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Mine tailings dams: Characteristics, failure, environmental impacts, and remediation

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In this article, a review of the characteristics, types and magnitudes, environmental impacts, and remediation of mine tailings dam failures is presented, covering the characteristics of the tailings held within these dams, what best safety practice is for these structures, and what adverse effects such accidents might have on the wider environment and how these might be mitigated.
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This article is published in Applied Geochemistry.The article was published on 2014-12-01 and is currently open access. It has received 524 citations till now. The article focuses on the topics: Tailings.

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Geochemical and mineralogical aspects of sulfide mine tailings

TL;DR: In this article, the authors investigated the effect of acid acid neutralization on the mobility of sulfide-oxidation products within sulfide mine tailings and found that the extent of acid neutralisation is a principal control on the pore-water pH.
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Fundão tailings dam failures: the environment tragedy of the largest technological disaster of Brazilian mining in global context

TL;DR: In this paper, the authors characterize the Fundao Tailings Dam and structural failures; improve the understanding of the scale of the disaster; and assess the largest technological disaster in the global context of tailings dam failures.
Journal ArticleDOI

Alkaline residues and the environment: A review of impacts, management practices and opportunities

TL;DR: The potential for recovery of metals critical to e-technologies, such as vanadium, cobalt, lithium and rare earths, from alkaline residues is considered in this paper.

Mine Wastes Characterization Treatment And Environmental Impacts

TL;DR: In this paper, a mine wastes characterization treatment and environmental impacts were downloaded from the Internet and infected with a virus inside their desktop computer, instead of enjoying a good book with a cup of tea in the afternoon.
References
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Book

Treatise on geochemistry

TL;DR: This extensively updated new edition of the widely acclaimed Treatise on Geochemistry has increased its coverage beyond the wide range of geochemical subject areas in the first edition, with five new volumes which include: the history of the atmosphere, geochemistry of mineral deposits, archaeology and anthropology, organic geochemistry and analytical geochemistry as discussed by the authors.
Journal ArticleDOI

Antimony in the environment: a review focused on natural waters: I. Occurrence

TL;DR: Antimony is ubiquitously present in the environment as a result of natural processes and human activities as discussed by the authors and is considered to be priority pollutants interest by the USEPA and the EU.
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Developing a framework for sustainable development indicators for the mining and minerals Industry

TL;DR: In this article, the authors proposed a framework for sustainability indicators as a tool for performance assessment and improvements in the mining and minerals industry, which includes economic, environmental, social and integrated indicators.
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Remediation technologies for heavy metal contaminated groundwater.

TL;DR: Thirty five approaches for groundwater treatment have been reviewed and classified under three large categories viz chemical, biochemical/biological/biosorption and physico-chemical treatment processes for a better understanding of each category.
Book

Mine Wastes: Characterization, Treatment and Environmental Impacts

TL;DR: In this paper, a thorough, up-to-date overview of wastes accumulating at mine sites is provided, dealing comprehensively with sulfidic mine wastes, mine water, tailings, cyanidation wastes of gold-silver ores, radioactive wastes of uranium ores and wastes of phosphate and potash ores.
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Frequently Asked Questions (18)
Q1. What contributions have the authors mentioned in the paper "Mine tailings dams: characteristics, failure, environmental impacts, and remediation" ?

In this paper, the authors reviewed the short-, medium-and longer-term effects of these impacts and concluded that tailings are best kept isolated from the floodplain environment in such watertight impoundments. 

Further collaborative research in the fields of engineering ( e. g., the influence of cementation on impoundment stability ), geomorphology ( e. g., the effects of changing flood occurrence on the remobilisation of contaminated floodplain sediments ), mineralogy ( e. g., the secondary mineral contaminant-sink assemblage ), chemistry ( e. g., the influence of oxidation on particular minerals ) and toxicology ( e. g., quantifying the role of the wind as a contaminant vector ) is required. It may be, however, that the accounting practices applied to the individual companies concerned do not provide a full and accurate assessment of the potential environmental cost and risk of tailings dam failure. 

Tailings dam spills can contaminate natural waters in the short-term, but in the medium- to longerterm (years to centuries) contaminant concentrations are likely to fall because of the effects of sediment and aqueous dilution and uptake by solid phases in the river bed and floodplain. 

Sampling on 12 and 13 November 1996 showed that river waters collected nextto the dam breach had > 2,500 mg L-1 Pb, and that this only fell gradually over 50 km to concentrations of ~ 500 mg L-1. 

Approaches to the handling and storage of tailings include riverine disposal, submarine disposal, wetland retention, backfilling, dry stacking and storage behind dammed impoundments (Lottermoser, 2007). 

For instance,immediately after the March 1626 failure of the Bolivian San Ildefonso dam, enormous quantities of tailings and Hg amalgam were released into the Pilcomayo catchment (Rudolph 1936; Gioda et al., 2002). 

Depending on the interaction between source mineralogy and localconditions, such as pH, climate and redox state, particular secondary minerals may form. 

Tailings dams are commonly constructed from readily available local materials, rather thanthe concrete used, for example, in water-retention dams. 

In addition, tailings dam failures may lead to further losses arising from business and supply chain interruption, particularly when large third party material damage or casualties occur and authorities close down an operation (e.g., Mahrla, 2011). 

The most common remedial measure taken for tailings dam spills, however, is the removalof the spilled tailings from the affected areas to a storage area. 

In order to preserve structural integrity of successive raises of dams, they are ideallyunderlain by a competent sand-sized layer rather than a loose, potentially incompetent clay-sized. 

Lásló (2006) calculated that the January spill released up to 120 tonnes of cyanide and metallic elements into the catchment, whereas the March spill, although not as extensive, released significant amounts of Pb, Cu and Zn. 

To that end it is appropriate to allow for good drainage of the dam by providing for a wide tailings ‘beach’ (defined as the sub-aerial tailings disposal point), which differentiates the tailings material by size, ensuring that the sand size larger (more permeable) particles form the dam structure, whereas finer (less permeable) clay sized particles are more distally dispersed. 

Good maintenance programmes are, therefore, an essential requirement of effective tailings impoundment management, a vital component of which is a comprehensive surveillance programme (Martin and Davies, 2000). 

Rather than initially installing a finalized full capacity structure, intermediate retaining embankments are normally constructed and then raised as storage demand increases (Lottermoser, 2007). 

The sheer magnitude and often toxic nature of the material held within tailings dams means that their failure, and the ensuing discharge into river systems, will invariably affect water and sediment quality, and aquatic and human life for potentially hundreds of km downstream (Edwards, 1996; Macklin et al. 

Dennis et al. (2009) have calculated that 155,000 tonnes of Pb, or 28% of the estimated total production, is stored within fluvial sediments in the Swale catchment. 

In this respect the negatively charged oxygen atoms in secondary minerals such as sulfates, carbonates, phosphates and arsenates may be significant sorption sites, with the negatively charged hydroxyl and oxygen ions found on the surface of primary and secondary oxide and clay minerals of particular significance.