Mercury (Hg) is a contaminant of global concern due to its long-range atmospheric transport and high toxicity. The focus of this research is on the role of the forest canopy in the accumulation, and delivery of Hg to the soil Hg pool. Particular focus is on the role of atmospheric speciation of Hg on deposition. An urban-rural gradient was examined from Mississauga to Dorset, Ontario, to determine the role of locally emitted Hg: RGM, and PM on deposition. [GEM] was measured to be similar at both sites, and [PM] and [RGM] were greater in the urban location. Seasonal accumulation of Hg on foliar surfaces was dominated by GEM, and similar at the urban (8.74 ng cm-2) and rural (9.80 ng cm-2) locations. Increased [PM] and [RGM] at the urban location resulted in a transient upper canopy Hg pool, and throughfall enrichment at the urban site.

Mercury (Hg) is a contaminant of global concern due to its long-range atmospheric transport and high toxicity. The focus of this research is on the role of the forest canopy in the accumulation, and delivery of Hg to the soil Hg pool. Particular focus is on the role of atmospheric speciation of Hg on deposition. An urban-rural gradient was examined from Mississauga to Dorset, Ontario, to determine the role of locally emitted Hg: RGM, and PM on deposition. [GEM] was measured to be similar at both sites, and [PM] and [RGM] were greater in the urban location. Seasonal accumulation of Hg on foliar surfaces was dominated by GEM, and similar at the urban (8.74 ng cm-2) and rural (9.80 ng cm-2) locations. Increased [PM] and [RGM] at the urban location resulted in a transient upper canopy Hg pool, and throughfall enrichment at the urban site.

Thesis (M.S.)--Auburn University, 2007. / Abstract. Vita. Includes bibliographic references (ℓ. 62-65)

Thesis (Ph. D.)--University of Wisconsin, 1952. / Typescript (carbon copy). eContent provider-neutral record in process. Description based on print version record. Includes bibliographical references (leaf 44).

Thesis (Ph. D.)--Lehigh University, 2006. / Includes vita. Includes bibliographical references (leaves 257-274).

The effects of sublethal additions of mercuric chloride were studied in the marine diatom Skaletonema costatug (Grev.) Cleve grown in ammonium-limited chemostats and batch cultures. In the short-term Hg exposure (up to 5 hours), unexposed chemostat effluents were simultaneously perturbed with 5 μM NH₄Cl and Hg concentrations ranging from 0.04 to 5.53 nM HgCl₂. In the long-term Hg exposure (679. 5 hours), ammonium-starved effluents were only perturbed with 5 μM NH₄Cl. In the short-term Hg exposure, when the effluent from the chemostat culture was starved for 1.5 hours, Hg decreased the affinity for the substrate (increased Ks value) and the rate of ammonium assimilation or the internally controlled uptake rate, Vimax . When the effluent was starved for 30 hours, only Vimax was reduced. These effects occurred between 1.84 and 3,68, and at 0,18 nM HgCl₂ in effluents starved for 1.5 and 30 hours, respectively. The maximum rate of uptake, Vs, was not depressed. In the long-term Hg exposure, at least 0.37 nH HgCl₂ decreased the specific growth rate and the maximum cell density, while the chlorophyll a per cell increased. A period of population decline was followed by resumption of growth. Morphological alterations were observed before and after the recovery. In the long-term experiment, six days of continual exposure to 0.37 nM HgCl₂ gradually increased the Ks value without affecting Vs and Vimax. The results from exposure to 3.68 nM HgCl₂ were similar to the short-term Hg exposure, since both the substrate affinity (Ks value) and the assimilatory rate Vimax were impaired. In addition, the maximal uptake rate, Vs, was also reduced after exposure to 3.68 nM HgCl₂ for six days in the long-term experiment. After resumption of growth in the Hg-treated cultures, when a new steady-state was established, the affinity for the substrate and assimilatory rates increased in phase D (day 23) compared to phase A (day 6). The recovery of growth and nutrient uptake rates in phase D, may have been partially mediated by the acquisition of Hg tolerance and the appearance of cells of a different stage of the sexual life cycle, as suggested by differences in cell size and chemical composition. An attempt was made to determine whether a short-term physiological response (Hg induction of metallothionein synthesis) could be responsible for the recovery. The 250 nm absorbance profile, of nutrient-saturated cultures exposed for 90 to 116 hours to sublethal concentrations of mercury, showed no large absorbance peak in the medium molecular weight pool, corresponding to laetallothionein, as it occurs in animals exposed to heavy metals. The intracellular distribution and levels of Cu, Zn, and Hg in S. costatum, grown in nutrient-saturated batch cultures, were affected by 0.37 nM HgCl₂. A concentration equal to or greater than 1.84 nM HgCl₂ reduced the growth rate and cell density, possibly due to the accumulation of Hg in the high m.w. pool. Exposure to 1.84 nM HgCl₂ prior to a second addition of 5.53 nM reduced Hg levels in ths high m.w. pool. Upon Hg exposure, Zn levels decreased in the high and low m.w. fractions but gradually increased in the medium m.w. pool. Copper slightly increased in the high m.w. pool but remained constant in the medium and low m.w. pools, in relation to total intracellular levels. High levels of Cu and Zn in the low m.w. pool suggests that a substance of a lower m.w., than usually reported for metallothionein, may be involved in the storage and detoxification of heavy metals in S. costatum. / Science, Faculty of / Botany, Department of / Graduate

Thesis (M.S.) in Civil Engineering--University of Maine, 2002. / Includes vita. Includes bibliographical references (leaves 80-85).

This work presents the first comprehensive study of Hg dynamics within Arctic multiyear sea ice, followed by a mechanistic study of Hg behaviour in new and growing experimental sea ice. Multiyear sea ice taken from the eastern Beaufort Sea and McClure Strait showed total Hg concentrations ranging from 0.12 to 12.2 ng L-1. Both vertical distribution patterns and regional differences can be explained by the sources and dynamics of particulate matter in sea ice. Methylated mercury was measured in Arctic sea ice: ratios of methylated to total Hg reached 0.4 within bottom ice, suggesting the potential occurrence of in situ methylation in sea ice. The dominant role of particulate dynamics in controlling Hg distribution in sea ice was supported by a mesocosm-scale study at the Sea-ice Environmental Research Facility. This suggests that melting multiyear sea ice represents a considerable loading of total and methylated Hg into the Arctic Ocean.

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