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3500 - Local Oversight Program
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PR0544468
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Last modified
5/16/2019 4:30:55 PM
Creation date
5/16/2019 4:23:57 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
WORK PLANS
RECORD_ID
PR0544468
PE
3528
FACILITY_ID
FA0025278
FACILITY_NAME
RENTAL MACHINERY COMPANY
STREET_NUMBER
1821
Direction
E
STREET_NAME
CHARTER
STREET_TYPE
WAY
City
STOCKTON
Zip
95205
CURRENT_STATUS
02
SITE_LOCATION
1821 E CHARTER WAY
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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24 July 1997 <br /> AGE-NC Project No. 97-0349 <br /> Page 3 of 5 <br /> will be advanced within the former UST area. The proposed soil probe boring location is illustrated <br /> on Figure 2. <br /> Discrete soil samples will be collected at five-foot intervals beginning at a depth of 5-feet bsg using <br /> a Geoprobe soil sampling assembly loaded with four pre-cleaned 1.125-inch by 6-inch brass sleeves. <br /> Soil samples will be preserved by covering both ends of the second brass sleeve with Teflon sheets, <br /> capping and sealing with tape. Each sample sleeve will be labeled with the following information: <br /> soil probe boring location, depth, time, date and sampler's initials. <br /> Initially,soil samples will be collected to a depth of 50 feet bsg. If petroleum hydrocarbon-impacted <br /> soil is encountered during probing activities,probe borings may be advanced to greater depths in an <br /> attempt to determine the vertical extent impacted soil. <br /> One grab ground water sample will be collected from the probe boring. The grab ground water <br /> sample will be collected using a Geoprobe water sampling assembly. For the sampling assembly, <br /> probe rods will be fitted with a retractable ground water screen and advanced to the total depth of <br /> each probe boring;the rods will then be pulled upward to allow ground water to flow into the screen. <br /> A bailer fitting will then'be placed on the end of 3/s-inch diameter polyethylene tubing, inserted <br /> through the rod assembly into the exposed screen, through which water will be manually pumped. <br /> 3.2. EQUIPMENT DECONTAMINATION <br /> All probing rods, sampling tools and sample liners used for sample collection will be thoroughly <br /> rinsed with clean water after washing with a solution of Alconox. <br /> 3.3. LABORATORY ANALYSIS <br /> Selected soil samples will be analyzed for TPH-d, BTE&X and methyl tert-butyl ether(MTBE) in <br /> accordance with EPA methods 8015m and 8020/602. Furthermore, the gr ground water sarn le <br /> will also be analyzed for volatile organics in accordance with EPA metho 82 . abcratory reports <br /> and sample chain-of-custody documentation will be presented in a report with the findings and <br /> recommendations. Soil samples will be selected for analysis based upon field observations. <br /> 24 July 1997 <br /> AGE-NC Project No: 97-0349 <br /> Page 4 of 5 <br /> 4.0. PROCEDURES <br /> 4.1. ADVANCEMENT OF SOIL PROBE BORINGS <br /> The following procedures will be performed for the installation of probing(s): <br /> 1. Notify the PHS-EHD at least 48 hours prior to commencement of any work. <br /> 2. Initially,advance one(1)soil probe boring at the site to a depth of approximately 50 feet bsg. <br /> if petroleum hydrocarbon-impacted soil is encountered during probing activities, probe <br /> borings may be advanced to greater depths in an attempt to determine the extent impacted <br /> soil. <br /> 3. Probe borings will using a van-mounted Geoprobe probing unit equipped with 1.125-inch <br /> diameter rods. Proposed probe boring location is depicted on Figure 2. <br /> 4. Decontaminate sampling equipment in an Alconox solution and rinse with water prior to <br /> each sampling run. <br /> 5. Obtain soil samples at five foot intervals using a Geoprobe soil sampling assembly pre- <br /> loaded with four 1.125-inch by 6-inch brass sleeves. <br /> 6. Preserve soil samples in the second brass sleeve by covering both ends with Teflon sheets, <br /> capping,and sealing with tape. Each sample will be labeled with the following: site location, <br /> sample identification, depth, time and date. <br /> 7. Document samples on a chain-of-custody form. <br /> 8. Store samples in a chilled container and transport to a State-certified laboratory for analysis. <br /> 9. Monitor soil sample duplicates for the presence of volatile organics using a photo-ionization <br /> detector (PID) pre-calibrated to isobutylene. <br /> 10. Log soil sample duplicates in accordance with the Unified Soil Classification System. <br /> 11. Collect a grab ground water sample from selected probings. Ground water samples will be <br /> collected using a Geoprobe water sampling assembly. A ground water sample will be <br /> collected at each sampling point in 40-m1 VOA vials containing hydrochloric acid and one- <br /> liter amber bottles. <br /> 12. Transmit each ground water sample to a State-certified laboratory under chain-of-custody <br /> procedure. <br /> 13. Backfill each probe boring to surface grade using Portland type II cement. <br /> 14. Selected soil and grab ground water samples will be analyzed by a State-certified laboratory <br /> Advaneed GeoEnvironmental,Inc. <br />
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