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ARCHIVED REPORTS XR0011342
EnvironmentalHealth
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3500 - Local Oversight Program
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PR0544624
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ARCHIVED REPORTS XR0011342
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Entry Properties
Last modified
7/3/2019 6:27:54 PM
Creation date
7/3/2019 3:53:28 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0011342
RECORD_ID
PR0544624
PE
3526
FACILITY_ID
FA0005206
FACILITY_NAME
GEORGES SERVICE
STREET_NUMBER
1600
Direction
W
STREET_NAME
DURHAM FERRY
STREET_TYPE
RD
City
TRACY
Zip
95376
APN
25510004
CURRENT_STATUS
02
SITE_LOCATION
1600 W DURHAM FERRY RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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' Geologwaf?echnics 2nc Page 3 f - <br /> Groundwater Monitoring Report <br /> Project No 425 2 <br /> June 9, 2000 <br />' Table 2 of Appendix A summarizes the intermediate depth groundwater gradients and levels <br /> to date Table 2 also summarizes the groundwater level data from the deep well, MW-202 <br />' Figure 2 is a map showing both the water table and intermediate groundwater gradients <br />' 1.1.2 Vertical Groundwater Gradients <br /> Vertical groundwater gradients were calculated using MW-2 / 102 (shallow/intermediate well <br /> pair) and MW-102 / 202 (intermediate/deep well pair) During the March 2000 event the <br /> vertical groundwater gradient in the shallow/intermediate well parr was in an upward <br /> direction with a magnitude of 18 Mmes that of the horizontal gradient The vertical gradient <br /> in the intermediate/deep well pair was also upward at a magnitude 9 times that of the <br /> horizontal gradient <br />' This site has experienced both negative (downward) vertical gradients and positive (upward) <br /> vertical gradients Typically the negative vertical gradients are 1 75 to 2 times greater than <br />' gradients in a horizontal direction and the positive vertical gradients are an order of <br /> magnitude greater than horizontal <br /> Refer to Table 3 of Appendix A for a summary of the vertical gradients calculated <br /> 1.2 Groundwater Sampling Procedure <br /> On March 31, 2000 Del-Tech Geotechnical Support personnel arrived on-site, opened the <br /> wells, and measured the depth to water with an electrically actuated sounding tape The <br /> water level reading was recorded to an accuracy of 0 01 foot In wells where free floating <br /> product was suspected, a clear disposable bailer was used to gauge the interface <br /> Stagnant water in the well casing was purged using a Centrifugal pump as recorded in the <br /> field logs (Appendix C) The rate of well purging was monitored The wells were purged of <br /> at least three casing volumes or until the groundwater parameters (temperature, conductivity, <br /> and pH) had stabilized (Appendix Q indicating that water, representative of actual aquifer <br /> conditions, was entering the well Groundwater parameter stabilization was characterized by <br /> ' three successive readings within 10% <br /> Before a sample was collected, the well's water level was allowed to recharge to at least 80% <br /> of its initial level All water removed from the monitoring wells and not used as a sample, <br /> was placed in a 55 gallon DOT (Department of Transportation 17-H) approved container that <br /> is properly labeled and temporally stored on-site <br /> 1 <br />
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