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<br />..... " <br /> <br />.. <br />,. <br /> <br />200600526 <br /> <br /> EXHIBIT B-2 <br />Table 2 - Notification of Hazardous Substance Storage, Release or Disposal <br /> Name of Hazardous Date of Storage, <br />Property Substance(s) Stored Release or Remedial Actions <br />Description (S), Released (R) or Disposal <br />Disposed (D) <br />Parcel 8A Explosive Periods of A number of containers of pesticides, herbicides, and other <br />Shop Area compounds and ammunition chemicals from Building S-37 were disposed of by DRMO in 1993 <br />Approximately waste including production through 1994. <br />32.387 acres 2,4,6-TNT and RDX between 1942 and Investigation of the Shop Area determined that there were <br />of land in laundry 1973 unacceptable concentrations of lead in soil. Soils contaminated with <br /> wastewater (Building lead were identified in the 1996 RI in the Shop Area, directly <br /> S-4, sumps, open east/northeast of Building S-22. The 1999 ROD identified the <br /> ditches, and selected remedy as excavation and off-site disposal of lead- <br /> leachfields) (S) (R) contaminated soil to or below the RAO of 400 1-191g, and deed <br /> restrictions to prevent residential use. <br /> Solvents and paints, Soil excavation activities were performed at the Shop Area (Parcel <br /> including lead-based 1942-1990 <br /> paint were used and 8A) in June 2000. All confirmation sample lead concentrations were <br /> stored in the paint below the RAO for lead. All excavations were backfilled with clean <br /> fill. The contaminated soil was disposed of at the Grand Island <br /> shop (Building S-22) Municipal Landfill. The selected remedy for lead in soil of excavation <br /> (S) and disposal has been achieved. The 2004 Final First Five-Year <br /> Paints, pesticides, Review Report determined that the selected remedy for OU3 <br /> remains protective of human health and the environment. <br /> solvents, oils, and <br /> other chemicals in 1942-1990 Beginning in December 2003, decontamination by thermal <br /> Paint Spray Shop decomposition and demolition of BUildings S-4 and S-5 in Parcel 8A <br /> and pesticide mixing in the Shop Area was performed for residual explosive contaminants. <br /> (Building S-37) (S) On October 20, 2004, the contractor performing this work certified <br /> that the identified buildings had been decontaminated to a 5X level <br /> and therefore the affected parcels of land could be transferred for <br /> sale. <br /> For the work that is performed in accordance with loep 385.1, the <br /> 5X designation indicates that no significant amounts (not enough to <br /> present an explosive safety hazard) of contamination remain. <br /> Several criteria must be met to achieve the 5X certification. Among <br /> these criteria are thermal decomposition of buildings at a sufficiently <br /> high temperature and a determination that explosive soil is not <br /> present. For the Shop Area sites, the criteria used to determine <br /> whether soil was considered explosive was a determination that the <br /> soil did not contain greater than 10% by weight of any secondary <br /> explosive or mixture of secondary explosives in soil samples. <br /> The >10% by weight explosives level is not a measure of toxicity <br /> hazard. Toxicity hazards due to explosive chemicals were evaluated <br /> in the 1996 RI, 1998 FS for OU3, and 1999 ROD for OU3. In the <br /> OU3 ROD, explosive contaminant soil cleanup levels established for <br /> the Shop Area include the following: <br /> 102 1-19lg of 1,3,5-trinitrobenzene <br /> 191 1-19lg of 2,4,6- trinitrotoluene <br /> The OU3 ROD determined that no explosive contaminants exceeded <br /> the cleanup levels established for the Shop Area. <br /> <br />EXHIBIT "B-2" A TT ACHED TO AND MADE <br /> <br />A PART OF QUITCLAIM DEED <br />