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<br />     		Laboratory Analysis
<br />  '		We submitted the groundwater samples from wells MW-1, MW-3 and GWX-1 to Moore Twining
<br />     		Laboratories,  Inc. (MTL), a California Department of Public Health-certified (CDPH) analytical
<br />  '		laboratory  located  in  Fresno,  California,  for the analysis of TPHg following the United  States
<br />     		Environmental Protection Agency (EPA) Test Method 8015B. MTL also analyzed each sample for
<br />     		BTEX, FOCs,  1,2-DCA,  naphthalene and ethanol following EPA Test Method  8260B. We also
<br />     		submitted groundwater samples from wells MW-1, MW-3  and GWX-1  to California Laboratory
<br />  '		Services (CLS), a CDPH-certified analytical laboratory located in Rancho Cordova, California, for the
<br />     		analysis of CrVI following EPA Test Method 7199.
<br />  '		Groundwater Analytical Results
<br />     		The laboratory reports and chain-of-custody documentation are in Appendix B.TPHg and BTEX were each
<br />  '		reported for the samples collected from wells MW-1, MW-3 and GWX-1, with TPHg concentrations of
<br />     		7,300, 1,200 and 210 µg/l, respectively. Benzene was reported at 500, 9.3 and 36 pg/I, respectively for the
<br />     		three samples, and the reported toluene, ethylbenzene and total xylenes concentrations ranged from 2.2 µg/1
<br />  '		ethylbenzene (MW-3) to 403 pg/I total xylenes (MW-1). Naphthalene was reported at 56 and 3.0 µg/I
<br />     		respectively, for samples MW-1 and MW-3. MTBE, ethanol, TAME, ETBE, DIPE, TBA and 1,2-DCA
<br />     		were not reported at concentrations equal to or greater than their respective laboratory reporting limits(RLs)
<br />  '		for each of the samples analyzed. CrVI was reported at 10.0 µg/1 for the sample collected from well
<br />     		GWX-l.The site-related groundwater data are summarized in Tables 1,2 and 3.
<br />     		The field quality assurance/quality control (QA/QC) implemented for the October 2011  rebound
<br /> i '		monitoring included the collection of one duplicate groundwater sample and the submittal of a trip
<br />     		blank.  The duplicate sample was collected from MW-1  and  labeled as MW-14, a non-existent
<br />     		monitoring well. When comparing the results of primary sample MW-3 with its respective duplicate
<br />     		sample (see Appendix B for MW-14 results), CrVI, FOCs, 1,2-DCA and ethanol were not reported at
<br />     		concentrations equal to or greater than their respective RLs, and TPHg, BTEX and naphthalene were
<br />     		each reported at similar concentrations [relative percent difference (RPD) < 25%] for both samples,
<br />  '		thus showing good repeatability for each of these analyses. None of the tested analytes were reported
<br />     		equal to or greater than their respective laboratory RLs for the trip blank.
<br />  '		We also reviewed the QA/QC data provided with MTL's and CLS' analytical laboratory reports.
<br />     		These data show acceptable surrogate recoveries and non-detect results for each of the method blanks
<br />     		and acceptable recoveries and RPDs for each of the matrix spikes (MS), matrix spike duplicates
<br />     		(MSDs) and laboratory control samples (LCS) except for the CrVI analyses MSD that had a recovery
<br />     		greater than the upper limit of 125%. However, CLS states that the laboratory was in control because
<br />     		the LCS was within acceptance limits. Based on the elevated MSD recovery,the CrVI result for sample
<br />     		GWX-1 must be considered an estimated value with the potential to be less than the reported value.
<br />  '		Based on the field and laboratory QA/QC data, no additional qualification of the October 2011 data
<br />     		presented herein is necessary, and the data are of sufficient quality for the purposes of this report.
<br />  '				FOURTH QUARTER — 2011 — NOVEMBER REBOUND MONITORING
<br />     		Groundwater Level Measurements
<br /> tOn November 29, 2011, we measured the depth to groundwater in wells MW-1, MW-3 and GWX-1
<br />     		using an electronic water level indicator. Groundwater was encountered at 26.76, 25.41 and 26.64 feet
<br /> '		below TOC in the three wells, respectively. A summary of the TOC elevations, depth to groundwater
<br />     		measurements and groundwater elevations is presented in Table 1.
<br />     		Project No.59183-06-03					-4-       					January 30,2012
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