Three Star Anodizing Record of Decision (PDF) - New York State ...
Three Star Anodizing Record of Decision (PDF) - New York State ...
Three Star Anodizing Record of Decision (PDF) - New York State ...
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integrity.<br />
Because the MGP area is currently a heavily vegetated area with value as a natural resource, the soil<br />
cover would incorporate a 25-feet wide buffer area along Wappinger Creek on the MGP area. This<br />
portion <strong>of</strong> the soil cover would be constructed by excavating the soil to a depth <strong>of</strong> approximately 1<br />
foot. The excavated cinder-containing fill material would be disposed <strong>of</strong>f site, and all or most <strong>of</strong> the<br />
trees and other vegetation would be removed as needed . The excavation would be backfilled with<br />
clean fill. The ground surface would be restored using appropriate native plantings.<br />
Groundwater Monitoring. Groundwater monitoring would be implemented to track concentrations <strong>of</strong><br />
VOCs and inorganic constituents in groundwater and would be instrumental in detecting changes in<br />
concentrations. Groundwater monitoring would consist <strong>of</strong> periodic sampling <strong>of</strong> wells with analysis<br />
<strong>of</strong> VOCs and inorganic constituents.<br />
Site Management Plan. Since impacted soil and contaminated groundwater would remain onsite, a<br />
site management plan (SMP) would be implemented to ensure the continuing protection <strong>of</strong> human<br />
health and the environment. The SMP would consist <strong>of</strong> management <strong>of</strong> the final cover system over<br />
contaminated soils, the lagoon containment system, and the erosion control system along the creek.<br />
The SMP would also include continued evaluation <strong>of</strong> the potential for vapor intrusion for on-site<br />
buildings developed on the site, periodic groundwater monitoring, identification <strong>of</strong> site use<br />
restrictions, and provisions for the continued proper operation and maintenance <strong>of</strong> the components <strong>of</strong><br />
the remedy.<br />
Periodic Certification. A periodic certification would be submitted to the Department. The<br />
document would certify that the SMP continues to be implemented, that the institutional controls and<br />
engineering controls are still in place and unchanged, and would state that nothing has occurred that<br />
would impair the ability <strong>of</strong> the remedy and site management to protect public health or the<br />
environment.<br />
Present Worth: ........................................................... $4,520,000<br />
Capital Cost: ............................................................ $3,540,000<br />
Annual Costs: ...............................................................$80,000<br />
Alternative 4: Vat Removal, Lagoon Excavation and Limited Soil Excavation and Cover<br />
Alternative 4 would consist <strong>of</strong> vat removal, sediment removal from the <strong>Three</strong> <strong>Star</strong> lagoon, limited<br />
soil excavation with <strong>of</strong>f-site disposal and placement <strong>of</strong> a soil cover over all areas <strong>of</strong> the site where<br />
surface and shallow soil contamination exceeds commercial SCGs. The areas that would be<br />
remediated under Alternative 4 are depicted in Figure 6. Alternative 4 would also include some <strong>of</strong><br />
the same active remedial actions described in Alternative 3; vapor control, removal and <strong>of</strong>f-site<br />
disposal <strong>of</strong> surface debris, demolition and <strong>of</strong>f-site disposal <strong>of</strong> the former gas holders, excavation <strong>of</strong><br />
impacted soil and soil cover over specific areas <strong>of</strong> the site. Alternative 4 would include the same<br />
access restrictions, groundwater monitoring, environmental easement, SMP and, if necessary, indoor<br />
vapor control described in Alternatives 2 and 3.<br />
Subsurface soil excavation and <strong>of</strong>f-site disposal. To address the VOC contamination exceeding<br />
SCGs, significant soil excavation would be conducted in the dry well area at the Axton-Cross<br />
building. Based on analytical results, it is anticipated that excavation <strong>of</strong> the former dry well area soil<br />
<strong>Three</strong> <strong>Star</strong> <strong>Anodizing</strong> Inactive Hazardous Waste Disposal Site March 2009<br />
RECORD OF DECISION Page 24