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ARCHIVED REPORTS_XR0006762
Environmental Health - Public
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EHD Program Facility Records by Street Name
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2900 - Site Mitigation Program
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PR0508124
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ARCHIVED REPORTS_XR0006762
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Last modified
7/27/2020 3:21:02 PM
Creation date
7/27/2020 2:18:12 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0006762
RECORD_ID
PR0508124
PE
2950
FACILITY_ID
FA0007949
FACILITY_NAME
7 ELEVEN #21756
STREET_NUMBER
853
Direction
E
STREET_NAME
YOSEMITE
STREET_TYPE
AVE
City
MANTECA
Zip
95336
APN
22332015
CURRENT_STATUS
01
SITE_LOCATION
853 E YOSEMITE AVE
P_LOCATION
04
P_DISTRICT
003
QC Status
Approved
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EHD - Public
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commuted lo}our Succes4 <br /> u A L , T Y A S S U R A N C E F 0 0 T R <br /> ' METHOD REFERENCES <br /> (1) EPA SW-846, Test Methods for Evaluating Solid Waste, Third Edition, September 1986, and Updates I, Ii, I:A, 118, 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) 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 600/4-89-001, 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 to 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 /> tevel 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 /> = Not analyzed N I = riot Ignitable <br /> N/A = Not applicable S I. a 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 /> HC = 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 ditution 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 lints due to actual differences in <br /> the sample matrix. <br /> (e) = The lint listed for flammability indicates the upper Limit for the test. Samples are not tested at temperatures <br /> above 140 Fahrenheit since only samples which vitt sustain ignition at temperatures below 140 are considered <br /> flammable. <br /> (f) = Results for this hydrocarbon range did not onteh 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 S8 = Storage Blank Core Laboratories: Aurora, Colorado *AU <br /> R9 = Reagent Blank MS = Matrix Spike Casper, Wyoming *CA <br /> ICS = Initial Calibration Blank MSD = Matrix Spike Duplicate Corpus Christi, Texas *CC <br /> CC8 = Continuing Calibration Blank MD a Matrix Duplicate Edison, New Jersey *ED <br /> CS = Calibration Standard BS a Blank Spike Houston, Texas (Env) *HE <br /> ICY = Initial Calibration s5 = surrogate Spike Houston, Texas (Pet) *HP <br /> Verification LCs = Laboratory Control Indianapolis, Indiana *IN <br /> CCV = Continuing Calibration Standard Lake Clherles, Leuisiana *LC <br /> Verification RS = Reference Standard Long Beath, Catifornia *LB <br /> Valparaiso, Indiana *VP <br /> Bakersfield, California *BK <br /> 1250 Gene Autry Way Autry Way <br /> Anaheim, CA 92805 <br /> (714) 937-1094 /u/matt/logs n forms/footer.fon <br /> a part of <br /> �4t�i11 I Ont 1t11 I-L Ei, <br />
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