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ARCHIVED REPORTS XR0012675
Environmental Health - Public
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EHD Program Facility Records by Street Name
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3500 - Local Oversight Program
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PR0544638
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ARCHIVED REPORTS XR0012675
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Last modified
7/9/2019 3:41:34 PM
Creation date
7/9/2019 1:43:44 PM
Metadata
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Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0012675
RECORD_ID
PR0544638
PE
3528
FACILITY_ID
FA0004027
FACILITY_NAME
HENDRIX FORK LIFT INC
STREET_NUMBER
103
Direction
N
STREET_NAME
E
STREET_TYPE
ST
City
STOCKTON
Zip
95205
APN
15318001
CURRENT_STATUS
02
SITE_LOCATION
103 N E ST
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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�a <br /> J. H. KLEINFELDER&ASSOCIATES <br /> File: 24-1045-2/271704 `�- --•� `1� ,�c . <br /> r December 1, 1986 <br /> Page 2 <br /> A1,11 <br /> laboratory <br /> laboratory for quantified chemical analysis. After proper developmenlikSa <br /> water sample will be collected from the monitoring well and delivered to a <br /> State approved laboratory for chemical analysis. A report presenting <br /> information obtained from field and laboratory activities would be <br /> prepared. <br /> Soil BoriagslSoil-SamRling <br /> We recommend the placement of one initial soil boring B-1 at the <br /> proposed location shown on Plate 1. Should volatile hydrocarbons be <br /> detected by field screening in the initial boring, four additional borings <br /> B-2 through B-5 would be drilled at locations shown on Plate 1. The <br /> borings would be drilled by a truck-mounted drilling rig with hollow stem <br /> auger. To minimize the possibility of cross contamination, all auger and <br /> associated drilling equipment would be steam cleaned prior to the drilling <br /> of each boring. The soil sampler and brass liners would be cleaned in a <br /> trisodium phosphate bath followed by a tap water bath and final distilled <br /> water rinse before the collection of each sample. <br /> Soil samples would be collected at five foot intervals from each . <br /> boring, starting at the surface and terminating 10 feet above anticipated <br /> standing ground water. Soil samples would be collected by advancing the <br /> boring to a point immediately above the sampling depth and then driving a <br /> Modified California Sampler into the soil.. Samples will be screened in <br /> the field for volatile hydrocarbons with a portable field photoionization <br /> detector (PID) and then sealed with aluminum foil and plastic caps. The <br /> samples would be immediately stored in an iced cooler under <br /> chain-of-custody. Upon completion of drilling and sampling, the boring <br /> would be backfilled with a cement-bentonite alurry to minimize the <br /> possibility of creating a conduit for contaminant transport from the <br /> surface to groundwater. <br /> Wall -Construction <br /> If the initial boring contains petroleum hydrocarbons, a monitoring <br /> well would be completed in one of the soil borings. According to our <br /> estimates, ground water should be encountered approximately 40 to 60 feet <br /> below the ground surface. The monitoring well would be completed to a <br /> depth of 15 feet below the ground water table or five feet into'the first <br /> saturated clay layer encountered. The wells will be constructed of <br /> two-inch flush threaded PVC pipe, perforated with 20 feet of 0.020 inch <br /> machine—slotted--screen. -I f—the—aquifer_-is--found-to be--in aconfined-- <br /> condition, <br /> confined condition, the well screen would begin at the depth where water was first <br /> encountered. If it is unconfined, the well screen would extend 5 feet <br /> above ..the water table. The termination of the well will be a maximum of <br /> 15 feet below the water table or into the first competent clay layer below <br />
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