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ARCHIVED REPORTS XR0000736
EnvironmentalHealth
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3500 - Local Oversight Program
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PR0544155
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ARCHIVED REPORTS XR0000736
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Last modified
2/15/2019 4:43:36 PM
Creation date
2/15/2019 1:57:37 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0000736
RECORD_ID
PR0544155
PE
3526
FACILITY_ID
FA0000185
FACILITY_NAME
CITY GAS & LIQUOR
STREET_NUMBER
16470
STREET_NAME
CAMBRIDGE
STREET_TYPE
ST
City
LATHROP
Zip
95330
APN
19643032
CURRENT_STATUS
02
SITE_LOCATION
16470 CAMBRIDGE ST
P_LOCATION
07
P_DISTRICT
003
QC Status
Approved
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EHD - Public
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i <br /> F1 S ECOR <br /> ATTACHMENT G <br /> f FIELD AND LABORATORY PROCEDURES <br /> Exploratory Drilling <br /> F Vertical delineation soil borings were advanced using narrow diameter, direct push <br /> technology to approximately 70 feet below ground surface. Barings were logged by a <br /> F1 SECOR International Incorporated geologist using the Unified Soil Classification System and <br /> standard geologic techniques. Soil samples for logging will be collected continuously. Soil <br /> samples for chemical analysis were retained in acetate tubing, capped with Teflon squares <br /> and plastic end caps, and sealed in clean zip-lock bags. Groundwater samples were <br /> F1 collected using a hydropunch sampler and clean dedicated acetate tubing attached to a <br /> peristaltic pump. The samples were placed on ice for transport to the laboratory <br /> accompanied by chain-of-custody documentation. Down-hole drilling and sampling <br /> I F <br /> equipment was steam-cleaned prior to and following the completion of each soil boring. <br /> Down-hole sampling equipment was washed in a tri-sodium phosphate or alconox solution <br /> a <br /> between samples. <br /> Borings for wells were drilled using 8-inch hollow-stem auger drilling equipment. No soil <br /> samples were collected from the borings. <br /> F", <br /> Groundwater Monitoring Well Installation and Development <br /> Each groundwater monitoring well was completed by installing a 2-inch diameter, flush- <br /> r- threaded, schedule 40 PVC casing with 0.020-inch factory-slotted screens. Approximately <br /> 20 feet of screen was used to construct the monitoring wells. A #3 sand pack was placed in <br /> the annular space across the screened interval, extending approximately 2-feet above the <br /> top of the screen. A 2-foot bentonite transition seal was placed atop the sand pack, followed <br /> by a neat cement seal, extending from the top of the bentonite transition seal to the ground <br /> surface. The boring logs show well construction details. <br /> The development procedure for each well consisted of swabbing the screen interval and <br /> ` pumping or bailing approximately ten casing volumes of water from the wells. The well <br /> development sheets are included in Appendix F. <br /> Soil Cuttings and Purge Water <br /> Soil cuttings generated during drilling operations and water generated during equipment <br /> cleaning and sampling were stored onsite in 55-gallon drums onsite pending <br /> characterization. The soil and water will be removed from the site by a licensed disposal <br /> contractor and transported to an appropriate disposal or treatment facility for proper disposal. <br /> Laboratory Procedure <br /> Soil samples exhibiting positive PID detections or a minimum of three samples from each <br /> boring (including the deepest sample) were analyzed for TPHg, BTEX, and fuel oxygenates <br /> F: <br /> (MtBE, EtBE, DIPS, TAME, TBA, EDB, 1,2-DCA, and ethanol) by EPA Method 8260B and <br /> F ' for total lead using EPA method 60106. <br /> L1{ <br /> F'. <br /> r • <br />
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