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ARCHIVED REPORTS_XR0009200
Environmental Health - Public
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ARCHIVED REPORTS_XR0009200
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Last modified
5/6/2020 11:40:55 AM
Creation date
5/6/2020 11:26:25 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0009200
RECORD_ID
PR0545651
PE
3528
FACILITY_ID
FA0002479
FACILITY_NAME
7-ELEVEN INC #17334
STREET_NUMBER
4501
Direction
N
STREET_NAME
PERSHING
STREET_TYPE
AVE
City
STOCKTON
Zip
95207
APN
11017004
CURRENT_STATUS
02
SITE_LOCATION
4501 N PERSHING AVE
P_LOCATION
01
P_DISTRICT
002
QC Status
Approved
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EHD - Public
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Committed ed To Your Success <br />' Q U A T Y A S S U R A N C E F O O T E R <br />' ►SETNOG REFERENCES <br /> (1) EPA Sof-846, Test Methods for Evaluating Solid Waste, Third Edition, September 1486, and Updates I, II, IIA, 118, and III <br /> (2) Standard Methods for the Examinat,on of Yater and wastewater, 18th Edition, 1992 <br />' (3) EPA 600/4-79-020, Methods of Chemical Analysis for waters and wastes, March 1983 <br /> (4) Federal Register, Friday, October 26, 1984 (40 CFR Part 136) <br /> (5) American Society for Testing and Materials, Volumes 5 01, 5 02, 5 03, 1992 <br /> (6) EPA 600/4-84-001, Short-term Methods for Estimating the Chronic Toxicity of Effluents and Receiving Waters to Fresh <br /> Water Organisms <br /> (7) EPA 600/4-90-027, Methods for Measuring the Acute Toxicity of Effluent and Receiving Waters to Fresh Water and Marine <br /> Organisms, Fourth Edition <br /> COMMENTS <br />' All methods of chemical analysis have a statistical uncertainty associated with the results Unless otherwise indicated, <br /> the data in this report are within the Limits of uncertainty as specified in the referenced method Quality control <br /> acceptance criteria are based either on Limits specified in the referenced method or on actual laboratory performance. <br />' The date and time of analysis indicated on the QC report may not reflect the actual time of analysis for QC samples Data <br /> reported in the AA report may be lover than sample data due to dilution of samples into the calibration range of the analysis <br /> Sample concentrations for solid samples are calculated on an as received (vet) basis unless otherwise indicated UnLess <br /> otherwise indicated, volatiles by gas chromatography (GC) are reported from a single column. Volatiles analyses by GC on tow <br /> Level soils are conducted at room temperature TCLP extractions are performed at sample amounts, approved by the State of <br /> California <br /> FLAGS, FOOTNOTES, AND ABBREVIATIONS (as needed) <br /> NA = Not analyzed N 1. z Not Ignitable <br /> N/A = Not applicable $.I - Sustains Ignition <br /> ug/L = Micrograms per liter I(NS) = Ignites, but does not Sustain Ignition <br /> mg/L = Milligrams per liter RPD = Relative Percent Difference <br />' ND = Not detected at a value greater than the reporting limit <br /> NC = Not calculable due to values lower than the detection limit <br /> (a) = Surrogate recoveries were outside acceptable ranges due to matrix effects <br /> (b) = Surrogate recoveries were not calculated due to dilution of the sample below the detectable range for the surrogate. <br /> (c) = Matrix spike recoveries were outside acceptable ranges due to matrix effects <br /> (d) = Relative Percent Difference (RPD) for duplicate analysis outside acceptance limits due to actual differences in <br /> the sample matrix. <br /> (e) = The limit listed for flammability indicates the upper limit for the test. Samples are not tested at temperatures <br /> above 140 Fahrenheit since only samples which will sustain ignition at temperatures below 140 are considered <br /> ftaamable. <br /> (f) = Results for this hydrocarbon range did not match a typical hydrocarbon pattern. Results were quantified using a <br /> diesel standard, however, the hydrocarbon pattern did not match a diesel pattern. <br /> (g) = Results for this hydrocarbon range did not match a typical hydrocarbon pattern. Results were quantified using a <br /> 1 gasoline standard, however, the hydrocarbon pattern did not match a gasoline pattern. <br /> (h) = Nigh dilution due to matrix effects <br /> QC SAMPLE IDENTIFICATIONS SUBCONTRACTED LABORATORY LOCATIONS <br /> MB = Method Blank SB = storage Blank Core Laboratories: Aurora, Colorado *AU <br />' R8 = Reagent Blank MS - Matrix Spike Casper, Wyoming *CA <br /> ICS = Initial Calibration Blank MSD a Matrix Spike Duplicate Corpus Christi, Texas *CC <br /> CC8 = Continuing Calibration Blank MD = Matrix Duplicate Edison, New Jersey *BD <br /> C5 = Calibration Standard BS s Blanc Spike Houston, Texas (Env) *HE <br /> ICY = Initial Calibration SS = Surrogate Spike Houston, Texas {Pet) *'HP <br /> Verification LCS = Laboratory Control Indianapolis, Indiana *IN <br /> CCV = Continuirg Calibration standard Lake Charles, Louisiana *LC <br /> Verification AS = Reference Standard Long Beach, California *la <br />' Valparaiso, Indiana *VP <br /> Bakersfield, California *8K <br />' 1250 Gene Autry way Autry way <br /> Anaheim, CA 92805 <br /> (714) 437-1094 /u/matt/logs n forms/footer.form <br />' a part of <br /> Scsnz [i�iu Sin itc,ln <br />
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