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SITE INFORMATION AND CORRESPONDENCE
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Last modified
4/3/2020 2:10:20 PM
Creation date
4/3/2020 1:50:02 PM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
RECORD_ID
PR0524190
PE
2965
FACILITY_ID
FA0016241
FACILITY_NAME
STOCKTON REGIONAL WATER CONTROL FAC
STREET_NUMBER
2500
STREET_NAME
NAVY
STREET_TYPE
DR
City
STOCKTON
Zip
95206
APN
16333003
CURRENT_STATUS
01
SITE_LOCATION
2500 NAVY DR
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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FACT SHEET ORDER NO. R5-2002- -30- <br /> CITY OF STOCKTON <br /> REGIONAL WASTEWATER CONTROL FACILITY <br /> SAN JOAQUINCOUNTY LATE REVISIONS <br /> detect Basin Plan objective are required. A TMDL for mercury in the Delta is scheduled for <br /> completion by December 2005 while the TMDL for Group A pesticides is scheduled for <br /> December 2011. The US EPA has not presented a TMDL completion date for dioxin/furans <br /> and PCBs. <br /> In addition to the 303(d) listing, the Basin Plan sets forth a water quality objective which <br /> requires that organo-chlorine pesticides not be present in the water column in detectable <br /> concentrations. The SIP designates acceptable minimum levels for lindane, endrin aldehyde <br /> and DDT at 0.02 µg/1, 0.01 µg/I and 0.01 µg/1,respectively. The detectable organo-chlorine <br /> pesticide effluent concentrations and corresponding reporting levels are above the SIP <br /> minimum levels and exceed the Basin Plan objective. Because of the SJR 303(d) listing, no <br /> mixing zone or dilution credits are available for these constituents. Based on the <br /> considerations listed above, effluent limitations for Group A pesticides are needed within the <br /> Order. <br /> 11.2 Reasonable Potential Analysis <br /> Priority pollutant constituents were analyzed in the effluent from April 1995 to April 2000 and <br /> the receiving water(location R-1) from July 1993 to June 1998. The results of these analyses <br /> were evaluated for their reasonable potential to exceed Basin Plan and CTR criteria. Section <br /> 1.3 of the SIP establishes the guidance for reasonable potential analysis. Table 11-1 <br /> summarizes the reasonable potential analysis of the detected inorganic, human health, and <br /> bioaccumulative constituents. From this analysis, the inorganic pollutants copper and cyanide <br /> were found to have a reasonable potential to cause or contribute to the exceedance of the <br /> applicable aquatic life priority pollutant criteria. <br /> There were twelve (12) human carcinogenic compounds present in either the RWCF effluent <br /> or in the ambient receiving water. As summarized in Table 11-1, eight (8) of the twelve (12) <br /> constituents were determined by the SIP process to present reasonable potential to exceed a <br /> one-in-a-million incremental human cancer risk criteria for water and/or organism <br /> consumption. In addition, three (3) of the eight (8) constituents listed in Table 11-1, <br /> dichloromethane, PCE, and TCE, were shown to have reasonable potential as a result of <br /> detectable concentrations in the background receiving water, monitoring location R-1, which <br /> exceeded CTR criteria. <br /> As discussed in the previous section, mercury, dioxin/f trans, PCBs, and Group A organo- <br /> chlorine pesticides, are California 303(d) listed pollutants causing impairment in Delta <br /> waterways. As required in Step 7 of Section 1.3 of the SIP, if a special condition exists (i.e., <br /> 303(d) listing for a pollutant) a reasonable potential to exceed water quality criteria is <br /> automatic. <br /> 11.3 Inorganic Prioritv Pollutants <br /> 11.3.1 Inoreanic Priority Pollutant Effluent Limitation Calculations <br /> Based on the information received to date from the Discharger, only the use of a steady-state <br /> model for calculating effluent limitations in the SIP can be justified at this time. Also, in the <br />
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