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FIELD DOCUMENTS_1982-1985
EnvironmentalHealth
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2900 - Site Mitigation Program
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PR0009002
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FIELD DOCUMENTS_1982-1985
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Last modified
6/17/2020 3:05:54 PM
Creation date
6/17/2020 1:48:37 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
FIELD DOCUMENTS
FileName_PostFix
1982-1985
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
02
SITE_LOCATION
200 N WAGNER AVE
P_LOCATION
99
P_DISTRICT
002
QC Status
Approved
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EHD - Public
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March 5, 1984 <br /> Minimum Conditions for Corrective Actions at the Marley Cooling Tower, <br /> Company, Stockton, San oaquin unty, California <br /> 1 . Within thirty (30) calendar days from the date of settlement, Marley shall <br /> submit to the Department for approval a sampling plan to determine the <br /> areal and vertical extent of soil and groundwater contamination in the <br /> north section of the facility (north of the railroad tracks) . The <br /> samplingrription <br /> an shall include, but shall not be limited to, the following: <br /> a. A desof chemicals to be analyzed and the rationale for <br /> each proposed sample. The analysis should be done for total heavy <br /> metals. For heavy metals other than chromium if the total level for <br /> the metal is between the soluble threshold limit concentration (STLC) <br /> and the total threshold limit concentration (TTLC) , the waste extrac- <br /> tion test (WET) must be done. For chromium, if the total level is <br /> between 5 ppm and 2,500 ppm, the WET must be done. If the soluble <br /> level for chromium based on the 'WET is greater than 5 ppm, then the <br /> sample must be analyzed for hexavalent chromium (Cr VI) . The <br /> procedures to be used for these analyses are those listed in the <br /> California Assessment Manual (CAM) , October 1982, and the limits (TTLC <br /> and STLC) to be used are those listed in the Criteria and Guidlines for <br /> Identification of Hazardous and Extremely Hazardous Wastes, September <br /> 1983. If the draft criteria regulations have been adopted, the <br /> procedures therein shall be followed, except that the chromium limits <br /> above shall be used for determining the need for analysis of <br /> extractable and hexavalent chromium. <br /> b. A systematic waste material, soil and groundwater sampling/analysis <br /> program to define dimensions and depth of hazardous waste deposits <br /> and soil and groundwater contamination. The sampling shall be in a <br /> tight grid pattern in the areas of the retort pit, the drip pad, the <br /> storage tanks, and the waste water percolation pond. The rest of the <br /> site shall be sampled in a more open grid pattern. In the tightly <br /> grided areas soil sampling shall be done immediately beneath the as- <br /> phalt, and at five foot increments down to eighty feet. In the open <br /> grided areas soil sampling shall be done immediately beneath the as- <br /> phalt, at 2 feet, at 5 feet, and 5 foot increments down to forty feet. <br /> In two locations near the highest areas of contamiantion sections of <br /> asphalt shall be removed. Each section of asphalt shall be cut in half <br /> and the one half cut in half again as illustrated below. <br /> PW trt <br /> t.t <br /> L <br /> Each subsection of asphalt shall be analyzed for heavy metals, <br /> specifically arsenic, copper and chromium. <br />
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