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ARCHIVED REPORTS (2)
EnvironmentalHealth
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EHD Program Facility Records by Street Name
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WAGNER
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2900 - Site Mitigation Program
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PR0541087
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ARCHIVED REPORTS (2)
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Last modified
2/22/2019 6:51:23 PM
Creation date
2/22/2019 3:50:25 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
RECORD_ID
PR0541087
PE
2959
FACILITY_ID
FA0023524
FACILITY_NAME
SPX MARLEY COOLING FACILITY
STREET_NUMBER
200
Direction
N
STREET_NAME
WAGNER
STREET_TYPE
AVE
City
STOCKTON
Zip
95215
APN
14331007
CURRENT_STATUS
01
SITE_LOCATION
200 N WAGNER AVE
P_LOCATION
01
QC Status
Approved
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TMorelli
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EHD - Public
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• Field Duplicate Comparison <br /> • Detection Limits <br /> Summary of Findings: <br /> All samples were analyzed according to the accompanying chains of custody and all analytical holding <br /> times were met. <br /> QC data were reviewed for laboratory and instrument precision and accuracy from LCS/LCSD recoveries <br /> and relative percent differences (RPDs) and MS/MSD sample recoveries and RPDs. All quality control <br /> elements were found to be within acceptable limits with the following exceptions: <br /> • The MS/MSD percent recoveries associated with the analysis of MW-204(S-8)were less than <br /> the lower control limit for hexavalent chromium. Hexavalent chromium was detected in the <br /> sample and was qualified as estimated (J). <br /> • The MS percent recovery associated with the metals analysis of MW-303 was less than the lower <br /> control limit for iron. Iron was detected in the sample and was qualified as estimated (J). <br /> • The MS/MSD percent recoveries and RPDs associated with the metals analysis of EW-1 were <br /> not meaningful for manganese. The concentration of manganese in the parent sample was <br /> greater than four times the concentration used for the spike. Therefore, the criteria were not <br /> evaluated. <br /> • The MS/MSD percent recoveries and RPD associated with the analysis of MW-324 (1-10) and <br /> MW-204 (S-8) were not meaningful for sulfate. The concentration of sulfate in the parent <br /> samples was greater than four times the concentration used for the spike. Therefore, the criteria <br /> were not evaluated. <br /> Field sampling precision was also evaluated by using the calculated RPD between results reported for the <br /> field duplicate pairs, which are listed above. All RPD results were found to be within the acceptable limits <br /> for precision for all methods with the following exception: <br /> • The field duplicate pair MW-102 and MW-102 Dup had an RPD that was greater than the control <br /> limit for arsenic; the results were qualified as estimated (J) in the both samples. <br /> No target analytes were detected in any method blank or field QC samples with the following exceptions: <br /> • Field Blank collected on January 24, 2013 was associated with the analysis of eleven samples <br /> and had TOC detected at 0.1 milligrams per liter (mg/L). MW-320 had TOC detected below the <br /> reporting limit and less than five times the blank result, and was qualified as not detected (U) at <br /> the reporting limit. <br /> • Equipment Rinse and Field Blank collected on January 25, 2013 were associated with the <br /> analysis of 18 samples and had TOC detected at 0.4 and 0.3 mg/L, respectively. MW-303, TW- <br /> 16, and TW-16 Dup had TOC detected below the reporting limit and less than five times the blank <br /> result, and were qualified as not detected (U) at the reporting limit. TW-17, TW-14, and TW-12 <br /> had TOC detected above the reporting limit, but less than five times the blank concentration, and <br /> were qualified as estimated (J). <br /> Page 2of6 <br />
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