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SITE INFORMATION AND CORRESPONDENCE 1980-1999
Environmental Health - Public
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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
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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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correlation exists between pH metal solubility and concentrations of metals that create thresholds of <br /> inhibitory effects in activated sludge treatment processes. <br /> We propose utilizing influent pH values as a tripping mechanism for the Discharger to <br /> conduct additional sampling for zinc,lead and cyanide. The Discharger should be required to have <br /> the daily composite sample analyzed for these pollutants anytime the influent pH meter shows that <br /> the treatment plant has received wastewater containing a pH value less than 6 or greater than 10 for <br /> any accumulative one hour period. <br /> Similarly, many organic pollutants interfere with POTW processes, such as alcohols, <br /> phenols, cyanide, chlorinated hydrocarbons, pesticides, organic nitrogen compounds, surfactants, <br /> oil and grease, and miscellaneous organic chemicals. Chlorinated compounds such as chloroform, <br /> carbon tetachloride and 1,1,1 trichloroethane are toxic to the anaerobic digestion process at very <br /> low concentrations (0.5 to 1 mg/1). Sulfide compounds (especially hydrogen sulfide, H2S) are <br /> known to inhibit the anaerobic digestion process under certain conditions. These inhibitory effects <br /> can increase the likelihood of pollutants being bypassed cough the treatment system. Any <br /> exceedance of reported levels of these constituents known to inhibit activated sludge, anaerobic <br /> digestion and nitrification processes should trigger requirements for additional sampling. <br /> B. Influent Monitoring Of Industrial Wastewater To Ponds. <br /> There is no requirement to monitor for pH. A continuous reading meter should be <br /> required. This will help to determine if the wastewater is septic and odor causing,help detect illicit <br /> discharges of acidic waste and prevent the application of hazardous wastes to land. A continuous <br /> reading conductivity meter should also be required. Priority pollutants should be required as part <br /> of influent monitoring of industrial wastewater to the ponds because the Discharger has identified <br /> several metal finishing processes that discharge into this line. The regulated pollutants including <br /> total toxics organics can be found in 40 CFR 433. Priority pollutants should be sampled twice <br /> annually as a composite sample because the primary discharger has been noted as a cannery <br /> operation that can have seasonal variation in its discharge. For example: peaches and apricots are <br /> processed in the early summer months while tomatoes are generally processed in the late summer <br /> months. Peaches may receive pesticide spraying prior to harvest whereas tomatoes are generally <br /> defoliated prior to harvest. <br /> The Tentative Permit states that the"[d]ischarge of waste classified as `hazardous' under <br /> Section 2521,Chapter 12 of Title 23 or `designated', as defined in Section 13173 of California <br /> Water Code is prohibited." However,the industrial waste from the industrial line is used for <br /> irrigation. How can the Regional Board determine compliance with this restriction unless it <br /> requires the Discharger to, as least annually,test for hazardous waste constituents. Additionally, <br /> DeltaKeeper,Tentative NPDES Permit,Lodi, 17 December 1999,Page 9. <br />
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