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2900 - Site Mitigation Program
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PR0518600
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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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EHD - Public
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Mr. Kirk Williams • - 4 - • 25 April 2008 <br /> Low-level analyses (SRL 524M) of 1,2,3-TCP are removed from the schedule for upgradient <br /> well MW-10. Concentrations of 1,2,3-TCP on-site are several orders of magnitude greater <br /> than those found in MW-10, and at the present time, knowledge of low levels of 1,2,3-TCP <br /> coming from upgradient sources will not affect remediation or site assessment. As <br /> remediation becomes more complete, low-level analyses should be reinstated in the <br /> upgradient monitoring well. <br /> The monitoring well network also includes redundancy around the center of mass. The <br /> monitoring frequency for some of the redundant wells has been reduced, such as MW-13A <br /> and MW-13B. Immediately downgradient of the center of mass, MW-8 is added to the <br /> monitoring network. In MW-8, 1,2,3-TCP will be measured on a biennial basis. This identifies <br /> if the center of mass is approaching a residential neighborhood. Further downgradient of the <br /> center of mass, MW-6 shall continue to be monitored for herbicides and pesticides. This well <br /> serves as a sentry well for these compounds. <br /> In this draft MRP, two wells will not be regularly sampled for constituents (MW-3 and E-2). <br /> These two wells shall be included in the annual water level monitoring network to ensure that <br /> they are located and inspected at least once a year. <br /> One of the C-zone wells is situated near the center of mass of the constituents (MW-7). This <br /> well serves as a sentry well in the vertical plane and shall continue to be sampled for <br /> constituents observed in the B-zone. <br /> Analytical Methods and Detection Limits <br /> GeoSyntec Consultants identified that in Spring 2002, Western Farm Service sampled <br /> monitoring wells for triazine pesticides, organochlorine compounds, and organophosphate <br /> compounds. Since these analytes were not detected, they are not proposed in the draft MRP. <br /> There are three methods for identifying 1,2,3-TCP in groundwater, each method has a very <br /> different detection limit. The most expensive method has the lowest detection limit. This is <br /> SRL 524M, also referred to as low-level analysis, and can achieve a detection limit of 0.005 <br /> ug/L for 1,2,3-TCP. EPA Method 504.1, the fumigant analysis, can achieve a detection limit <br /> of 0.02 ug/L for 1,2,3-TCP, and EPA Method 8260B (for volatile organic compounds) achieves <br /> 5 ug/L. When concentrations of 1,2,3-TCP are higher than 0.02 ug/L in groundwater, Western <br /> Farm Service may use less expensive methods that have higher detection limits than the low <br /> level method, provided that they are appropriate for the concentrations typically observed. <br /> The draft MRP identifies which of the monitoring points contain 1,2,3-TCP at concentrations <br /> great enough to warrant analyses with higher detection limits. <br /> In 2004, Western Farm Service changed analytical laboratories, which brought about the <br /> following changes: <br /> • the new laboratory cannot meet the detection limits for chlorinated herbicides that was <br /> achievable by the previous laboratory; <br /> • the new laboratory conducts carbamate/urea analyses using EPA Method 632, which <br /> does not include bromacil, whereas the previous laboratory analyzed by EPA Method <br /> 8321, which did include bromacil; <br />
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