent remains near the surface, the more treatment is enhanced due to natural <br /> processes within the soil. Based on the Stomar clay soils anticipated near the surface, the <br /> potential for effluent to remain near the surface is likely. <br /> 2.0 GROUNDWATER ANALYSIS <br /> 2.1 Regional Groundwater <br /> Regional groundwater information was obtained from a variety of sources. According to the <br /> California Department of Water Resources Water Data Library, between 1958 and 1991, <br /> groundwater measured between 7.2 feet and 19 feet below ground surface(bgs)at a groundwater <br /> well located approximately 1,000 feet north of the site. Based on a review of the Groundwater <br /> Information Center Interactive Map, (https://gis.water.ca.gov) Fall 2013, Fall 2014, and Fall 2016 <br /> groundwater depth and elevation maps, groundwater depth lies between approximately 90 and <br /> 140 feet bgs. Spring groundwater data for the site was not available on the groundwater <br /> information center website. Based on a review of the San Joaquin County Flood Control and <br /> Water Conservation District Groundwater Report, in Fall 2016 depth to groundwater near the site <br /> Responsive■ Resourceful ■ Reliable 3 <br />