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ARCHIVED REPORTS_XR0012337
Environmental Health - Public
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EHD Program Facility Records by Street Name
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M
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MARCH
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2701
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3500 - Local Oversight Program
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PR0545517
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ARCHIVED REPORTS_XR0012337
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Last modified
3/12/2020 12:15:06 AM
Creation date
3/11/2020 11:14:45 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0012337
RECORD_ID
PR0545517
PE
3528
FACILITY_ID
FA0003798
FACILITY_NAME
MARCH LANE 76*
STREET_NUMBER
2701
Direction
W
STREET_NAME
MARCH
STREET_TYPE
LN
City
STOCKTON
Zip
95219
APN
11619007
CURRENT_STATUS
02
SITE_LOCATION
2701 W MARCH LN
P_LOCATION
01
P_DISTRICT
002
QC Status
Approved
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EHD - Public
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' B-2 <br /> 5.1 Geombe Ground Water_Sarnpling <br /> Grab samples of ground water were recovered from each Geoprobe borehole using a peristaltic pump and <br /> ' tygon tubing which was inserted through the hollow Geoprobe rods The ground water samples were <br /> sealed in appropriate containers and stored in an ice chest cooled to approximately 4 degrees centigrade <br /> ' with crushed ice Upon completion of ground water sampling each borehole was sealed with a neat <br /> cement slurry mixed in a ratio of 5 gallons of water to each. 94 pound bag of cement, and emplaced with <br /> a tremie pipe <br /> 5.2 Abandonment of Geoprobe Borings <br /> Each Geoprobe sod boring was backfilled using a cement grout slurry Soil borings were abandoned by <br /> grouting through a tremae pipe with a cement/bentonite grout slurry upon completion of driIlmg <br /> 6.0 SOIL CLASSIFICATION <br /> ' As the soil samples were obtained in the field, they were classified by the geologist in accordance with <br /> the Unified Soil Classification System (USCS) Representative portions of the samples were retained for <br /> ' further examination and for verification of the field classification Logs of the borings indicating the <br /> depth and identification of the various strata, the "N" value, and pertinent information regarding the <br /> method of manntannmg and advancing the borehole were made and are presented in Appendix E <br /> ' 6.1 Sail Sample Screening/Flame Ionization Detector Method <br /> After the soil sample ziplock bags were brought to ambient temperature, the headspace vapors of the soil <br /> ' sample in the bag was screened with a flame ionization detector (FID) The corner of the sample bag <br /> was opened and the FID probe immediately placed within the headspace The highest observed reading <br /> ' was recorded on the boring logs. <br /> ' 6.2 Disposal of Soil <br /> Soil generated during the field operations was stored on-site and covered with plastic sheeting pending <br /> laboratory analytical results Two "stockpile" soil samples were collected from the soil per approximately <br /> every 50 cubic yards Samples were collected by digging approximately two feet into the soil pile and <br /> ' colIecting a sample using a 2-inch diameter, 6-inch long brass tube and capping each end with teflon and <br /> plastic caps The soil samples were composited by the laboratory into one sample for each of the <br /> R.PT160 SIS <br /> 1 <br />
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