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Three Star Anodizing Record of Decision (PDF) - New York State ...

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the former raceway. Concentrations <strong>of</strong> inorganics were not significantly elevated below 22 ft in<br />

BMW-2.<br />

Groundwater<br />

VOCs were below SCGs in shallow groundwater collected from the upper raceway (MW-11)<br />

and next to the creek in the Building 12 Area (MW-8). In general, with the exception <strong>of</strong><br />

naphthalene, VOCs were not detected at significant concentrations within the groundwater and<br />

soil within the raceway.<br />

Naphthalene was detected at 160 ppb in shallow groundwater at MW-11 located in the upper<br />

raceway. Naphthalene was also present in deep groundwater beneath the MGP area at 77 ppb<br />

compared to the SCG <strong>of</strong> 10 ppb. No other SVOCs were present above SCGs in MW-11.<br />

Naphthalene was not detected in significant concentrations in groundwater in other areas <strong>of</strong> the<br />

Site, which suggests that there may have been some discharge <strong>of</strong> these materials to the former<br />

raceway.<br />

In the upper raceway (MW-13) total phenol was detected in shallow groundwater at 11 ppb.<br />

Shallow groundwater in each <strong>of</strong> the wells, MW-11 and BMW-2, within the former raceway<br />

contained up to 13 metals and cyanide above water quality standards in unfiltered samples. The<br />

widest range <strong>of</strong> constituents and highest concentrations were detected in MW-11 in the shallow<br />

groundwater under the raceway including concentrations <strong>of</strong> antimony (1,400 ppb), arsenic (1,100<br />

ppb) cadmium (22 ppb), chromium (1,700 ppb), copper (3,400 ppb), nickel (230 ppb), zinc<br />

(6,400 ppb) and cyanide (1,300 ppb) at concentrations well above groundwater standards. The<br />

deeper groundwater in this area (BMW-2) contained seven inorganics above water quality<br />

standards including antimony and mercury concentrations over 25 times the standards.<br />

Because <strong>of</strong> the highly elevated inorganics observed in raceway groundwater in the 2002<br />

sampling, an additional sample was obtained from the well in November 2008 for further<br />

analysis. The sample was split to allow for analysis <strong>of</strong> an unfiltered and a filtered sample. In the<br />

unfiltered sample, the inorganics detected were all at much lower concentrations than those<br />

detected in the 2002 sample. In some cases, inorganics detected in 2002 were undetectable in<br />

the filtered 2008 analysis. At 54 ppb, arsenic was the only inorganic detected above its<br />

groundwater SCG (25 ppb). The significant decrease in inorganic contaminants in the filtered<br />

sample relative to the unfiltered sample shows that the inorganics contamination is<br />

predominantly in the form <strong>of</strong> solids and particulate suspended in the groundwater sample and not<br />

dissolved in groundwater. The inorganics are much less mobile as suspended solids, than they<br />

would be if dissolved in the water.<br />

The data support the anecdotal information that the lower raceway was used as a conduit for<br />

disposal <strong>of</strong> liquid waste and possibly solids. The data indicate that the inorganics present in the<br />

soil in the lower raceway have not impacted groundwater. Surface soil contamination identified<br />

during the RI/FS in the lower raceway will be addressed in the remedy selection process.<br />

Building 21/22 Area<br />

Surface Soil<br />

In surface soil sample SS-08, cadmium (6.8 ppm), nickel (40 ppm) and zinc (333 ppm) were<br />

<strong>Three</strong> <strong>Star</strong> <strong>Anodizing</strong> Inactive Hazardous Waste Disposal Site March 2009<br />

RECORD OF DECISION Page 12

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