Literature DB >> 27139305

Composition and fate of mine- and smelter-derived particles in soils of humid subtropical and hot semi-arid areas.

Vojtěch Ettler1, Zdenek Johan2, Bohdan Kříbek3, František Veselovský3, Martin Mihaljevič4, Aleš Vaněk5, Vít Penížek5, Vladimír Majer3, Ondra Sracek6, Ben Mapani7, Fred Kamona7, Imasiku Nyambe8.   

Abstract

We studied the heavy mineral fraction, separated from mining- and smelter-affected topsoils, from both a humid subtropical area (Mufulira, Zambian Copperbelt) and a hot semi-arid area (Tsumeb, Namibia). High concentrations of metal(loid)s were detected in the studied soils: up to 1450mgAskg(-1), 8980mgCukg(-1), 4640mgPbkg(-1), 2620mgZnkg(-1). A combination of X-ray diffraction analysis (XRD), scanning electron microscopy (SEM/EDS), and electron probe microanalysis (EPMA) helped to identify the phases forming individual metal(loid)-bearing particles. Whereas spherical particles originate from the smelting and flue gas cleaning processes, angular particles have either geogenic origins or they are windblown from the mining operations and mine waste disposal sites. Sulphides from ores and mine tailings often exhibit weathering rims in contrast to smelter-derived high-temperature sulphides (chalcocite [Cu2S], digenite [Cu9S5], covellite [CuS], non-stoichiometric quenched Cu-Fe-S phases). Soils from humid subtropical areas exhibit higher available concentrations of metal(loids), and higher frequencies of weathering features (especially for copper-bearing oxides such as delafossite [Cu(1+)Fe(3+)O2]) are observed. In contrast, metal(loid)s are efficiently retained in semi-arid soils, where a high proportion of non-weathered smelter slag particles and low-solubility Ca-Cu-Pb arsenates occur. Our results indicate that compared to semi-arid areas (where inorganic contaminants were rather immobile in soils despite their high concentrations) a higher potential risk exists for agriculture in mine- and smelter-affected humid subtropical areas (where metal(loid) contaminants can be highly available for the uptake by crops).
Copyright © 2016 Elsevier B.V. All rights reserved.

Entities:  

Keywords:  Heavy mineral fraction; Mineralogy; Mining; Smelting; Soil; Weathering

Year:  2016        PMID: 27139305     DOI: 10.1016/j.scitotenv.2016.04.133

Source DB:  PubMed          Journal:  Sci Total Environ        ISSN: 0048-9697            Impact factor:   7.963


  3 in total

1.  Spatial distribution of smelter emission heavy metals on farmland soil.

Authors:  Weiqin Xing; Yali Zheng; Kirk G Scheckel; Yongming Luo; Liping Li
Journal:  Environ Monit Assess       Date:  2019-01-29       Impact factor: 2.513

2.  Lead source and bioaccessibility in windowsill dusts within a Pb smelting-affected area.

Authors:  Weiqin Xing; Hao Yang; James A Ippolito; Yuqing Zhang; Kirk G Scheckel; Liping Li
Journal:  Environ Pollut       Date:  2020-06-29       Impact factor: 8.071

3.  Atmospheric deposition of arsenic, cadmium, copper, lead, and zinc near an operating and an abandoned lead smelter.

Authors:  Weiqin Xing; Hao Yang; James A Ippolito; Qiang Zhao; Yuqing Zhang; Kirk G Scheckel; Liping Li
Journal:  J Environ Qual       Date:  2020-10-26       Impact factor: 3.866

  3 in total

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