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SITE INFORMATION AND CORRESPONDENCE
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Last modified
12/7/2018 10:53:10 AM
Creation date
12/7/2018 10:30:36 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
RECORD_ID
PR0518600
PE
2960
FACILITY_ID
FA0013996
FACILITY_NAME
CROP PRODUCTION SERVICES
STREET_NUMBER
1905
Direction
N
STREET_NAME
BROADWAY
City
STOCKTON
Zip
95205
APN
14315004
CURRENT_STATUS
01
SITE_LOCATION
1905 N BROADWAY
P_LOCATION
99
P_DISTRICT
001
QC Status
Approved
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• MEMORANDUM • <br /> ,CALIFORNIA REGIONAL WATER QUALITY CONTROL BOARD - CENTRA F oAe :LEY 36EGGI�ON <br /> 3443 Routier Road, Suite A ATSS Phone: 8-495-5600 <br /> Sacramento, CA 95827-3098 <br /> FROM: Wendy Wyels <br /> Ag Regulatory Unit <br /> T0: Rudy Chief Ag Regulatory Unit <br /> Wendy Cohen, Chief <br /> Well Investigation Unit <br /> DATE: 21 August 1991 <br /> SIGNATURE: <br /> SUBJECT: REVIEW OF THE PHASE II ASSESSMENT FOR BREA AG, STOCKTON; <br /> SUMMARY OF MEETING <br /> Report Review <br /> Brea Ag's consultants, Kleinfelder, have submitted a "Phase II Soil and Groundwater <br /> Assessment Report" for the Brea Ag facility in Stockton. Construction activities (for <br /> a new liquid fertilizer containment area) began at the site last fall . Because three <br /> dry wells were found where the new concrete pad was to be poured, soil samples were <br /> taken. Construction work stopped, and additional samples (from three borings) were <br /> collected in April . Because the April soil samples contained elevated levels of DDT, <br /> ;i nitrogen, and 1,2-dichloropropane (1,2-DCP) , Brea Ag asked Kleinfelder to do additional <br /> investigative work. <br /> The Phase II investigation encompassed the drilling of two deep soil borings, sampling <br /> groundwater with a BAT probe, and sampling Brea Ag's domestic well . All field work and <br /> analytical work appears adequate. <br /> The soil samples show decreasing amount of nitrate, and total Kjeldahl <br /> the highest concentrationstions of nitrate was from 31- <br /> nitrogen (TKN) with depth, although <br /> 61' below ground surface. <br /> ntered at 78' , the borings were advanced to 81' and <br /> Although groundwater was first encou <br /> 911 . Nitrate-nitrogen was detected at concentrations of 1T2.8 andhe 20.7 pfor bothDabo e <br /> the MCL of 10 ppm. 1,2-DCP was found at 27 and 8.8 ppb <br /> is <br /> 5 ppb; however, EPA's 1-in-a-million cancer risk estimate is 0.5 ppb. <br /> There are two errors in the "Conclusions and Recommendations" section of the report. <br /> 1 . Kleinfelder states that there is "a proposed MCL of 0.5 ug/l for 1,2-DCP in <br /> drinking water . According to Dr. Jon Marshack, and his "Water quality Goals" <br /> booklet, the EPA primary MCL goal for 1,2-DCP is 5.0 ppb, and the EPA 1 . In <br /> million cancer risk is 0.5 ppb. These numbers have been b�numberdwould be used <br /> setting clean-up goals for the groundwater basin, the 0.5 pp <br /> because our Basin Plan states that there be no toxicity in groundwater, and DHS has <br /> determined that cancer risk numbers are equated with toxicity. <br /> 2. Kleinfelder states that "TKN is the total amount of nitrogen available in a given <br /> sample. This is not correct. According to "Standard Methods," the TKN analysis <br /> determines nitrogen forms in the trinegative state, and does not take into account <br /> nitrate, nitrite, nitrile, and other more esoteric forms of nitrogen. Therefore, <br />
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