Cottongrass effects on trace elements in submersed mine tailings.

Phytostabilization may limit the leakage of metals and As from submersed mine tailings, thus treatment of acid mine drainage with lime could be reduced. Tall cottongrass (Eriophorum angustifolium Honckeny) and white cottongrass (E. scheuchzeri Hoppe) were planted in pots with unlimed (pH 5.0) and limed (pH 10.9) tailings (containing sulfides) amended with sewage sludge (SS) or a bioashsewage sludge mixture (ASM). Effects of the amendments on plant growth and plant element uptake were studied. Also, effects of plant growth on elements (Cd, Cu, Pb, Zn, and As), pH, electrical conductivity (EC), and concentrations of SO4(2-), in the drainage water as well as dissolved oxygen in tailings, were measured. Both plant species grew better and the shoot element concentrations of white cottongrass were lower in SS than in ASM. Metal concentrations were lowest in drainage water from limed tailings, and plant establishment had little effect on metal release, except for an increase in Zn levels, even though SO4(2-) levels were increased. In unlimed tailings, plant growth increased SO4(2-) levels slightly; however, pH was increased and metal concentrations were low. Thus, metals were stabilized by plant uptake and high pH. Amendments or plants did not affect As levels in the drainage water from unlimed tailings. Thus, to reduce the use of lime for stabilizing metals, phytostabilization with tall cottongrass and white cottongrass on tailings is a sound possibility.

[1]  S. Caporn,et al.  Remediation of contaminated land by formation of heavy metal phosphates , 1996 .

[2]  J. Barko,et al.  Effects of Freshwater Macrophytes on Sediment Chemistry , 1988 .

[3]  J. P. Grime,et al.  Seed germination in response to diurnal fluctuations of temperature , 1977, Nature.

[4]  R. A. Smith,et al.  THE USE OF METAL TOLERANT PLANT POPULATIONS FOR THE RECLAMATION OF METALLIFEROUS WASTES , 1979 .

[5]  R. Delaune,et al.  Effect of redox potential and pH on arsenic speciation and solubility in a contaminated soil , 1991 .

[6]  H. Rydin,et al.  Utilization of waste products and inorganic fertilizer in the restoration of iron-mine tailings , 1989 .

[7]  I. Paspaliaris,et al.  The use of municipal sewage sludge for the stabilization of soil contaminated by mining activities. , 2000, Journal of hazardous materials.

[8]  K. Kalbitz,et al.  Mobilization of heavy metals and arsenic in polluted wetland soils and its dependence on dissolved organic matter. , 1998, The Science of the total environment.

[9]  P. Whitbread-Abrutat The potential of some soil amendments to improve tree growth on metalliferous mine wastes , 1997, Plant and Soil.

[10]  H. Holmström Geochemical processes in sulphidic mine tailings : field and laboratory studies performed in northern Sweden at the Laver, Stekenjokk and Kristineberg mine-sites , 2000 .

[11]  H. Holmström,et al.  Geochemical investigations of sulfide-bearing tailings at Kristineberg, northern Sweden, a few years after remediation. , 2001, The Science of the total environment.

[12]  W. Armstrong,et al.  Phragmites australis: Venturi- and humidity-induced pressure flows enhance rhizome aeration and rhizosphere oxidation , 1992 .

[13]  J. Grimalt,et al.  The mine tailing accident in Aznalcollar. , 1999, The Science of the total environment.

[14]  F. Fairbrother,et al.  Book reviewA text-book of quantitative inorganic analysis: A. I. Vogel: (including elementary instrumental analysis). 3rd Ed. Longmans, Green, London, 1962. Pp.xxx + 1216 70s. , 1963 .