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2900 - Site Mitigation Program
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PR0518632
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SITE INFORMATION AND CORRESPONDENCE
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Last modified
1/7/2020 2:52:57 PM
Creation date
1/7/2020 2:27:17 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
RECORD_ID
PR0518632
PE
2960
FACILITY_ID
FA0014022
FACILITY_NAME
ST SERVICES
STREET_NUMBER
2941
STREET_NAME
NAVY
STREET_TYPE
DR
City
STOCKTON
Zip
95206
CURRENT_STATUS
01
SITE_LOCATION
2941 NAVY DR
QC Status
Approved
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Ms Vicki Goodenow - 2 - 25 November 2009 r <br /> NuStar Terminals Stockton Facili. <br /> in our 8 July 2009 letter and requested submission of a report of the investigation with <br /> recommended locations for the 90-foot bgs wells by 30 October 2009. <br /> Pursuant to the Work Plan the Report summarizes the grab groundwater sampling and well <br /> installation activities conducted at the site between 31 August and 4 September. Five <br /> monitoring wells (ACA-3A/B, ACA-4A/B, ACA-3C, ACA-4C, AND ACA-5C) were installed <br /> where previous groundwater monitoring results indicated the presence of elevated <br /> concentrations of petroleum hydrocarbons. Grab groundwater samples were collected from <br /> the D-zone from borings ACA-3 and ACA-5 from 71.5 and 82.7 feet bgs, respectively to <br /> confirm results obtained from the borings NS-18 and NS-21. <br /> The results of the comparative laboratory analysis showed that glass filtration yielded the <br /> highest concentrations of TPHd at 2,300 pg/L and 970 pg/L for D-zone grab groundwater <br /> samples from ACA-3 and ACA-5, respectively. TPHd concentrations for ACA-3 and ACA-5 by <br /> laboratory analysis using no preparation were 560 pg/L and 670 pg/L, respectively. The <br /> results for silica gel cleanup, and silica gel cleanup combined with filtration were significantly <br /> lower for ACA-3 and non-detect (ND) for ACA-5. <br /> The results of the confirmation grab groundwater samples are lower than the results from the <br /> November 2008 investigation in which TPHd was detected in D-zone borings NS-18 and NS- <br /> 21 at 11,000 pg/L and 15,000 pg/L, respectively. In their 30 January 2009 report on these D- <br /> zone results, NuStar concluded that the November 2008 results were attributable either to an <br /> off-site source or interference from non-petroleum organics. The Report concludes that the <br /> silica gel results show that the TPHd results are being artificially elevated by the presence of <br /> biogenic or plant material and concludes that further investigation, or monitoring of the D-zone <br /> is unwarranted. <br /> We do not concur that the reduced concentrations resulting from the silica gel cleanups are an <br /> indication that no further investigation or monitoring of the D-zone is necessary. On 21 May <br /> 2009, Central Valley Water Board staff met with you and representatives of Ash Creek to <br /> discuss a path forward for the follow-up vertical delineation investigation. During that meeting <br /> you proposed using silica gel cleanup to prepare samples by 8015M Central Valley Water <br /> Board staff stated that we do not allow the use of silica gel cleanup because the process <br /> removed polar organics as well. By preparing the sample with silica gel, polar diesel break- <br /> down compounds including, aldehydes, alkenes, and keytones are inadvertently removed from <br /> the sample resulting in artificially reduced TPHd concentrations. <br /> In addition, even after the silica gel cleanup procedure, the analytical result for the D-zone <br /> grab groundwater sample from ACA-3 exceeded the water objective (WQO) of 100 pg/L. This <br /> laboratory analytical result offers conclusive evidence that documented fuel releases from the <br /> NuStar facility in the past have degraded groundwater quality down to or below the D-zone. <br /> Monitoring wells at this location screened at or below the depth of the ACA-3 sample are <br /> necessary to delineate the vertical extent of the diesel pollution and promote cleanup. <br />
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