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SITE INFORMATION AND CORRESPONDENCE 1980-1999
Environmental Health - Public
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EHD Program Facility Records by Street Name
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THORNTON
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2900 - Site Mitigation Program
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PR0516806
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SITE INFORMATION AND CORRESPONDENCE 1980-1999
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Last modified
9/26/2019 8:48:37 AM
Creation date
9/26/2019 8:26:30 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
FileName_PostFix
1980-1999
RECORD_ID
PR0516806
PE
2965
FACILITY_ID
FA0012817
FACILITY_NAME
WHITE SLOUGH WATER POLLUTION CONTRO
STREET_NUMBER
12751
Direction
N
STREET_NAME
THORNTON
STREET_TYPE
RD
City
LODI
Zip
95241
APN
05513016
CURRENT_STATUS
01
SITE_LOCATION
12751 N THORNTON RD
P_LOCATION
02
P_DISTRICT
004
QC Status
Approved
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Finally, the hardness level used to apply the criteria (1 10 mg/1) is not reflective of <br /> expected conditions or more recent test results. Effluent data in 1993-94 indicated a <br /> typical hardncss of 110 mg/1. More recent test results (1996 to present) show that effluent <br /> hardness in 11 of 13 test was 120 mg/I or greater. The lowest hardness readings were 110 <br /> mg/l and appear to be associated with Wet weather periods. Thus,.any analysis of metals <br /> should use a minimum hardness of 120 rrb/l or higher. <br /> Given the available information that dissolved zinc levels, before con.sidera[ion of <br /> dilution, arc below EPA's objectives and that zinc is not in a toxic form,there is no basis <br /> to conclude that stringent Zinc limitations are necessary at this time. Tf dilution were <br /> considered, there would be no basis for establishing a zinc limitation, even using the <br /> Regional Board's worst case assumptions. Until valid data is collected and reasonable <br /> translator coefficients can be detennined, the effluent limitation for zinc should be <br /> »toriitor only. A schedule of compliance in the permit to complete this study would he <br /> necessary and appropriate for conducting such monitoring. <br /> Lead <br /> The City objects to the monthly average effluent limitation for lead because the <br /> Regional Board based the limitation on a direct (end-of pipe) application of EPA's <br /> dissolved Fater quality criteria, without providing for dilution, but adjusting for hardness <br /> and converting to total recoverable metal. The available performance data do not show <br /> that dissolved lead is discharged or present in the receiving waters. (.See, lead data, Table <br /> 1 —Effluent Metals Testing Data.) Total recoverable metals levels have reached 9 ug/1 <br /> with no measured dissolved component, indicating a minimum translator of 8.5. Thus, <br /> the conservative translator approach used by staff to conclude dissolved lead levels in <br /> Dredger Cut exceed EPA criteria is clearly misplaced. <br /> As noted with zinc, the Regional Board staff failed to apply an appropriate <br /> dissolved-to-total translator to determine the effluent limitation as recommended by EPA. <br /> If the Regional Board had followed EPA's translation method, the correct monthly <br /> average total recoverable effluent limitation would have been at least four times the value <br /> included in the Permit. ,Cee, Translator Guidance at pp. 5 -10 (Attachment 2) and <br /> t ESPermitComm ms Exhibit 2 Page 7 1JJ17i99 <br />
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