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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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WASTE DISCHARGE REQUJREMERS ORDER NO. • 5 <br /> CITY OF LATHROP AND METROPOLITAN LIFE INSURANCE COMPANY <br /> CROSSROADS TREATMENT PLANT NO. 1, SAN JOAQUIN COUNTY <br /> 27. To evaluate the longterm infiltration rate, the Discharger performed double ring infiltrometer tests <br /> at each proposed land application area using treated effluent. Two tests were performed at each <br /> area. The test results are summarized below: <br /> TEST SITE INFILTRATION RATE (in/hr) <br /> Land App. Site 1 Land App. Site 2 Land App. Site 3 <br /> NDR-1 NDR-2 NDR-3 NDR-4 NDR-5 NDR-6 <br /> Average 0.95 0.77 2.56 2.70 1.16 3.32 <br /> 28. Based on the National Resource Conservation Service soil survey, the soils in the proposed land <br /> application areas are Tinnin loamy coarse sand, Veritas fine sandy loam, Merritt silty clay loam, <br /> and Timor loamy sand. Published infiltration rates for the soils range from 0.3 to 3.0 in/hr. <br /> Groundwater Considerations <br /> 29. Based on groundwater elevations measured on 25 January 2001 in wells located in the land <br /> application areas,the groundwater flow direction was to the west-southwest; the groundwater <br /> gradient was approximately 0.0012 foot per foot. Groundwater flow direction measured at the <br /> evaporation/percolation ponds is influenced by groundwater mounding. Therefore the flow <br /> direction measured in the land application areas is considered to be more reliable. <br /> 30. The Discharger has been monitoring groundwater quality in Wells W-1, W-2, W-3, and W-4 at the <br /> treatment plant 1995 to 2001. Average groundwater quality is provided in the table below: <br /> Well TC N TDS (mg/1) NO,as N Depth (ft) <br /> W-1 <1.1 1,550 0.5 13.7 <br /> W-2 <l.l 1,742 12.0 12.9 <br /> W-3 2.1 1,879 60.1 15.6 <br /> W-4 <l.l 1,199 0.6 12.8 <br /> TC denotes total coliform organisms,MPN denotes most probable organisms per 100 nil sample,TDS denotes total <br /> dissolved solids,NO3 as N denotes nitrate reported as nitrogen. <br /> 31. Of the wells located at the treatment facility, only Wells W-1 through W-4 are sampled for chemical <br /> analyses. Well W-4 is located upgradient of the facility and wastewater ponds; Well W-4 possesses <br /> lower concentrations of TDS and nitrate concentrations. This data indicates the existing wastewater <br /> treatment facility has impacted groundwater quality. This Order includes provisions that will <br /> improve the quality of wastewater in the future. <br /> 32. Background groundwater quality at the land application areas was measured in a sampling event <br /> performed on 29 and 30 January 2001. The analytical data is presented in the table below: <br /> Well TDS EC Sodium Chloride Sulfate NO3 TKN TCO FC <br /> MW-1 2,540 3,750 496 543 904 0.107 <0.5 DET <1.0 <br /> MW-2 2,450 3,380 422 420 934 8.89 <0.5 DET <1.0 <br /> MW-3 1,310 1,990 330 123 439 <1.0 <0.5 DET <1.0 <br />
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