Ferric minerals and organic matter change arsenic speciation in copper mine tailings

Arsenic (As) is commonly associated with Cu ore minerals, with the resultant risk that As can be released offsite from mine tailings. We used synchrotron-based fluorescence X-ray absorption near-edge spectroscopy (XANES) imaging to provide in situ, laterally-resolved speciation of As within tailings...

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Veröffentlicht in:Environmental pollution (1987) 2016-11, Vol.218, p.835-843
Hauptverfasser: Wang, Peng, Liu, Yunjia, Menzies, Neal W., Wehr, J. Bernhard, de Jonge, Martin D., Howard, Daryl L., Kopittke, Peter M., Huang, Longbin
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container_end_page 843
container_issue
container_start_page 835
container_title Environmental pollution (1987)
container_volume 218
creator Wang, Peng
Liu, Yunjia
Menzies, Neal W.
Wehr, J. Bernhard
de Jonge, Martin D.
Howard, Daryl L.
Kopittke, Peter M.
Huang, Longbin
description Arsenic (As) is commonly associated with Cu ore minerals, with the resultant risk that As can be released offsite from mine tailings. We used synchrotron-based fluorescence X-ray absorption near-edge spectroscopy (XANES) imaging to provide in situ, laterally-resolved speciation of As within tailings which differed in magnetite content (5–12%) and organic matter content (0–5%). Although the total As content was lower in tailings with low magnetite (LM), the soluble (pore water) As was actually 7-times higher in LM tailings than in high magnetite (HM) tailings. Additionally, amendment with 5% sugarcane mulch residues (SMR) (for revegetation) further increased soluble As due to the dissolution and oxidation of arsenopyrite or orpiment. Indeed, in HM tailings, arsenopyrite and orpiment initially accounted for 88% of the total As, which decreased to 48% upon the addition of SMR – this being associated with an increase in AsV-ferrihydrite from 12% to 52%. In LM tailings, the pattern of As distribution and speciation was similar, with As as AsV-ferrihydrite increasing from 57% to 75% upon the addition of SMR. These findings indicate that changes in ore processing technology, such as the recovery of magnetite could have significant environmental consequences regarding the As mobilisation and transformation in mine tailings. [Display omitted] •Changes in ore processing technology could affect As behaviour in tailings.•Laterally-resolved As speciation was mapped using synchrotron-based XANES imaging.•Addition of organic matter increased the dissolution and oxidation of arsenopyrite.•The removal of magnetite enhanced As mobilisation and risk in mine tailings. The recovery of magnetite has increased the oxidation and dissolution of arsenopyrite, consequently resulting in an increase in As mobilisation and risk in mine tailings.
doi_str_mv 10.1016/j.envpol.2016.08.007
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Bernhard ; de Jonge, Martin D. ; Howard, Daryl L. ; Kopittke, Peter M. ; Huang, Longbin</creator><creatorcontrib>Wang, Peng ; Liu, Yunjia ; Menzies, Neal W. ; Wehr, J. Bernhard ; de Jonge, Martin D. ; Howard, Daryl L. ; Kopittke, Peter M. ; Huang, Longbin</creatorcontrib><description>Arsenic (As) is commonly associated with Cu ore minerals, with the resultant risk that As can be released offsite from mine tailings. We used synchrotron-based fluorescence X-ray absorption near-edge spectroscopy (XANES) imaging to provide in situ, laterally-resolved speciation of As within tailings which differed in magnetite content (5–12%) and organic matter content (0–5%). Although the total As content was lower in tailings with low magnetite (LM), the soluble (pore water) As was actually 7-times higher in LM tailings than in high magnetite (HM) tailings. Additionally, amendment with 5% sugarcane mulch residues (SMR) (for revegetation) further increased soluble As due to the dissolution and oxidation of arsenopyrite or orpiment. Indeed, in HM tailings, arsenopyrite and orpiment initially accounted for 88% of the total As, which decreased to 48% upon the addition of SMR – this being associated with an increase in AsV-ferrihydrite from 12% to 52%. In LM tailings, the pattern of As distribution and speciation was similar, with As as AsV-ferrihydrite increasing from 57% to 75% upon the addition of SMR. These findings indicate that changes in ore processing technology, such as the recovery of magnetite could have significant environmental consequences regarding the As mobilisation and transformation in mine tailings. [Display omitted] •Changes in ore processing technology could affect As behaviour in tailings.