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SITE INFORMATION AND CORRESPONDENCE
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3500 - Local Oversight Program
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PR0545036
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SITE INFORMATION AND CORRESPONDENCE
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Last modified
12/9/2019 3:25:24 PM
Creation date
12/9/2019 2:40:49 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
SITE INFORMATION AND CORRESPONDENCE
RECORD_ID
PR0545036
PE
3528
FACILITY_ID
FA0004837
FACILITY_NAME
B & B EQUIPMENT CO
STREET_NUMBER
3132
STREET_NAME
FARMINGTON
STREET_TYPE
RD
City
STOCKTON
Zip
95205
APN
17306002
CURRENT_STATUS
02
SITE_LOCATION
3132 FARMINGTON RD
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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w1I - <br /> TA6W 1 - CHECKLIST OF REQUIREDWTA <br /> FOR NO FURTHER ACTION REQUESTS AT UNDERGROUND TANK SITES <br /> Site Name and Location: BBB Equipment,3132 Farmington Road,Stockton,San Joaquin County <br /> 0 I.Distance to production wells for municipal, domestic, agriculture, As shown in GeoTracker, the closest municipal well is i <br /> industry and other uses within 2000 feet of the site; about 804 feet southeast of the site. An on-site well is <br /> approximately 100 feet northwest of the former UST. <br /> 2. Site maps, to scale, of area impacted showing locations of former and existing tank systems, One wasgallon waste oil <br /> UST was removed in 4/89. A <br /> excavation contours and sample locations, boring and monitoring well elevation contours, site map is provided in the <br /> gradients, and nearby surface wafers, buildings, streets, and subsurface utilities; <br /> it Investigation Report <br /> ❑y 3. Figures depicting ir'thology(cross section), treatment system diagrams; The backfill material consists of gravelly clay to <br /> 5 feet,and the native material consists of silty <br /> clay to 12 feet the total depth investigated. <br /> ❑N 4. Stockpiled soil disposed off-site(quantify); The disposition of excavated soil was not presented. The Bolls were <br /> likely returned to the tank pit excavation. <br /> 5. Monitoringwells remainingon-site, fate; Groundwater was not encountered during assessment activities, and <br /> . monitoring.wells=were not installed. <br /> FN 1 6. Tabulated results of all groundwater elevations and.depths'to water,• Groundwater was not encountered at 12 feet The <br /> depth to water is estimated at 50 to 90 feet <br /> 7.Tabulated results of all sampling and analyses: The maximum concentrations in soil show TPHd at 240 mg/kg in one <br /> sample,and lead at 140 mg/kg in a second sample. All other <br /> Detection limits for confirmation sampling constituents including MtBE were non-detect at acceptable detection f <br /> Lead analyses limits. Maximum lead using the distilled water WET procedure show <br /> soluble concentrations at 0.2 mg/1 at 12 feet <br /> y� 8. Concentration contours of contaminants found and those remaining in soil !i A backhoe was used to excavate a trench <br /> and groundwater, both on-site and off-site: across the former UST area. Four discrete <br /> soli samples identified TPHd and lead in <br /> Y❑ Lateral and Vertical extent of soil contamination 1 soil to 12 feet Groundwater was not <br /> ❑ Lateral and ❑ Vertical extent of groundwater contamination <br /> encountered. <br /> 9. Zone of influence calculated and assumptions used for subsurface <br /> N soil contamination <br /> for he soil and <br /> Based on the limited <br /> remediation system and the zone of capture attained o f <br /> groundwater remediation system; site remediation was not required. E <br /> .i <br /> 0 10.Reports/information Y❑ Unauthorized Release Form [9 QMRs <br /> El Baring logs 0 PAR 0 FRP E] Soil Sampling Report, !November 2001 <br /> ❑ 11.Best Available Technology(BAT)used or an explanation for not using BAT;' The UST was removed. <br /> " " _'* " r """"""" Soil contamination remains ince formerr tankpit-area.—Th e contamination sj <br /> ❑ 12.Reasons why background warms <br /> unattainable using BAT, limited in extent,relatively immobile,and does not present a significant threat <br /> • <br /> to water quality. <br /> ❑ 13.Mass balance calculation of substance M <br /> treated versus that remaining, <br /> Based on the limited sail contamination,a mass balance was not required. j <br /> it <br /> ❑ 14.Assumptions,parameters, calculations and model used in risk Based on the limited soil contamination,a risk <br /> assessments, and fate and transport modeling; assessment was not required. <br /> 15. Rationale why conditions remaining at site will not adversely Contaminants In soil are relatively immobile and limited <br /> impact water quality, health, or other beneficial uses;and in extent.' The contamination will naturally attenuate and <br /> degrade.'i. <br /> By: Comments: One 110-gallon waste oil UST was removed from the B&B Equipment maintenance garage area in <br /> MH April 1989. Soil contamination was identified during the tank removal activities, and additional soil samples were <br /> collected from a 17'x 2'x 12'deep trench in September 2001. These samples were analyzed for TPHg, TPHd, BTEX, <br /> II Date: and fuel oxygenates, and only TPHd and lead were identified. The soil samples were also analyzed for lead using the j <br /> 215102 distilled water WET procedure, and concentrations are reported at 0.2 jmg17. The native soil to 12 feet consists of silty <br /> clay, and the depth to groundwater is estimated at 50 to 90 feet. Due to the fine-grained nature of subsurface lithology, <br />�. and the low mobility and solubility of lead, Board staff believe that sufficient attenuation will occur and the lead will likely j <br /> not impact groundwater. Based on the investigation completed to date, Board staff concur with San Joaquin County's <br /> closure recommendation. !° <br /> 1 <br />
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