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SITE INFORMATION AND CORRESPONDENCE
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Last modified
2/14/2019 3:46:08 PM
Creation date
2/14/2019 9:40:06 AM
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
RECORD_ID
PR0517323
PE
2960
FACILITY_ID
FA0013339
FACILITY_NAME
MT HOUSE SITES 1-6
STREET_NUMBER
0
STREET_NAME
BYRON
STREET_TYPE
RD
City
TRACY
Zip
95376
CURRENT_STATUS
01
SITE_LOCATION
BYRON RD
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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Appendix E.1:Data Usability Summary <br /> Field Duplicate <br /> Groundwater sample SB-37-WD-091111 is a field duplicate of SB-37-W-091111. <br /> Acenaphthene was the only target compound detected in either the parent sample or field <br /> duplicate. The RPD for the acenaphthene was 0%,because the compound was detected at <br /> 0.016 micrograms per liter(µg/L) in both samples. <br /> MS/MSDs <br /> Project-specific MS/MSD samples were collected with groundwater sample SB-35-W-091110. <br /> The %Rs for acenaphthene, acenaphthylene, fluoranthene, fluorene, naphthalene, and <br /> phenanthrene were above the laboratory control limits in the MS and MSD. The unspiked <br /> sample was non-detect for these compounds, so no data were qualified. The laboratory also <br /> randomly selected project samples to prepare MS and/or MSDs for some analytical batches. All <br /> randomly selected project samples were within laboratory control limits were one exception. <br /> The %R for chloride was 144 percent, above the control limit of 110 percent, in the MS prepared <br /> form sample SB-42-W-091116. There was no MSD analyzed. The result for chloride in the <br /> sample was qualified E for a potential high bias caused by matrix interference. <br /> Internal Standard Area Counts <br /> Internal standard area counts were not verified for samples during this data review. However, <br /> the laboratory noted that one of the internal standard areas were outside the QC limits for the <br /> PAH analysis in sample FosterWell-1-W-091118. The sample was re-analyzed and the internal <br /> standard was outside the QC limits again indicating a matrix effect. The results for <br /> benzo(b)fluoranthene, benzo(k)fluoranthene,benzo(a)pyrene, indeno(1,2,3-cd)pyrene, <br /> dibenz(a,h)anthracene, and benzo(g,h,i)perylene were qualified E as estimated. <br /> Representativeness <br /> Representativeness was assessed through the evaluation of method blank samples, trip and <br /> equipment blank samples, chain-of-custody forms, preservation, and holding times. <br /> Method Blank Results <br /> Laboratory method blanks were evaluated for any detection above the laboratory MDL. No <br /> target analytes were detected in any of the method blanks analyzed as part of this data set with <br /> one exception. Benzo(a)pyrene was detected at 0.0035 µg/L in one method blank. The <br /> compound was detected at similar concentrations in the associated groundwater samples SB-41- <br /> W-091116 and SB-42-W-091116. The samples were re-extracted outside the method hold time <br /> and benzo(a)pyrene was not detected. The results in the original analysis were qualified E to <br /> indicate they are likely due to contamination introduced during the analysis and not <br /> representative of field conditions. <br /> Field QC Results <br /> Five trip blanks, one field blank, and two equipment rinsate blanks were submitted with the <br /> samples. No target analytes were detected in any of the field QC samples, with the following <br /> exceptions: <br /> • Benzo(a)pyrene, dibenz(a,h)anthracene, and phenanthrene were detected in equipment <br /> rinsate blank QA-Tubing-R-091110. The analytes were not detected in any associated <br /> groundwater sample SB-35-W-091110. <br /> E.1-4 —– =— <br /> Frain Science to Solutions <br />
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