•Laterally-resolved As speciation was mapped using synchrotron-based XANES imaging.•Addition of organic matter increased the dissolution and oxidation of arsenopyrite.•The removal of magnetite enhanced As mobilisation and risk in mine tailings. 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Additionally, amendment with 5% sugarcane mulch residues (SMR) (for revegetation) further increased soluble As due to the dissolution and oxidation of arsenopyrite or orpiment. Indeed, in HM tailings, arsenopyrite and orpiment initially accounted for 88% of the total As, which decreased to 48% upon the addition of SMR – this being associated with an increase in AsV-ferrihydrite from 12% to 52%. In LM tailings, the pattern of As distribution and speciation was similar, with As as AsV-ferrihydrite increasing from 57% to 75% upon the addition of SMR. These findings indicate that changes in ore processing technology, such as the recovery of magnetite could have significant environmental consequences regarding the As mobilisation and transformation in mine tailings. [Display omitted] •Changes in ore processing technology could affect As behaviour in tailings.•Laterally-resolved As speciation was mapped using synchrotron-based XANES imaging.•Addition of organic matter increased the dissolution and oxidation of arsenopyrite.•The removal of magnetite enhanced As mobilisation and risk in mine tailings. 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Although the total As content was lower in tailings with low magnetite (LM), the soluble (pore water) As was actually 7-times higher in LM tailings than in high magnetite (HM) tailings. Additionally, amendment with 5% sugarcane mulch residues (SMR) (for revegetation) further increased soluble As due to the dissolution and oxidation of arsenopyrite or orpiment. Indeed, in HM tailings, arsenopyrite and orpiment initially accounted for 88% of the total As, which decreased to 48% upon the addition of SMR – this being associated with an increase in AsV-ferrihydrite from 12% to 52%. In LM tailings, the pattern of As distribution and speciation was similar, with As as AsV-ferrihydrite increasing from 57% to 75% upon the addition of SMR. These findings indicate that changes in ore processing technology, such as the recovery of magnetite could have significant environmental consequences regarding the As mobilisation and transformation in mine tailings. [Display omitted] •Changes in ore processing technology could affect As behaviour in tailings.•Laterally-resolved As speciation was mapped using synchrotron-based XANES imaging.•Addition of organic matter increased the dissolution and oxidation of arsenopyrite.•The removal of magnetite enhanced As mobilisation and risk in mine tailings. The recovery of magnetite has increased the oxidation and dissolution of arsenopyrite, consequently resulting in an increase in As mobilisation and risk in mine tailings.</abstract><cop>England</cop><pub>Elsevier Ltd</pub><pmid>27524252</pmid><doi>10.1016/j.envpol.2016.08.007</doi><tpages>9</tpages><orcidid>https://orcid.org/0000-0001-8622-8767</orcidid><orcidid>https://orcid.org/0000-0003-4948-1880</orcidid></addata></record>
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identifier ISSN: 0269-7491
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subjects Arsenic - analysis
Arsenicals - analysis
Copper
Ferric Compounds - chemistry
Ferrosoferric Oxide - chemistry
Fluorescence-XANES imaging
Iron - chemistry
Iron Compounds - analysis
Laterally-resolved speciation
Magnetite removal
Minerals - analysis
Minerals - chemistry
Mining
Ore processing technology
Saccharum
Soil - chemistry
Soil Pollutants - analysis
Solubility
Sulfides - analysis
Transformation
Water Pollutants, Chemical - analysis
title Ferric minerals and organic matter change arsenic speciation in copper mine tailings
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