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FIELD DOCUMENTS AND WORK PLANS 1988
Environmental Health - Public
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FIELD DOCUMENTS AND WORK PLANS 1988
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Last modified
2/22/2019 9:26:14 PM
Creation date
2/22/2019 2:35:11 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
FIELD DOCUMENTS
FileName_PostFix
AND WORK PLANS 1988
RECORD_ID
PR0009002
PE
2960
FACILITY_ID
FA0004040
FACILITY_NAME
SPX COOLING TECHNOLOGIES INC
STREET_NUMBER
200
Direction
N
STREET_NAME
WAGNER
STREET_TYPE
AVE
City
STOCKTON
Zip
95215
APN
14331007
CURRENT_STATUS
01
SITE_LOCATION
200 N WAGNER AVE
P_LOCATION
99
P_DISTRICT
002
QC Status
Approved
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INFORMATION SHEET • • <br /> MARLEY COOLING TOWER CO. <br /> STOCKTON, SAN JOAQUIN CO. -2- <br /> The Stockton Diverting Canal is an engineered drainage way connecting Upper Mormon <br /> Slough to the Calaveras River near the Southern Pacific Railroad crossing. Upper <br /> Mormon Slough is actually the South Fork of the Calaveras River below Bellota. <br /> From 1 October to 1 April every year, the East Stockton Water District dams the <br /> Calaveras River at its fork with Upper Mormon Slough, thus diverting all flows <br /> through Upper Mormon Slough and the Stockton Diverting Canal . <br /> From 1 April to 1 October every year, flows are split between the Calaveras River <br /> and Upper Mormon Slough. A series of check dams are installed along the Calaveras <br /> River, Upper Mormon Slough, and the Stockton Diverting Canal to provide irrigation <br /> water for adjacent farmers. During this time, there are periods of no flow in the <br /> Stockton Diverting Canal . <br /> Basis for Effluent Limitations <br /> The beneficial uses of the Stockton Diverting Canal are industrial and agri- <br /> cultural supply; recreation; esthetic enjoyment; navigation; and preservation of <br /> fish and wildlife. These uses are protected by basing effluent limitations on <br /> standards to protect aquatic life, human health, agricultural irrigation, and the <br /> Regional Board's Basin Plan Objectives. The applicable standards for each of the <br /> potential contaminants at MCTC are shown in Table 1. <br /> Table 1 standards reflect acceptable levels for instream uses. To determine <br /> effluent limits, the most restrictive standard for each constituent was selected. <br /> Thus , the respective values used were 6.5 ug/l for Copper, 50 ug/l for Total <br /> Chromium, 11 ug/l for Hexavalent Chromium, 10 ug/l for Arsenic, and 500 mg/l for <br /> Total Dissolved Solids. <br /> Since conditions of no flow do exist in the Stockton Diverting Canal , the initial <br /> effluent limits were set without considering any dilution. Thus, the limits <br /> require effluent quality equal to instream requirements based on the most <br /> stringent standard for each constituent above (Effluent Limit A.1.) . <br /> For periods of increased flow, the resultant dilution capacity of the Diverting <br /> Canal was afforded Marley' s discharge. Formulas for determining alternative Daily <br /> Maximum and Monthly Average limits were developed. Adjusted Daily Maximum limits <br /> are based on a 1 :1 dilution ratio of the discharge to the receiving stream flow. <br /> This allows some flexibility in day-to-day plant operations without exceeding <br /> instream use standards. Adjusted Monthly Average limits use a factor of safety of <br /> three times the average monthly discharge rate. This utilizes dilution capacity <br /> of the stream while maintaining a margin of safety for instream values. <br /> No limits were allowed to exceed drinking water standards since treatment tech- <br /> nology exists and to limit the total mass loadings to the Calaveras River and the <br /> Delta. Thus, limits were set at 65 ug/l for Copper, 50 ug/l for Total Chromium, 50 <br /> ug/1 for Arsenic, and 1000 ng/l for Total Dissolved Solids (Effluent Limitation <br /> A.2.) . Additionally, constituent values in the downstream receiving water must <br /> not exceed the selected use standards (Receiving Water Limitation D.1.) <br /> Revised:GAR:gs:6/0;/88 <br />
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