Hostname: page-component-76fb5796d-zzh7m Total loading time: 0 Render date: 2024-04-27T00:13:55.495Z Has data issue: false hasContentIssue false

Legacy base metal slags can generate toxic leachates

Published online by Cambridge University Press:  30 January 2018

Adijat T. Awoniran*
Affiliation:
Department of Environmental Sciences, Macquarie University, Sydney 2109, Australia
Annelly Ketheson
Affiliation:
Department of Earth and Planetary Sciences, Macquarie University, Sydney 2109, Australia
Sandra Piazolo
Affiliation:
Department of Earth and Planetary Sciences, Macquarie University, Sydney 2109, Australia School of Earth and Environment, University of Leeds, Leeds LS2 9JT, UK
Damian B. Gore
Affiliation:
Department of Environmental Sciences, Macquarie University, Sydney 2109, Australia
*
a)Author to whom correspondence should be addressed. Electronic mail: adijat.awoniran@students.mq.edu.au

Abstract

Slags sourced from a derelict zinc–lead–copper–silver–tungsten mine were examined for their bulk elemental composition and mineralogy. pH, oxidation–reduction potential, and the leachability of selected elements (sulphur, calcium, iron, copper, zinc, and lead) were assessed during a 130-day deionised water extraction conducted under oxic conditions. Slags were rich in silicon, iron, copper, zinc, and lead, hosted within minerals including quartz (SiO2), goethite [FeO(OH)], augite [Ca(Mg,AI,Fe)Si2O6], and lead (Pb0). Leachates from the slags increased in analyte concentration throughout the 130-day experiment, with iron, copper, zinc, and lead attaining >5 mg l1 in some samples. These findings indicate that this pyrometallurgical waste should not be considered environmentally inert, as leachates emanating from them in the field might pose a significant risk to the environment.

Type
Technical Articles
Copyright
Copyright © International Centre for Diffraction Data 2018 

Access options

Get access to the full version of this content by using one of the access options below. (Log in options will check for institutional or personal access. Content may require purchase if you do not have access.)

