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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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EHD - Public
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INFORMATION SHEET OR NO. R5-2004-0028 15 <br /> CITY OF MANTECA, CITY LATHROP AND DUTRA FARMS <br /> WASTEWATER QUALITY CONTROL FACILITY <br /> SAN JOAQUIN COUNTY <br /> adequately nitrifies and denitrifies the waste stream to protect the beneficial uses of municipal and <br /> domestic supply. <br /> 10 Ammonia-Nitrogen <br /> This section provides a detailed discussion and evaluation of ammonia in the effluent. <br /> A review of the Discharger's monitoring reports from January 1998 through December 2002 shows an <br /> average ammonia effluent concentration of 18 mg/1, a minimum concentration of less than 0.1 mg/l, <br /> and a maximum concentration of 43 mg/l. The data indicate very little seasonal fluctuation. Receiving <br /> water monitoring(R-1) was conducted from January 2002 through December 2002 (see Table 4). The <br /> receiving water data showed an average of 0.2 mg/l with a minimum of less than 0.01 mg/l and a <br /> maximum of 1.4 mg/l. <br /> 10.1 Toxicity Criteria <br /> The USEPA 1999 Update of Ambient Water Quality Criteria for Ammonia provides the applicable <br /> water quality criteria for this pollutant. Ammonia is not a priority pollutant; therefore, USEPA <br /> guidance,rather than the SIP, is applicable for reasonable potential and effluent limitation calculations. <br /> Section 4.3.3 of the TSD allows the consideration of exposure duration in evaluating toxicity to <br /> organisms passing through a mixing zone. When evaluating either an acute or chronic mixing zone for <br /> ammonia,the pH of the mixture of effluent and receiving water should be used to determine <br /> appropriate criteria to be applied within that mixing zone. The pH in the mixing zone will be a <br /> function of the effluent pH and the ambient dilution water pH being mixed together. The pH is an <br /> important factor because toxicity of ammonia increases logarithmically as pH increases. <br /> 10.2 Consideration of Aquatic Organisms <br /> The most stringent acute ammonia criteria are applied when salmonoids are present within the water <br /> column. The San Joaquin River at Manteca is a migratory path for salmon, and they are likely to be <br /> present in the river at any time of the year. The chronic ammonia criteria are most stringent when <br /> early life stages (ELS) of aquatic species are present. In response to a request for information <br /> regarding the time of year ELS of fish are present in the San Joaquin River near the Deep Water Ship <br /> Channel (DWSC), a Department of Fish and Game memorandum, dated <br /> 27 February 2001, states ELS of multiple fish and invertebrates species are present in the San Joaquin <br /> River year-round. Therefore,both acute and chronic ammonia toxicity are based on the assumption <br /> that both salmonids and ELS of fishes are present in the San Joaquin River near the Manteca WQCF <br /> outfall year-round. <br /> 10.3 Reasonable Potential Evaluation <br /> The reasonable potential evaluation shows that the WQCF effluent has reasonable potential to cause or <br /> contribute to an in-stream excursion above USEPA acute and chronic water quality criteria for <br /> ammonia. This has been demonstrated by determining reasonable potential based on critical <br />
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