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ARCHIVED REPORTS_XR0003506
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ARCHIVED REPORTS_XR0003506
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Last modified
2/3/2020 12:33:04 PM
Creation date
2/3/2020 11:50:27 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0003506
RECORD_ID
PR0545285
PE
3528
FACILITY_ID
FA0006068
FACILITY_NAME
PALADIN MILEAGE CENTER
STREET_NUMBER
2421
STREET_NAME
HOLLY
STREET_TYPE
DR
City
TRACY
Zip
95376
CURRENT_STATUS
02
SITE_LOCATION
2421 HOLLY DR
P_LOCATION
03
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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v y I <br /> L <br /> 16 October 1996 <br /> AGE-NC Project No 96-0211 <br />' s Page 2 of 6 <br /> 2 3 GROUND WATER DEPTH AND FLOW DIRECTION <br /> r I <br /> Based on data obtained from monitoring wells located on nearby properties, ground water depth in <br /> the area of the site is'approximate ly 5 to 6 feet below surface grade (bsg) Regional ground water <br />' flow direction is north or northeast, however, ground water flow direction can vary locally and <br /> seasonally ' <br /> 1 , <br /> 30. PROCEDURES <br /> 3 1 MONITORING WELL INSTALLATION <br />' 3 1 1 DRILLING AND SOIL SAMPLING <br /> On 02 July 1996, four soil borings were drilled on the site to a depth of fifteen feet bsg Boring B 1 <br />' was advanced west of the former UST dispensers and backfilled with grout to the surface A grab <br /> gourd water sample was collected from boring B 1 Boring B2 was advanced south of t1=c former <br /> UST dispensers and was converted to monitoring well MW-3 Boring B3 was advanced northeast <br /> of the,former UST dispensers and converted to monitoring well MW-2 Boring B4 was advanced <br /> on the northein edge of the site and completed as ground water monitoring well MW-1 <br /> The installation of MW-I through MW-3 was performed rising a truck-mounted CME 75=H I drill <br /> rig equipped with continuous Dight, eight inch hollow-stem augers Fhe drill rig and two-pian ci ew <br />' were supplied by Soils Exploration Services (SES) of Benicia, California' The locations of the <br /> borings are shown on Figure 2 <br /> Samples were collected in each boring using a split tube sampler loaded with three clean, 2- by 6- <br /> inch brass sleeves A 140-pound hammer was used to advance the sampler eighteen inches the <br /> p p g <br /> number of blows required to advance the sampler in six-inch increments was recorded on the boring <br />' logs All sampling equipment was washed in an Alconox solution and rinsed twice with water prior <br /> to each sampling run <br /> The leading soil-tilled sampling sleeve was preserved for laboratory analysis Both ends of the <br /> leading sleeve were covered with Teflon sheets, capped and sealed with tape The samples were <br />' labeled, stored in a chilled) container and transported under chain-of-custody to McCampbell <br /> r Analytical, Inc (MAI) in Pacheco, California <br /> F <br />' Selected samples were analyzed for total petroleum hydrocarbons quantified as gasoline (TPH-g), <br /> volatile aromatics (benzene, toluene, ethyl benzene and xylenes BTE&X) with methyl-tert-butyl <br /> ether(MTBE) in accordance with EPA methods 5030/8015m and 8020, respectively <br /> 1 4 I <br /> I ` I <br />
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