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Final Remedial Action Completion Report for the ... - Rvaap.org

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<strong>Remedial</strong> <strong>Action</strong> <strong>Completion</strong> <strong>Report</strong><br />

June 2008<br />

Remediation of Soils and Dry Sediments at RVAAP 08-11 (LLs 1-4)<br />

Page 3-22<br />

discussed in <strong>the</strong> RAWP (Shaw 2007b). Shaw’s intrusive activities continued past <strong>the</strong> normal<br />

growing season <strong>for</strong> <strong>the</strong> required seed mixtures; however, Shaw applied <strong>the</strong> seed mixtures <strong>for</strong> <strong>the</strong><br />

completed areas as best possible. Only native species as identified in <strong>the</strong> INRMP were applied.<br />

At a minimum, annual rye was placed to provide a quick temporary cover at <strong>the</strong> restored areas.<br />

The annual rye was mixed with o<strong>the</strong>r more permanent species to provide long-term cover once<br />

<strong>the</strong> annual rye died off. No non-natives species were introduced. Since most of <strong>the</strong> excavation<br />

areas have not yet re-established vegetation, Shaw has maintained E&S controls consisting of silt<br />

fence and diversion barriers <strong>for</strong> rainwater run-on. Areas where <strong>the</strong> seed was applied were<br />

covered with a minimum of three bales of straw per every 1,000 ft 2 of disturbed area.<br />

3.8.2 Borrow Source Material<br />

Prior to bringing <strong>the</strong> material to <strong>the</strong> RVAAP, Shaw collected a borrow source sample at <strong>the</strong> exact<br />

location at <strong>the</strong> source where <strong>the</strong> soils were to be taken from. The sample was submitted to<br />

Kemron <strong>for</strong> <strong>the</strong> full suite of analytical parameters that included VOCs, SVOCs,<br />

herbicides/pesticides, PCBs, in<strong>org</strong>anics/mercury, and pH. Analytical results indicated all results<br />

were ei<strong>the</strong>r non-detect or below <strong>the</strong> applicable background concentrations with <strong>the</strong> exception of<br />

arsenic at 17.8 mg/kg. This concentration was below <strong>the</strong> applicable cleanup goal of 31 mg/kg<br />

<strong>for</strong> arsenic and Ohio EPA concurred that <strong>the</strong> metal concentration was naturally occurring.<br />

Shaw collected an additional sample prior to <strong>the</strong> 5,000 cubic yard interval of material to be<br />

brought on-site from <strong>the</strong> Route 5 Sand & Gravel source. The sample was again submitted to<br />

Kemron <strong>for</strong> <strong>the</strong> full suite of analytical parameters as <strong>for</strong> <strong>the</strong> initial sample. All results <strong>for</strong> this<br />

second sample were ei<strong>the</strong>r non-detect or below <strong>the</strong> applicable background concentrations,<br />

consistent with <strong>the</strong> initial sample from <strong>the</strong> backfill source.<br />

In all, a total of 9,772 tons (approximately 7,000 cubic yards) of borrow source material was<br />

brought on-site from Route 5 Sand & Gravel. Shaw regularly inspected <strong>the</strong> condition of <strong>the</strong> soils<br />

that were brought on-site to ensure <strong>the</strong> material was free of debris, large stones or leaching water.<br />

A summary of analytical results <strong>for</strong> <strong>the</strong> borrow source material are presented in <strong>the</strong> data tables<br />

(Table B-4) in Appendix B. The laboratory reports and associated data evaluation reports are<br />

presented in Appendix G included as an electronic attachment to this RACR.<br />

3.9 COORDINATION WITH BRAC DEMOLITION CONTRACTOR<br />

Shaw’s work was per<strong>for</strong>med concurrently with <strong>the</strong> demolition of <strong>the</strong> remaining buildings at LLs<br />

2-4. Shaw coordinated its activities with PIKA, <strong>the</strong> BRAC demolition contractor, to minimize<br />

potential disturbance to <strong>the</strong> proposed remediation areas by <strong>the</strong> demolition activities prior to<br />

excavation. Minor schedule interruptions associated with <strong>the</strong> demolition activities were<br />

encountered by Shaw due to limited access to <strong>the</strong> various load lines during demolition and delays<br />

in debris removal, in particular LL 4. It is expected that proposed future BRAC demolition<br />

activities of <strong>the</strong> remaining building slabs and foundations will disturb <strong>the</strong> areas previously<br />

backfilled and seeded by Shaw, and restoration of <strong>the</strong>se areas following <strong>the</strong> demolition activities<br />

will be addressed by <strong>the</strong> Army.<br />

*** FINAL***

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