My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
INSTALL_2022
EnvironmentalHealth
>
EHD Program Facility Records by Street Name
>
G
>
GRANT LINE
>
3250
>
2300 - Underground Storage Tank Program
>
PR0518288
>
INSTALL_2022
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
1/18/2023 9:33:30 AM
Creation date
5/31/2022 1:10:56 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2300 - Underground Storage Tank Program
File Section
INSTALL
FileName_PostFix
2022
RECORD_ID
PR0518288
PE
2351
FACILITY_ID
FA0013810
FACILITY_NAME
COSTCO WHOLESALE #658
STREET_NUMBER
3250
Direction
W
STREET_NAME
GRANT LINE
STREET_TYPE
RD
City
TRACY
Zip
95377
CURRENT_STATUS
01
SITE_LOCATION
3250 W GRANT LINE RD
P_LOCATION
03
QC Status
Approved
Scanner
SJGOV\kblackwell
Tags
EHD - Public
Jump to thumbnail
< previous set
next set >
There are no annotations on this page.
Document management portal powered by Laserfiche WebLink 9 © 1998-2015
Laserfiche.
All rights reserved.
/
620
PDF
Print
Pages to print
Enter page numbers and/or page ranges separated by commas. For example, 1,3,5-12.
After downloading, print the document using a PDF reader (e.g. Adobe Reader).
View images
View plain text
SOIL SAMPLING ACTIVITIES AND REQUESTED LABORATORY ANALYSES <br /> On June 17, 2022, Kleinfelder staff met at the Site with Inspector Presto and Jones Covey's <br /> foreman, Mr. Joseph Malcolm, to perform soil sampling at the locations of six fuel dispensers and <br /> associated removed fuel system piping that had been removed prior to the tie of the sampling. As <br /> directed by Inspector Pesto, Kleinfelder collected soil samples beneath the pea gravel fill material <br /> at a depth approximately 2 feet into the "native" soil (equating to approximately 6 feet to 7 feet <br /> bgs) at the former fuel dispenser locations and at intervals of approximately 20 linear feet in the <br /> piping trenches. As the pea gravel and soils were excavated, they were screened for the potential <br /> presence of volatile organic vapors using a calibrated photo-ionization detector(PID). No volatile <br /> organic vapors were detected by the PID at concentrations at or above the instrument's detection <br /> limit. The excavated material was then temporarily stockpiled on Site. In total, 13 soil samples <br /> were collected during the June 17, 2022 sampling event, including six dispenser location soil <br /> samples (designated D-1 through D-6), five piping trench soil samples (designated P-1 through <br /> P-5), and two excavated material stockpile samples (designated SP-1 and SP-2). Figure 2 shows <br /> the approximate locations where each sample was collected. The soil samples were collected <br /> from the bucket of the contractor's excavator and transferred into laboratory-provided glass jars. <br /> The stockpile material samples were also placed in laboratory provided glass jars. Field <br /> preservation of the samples for laboratory analysis of VOCs was performed pursuant to US EPA <br /> Method 5035. Photographs of the Site and selected sampling locations are presented on Figures <br /> 3 through 7. <br /> A second sampling event occurred on June 30, 2022, when Kleinfelder returned to the Site <br /> following the removal of additional fuel system piping. Two soil samples(designated P-6 and P-7) <br /> were collected from the newly-excavated piping trench using the same methodology described <br /> above. The approximate locations from which the samples were collected are included on <br /> Figure 2. As with the first sampling event, no total volatile organic vapors were detected at a <br /> concentration at or above the PID's detection limit in the excavated pea gravel and soil. <br /> The soil samples collected during each of the two sampling events were submitted, accompanied <br /> by chain of custody, to Kleinfelder's laboratory subcontractor, Pace Analytical® Laboratory <br /> Sciences (Pace Analytical), located in Bakersfield, California, for analysis. Pursuant to <br /> San Joaquin County's requirements, the samples were analyzed for gasoline-range total <br /> petroleum hydrocarbons (as total purgeable petroleum hydrocarbons) and VOCs including fuel <br /> oxygenates using US EPA Method 8260B and for total lead using US EPA Method 6010B. The <br /> soil samples were analyzed using a rush 24-hour results-reporting turn-around-time. <br /> SOIL SAMPLING ANALYTICAL RESULTS <br /> The analytical results are summarized in attached Table 1, and copies of Pace Analytical's <br /> laboratory reports are provided in the last attachment section that follows the table attachment. <br /> As the table and laboratory reports indicate, TPH-g as total purgeable petroleum hydrocarbons <br /> and VOCs were not detected in the samples at concentrations at or above their respective PQLs, <br /> which varied by sample and analyte. Total lead was present in the soil samples collected on <br /> June 17, 2022 at concentrations ranging from 4.3 milligrams per kilogram (mg/kg) to 7.3 mg/kg, <br /> and present in the two June 30, 2022 samples at concentrations of 7.6 mg/kg and 8.2 mg/kg, <br /> although the laboratory flagged the latter two samples' total lead results with a "J" laboratory <br /> qualifier, indicating the results are estimated values, and an "A10" qualifier, indicating detection <br /> and quantitation limits for lead were raised due to matrix interference. Kleinfelder compared the <br /> total lead analytical results for the June 17 and 30, 2022 samples to the current(July 2019) Tier 1 <br /> 20224378.001A/LH22R143097 Page 2 of 4 July 25, 2022 <br /> Copyright 2022 Kleinfelder <br /> KLEINFELDER 24411 Ridge Route Dr., Suite 225, Laguna Hills, CA 92618 p 1949.727.4466 f 1949.727.9242 <br />
The URL can be used to link to this page
Your browser does not support the video tag.