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Zn isotope study of atmospheric emissions and dry depositions within a 5 km radius of a Pb–Zn refinery
Authors:Nadine Mattielli  Jérôme CJ Petit  Karine Deboudt  Pascal Flament  Esperanza Perdrix  Aurélien Taillez  Juliette Rimetz-Planchon  Dominique Weis
Institution:1. Institute of Geochemistry and Petrology, Department of Earth Sciences, ETH Zürich, NW D81.4, Clausiusstrasse 25, 8092 Zürich, Switzerland;2. Institute of Earth Sciences, Hebrew University of Jerusalem, 91904 Jerusalem, Israel;3. Department of Earth Sciences, University of Bristol, Wills Memorial Building, Queens Road, Bristol BS8 1RJ, UK;4. James Hutton Institute, Craigiebuckler, Aberdeen AB15 8QH, UK;5. Department of Crop and Soil Science, Oregon State University, 3041 Ag & Life Sciences Building, Corvallis, OR 97331, USA;6. Department of Geography, University of California, Santa Barbara, CA 93106-4060, USA;1. Université de Bordeaux UMR 5805 EPOC-OASU, TGM, Avenue des Facultés, 33405 Talence cedex, France;2. Université Libre de Bruxelles, Department of Earth and Environmental Sciences, G-Time, CP160/02, Av F.D. Roosevelt 50, B-1050 Brussels, Belgium
Abstract:The present paper examines the use of zinc isotopes as tracers of atmospheric sources and focuses on the potential fractionation of Zn isotopes through anthropogenic processes. In order to do so, Zn isotopic ratios are measured in enriched ores and airborne particles associated with pyrometallurgical activities of one of the major Pb–Zn refineries in France. Supporting the isotopic investigation, this paper also compares morphological and chemical characteristics of Zn particles collected on dry deposition plates (“environmental samples”) placed within a 5 km radius of the smelter, with those of Zn particles collected inside the plant (“process samples”), i.e. dust collected from the main exhaust system of the plant. To ensure a constant isotopic “supply”, the refinery processed a specific set of ores during the sampling campaigns, as agreed with the executive staff of the plant. Enriched ores and dust produced by the successive Zn extraction steps show strong isotope fractionation (from ?0.66 to +0.22‰) mainly related to evaporation processes within the blast furnaces. Dust from the main chimney displays a δ66Zn value of ?0.67‰. Application of the Rayleigh equation to evaluate the fractionation factor associated with the Zn vapor produced after a free evaporation gives a range of αore/vapor from 1.0004 to 1.0008. The dry deposits, collected on plates downwind of the refinery, display δ66Zn variations of up to +0.7‰. However, it is to be noted that between 190 and 1250 m from the main chimney of the refinery, the dry deposits show a high level of large (>10 μm) Zn, S, Fe and O bearing aggregates characterized by positive δ66Zn values (+0.02 to +0.19‰). These airborne particles probably derive from the re-suspension of slag heaps and local emissions from the working-units. In contrast, from 1720 to 4560 m, the dry deposits are comprised of small (PM10) particles, including spherical Zn-bearing aggregates, showing negative δ66Zn values (?0.52 to ?0.02‰). Our results suggest that the source of the distal dry fallouts is the main chimney plume, whose light Zn isotopic signature they preserve. Based on Zn isotopic analysis in combination with morphological and chemical characteristics of airborne particles, the present study suggests the traceability of smelter dusts by Zn isotopes.
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