HEAVY METAL CONTAMINATION OF BOTTOM SEDIMENTS FROM PAST MINING OPERATIONS AT COOKS POND, MADISON, NEW HAMPSHIRE
Five cores were collected from Cooks Pond using a Uwitec gravity corer with secondary hammer action. Sample sites were determined based on distance from the tailings fan and pond bathymetry. Cores (90mm diameter) were collected in water depths ranging from 4.5m to 7.5m and were 60-100cm in length. Sediment from a subset of the cores was sampled from the core barrel at 1cm intervals. In these samples, Pb and Zn were extracted using EPA method 3050A and analyzed by Inductively Coupled Plasma (ICP-OES). Mercury was measured directly by cold vapor atomic adsorption using a Teledyne Leeman Labs Hydra IIC Hg Analyzer. A second set of cores was split and scanned using an ITRAX core scanner. Fish were collected by seine net and hand line, and fillets were analyzed for Hg.
Samples show a sharp increase in Hg, Zn and Pb within a high density layer in the top third of the cores reaching concentrations as high as: 460 ppb Hg, 12,000 ppm Zn, and 7,600 ppm Pb. Metal concentrations also decrease with distance away from the processing plant. Analysis of piscivorous fish within the pond show Hg concentrations as high as 1200 ppb.
Washing of mine tailings into the pond explains the increase in Zn and Pb in the sediment. This material added high density mineral matter to the normally low density organic rich sediment and flooded the ecosystem with heavy metals. Mercury, typically associated with organic material, was regionally deposited from atmospheric deposition during the Industrial Revolution. The high Hg concentration within the high density portion of the core is somewhat of a conundrum. It might be expected that the influx of tailings would have diluted the atmospheric Hg. It is possible that Hg was used in the processing of the ore, but there is no historical record of its use.