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Arsenic speciation and distribution in the Carnon estuary following the acute discharge of contaminated water from a disused mine
Institution:1. Department for Visceral Surgery and Medicine, Bern University Hospital, University of Bern, Switzerland;2. Bern Center for Precision Medicine, Switzerland;3. ICTP – The Abdus Salam International Centre for Theoretical Physics, Strada Costiera 11, 34151 Trieste, Italy;1. Department of Medicine, University of Arizona, Tucson, AZ;2. Hematology and Oncology, H. Lee Moffitt Cancer Center, Tampa, FL;3. Molecular Pharmacology and Experimental Therapeutics, Mayo Clinic, Rochester, MN;4. Department of Pathology, University of Arizona, Tucson, AZ;5. Zhongda Hospital, School of Medicine, Southeast University, Nanjing, China;6. Department of Hematology, Leukemia Research Institute, The Catholic University of Korea, Seoul, South Korea;7. Arizona Cancer Center, University of Arizona, Tucson, AZ;8. Center for Health Outcomes and PharmacoEconomic Research, University of Arizona, Tucson, AZ
Abstract:In February 1991 Wheal Jane, a tin mine in S.W. England, was closed, the mine drainage pumps were removed and underground water levels were left to rise. By January 1992 the build up of water in the mine was sufficient to cause the Nangiles adit to burst, and contaminated mine water containing high levels of arsenic overflowed into the Carnon River. The river in turn drained into an estuary system which reaches the sea at Falmouth. A contingency plan was introduced, with water being pumped from the mine and treated before discharge through a tailings dam. This brought the discharge from Nangiles under control by late February 1992, although flow recommenced from mid-April until early July 1992.The immediate impact of the discharge and treatment operation on the distribution and speciation of arsenic in the river was the presence of high concentrations of dissolved arsenite, with a level of 240 μg As l−1 being measured below the mine tailings dam. Elevated concentrations of arsenite, typically 9 μg As l−1, persisted in the saline region of the Carnon estuary. By the following July the levels of arsenite had dropped significantly in the river but the levels in Restronguet Creek remained essentially unchanged. In comparison with the arsenite concentrations, the arsenate levels were comparatively low in the whole river/estuary system in the February following the initial discharge. A significant increase was however found in the saline region in the following July.Methylated arsenic species were absent from the river but were present in the biologically productive saline region during the warmer summer sampling period. The July concentrations of dimethylarsenic ranged from 1.0 to 2.1 μg As l−1 and monomethylarsenic from 0.2 to 0.5 μg As l−1.
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