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� <br />' <br />S:i/;\NOhI �1���iLSQf•�!. I1�C. <br />and operated to dcwater lhe ad��ance outwash as the cxcavation depth approaches the primary <br />water-bcaring zone and thc piczometric surface in thc advance outwash. <br />We completed a de�vutcring analysis for thc project bascd on the soil and groundwater conditions <br />dcscribed in Section 9.0 and aquifcr parameters estimated from lhe slug tcsting (Scction G.0 and <br />rlppendix D). Our analysis indicates that a dcep dewatering system consisting of 12 perimcter <br />wells will �c required for initial dcpress��rization of thc advance outwash aquifer. Eight wells <br />shouid be instalicd on approximately 50-foot centers along the western-most excavation edge <br />and along half of the northern excavation edgc (westem hal�; two wells should bc inst�lled <br />along thc south cdgc about 1 ZS to l50 fcct apart; and two wclis should bc installcd along the cast <br />excavation edgc ncar thc north corncr, about SO to100 fcet apart. The wcll diameter should be G <br />to S inches and thc maximum well dcpth will probably not cxcecd 100 fect. Thc rotal discharge <br />from thc 12-wcll systcm will likcly be from ]00 to 250 gallons per minutc. <br />Pollowing the initial depressurization, a secoud dewatcring system consisting of a vacuum <br />cxtraction/wcll point systcm, installcd ,u an anglc into thc soil, �+�ould providc construction <br />dewatering of the primary water-bearing unit (ad��ance ouhvash) as the excavation approaches <br />the piczometric surface and thc top of thc aquifcr. Thc u�cll points should be: 1) operated while <br />continuing the usc of die decp dcwatciing wcll systcm; 2) installcd Gom within the ercavation <br />and around thc entire perimeter of thc cxcavation; and, 3) installed on approxim�tely 6- to 9-foot <br />ccntcrs, altcmating �vith soil nail locations. Thc ��•cIl points ���ould bc installcd through and <br />bchind thc cxisting soil nail ���all cscavation f:ice and angled dowmvard into thc aquifcr. <br />Installation of the well point system should begin approximatcly 15 fect above thc bottom of the <br />aquifcr. '1'he total discharge from thc ��acuum estractionhvcll point system will likely bc from <br />I50 l0 200 gallons per minute. Additional lifts ancUor ���ell points may bc rcquired if signi(icant <br />�+�atcr-bcaring •r.ones arc cncountcrcd bclow thc primary �eatcr-bcaring zonc. <br />10.12 Yolentially Contaminaled Ground«�ater Collection, Trcatment, ancl Uisposal <br />In addition to contaminated soil, contaminatcd groundwatcr is present on site and will require <br />action during conslruction. B:�scd on thc analytical test results, somc of this groundwatcr may <br />not be suitablc for discharging direcUy into the se���cr and would thcreforc rcquirc isolation for <br />trcatment ancllor disposal. The constn�ction ground���ater from the soil nail drainagc matcrial, <br />dewateiin�, ���ells, ���cll points, and any swnps that may be used, would need to Ue collected, <br />an:�l}'��d (testcd). possihly Ue:ued, and then dispused. If an:il1'sis indicates that the eround���ater <br />.i. i.n��i. u.�ris �:i ,,�,�i�a 3I - I-0964d-005 <br />l9 <br />