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SITE INFORMATION AND CORRESPONDENCE
Environmental Health - Public
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2900 - Site Mitigation Program
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PR0505548
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SITE INFORMATION AND CORRESPONDENCE
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Last modified
5/17/2019 9:18:25 AM
Creation date
5/17/2019 8:58:06 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
RECORD_ID
PR0505548
PE
2960
FACILITY_ID
FA0006852
FACILITY_NAME
OCCIDENTAL CHEMICAL CORP
STREET_NUMBER
1904
Direction
W
STREET_NAME
CHARTER
STREET_TYPE
WAY
City
STOCKTON
Zip
95205
APN
16302041
CURRENT_STATUS
01
SITE_LOCATION
1904 W CHARTER WAY
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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Mr. Frank Barone • - 2 - • 22 January 2008 <br /> MW-30 Work Plan <br /> The Annual 2007 Report proposes to install MW-30 about 350 feet downgradient of <br /> MW-27. It is proposed to have a screened interval between about 12 and 27 feet below <br /> ground surface, similar to MW-27 and other shallow monitoring wells in the vicinity. <br /> Exploratory borings logged by'Geomatrix in 1997 and 1999 show that an upper sand <br /> lens is expected to be intercepted between 12 and 30 feet below ground surface. <br /> Regional Water Board staff concur with the work plan to install MW-30. As stated in the <br /> Annual 2007 Report, the monitoring well will be installed by March and sampled in <br /> conjunction with the first semi-annual groundwater monitoring event, which occurs in <br /> the first quarter (January-March). <br /> Please provide the boring log and monitoring well installation diagram and a brief <br /> description of the installation in the next semi-annual monitoring report, which is due <br /> 1 June 2008. <br /> Groundwater Gradient Trends <br /> Geomatrix Consultants discovered a leak in an irrigation pipe that created a <br /> groundwater mound beneath the facility. The pipe was repaired in October 2007, but <br /> the mound interfered with the ability to establish whether phytoremediation is exerting <br /> hydraulic control over the groundwater plume. Geomatrix will provide an analysis of <br /> hydraulic capture in the fall of 2008, which will be reported in the 2008 annual <br /> monitoring report, which is due by 1 December 2008. <br /> Soil Sampling Results <br /> As presented in the Soil Sampling Report, discrete soil sampling data is obtained semi- <br /> annually from depths ranging from soil surface to five feet below ground surface. The <br /> data has been collected since 2003 and show that over time, nitrogen concentrations <br /> are declining between the soil surface and three feet deep. Between three and five feet <br /> below ground surface, the data does not show a clear trend of either decreasing or <br /> increasing concentrations of nitrogen. The cleanup goal for nitrogen in soil is <br /> 200 mg/kg, which is exceeded in about 30% of the soil samples. The data show that <br /> nitrate is not accumulating in the soil profile. <br /> The soil analyses include tests for carbamate/urea compounds, organochlorine <br /> compounds, triazines, chlorinated herbicides. Triazine compounds and chlorinated <br /> herbicides have not been detected in any soil samples since 2005. Organochlorine <br /> compounds DDT and endrin are found in the upper foot of soil at concentrations below <br /> the cleanup goals. Carbamate compounds bromacil, diuron and tebuthiuron are <br /> generally also found in the upper three feet of soil, and consistently have been below <br /> the cleanup goals. <br /> Revision to Soil Sampling Schedule <br /> Four years of semi-annual soil sampling have shown that organic constituents of <br /> concern are consistently below cleanup goals and are not increasing in the soil profile. <br /> The soil sampling program proposed in the 2001 Phytoremediation Work Plan prepared <br /> by Geomatrix Consultants may be reduced in scope and frequency. MSRMI may <br /> discontinue analyses for organic constituents in soil, and may sample annually for <br />
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