TRACING MULTIPLE MERCURY SOURCES IN RIVER SEDIMENTS NEAR THE TVA KINGSTON SITE USING HG STABLE ISOTOPE RATIOS
202Hg/198Hg abundance ratios are expressed as δ202Hg values, which are per mil deviations from NIST SRM-3133. Odd isotope anomalies were also measured and are reported as Δ199Hg and Δ201Hg.
Our results suggest three distinct δ202Hg “signatures” for the three likely sources influencing the system. Average δ202Hg values for the Clinch River, Kingston fly-ash, and the natural background (represented by Emory River Mile Marker 12 samples) are -0.26 ± 0.16‰, -1.71 ± 0.42‰, and -1.17 ± 0.13‰, respectively. The data suggest that the upstream Clinch River is dominated by near-zero δ202Hg values, possibly due to the Y-12 plant near Oak Ridge. Sediment samples around the Kingston TVA plant, on both the Emory and Clinch rivers, are fully consistent with a three end-member mixing model. This model enables us to estimate the contributions of the three regional Hg sources to the total Hg inventory in each sediment sample.
The data also show that the Clinch River has Δ199Hg and Δ201Hg values distinct from the fly-ash and Emory River. The average 199Hg and 201Hg anomalies in the Clinch River samples are -0.10 ± 0.04‰ and -0.08 ± 0.02‰, respectively. The fly-ash and Emory River are indistinguishable from each other (Δ199Hg values of -0.22 ± 0.01‰ and -0.21 ± 0.06‰, respectively; Δ201Hg values of -0.16 ± 0.02‰ and -0.15 ± 0.03‰, respectively).
We infer from the data that Hg isotope ratios in river sediments really are semi-permanent “signatures” that do not change much with time. The range of values of Clinch River Mile 5.5 is 0.40‰ over an 11 month timescale, with no trend. The narrow overall range for these upstream samples suggests a lack of strong shifts as the Hg ages in the river system. However, it would be risky to simply assume that the Hg is completely chemically inert in the system.