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ARCHIVED REPORTS_XR0007983
Environmental Health - Public
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2900 - Site Mitigation Program
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PR0522692
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ARCHIVED REPORTS_XR0007983
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Last modified
4/2/2020 4:57:08 PM
Creation date
4/2/2020 4:20:03 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0007983
RECORD_ID
PR0522692
PE
2957
FACILITY_ID
FA0015465
FACILITY_NAME
FORMER MONTGOMERY WARDS AUTO SRV CTR
STREET_NUMBER
5400
STREET_NAME
PACIFIC
STREET_TYPE
AVE
City
STOCKTON
Zip
95207
APN
10227008
CURRENT_STATUS
01
SITE_LOCATION
5400 PACIFIC AVE
P_LOCATION
01
P_DISTRICT
002
QC Status
Approved
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EHD - Public
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PHASE VI SUBSURFACE INVESTIGATION Site Code 2163 <br /> Montgomery Ward Auto Service Center <br /> 5400 Pacific Avenue,Stockton, CA <br /> geologists The borings MW-4 through MW-6 were drilled to a depth of 68 feet bgs, while <br /> boring MW-3 had a termination depth of 67 feet bgs (see Figure 2) The borings were dnlIed <br /> using 10'/4-inch outside diameter continuous flight hollow stem augers Mr Mike Infurna of the <br /> County was on-site during most of the drilling and sampling activities All borings were logged <br />' in accordance with the Unified Soil Classification System (see Appendix A) <br /> Soil samples were obtained from each boring beginning at approximately five feet bgs and at <br /> approximately five-foot intervals thereafter until 65 feet bgs The samples were collected using <br /> six 2'/2-inch diameter by three-inch long brass tubes mounted within a 2'/z-inch inside diameter <br /> Modified California split-spoon drive sampler The sampler was attached to the down-hole <br /> hammer, lowered to the sampling depth, and then driven into the formation for the length of the <br />' sampler Hammer counts per six-inch of penetration of the barrel sampler were recorded to <br /> measure the consistency of the formation After sample recovery, the ends of the lowermost <br /> three-inch long tube were covered with aluminum foil and plastic caps taped over the ends <br />' Prior to use, all tubes were washed in a solution of Alconox detergent and tap water, rinsed with <br /> tap water and then with distilled water The samples were labeled with the sample point <br /> identification, EAT project number, depth interval, time and date, individually sealed in "Ziploc" <br />' plastic bags, and immediately placed into an ice chest chilled using crushed ice The samples <br /> were kept chilled until delivered to the laboratory for analytical testing All samples «ere <br /> logged on chain of custody record forms (see Appendix B) <br /> An HNU Model DL-101 Phototonizer/Datalogger calibrated against an isobutylene gas standard <br /> was used on soil contained in the second tube from the bottom of the shoe, at each sampling <br /> interval within the borings to determine if volatile hydrocarbon vapors were emanating directly <br /> from the soil Each sample was placed in an airtight "Ziploc" plastic bag The samples were <br /> allowed to sit in the sun, and then the head space in the bags was analyzed using the IDI U <br /> Photoionizer The results of this testing were recorded on the boring logs (see Appendix A) <br />' 3 2 MONITORING WELL CONSTRUCTION & DEVELOPMENT <br /> Borings MW-3 through MW-6 were converted to ground water monitoring wells MW-3 through <br />' MW-6, respectively (see Figure 2) Appendix C contains the County permit issued for <br /> construction of the wells All wells are constructed of four-inch inside diameter flush threaded <br /> Schedule 40 polyvinyl chloride (PVC) well casing The wells are designed with a slotted section <br />' (0 02-inch x two-inch slots) which extended from approximately 48 feet bgs to the termination <br /> depth of each well The annular space between the borehole wall and well casing was backfilled <br /> with grade #3 Morie sand to about two feet above the slotted section Aur e block was then <br /> used on the well to help develop the well and to set the sand pack surrounding the casing After <br />' using the surge block, additional sand was added to the annular well space until the top of the <br /> sand pack was two feet above the slotted section A two-foot thick layer of hydrated quarter- <br /> inch diameter bentonite pellets was placed directly on top of the sand pack as a sanitary seal, and <br />' the remaining annular space was backfilled with cement grout to the surface The grouting <br /> material used was Portland Neat Cement type II Potable water was used for mixing grouting <br /> materials Flush mounted lockable traffic grates are placed on all the wells Further, the grates <br /> are designed to prevent sheet flow from entering the wells appendix D contains the specific <br /> well construction details for each well Mr Mike Infurna of the County was present during the <br /> grouting of the wells <br /> The wells were developed on February 8, 1995 approximately two weeks after well installation <br /> Well development was performed by V & W Drilling Inc , using a Mobil B-61 HDX rig <br /> equipped with an eight-foot long, 3'/2-inch diameter stainless steel bailer The balling equipment <br /> 1 <br /> Project No 1232 5 ENVIRONMENTAL AUDIT, INC <br />
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