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ARCHIVED REPORTS_XR0012662
Environmental Health - Public
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2900 - Site Mitigation Program
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PR0507217
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ARCHIVED REPORTS_XR0012662
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Last modified
6/23/2020 5:14:51 PM
Creation date
6/23/2020 2:16:15 PM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0012662
RECORD_ID
PR0507217
PE
2950
FACILITY_ID
FA0007741
FACILITY_NAME
AUTO ZONE INC
STREET_NUMBER
1100
Direction
N
STREET_NAME
WILSON
STREET_TYPE
WAY
City
STOCKTON
Zip
95202
APN
11733035
CURRENT_STATUS
02
SITE_LOCATION
1100 N WILSON WAY
P_LOCATION
01
QC Status
Approved
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All analysis were performed on a laboratory grade Hewlett Packard model 5890 <br /> Series 11 gas chrorriatograph equipped with a Flame Ionization Detector (FID). A <br /> -- Restec F T-5 (15 meter by 0.53 micron) wide bore capillary column using <br /> nitrogen as the carrier gas was used to perform all analysis. All results were <br /> collected on a 80386 based personal computer utilizing Hewlett Packards PC <br /> - based chromatographic data collection and handling system. <br /> Quality Assurance <br /> The gas chromatograph was calibrated on a daily basis by preparing a 1.0 ng/ul <br /> gasoline solution in a 40ml air tight EPA vial from neat gasoline. A three point <br /> calibration consisting of 20, 50 and 100 ng injections were performed at the <br /> beginning of each day. A calibration factor based on a best fit line through <br /> these points was calculated using the HP data system. If the r2 factor generated <br /> from this line was not greater than 0.980, an additional three point calibration is <br /> performed. The calibrations curves for this project are included with this letter. <br /> Detection limits were calculated from this calibration to be 0.07 ng/ml. <br /> Concentrations reported for benzene, toluene and total xylenes are relative to the <br /> 50 ng gasoline standard and calculated by using the the relative percent of <br /> each compound versus the total <br /> In addition to the three point calibration, an additional mid-point continuing <br /> calibration- and duplicate analysis were performed after the tenth sample each <br /> day. This information is given in the Soil Gas Quality Assurance Table along with <br /> the results of all blanks. <br /> w: Subsurface Conditions <br /> Observations made during probe emplacement and removal showed soil types to <br /> be a hard, low plasticity brown clay. Near the tank, this clay showed greater <br /> moisture content than others areas. The depth of this clay is estimated to be at <br /> least 10 feet below ground surface based on the two 13 foot samples collected. <br /> �. These clays offered significant resistance to air flow, indicating that their effective <br /> porosity is low to negligible. <br /> Scope of Work <br /> To achieve the objectives of this study, a total of 22 soil gas points were tested <br /> for Total Volatile Petroleum Hydrocarbons (NPH) with BTX distinction. Sampling <br />` locations are given on Diagram 1. Of the 22 points, 2 points, SG-3 and SG-12 <br /> were tested at multiple depths (5 and 13 feet). Two samples were also analyzed <br /> at point SG-3 at 5 feet in an attempt to see if a shorter purging time would <br /> assist in the results. Three samples were collected at point SG-16 due to <br /> unusually_high_readings--in_the-_first_two_samples_collected--at.this <br /> probe was placed and the results came back very low (1.3 ng/ml). No odor <br /> was observed in the soil or from the pump indicating that the lower reading is <br /> OTI.9D0501 2 _ <br />
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