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INFORMATION SHEET,ORDER NO. 5-01-251 4- <br /> CITY-OF LATHROP AND CROSSROADS CREA LLC <br /> WASTEWATER TREATMENT FACILITY NO. 1 (CROSSROADS) <br /> SAN JOAQUIN COUNTY <br /> Constituent Units Value Beneficial Use Criteria or Justification <br /> Sodium mg/L 69 AGR' Sodium sensitivity on certain crops <br /> Total Dissolved Solids mg/L 450' AGR' Salt sensitivity° <br /> Total Coliform Organisms MPN/100 ml 2.2 MUN' Basin Plan <br /> 500 MUN' Recommended Secondary MCL' <br /> 1,000 MUN 1 Recommended Upper MCL s <br /> Chloroform 1 g/L 1.1 MUN 1 Narrative Toxicity Criteria1 ' <br /> Bromodichloromethane µg/L 0.27 MUN 1 Narrative Toxicity Criteria° <br /> Dibromodichloromethane µg/L 0.37 MUN 1 Narrative Toxicity Criteria10 <br /> Bromoform pg/L 4.3 MUN 1 Narrative Toxicity Criteria10 <br /> Total Trihalomethanes µg/L 80 MUN I MCL' <br /> pH pH Units 6.5 to MUN 1 Secondary MCL 9 <br /> 8.5 <br /> 1 Municipal and domestic supply <br /> 2 Council of the European Union,On the Quality of Water Intended for Human Consumption,Council Directive <br /> 98/83/EC(3 November 1998). <br /> 3 Agricultural supply <br /> 4 Ayers,R.S.and D.W.Westcot,Water Quality for Agriculture,Food and Agriculture Organization of the United <br /> Nations—Irrigation and Drainage Paper No.29,Rev. 1,Rome(1985) <br /> 5 Title 22,California Code of Regulations(CCR),section 64449,Table 64449-B <br /> 6 Title 22,CCR,section 64449,Table 64449-A <br /> 7 Title 22,CCR section 64431,Table 64431-A <br /> 8 United States Environmental Protection Agency <br /> 9 Title 22,CCR,section 64439 <br /> 10 California Environmental Protection Agency,Office of Environmental Health Hazard Assessment Cancer Potency <br /> Factor as a Drinking Water Level, California Environmental Protection Agency Toxicity Criteria Database. <br /> Municipal wastewater contains numerous dissolved inorganic waste constituents (i.e., salts,minerals) <br /> that together comprise total dissolved solids (TDS). Each component constituent is not individually <br /> critical to any beneficial use. Critical constituents are individually listed..The cumulative impact from <br /> these other constituents, along with the cumulative affect of the constituents that are individually listed <br /> can be effectively controlled using TDS as a generic indicator parameter. <br /> Not all TDS constituents pass through the treatment process and soil profile in the same manner or rate. <br /> Chloride tends to pass through both rapidly to groundwater, As chloride concentrations in most <br /> groundwaters in the region are much lower than in treated municipal wastewater, chloride is a useful <br /> indicator parameter for evaluating the extent to which effluent reaches groundwater. Boron is another <br /> TDS constituent that may occur in wastewater in concentrations greater than groundwater depending <br /> on the source water, to the extent residents use cleaning products containing boron, and whether any <br /> industrial dischargers utilize boron(e.g., glass production, cosmetics). Other indicator constituents for <br /> monitoring for groundwater degradation due to recharged effluent include total coliform bacteria, <br /> ammonia,total nitrogen, and Total Trihalomethanes (TTHMs), a by-product of chlorination. <br /> Dissolved iron and manganese are useful indicators to determine whether components of the W WTF <br /> with high-strength waste constituents, such as sludge handling facilities, are ineffective in containing <br /> waste. Exceptionally high TDS and nitrogen also typifies this type of release. <br />