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2900 - Site Mitigation Program
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PR0009063
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Entry Properties
Last modified
5/20/2024 1:41:40 PM
Creation date
5/2/2019 1:23:01 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0009063
PE
2960
FACILITY_ID
FA0003785
FACILITY_NAME
PACIFIC TRIPLE E LTD
STREET_NUMBER
8690
Direction
W
STREET_NAME
LINNE
STREET_TYPE
RD
City
TRACY
Zip
95304
APN
253-210-180-00
CURRENT_STATUS
01
SITE_LOCATION
8690 W LINNE RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
Scanner
WNg
Tags
EHD - Public
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L3 Pumping from New Extraction Well XW-1 <br /> An extraction well XW-1 will be constricted near MW-6, approximately 50-100 feet to the west <br /> of the existing MW-6, and located so as to minimize impact to the existing orchard. The <br /> extraction well will be designed according to Figure 4. The well will be drilled by a licensed well <br /> drilling contractor according to state regulations. Samples of aquifer material from the well will be <br /> collected every five feet below the water table and particle size analyses will be performed on at <br /> least three of the samples. The sandpack and screen slot size will be specified after results of the <br /> geologic logging and particle size analysis are available. T1iese materials will be chosen so as to <br /> maximize efficiency of the well. '11le well will be constructed and completed with a surface seal of <br /> at least 50 feet depth. <br /> 77ie necessary piping and electrical connections will be installed to the XW-1 site and pumping <br /> will commence at a rate of 20 gpm. Water will be transported back to the former rinsewater pond <br /> for treatment as described below. <br /> 3.4 'I3ie effect of pumping_on downgradient monitoring well MW-7 <br /> The model simulation shown in Figure 5 predicts that pumping from XW-t will contain the plume <br /> by creating a capture zone in the groundwater table that will enclose MW-7. The model predicts <br /> that the capture zone will have reached 300 feet beyond MW7 within a year. The effects of <br /> pumping should cause chloroform concentrations in MW-7 to return to background. It cannot be <br /> known at this time, when this will happen because actual pumping response may vary. Quarterly <br /> monitoring of MW-7 will continue, and decreases in chloroform concentrations after pumping has <br /> begun will be an indication that pumping is effective at containing the plume. <br /> 4. Disposal of Extracted Groundwater <br /> Water pumped from MW-4A and XW-1 will be aerated in the old rinse water pond and <br /> recirculated into the aquifer to provide oxygen to the bioremediation program. Water from XW-I <br /> will increase by four fold the amount of water returning to the pond (presently only water from <br /> MW-4A is aerated). As shown in Figure 5, the pumping activity at MW4-A and XW-I should <br /> recapture any water introduced through the pond. A Report of Waste Discharge (Appendix F) <br /> has been filed to document the ongoing practice of recirculating aquifer water from MW-4A <br /> through the pond and to prepare WDR for the additional quantities of water from pumping XW- <br /> 1. 'llic water being returned to the aquifer through the aeration pond is not only richer in oxygen, <br /> but it is also lower in chloroform than the groundwater being extracted. Sampling of pond water <br /> performed in May of 1994 indicated that water flowing into the pond from MW-4A contained <br /> 375 ug/l chloroform, whereas water from the surface of the pond which had passed through the <br /> aerator system contained only 32 ug/I chloroform. Venting of chloroform to the air in this manner <br /> L-a 1 1 <br /> CONDOR <br />
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