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ARCHIVED REPORTS XR0011295
EnvironmentalHealth
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EHD Program Facility Records by Street Name
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DURHAM FERRY
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1600
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3500 - Local Oversight Program
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PR0544624
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ARCHIVED REPORTS XR0011295
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Entry Properties
Last modified
7/3/2019 7:19:46 PM
Creation date
7/3/2019 3:48:44 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0011295
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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Geoloywaf'TecFuucs Inc Page 3 <br /> Groundwater Monitoring Report <br /> • Project No 425 2 <br /> November 17, 1997 <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 is used to gauge the interface <br /> Stagnant water in the well casing was purged using either a Grundfos pump or electronic <br /> bailer as recorded m the field logs (Appendix C) The rate of well purging was monitored <br /> The wells were purged of at least three casing volumes and until the groundwater parameters <br /> (temperature, conductivity, and pH) had stabilized (Appendix Q indicating that water, <br /> representative of actual aquifer conditions, was entering the well Groundwater parameter <br /> stabilization was characterized by three successive readings within 10% In this case the <br /> instrument was not calibrating properly, and pH measurements were not considered reliable <br /> Before a sample was collected, the welI's water level was allowed to recharge to at least 80% <br /> of it's 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-sate <br /> A bailer was used to collect each sample Bailer cleanliness was assured by collecting a <br /> bailer blank (pouring distilled water through the bailer and collecting it in a VOA vial) prior <br /> to collecting the analytical sample <br /> Extreme care was exercised whale collecting samples to prevent agitation of the water <br /> contained in the bailer Water samples were transferred from the bailer into 40 ml VOA vials <br /> preserved with hydrochloric acid using a bottom emptying device which minimizes sample <br /> aeration during transfer of the sample All samples were checked for head space bubbles, <br /> labeled, inserted into foam holders and placed in an ace chest cooled to 4°C for transport to <br /> the laboratory <br /> Disposable gloves were worn by the sampling technician while collecting all samples <br /> A chain of custody document, listingall collected and their intended samples p analyses, <br /> accompanied the samples from field to the laboratory, thereby providing a means to track <br /> their movement and insure their integrity <br /> 1.3 Laboratory Analyses <br /> The groundwater samples collected on September 19, 1997 were delivered to Sherwood Lab <br /> (Department of Health Services Certification No 1400), of Hilmar, California, for analysis <br /> The samples were analyzed using the following methods <br /> o EPA method 602 - BTEX <br /> i o EPA method 5030/8015(m) - TPH-Gasoline <br /> o EPA method 8260 - Ethanol, Tertiary Butanol, MTBE, DIPS, ETBE and TAME <br />
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