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ARCHIVED REPORTS_XR0008923
EnvironmentalHealth
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26 (STATE ROUTE 26)
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8203
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3500 - Local Oversight Program
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PR0545707
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ARCHIVED REPORTS_XR0008923
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Last modified
11/20/2024 8:48:28 AM
Creation date
5/13/2020 4:04:35 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0008923
RECORD_ID
PR0545707
PE
3528
FACILITY_ID
FA0003591
FACILITY_NAME
JOHN M RISHWAIN
STREET_NUMBER
8203
Direction
E
STREET_NAME
STATE ROUTE 26
City
STOCKTON
Zip
95215-9536
APN
10114021
CURRENT_STATUS
02
SITE_LOCATION
8203 E HWY 26
P_LOCATION
99
P_DISTRICT
002
QC Status
Approved
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EHD - Public
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I <br />' 19 October 2005 <br /> AGE-NC Project No 99-0645 <br />' Page 2 of 6 <br />' 22 SOIL-VAPOR EXTRACTION <br /> The SVE unit was observed or maintained weekly and monitored monthly During each monitoring <br /> event, the flow rate of extracted soil-vapor (Influent) was measured using a totalizing-flow Blue <br /> White roto-meter Vacuum potential was measured at the 2-Inch influent line by the magnehelic <br /> vacuum gauge In addition,the organic vapor concentrations in the influent stream(before entering <br />' the blower) and the effluent stream (after exiting the carbon unit) were measured using the organic <br /> vapor meter equipped with a photo-ionization detector(PID Thermo Environmental 580b, 10 0 eV, <br /> calibrated to isobutylene) A Magnehelic vacuum gauge was temporarily attached to the inlet of the <br /> blower to measure vacuum pressure exerted on the extraction well,and a cumulative flow meter was <br /> utilized downstream of the carbon canisters to monitor air flow Sampling ports were installed <br /> upstream of the knockout vessel and downstream of the 1,500-1b carbon vessels to recover influent <br /> and effluent SVE air flow samples used to monitor the efficiency of hydrocarbon removal, in <br /> addition,the influent and effluent streams were monitored routinely for the presence of organic vapor <br /> using a PID Field measurements,recorded at regular intervals are summarized in Table 1 The SVE <br /> was operated between March and July 2005, at which time the operation of the system was <br /> terminated, due to lack of influent contamination <br /> Influent and effluent soil-vapor samples were collected on 13 April,04 and 17 May, 08 June and 18 <br /> July 2005, the influent vapor samples were collected from within a vacuum chamber directly into <br /> Tedlar vapor bags, the effluent samples were collected directly out of the effluent stream The <br /> samples were labeled, placed in a cooler and transported under chain of custody to Cal Tech <br /> Environmental Laboratories (CTEL) in Paramount, a State of California Department of Health <br /> IServices (DHS)-certified analytical laboratories The soil-vapor samples were analyzed for <br /> • Total petroleum hydrocarbons quantified as gasoline (TPH-g) in accordance with EPA <br /> IMethod 8015 Modified and <br /> • Benzene, toluene, ethylbenzene and total xylenes (BTEX) and methyl tertiary butyl ether <br /> (MTBE) in accordance with EPA Method 8260b <br /> I <br /> 23 MONITORING WELL EVACUATION AND MONITORING <br /> On 12 April and 11 July 2005, the water level in each of three monitoring wells was measured <br /> relative to the top of the well casing using a Solinst water level meter After water levels were <br /> measured, a dedicated, disposable plastic bailer was used to purge each well Four and one-half to <br /> five gallons(a minimum of three well volumes)of water were removed from the wells Temperature, <br /> pH and conductivity of the purged water were measured at two-and-one-half gallon intervals in May <br /> • and one-and-one-half gallon interval in July using an Oakton water analyzer during purging The <br /> 1 Advanced GeoEnwonmental,Inc <br /> I <br />
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