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WORK PLANS_PART 2 FILE 1
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WORK PLANS_PART 2 FILE 1
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Last modified
5/26/2020 2:29:55 PM
Creation date
5/26/2020 1:27:03 PM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
FileName_PostFix
PART 2 FILE 1
RECORD_ID
PR0009015
PE
2960
FACILITY_ID
FA0004094
FACILITY_NAME
J R SIMPLOT (OCCIDENTAL CHEMICAL)
STREET_NUMBER
16777
STREET_NAME
HOWLAND
STREET_TYPE
RD
City
LATHROP
Zip
95330
APN
19818005
CURRENT_STATUS
02
SITE_LOCATION
16777 HOWLAND RD
P_LOCATION
07
P_DISTRICT
003
QC Status
Approved
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EHD - Public
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Addendum to the Well Installation and <br /> Hydraulic Testing Report and Additional <br /> ARCADIS Well Installation Work Plan <br /> Former Occidental Chemical Corporation <br /> Lathrop, California <br /> • Extraction from Simplot's primary water supply well at approximately 500 gpm and annual <br /> average extraction rate from the Simplot BSW at 250 gpm based on process water needs and <br /> seasonal historic pumping of the Simplot BSW <br /> • Installation and operation of Lathrop Water District well LWD-21 to the south of the Site and <br /> updated average extraction rates for all Lathrop Water District wells, based on the past six <br /> months of operation (January through June 2012). Total LWD system extraction rates were <br /> comparable to annually-averaged flow rates <br /> • Addition of proposed water table zone well EW-17 near the Ag Chem Area at an annual average <br /> extraction rate of 25 gpm (ARCADIS, 2012b) <br /> • Incorporation of new COC occurrence data collected in 2012, particularly in the Ag Chem Area <br /> (ARCADIS, 2012b), Simplot BSW, and at other locations east of South Howland Road <br /> • A recharge rate of 43%, totaling approximately 107 gpm,was assigned to the field south of <br /> Simplot ponds/lagoons to better represent recharge of the irrigation water.This estimate is based <br /> on ARCADIS'experience at a site in Southern California where extracted groundwater was used <br /> for agricultural purposes. <br /> A summary of the updated groundwater modeling results is presented in Appendix C.The overall goal <br /> of the expanded extraction and injection well network is to increase COC mass removal, in addition to <br /> continuing to maintain plume capture. Extraction wells were therefore placed in areas with high COC <br /> concentrations.The effectiveness of optimization of the treatment system and installation of EW-09 has <br /> already increased sulfolane mass removal and treatment(Figure 5). Over the past year, sulfolane <br /> mass removal has increased by two-fold from approximately 3 pounds per day(lbs/day)to over 6 <br /> lbs/day. <br /> The goal of expedited COC mass removal guided the placement and design flow rates of extraction and <br /> injection wells,within the 700 gpm flow rate limitation of the groundwater treatment system.The <br /> optimized groundwater extraction and injection well network was designed to be dynamic; extraction <br /> well and injection well flow rates will be periodically adjusted in response to measured trends in COC <br /> concentrations and groundwater elevations. As the system continues to operate over the next few <br /> years, additional extraction or injection wells may be necessary or existing wells may be turned off. <br /> A discussion of the detailed plans for extraction and injection within each aquifer zone is provided in <br /> Section 6. <br /> 2012-09-13 addendum well install work plan_hy test rpt.doca 6 <br />
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