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ARCHIVED REPORTS_XR0011999
EnvironmentalHealth
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3500 - Local Oversight Program
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PR0545892
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ARCHIVED REPORTS_XR0011999
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Last modified
7/22/2020 2:50:08 PM
Creation date
7/22/2020 2:38:56 PM
Metadata
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Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0011999
RECORD_ID
PR0545892
PE
3528
FACILITY_ID
FA0003601
FACILITY_NAME
ARCO STATION #826951*
STREET_NUMBER
130
Direction
S
STREET_NAME
WILSON
STREET_TYPE
WAY
City
STOCKTON
Zip
95205-5561
APN
15502064
CURRENT_STATUS
02
SITE_LOCATION
130 S WILSON WAY
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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. Cumulative FP Recovered to Date: NIA <br /> Approximate Depth to Groundwater: 43.01 to 43.69 feet below ground surface(b9s) <br /> Groundwater Flow Direction: Northeast <br /> Groundwater Gradient: 0.001 ft/ft <br /> INTERIM REMEDIATION SYSTEM OPERATION AND PERFORMANCE <br /> Equipment Inventory: Ozone Injection System (Manufactured by KVA�') <br /> Operating Molle: Operational <br /> Reporting Period: June 23, 2003 through September 29, 2003 <br /> Historical Highest TPHG Concentration: 55,000µg1L(MW-6, 2002) <br /> Historical Highest Benzene Concentration: 18,000µg/L(MW-8, 2001) <br /> Historical Highest MTBE Concentration: 85,000µg/L(MW-6, 2002) <br /> Highest TPHG Concentration this Period: 9,300µg/l_(MW-4) <br /> Highest Benzene Concentration this Period: 1,700µg/l_(MW-4) <br /> Highest MTBE Concentration this Period: 49,000µg/L(MW-6) <br /> Number of System Shutdowns This Period: 1 <br /> DISCUSSION: <br /> Groundwater elevations have decreased approximately 1.43 to 1.55 feet since the previous sampling <br /> event (May 19, 2003). Depth-to-water measurements were corrected to mean sea level (MSL) and used <br /> to construct a groundwater elevation contour map (Figure 3). Wells MW-9 and MW-10 are screened in a <br /> deeper portion of the water-bearing zone, and were not used in contouring. The groundwater flow <br /> direction on September 9, 2003, was northeast at a gradient of approximately 0.001 ft/ft. Groundwater <br /> flow directions have predominantly been toward the northeast and east during previous monitoring events. <br /> In addition to quarterly groundwater sampling, additional groundwater samples were collected during the <br /> third quarter 2003 sampling event to evaluate and optimize the performance of ozone injection system. <br /> Tabulated results of groundwater elevation and analytical summary of groundwater samples collected <br /> under ozone injection monitoring plan and quarterly monitoring program are presented in Tables 1 and 2. <br /> A discussion on the results of petroleum hydrocarbon concentrations is presented later in the remediation <br /> system status section of this report. <br /> REMEDIATION SYSTEM STATUS <br /> System Description <br /> The C-SpargeTM system, manufactured by KVA®, consists of a control panel (ozone generator, air <br /> compressor, and tubing manifold), and strategically located injection points (IW-1 through IW-5, see <br /> Figure 2) used to inject low concentrations of ozone into groundwater. In addition, the control panel also <br /> has a programmable timer that limits the amount of ozone injected into each injection point. The system <br /> injects a timed pulse of ozone at low flows and low pressures (10-30 psi) to each of the five injection <br /> points in a sequence. The ozone dissolved in groundwater is expected to oxidize petroleum hydrocarbons <br /> into carbon dioxide and water, and any un-reacted ozone will degrade to dissolved oxygen, which is likely <br /> to enhance natural biodegradation of residual petroleum hydrocarbons. <br /> R\Bp-Arco for URS154691Quarterly12003\Arco_5469_3Q03.doe 5TRA TU5 <br />
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