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r <br /> _ Received: 11 / 9/99 11 :24AM; 616 227 4349 -y COAA/SJOA EPU; Page 3 <br /> - 2iov-09-1999 10: 19 SWRCB/CLEAN WATER PRGMS 916 227 4349 P.03i35 <br /> from the 85-90 foot depth. It.is our opinion that the low levels of MTBE that have been <br /> sporadically detected in groundwater from some of the Site shallow wells are consistent with <br /> atmospheric washout. <br /> • The lateral extent of soil impacts has been identified.Hydrocarbon impacts in the soil appear to <br /> be limited to the area around the former product islands. <br /> 0 The lateral extent of groundwater impacts has been identified and is constrained by data from <br /> the monitoring well array. The downgradient extent of impacts to groundwater by TPHg is less <br /> than 100 ft from the Site property line. The downgxadient extent of Site benzene impacts to <br /> groundwater at concentrations greater than I ug/L are less than 80 ft. from the Site property <br /> line. <br /> • Chemical analytic data from Site soil sampling indicate that the vertical extent of soil impacts <br /> at the Site have been identified and do not extend below 70 ft bgs. <br /> Concentrations of TPHg and benzene are significantly attenuated below 50 to 60 ft bgs. <br /> THE PLUME IS STABLE AND iSELF REMEDIATING <br /> • An examination of 9 years continuous monitoring data for the site indicates that the <br /> groundwater plume is stable and has not substantially moved. Exhibits A and B illustrate the <br /> distribution of benzene in Site,shallow groundwater in May, 1990 and February, 1999. As <br /> shown, the maxunum extent of benzene in shallow groundwater has remained essentially <br /> unchanged over 9 years. <br /> Analysis of well elevation data indicates that there is an upward gradient at the Site. 'Pais <br /> calculation is based on quarterly monitoring data (3 quarters) collected after allowing the new <br /> well cluster to stabilize and utilization of current (February, 1999) well survey data which <br /> accounts for land subsidence which has occurred in the area. <br /> Concentrations of petroleum hydrocarbons in groundwater have declined significantly over the <br /> 11-year period of the monitoring record. <br /> • Multiple lines of biogeochemical data (including dissolved oxygen, nitrates, holo (II), sulfates, <br /> and dissolved methane data)presents strong evidence to indicate that the groundwater plume is <br /> undergoing microbially mediated aerobic and anaerobic biodegradation- As would be expected <br /> in a microbially active system, Exlu'bit C illustrates that nitrate is being depleted near the core <br /> of the plume as it is used as an ahernate electron acceptor to facffitate microbial degradation,of <br /> the Site petroleum hydrocarbons. Exhibit D illustrates that the concentrations of soluble <br /> ferrous iron are elevated near the core of the plume as ferric iron is reduced by microbially <br /> mediated biodegradation of Site petroleum hydrocarbons. <br /> I <br /> It is our opinion that the petrol=a hydrocarbon plume at the Site is adequately characterized to understand <br /> the lateral and vertical extent of impact. The groundwater impacts have been monitored for over 11 years. <br /> The data indicate that the plume is impactti ag a very limited volume of soil and groundwater. Site data also <br /> indicate that the plume is stable (not moving or expanding) and that the plume is self-remediating through <br /> the mechanisms of natural attenuation and biodegradation. Itis our opinion that water quality objectives <br /> Pecs: <br /> 2/3 <br />