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ARCHIVED REPORTS XR0004318
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3500 - Local Oversight Program
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PR0544686
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ARCHIVED REPORTS XR0004318
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Last modified
7/23/2019 11:42:41 AM
Creation date
7/23/2019 11:32:31 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0004318
RECORD_ID
PR0544686
PE
3528
FACILITY_ID
FA0000916
FACILITY_NAME
7-ELEVEN INC #19976
STREET_NUMBER
1399
Direction
N
STREET_NAME
MAIN
STREET_TYPE
ST
City
MANTECA
Zip
95336
APN
21633034
CURRENT_STATUS
02
SITE_LOCATION
1399 N MAIN ST
P_LOCATION
04
P_DISTRICT
003
QC Status
Approved
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EHD - Public
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1 <br /> CORE LABORATORIES <br /> Q U A L I T Y A S S U R A N C E F 0 0 T E R <br /> METHOD REFERENCES <br /> (1) EPA SW-845, Test Methods for Evaluating Solid Waste, Third Edition, September 1986, and Updates I, II, IIA, IIS, and III <br /> (2) Standard Methods for the Examination of Water and Wastewater, 18th Edition, 1992 <br /> (3) EPA 600/4-79-020, Methods of Chemical Analysis for Waters and Wastes, March 1983 <br /> (4) Federat 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 600/4-89-001, 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 QA report may be lower 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 (wet) basis unless otherwise indicated. Unless <br /> otherwise indicated, volatiles by gas chromatography (GC) are reported from a single column Volatiles analyses by GC on low <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.I = Not Ignitable <br /> N/A = Not applicable S 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 /> NO = Hot 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 /> flammable. <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 /> gasoline standard, however, the hydrocarbon pattern did not match a gasoline pattern. <br /> (h) = High 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 /> RB = Reagent Blank MS = Matrix Spike Casper, Vyceing *CA <br /> ICS = Initial Calibration Blank MSD = Matrix Spike Duplicate Corpus Christi, Texas *CC <br /> CCS = Continuing Calibration Blank MD = Matrix Duplicate Edison, New Jersey *ED <br /> CS = Calibration Standard BS = Blank Spike Houston, Texas (Env) *HE <br /> ICV m Initial Calibration SS - Surrogate Spike Houston, Texas (Pet) *HP <br /> Verification LCS = Laboratory Control Indianapolis, Indiana *IN <br /> CCV = Continuing Calibration Standard Lake Charles, Louisiana *LC <br /> Verification RS = Reference Standard Lang Beach, California *LB <br /> Valparaiso, Indiana *VP <br />' Bakersfield, California *EK <br /> 1250 Gene Autry Way Autry Way <br /> Anaheim, CA 92805 <br /> {714) 937-1094 /u/matt/Logs n forms/footer form <br /> Tna a aim coo cowls nanioa or nee o etas ono coma neo n In s soon a e naseo upon rdoa es noana malar al epmesetl talon cl en IDl venose a cl s ve ono cpn+annl a usa m s repo t nos peen mace Tne analrl cal resu ve ap ams o n!r P ala I on 1 <br /> e pre99etl lepres9nl Inc Desi IUOAmen!of CD a LdnfMatIX e9 Cwe Lebo etp ea hpweve+m wd ra my D expra55 Or mnte6 OI a V SYla dna 9rPresaly pSCla m5 Same a5 ID lna p ppu[t {y 0 ppe c p5 0 P pl IM en 55 0 <br /> any vel gd9 pod pt of ne mineral p onertY well nt SdnO n penneCl On win wh1Cn SCCn re001 5 Cseo p reletl uAOIp env reaepn whalsneve This repel I sna 1 n01 OD p CU CW n,whole o n M I w Input n e ver Clan apn ova G Go a La LO alp es <br />
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