Geochemical investigations of sulfide-bearing tailings at Kristineberg, northern Sweden, a few years after remediation

Citation
H. Holmstrom et al., Geochemical investigations of sulfide-bearing tailings at Kristineberg, northern Sweden, a few years after remediation, SCI TOTAL E, 273(1-3), 2001, pp. 111-133
Citations number
54
Categorie Soggetti
Environment/Ecology
Journal title
SCIENCE OF THE TOTAL ENVIRONMENT
ISSN journal
00489697 → ACNP
Volume
273
Issue
1-3
Year of publication
2001
Pages
111 - 133
Database
ISI
SICI code
0048-9697(20010612)273:1-3<111:GIOSTA>2.0.ZU;2-#
Abstract
In the Kristineberg mining area in northern Sweden, massive, pyrite-rich Zn -Cu ores are intercalated in ca, 1.9 Ga volcano-sedimentary rocks. Investig ations of a tailings impoundment remediated by means of both till coverage and raising the groundwater table have been undertaken. The aim of the stud !: was to characterise the tailings with respect to mineralogy, the chemica l composition of both the tailings and the pore water, and to try To identi fy the significant reactions that may have occurred before and after remedi ation. It was found that the oxidation front had reached down to depths of between approximately 0.1 and 1.15 m before remediation. The oxidation of s ulfides has produced high concentrations of some metals in the pore water; up to 26, 16, 4.1, 2.7 and 82 mg/l have been measured for Al, Mn. Fe and Zn , respectively. Concentrations of metals such as: Cd, Co, Cu, Ni and Ph are lower, with average concentrations of 18.4. 83.8 45. 79.6 and 451 mug/l, r espectively. Higher concentrations of major elements such as Ca, Fe, Mn, Mg and S have been measured at depth in pore water than at shallower levels. This is probably caused by hush out of elements after remediation and verti cal transport from the upper parts before remediation, The pH is relatively high, approximately 5.5 at most depths in the tailings, except in and arou nd the former oxidation zone where it is lower, and where the highest disso lved concentrations of elements such as As, Cd, Co, Cu, Pb and Zn occur. Th is is probably due to the release of metals secondarily retained below the oxidation front prior to the remediation, Since the groundwater table is ra ised, the groundwater reaches the retained metals, which leads to desorptio n of metals and dissolution of secondary minerals. (C) 2001 Elsevier Scienc e B.V. All rights reserved.