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ARCHIVED REPORTS_XR0005707 CASE 2
Environmental Health - Public
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ARCHIVED REPORTS_XR0005707 CASE 2
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Last modified
9/24/2020 12:29:38 AM
Creation date
8/6/2020 11:27:40 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0005707 CASE 2
RECORD_ID
PR0545951
PE
3528
FACILITY_ID
FA0003612
FACILITY_NAME
Yosemite Avenue Arco AmPm
STREET_NUMBER
1711
Direction
E
STREET_NAME
YOSEMITE
STREET_TYPE
Ave
City
Manteca
Zip
95336
CURRENT_STATUS
02
SITE_LOCATION
1711 E Yosemite Ave
P_LOCATION
04
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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URS <br /> Mr Mike Infurna Page 3 <br /> San Joaquin County Environmental Health Department <br /> ARCO 6020 <br /> September 29, 2003 <br /> was 35 feet bgs, MW-12 was drilled to a depth of 37 5 feet, and MW-13D was drilled to 70 feet bgs First <br /> groundwater was encountered at approximately 25 feet bgs in each boring <br /> Soil samples were collected at 5-foot intervals with a modified California split-spoon sampler The soils were <br /> logged by a URS geologist according to the Unified Soil Classification System No hydrocarbon staining, <br /> odor,or photoionization detector(PID)readings were noted for any of the soil samples Soil boring logs are <br /> included as Attachment C <br /> Selected soil samples were retained for laboratory analysis from each soil boring The soil samples were <br /> sealed in 2-inch-diameter brass sleeves with Teflon squares and plastic end caps The samples were then <br /> labeled and placed on ice in a cooler, pending delivery to Sequoia Analytical Laboratories in Petaluma, <br /> California The soil samples were analyzed for TPHg,benzene,toluene,ethylbenzene,and xylenes(BTEX), <br /> and for fuel oxygenates and additives including MtBE,tert-butyl alcohol(TBA),di-isopropyl ether(DIPE), <br /> ethyl tert-butyl ether(ETBE),TAME, 1,2-dichloroethane(1,2-DCA),ethylene dibromide(EDB),and ethanol, <br /> by EPA Method 8260B <br /> All downhole sampling equipment was decontaminated between samples by washing in a non-phosphate <br /> detergent solution Rinsate water was contained in DOT-approved, 55-gallon drums and stored on site <br /> pending sampling results and subsequent disposal <br /> The monitoring wells were constructed using 2-inch-internal diameter (ID), schedule 40, flush-threaded <br /> polyvinyl chloride(PVC)well casing Twenty feet of 020-inch machine-slotted well screen was set from 15 <br /> to 35 feet bgs m MW-11 and MW-12 Five feet of 0 020-inch machine-slotted well screen was set from 65 to <br /> 70 feet bgs in well MW-13D A Monterey No 3 silica sand filter pack was installed from the bottom of the <br /> boring to 2 feet above the well screen A 2-foot bentonite seal was placed above the sand pack Bentonite- <br /> cement grout was used to sea]the remaining annular space to the surface The wells were completed with 8- <br /> inch flush-mounted well boxes,and locking,water-tight well caps Well construction details are shown on the <br /> boring log in Attachment C Field and laboratory procedures are presented in Attachment D <br /> Groundwater Monitoring Well Development, Sampling, and Surveying. <br /> On July 24, 2003, Blaine Tech Services of San Jose, California,developed the newly installed groundwater <br /> monitoring wells by rigorously surging over the length of the screen interval and by purging 10 casing <br /> volumes of water from each well Well development field sheets are included as Attachment E <br /> On July 28,2003,Blaine Tech Services collected groundwater samples from the site groundwater monitoring <br /> wells, including the three new wells Groundwater samples were analyzed for TPHg, BTEX, and fuel <br /> oxygenates by EPA Method 8260B Attachment E presents detailed groundwater sampling field sheets <br /> K IWprocessU5 BP ARCO\0602012003 Assessment16020 Assessment&SCM 2003 doc <br />
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