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SITE INFORMATION AND CORRESPONDENCE
Environmental Health - Public
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2900 - Site Mitigation Program
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PR0523929
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SITE INFORMATION AND CORRESPONDENCE
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Last modified
5/30/2019 10:47:55 AM
Creation date
5/30/2019 10:22:06 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
RECORD_ID
PR0523929
PE
2965
FACILITY_ID
FA0016100
FACILITY_NAME
WRP #1/ CITY OF LATHROP
STREET_NUMBER
18800
STREET_NAME
CHRISTOPHER
STREET_TYPE
WAY
City
LATHROP
Zip
95330
APN
19813035
CURRENT_STATUS
01
SITE_LOCATION
18800 CHRISTOPHER WAY
QC Status
Approved
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INFORMATION SHEET 4- <br /> CITY OF LATHROP AND METROPOLITAN LIFE INSURANCE COMPANY <br /> WASTEWATER TREATMENT FACILITY NO. 1 (CROSSROADS) <br /> SAN JOAQUIN COUNTY <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 Title 22,CCR, section 64439 <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 on <br /> 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. Dissolved <br /> iron and manganese are useful indicators to determine whether components of the WWTF with high- <br /> strength waste constituents, such as sludge handling facilities, are ineffective in containing waste. <br /> Exceptionally high TDS and nitrogen also typifies this type of release. <br /> Treatment Technology and Control <br /> Given the character of municipal wastewater, secondary treatment technology is generally sufficient to <br /> control degradation of groundwater from decomposable organic constituents. Adding disinfection <br /> significantly reduces populations of pathogenic organisms, and reasonable soil infiltration rates and <br /> unsaturated soils can reduce them further. Neither organics nor total coliform organisms, the indicator <br /> parameter for pathogenic organisms, should be found in groundwater in a well-designed,well-operated <br /> facility. <br /> Chlorine disinfection of effluent causes formation of trihalomethanes, which are priority pollutants. <br /> Treatment to reduce these in wastewater generally has not been performed, and little is known at this <br /> point on the typical impact on groundwater. <br /> Municipal wastewater typically contains nitrogen in concentrations greater than water quality objectives, <br /> which vary according to the form of nitrogen. Degradation by nitrogen can be controlled by an <br />
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