References

American Society for Testing and Materials (ASTM) D1193-91. (1991). Water quality standards. Accessed 06 April 2017 http://www.muszeroldal.hu/assistance/waterstandards.pdf.Google Scholar
Bachmann, H.-G. (1982). The Identification of Slags from Archaeological Sites (Routledge, New York).Google Scholar
Banks, D., Younger, P. L., Arnesen, R-T., Iversen, E. R., and Banks, S. B. (1997). “Mine-water chemistry: the good, the bad and the ugly,” Environ. Geogra. 32, 157174.Google Scholar
Chand, S., Biswajit, P., and Kumar, M. (2016). “A comparative study of physicochemical and mineralogical properties of LD slag from some selected steel plants in India,” J. Environ. Sci. Technol. 9, 7587.CrossRefGoogle Scholar
Cooper, N. L., Bidwell, J. R., and Kumar, A. (2009). “Toxicity of copper, lead, and zinc mixtures to Ceriodaphnia dubia and Daphnia carinata ,” Ecotoxicol. Environ. Safety 72, 15231528.CrossRefGoogle ScholarPubMed
Digital Imaging Geological System (DIGS). (1976). Cordillera Mine, Tuena, Gunning. Accessed 30 Mar 2017. https://search.geoscience.nsw.gov.au/report/R00045002?q=cordillera%20mine&sort=score%20desc&t=all&a=true&p=false&s=false.Google Scholar
Ettler, V., Johan, Z., Kříbek, B., Šebek, O., and Mihaljevič, M. (2009). “Mineralogy and environmental stability of slags from the Tsumeb smelter, Namibia,” Appl. Geochem. 24, 115.Google Scholar
Fryirs, K., and Gore, D. (2013). “Sediment tracing in the upper Hunter catchment using elemental and mineralogical compositions: implications for catchment-scale suspended sediment (dis)connectivity and management,” Geomorphology 193, 112121.Google Scholar
Gore, D. B., Preston, N. J., and Fryirs, K. A. (2007). “Post-rehabilitation environmental hazard of Cu, Zn, As and Pb at the derelict Conrad Mine, eastern Australia,” Environ. Pollut. 148, 491500.CrossRefGoogle ScholarPubMed
Johnson, D. B., and Hallberg, K. B. (2005). “Acid mine drainage remediation options: a review,” Sci. Total Environ. 338, 314.Google Scholar
Julli, M. (1999). “Ecotoxicity and chemistry of leachates from blast furnace and basic oxygen steel slags,” Aus. J. Ecotoxicol. 5, 123132.Google Scholar
Kelly, M. (2015). “Former Pasminco worker reveals where tonnes of slag dumped around Cockle Bay and Speers Point park,” Newcastle Herald 07 Jan 2015. Accessed 21 Mar 2017. http://www.theherald.com.au/story/2803413/toxic-truth-slag-dumped-at-speers-point-park/.Google Scholar
Lottermoser, B. G. (2002). “Mobilization of heavy metals from historical smelting slag dumps, north Queensland, Australia,” Mineral. Mag. 66, 475490.Google Scholar
Mahieux, P.-Y., Aubert, J.-E., and Escadeillas, G. (2009). “Utilization of weathered basic oxygen furnace slag in the production of hydraulic road binders,” Constr. Build. Mater. 23, 742747.Google Scholar
Martínez-Sánchez, M. J., Navarro, M. C., Pérez-Sirvent, C., Marimón, J., Vidal, J., García-Lorenzo, M. L., and Bech, J. (2008). “Assessment of the mobility of metals in a mining-impacted coastal area (Spain, Western Mediterranean),” J. Geochem. Explor. 96, 171182.Google Scholar
MINDAT (2017). Cordillera Mine, Kangaloolah, Tuena, Georgiana Co., New South Wales, Australia. https://www.mindat.org/loc-77.html.Google Scholar
Morrison, A. L., and Gulson, B. L. (2007). “Preliminary findings of chemistry and bioaccessibility in base metal smelter slags,” Sci. Total Environ. 382, 3042.Google Scholar
Morrison, A. L., Swierczek, Z., and Gulson, B. L. (2016). “Visualisation and quantification of heavy metal accessibility in smelter slags: the influence of morphology on availability,” Environ. Pollut. 210, 271281.Google Scholar
Panayotova, M., Panayotov, V., and Sokolova, E. (2015). “Non-ferrous metals waste as metals’ resource. Part 1 – availability, chemistry and mineralogy,” Sustain. Dev. 3, 8593.Google Scholar
Parbhakar-Fox, A., Lottermoser, B., and Bradshaw, D. (2013). “Evaluating waste rock mineralogy and microtexture during kinetic testing for improved acid rock drainage prediction,” Mineral. Eng. 52, 111124.Google Scholar
Piatak, N. M., Seal, R. R. II, Hammarstrom, J. M. (2004). “Mineralogical and geochemical controls on the release of trace elements from slag produced by base- and precious-metal smelting at abandoned mine sites,” Appl. Geochem. 19, 10391064.Google Scholar
Piatak, N. M., Parsons, M. B., and Seal, R. R. II (2015). “Characteristics and environmental aspects of slag: a review,” Appl. Geochem. 57, 236266.Google Scholar
Romero, A., González, I., and Galán, E. (2006). “Estimation of potential pollution of waste mining dumps at Peña del Hierro (Pyrite Belt, SW, Spain) as a base for future mitigation actions,” Appl. Geochem. 21, 10931108.Google Scholar
Standards Australia. (1997). AS4439.3-1997. Wastes, sediments and contaminated soils – Part 3: Preparation of leachates – Bottle Leaching Procedure. https://infostore.saiglobal.com/STORE/PreviewDoc.aspx?saleItemID=382308.Google Scholar
Ströbele, F., Wenzel, T., Kronz, A., Hildebrandt, L. H., and Markl, G. (2010). “Mineralogical and geochemical characterization of high-medieval lead-silver smelting slags from Wiesloch near Heidelberg (Germany) – an approach to process reconstruction,” Archaeol. Anthropol. Sci. 2, 191215.Google Scholar
Strömberg, B., and Banwart, S. A. (1999). “Experimental study of acidity-consuming processes in mining waste rock: some influences of mineralogy and particle size,” Appl. Geochem. 14, 116.Google Scholar
Takeno, N. (2005). Atlas of Eh-pH Diagrams. Intercomparison of Thermodynamic Databases. (Geological Survey of Japan Open File Report No. 419). National Institute of Advanced Industrial Science and Technology. p 287.Google Scholar
Xue, Y., Wu, S., Hou, H., and Zha, J. (2006). “Experimental investigation of basic oxygen furnace slag used as aggregate in asphalt mixture,” J. Hazard. Mater. 138, 261268.Google Scholar