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1� <br /> Consolidated Forward andfill Page <br /> l conduct <br /> The appropriate responsible agenciee forCthe vertical RWQCB,n ovlr the existing el di ll(s) <br /> the liner and leachate collection system <br /> proposed in the JTD. <br /> 49 (F.6) <br /> Proposed as Part of the Project: <br /> Because of the potential for contamination from«`1L B and or A of the shallow <br /> groundwater table downgradient and adjacent to h 1ill bejsarnpledting at the sametfrequen='as'the <br /> within 300 feet of the eastern property boundary` <br /> monitoring wells onsite and for the same constituents(see CCR,Title 27)_ Final <br /> determination of the sampling program and the evaluation of the test results,along _ <br /> ility of the R%t QCB and must be carried ou:-Cer <br /> appropriate mitigation,is the responsib <br /> their permit authorization. <br /> Identified in This EIR: %ve!ls along Austin <br /> s the two on <br /> Water quality at the offsite wells, sac biannuall. (t«'�e a y ear)to determine the x-zn: : -at <br /> CyA wells. shall be in at leas <br /> the plume impacts them. Continued operation of the groundwater extraction systern <br /> =: <br /> ent <br /> site %will help limit the contaminant plume from ex <br /> ent far beyond the boundary of Austin Road i La�.d -b-,. <br /> will not address the offsite component <br /> unless the contamination is attenuated and diluted o%-er t:: =e or more extraction�z e::= <br /> brought on line per the AEE(2001b) Alternative 3 proposal. However,in their reg: AEE <br /> only remedy <br /> (2002a)report the proposed alternative 11 isput a letteth as r o Forward dated March li 2002.is <br /> time. The RWQCB accepted alternative 11 in the <br /> If the groundwater VOC concentrations <br /> that Alternative 3o not te at or some a rate variant on Alternat_-eis acceptable to j3 -be <br /> RWQCB then the Board willrequire <br /> implemented. The recent(AEE,2002a) <br /> atrends and triggerddendum to the at which <br /> procedures to analyze the hydrochem <br /> additional extraction wells would be considered. (Adanson,2002). <br /> 50(F•7) <br /> Identified in This EIR: undwater currently <br /> Two infiltration methods are currently used at the landfill. Most of the groundwater <br /> pumped by the former agricultural well is used onsite;thus,some q it er fr infiltrate it�O�� <br /> the unlined parts of the site and migrate back to the groundwater aqui <br /> extracted. Secondly,the treated groundwater from the groundwater extraction low and moves <br /> discharged into Littlejohn Creek currently,which both recharges aqui <br /> offsite. <br /> Treated groundwater from the groundwater extraction system is proposed It be infiwelled <br /> back to the aquifer through an infiltration basin(AEE, 2001 B,0 Balocand isaL�1 <br /> MND'-11. The infiltration basin would improve recharge to theaquifer <br /> designed to create a hydraulic barrierto inhibit tter to Forward dated Maer rard ch l Igr 002 agreed t° '11o�ti' <br /> tion of the <br /> groundwater plume. The RWQCB le <br /> for their recharge remedy(Alternative 11heo o font/ ter ard w�Iehoutt Alternatlls occurs. if the (eaten a a r <br /> puat mping)while quarterly monitmonitoringong <br /> VOC concentrations do not attenuate at a rate that is acceptable to the RWQCB theme&e <br /> tive 3,be implemen <br /> Board %rill require that Alternative 3, or some variant or,Alterna `�d•the <br /> the corrective <br /> edures to <br /> recent(AEE,2002a) addendum °concentrations <br /> at tto .p,additional extract on rani'_= z mould <br /> hydrochemical trends and triggerite- <br /> be considered. (Atkinson,2002). <br />