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Final Second Five-Year Review Report Fort Ord Superfund Site ...

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8.0 SITE 3 ROD<br />

This section presents background information on the <strong>Site</strong> 3 Interim ROD; a summary of remedial actions<br />

and a technical assessment of the actions taken at this site; identifies any issues related to the<br />

protectiveness of the remedy based on the review; presents recommendations and follow-up actions, if<br />

needed, to address issues identified during the review; and provides a statement regarding the<br />

protectiveness of the site remedy.<br />

8.1 Background<br />

<strong>Site</strong> 3, the Beach Trainfire Ranges, extends approximately 3.2 miles along the coastline of Monterey Bay<br />

at the western boundary of <strong>Fort</strong> <strong>Ord</strong>, and was used for small arms training since the 1940s. In general,<br />

trainees fired small arms weapons from firing lines in the eastern portion of the site toward targets spaced<br />

at varying intervals to the west. Spent ammunition accumulated on the east-facing (leeward) sides of the<br />

sand dunes that formed the "backstops" for the targets. <strong>Site</strong> 3 is proposed for reuse as a state park<br />

consisting of hiking trails, campgrounds, and ancillary facilities. The excavation of contaminated soil on<br />

this site is complete. A post remediation risk assessment for both ecological and human health was<br />

completed (HLA, 1998c, IT, 2000b). The Army has completed a proposed plan, public comment period,<br />

and ROD addressing ecological risks at this site as described in Section 8.2.5.<br />

<strong>Site</strong> 3 is also known as MRS 22 (see Section 13, which addresses MEC-related issues).<br />

8.2 Remedial Actions<br />

8.2.1 Soil Remedial Unit<br />

A human health based level of concern of 1,860 mg/kg for lead in soil was developed. Concentrations of<br />

lead above 1,860 mg/kg occur mainly in areas where greater than 10 percent of the surface is covered by<br />

spent ammunition. Although some areas with moderate bullet distribution contain lead above the human<br />

health based level of concern, the ERA recommended remediation only in areas of heavy bullet<br />

distribution to minimize impacts to the sensitive ecological habitat in other areas. Therefore, the SRU is<br />

defined by those areas of heavy bullet distribution (greater than 10 percent).<br />

8.2.2 Remedy Selection<br />

• Alternative 1: No Further Action<br />

• Alternative 2: Excavation, screening and soil treatment<br />

• Alternative 3: Excavation, screening and onsite disposal<br />

Selected Remedy<br />

Alternative 3 was the selected remedy and consists of mechanical and hand excavation of areas with<br />

greater than 10 percent coverage of spent ammunition and soil followed by mechanical separation using<br />

screens and gravity-feed separation techniques. Excavated soil would be placed in the OU 2 landfill as<br />

foundation layer, or would be disposed of at an appropriate landfill facility. This alternative provides<br />

flexibility in planning and management of the large volume of soil to be excavated from <strong>Site</strong> 3 through<br />

consideration of two options. Disposal Option 1, placement of the soil in the OU 2 landfill, would meet<br />

the intent and purpose of the CAMU regulations in that it would offer an onsite location for management<br />

of the soil in an innovative, cost-effective, and protective manner. Disposal Option 2, transportation,<br />

<strong>Final</strong><br />

8-1<br />

FORMER FT ORD 5YR REVIEW 2007_FINAL United States Department of the Army

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