2016
DOI: 10.36487/acg_rep/1608_51_pearce
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Waste material placement options during construction and closure risk reduction — quantifying the how, the why and the how much

Abstract: Technical aspects of waste rock characterisation and assessment have been the focus of considerable research over the past decade, with many guidance documents being published on the subject internationally and within Australia. While these documents provide detailed information on how to characterise waste rock, there is not a great amount of guidance on how the placement of waste rock can be optimised to account for the results of the characterisation studies. In this respect it could be reasonably concluded… Show more

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Cited by 3 publications
(2 citation statements)
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“…Our understanding of how waste management methods impact the generation and subsequent release of AMD has significantly improved over the past 20 years (e.g. Wilson 2011;Miller 2014;Pearce et al, 2016b). However, this better understanding of how waste management influences the generation and release of AMD from source facilities has not been coupled with an equal improvement in waste management itself, across the industry.…”
Section: Acid and Metalliferous Drainage Management Strategymentioning
confidence: 99%
“…Our understanding of how waste management methods impact the generation and subsequent release of AMD has significantly improved over the past 20 years (e.g. Wilson 2011;Miller 2014;Pearce et al, 2016b). However, this better understanding of how waste management influences the generation and release of AMD from source facilities has not been coupled with an equal improvement in waste management itself, across the industry.…”
Section: Acid and Metalliferous Drainage Management Strategymentioning
confidence: 99%
“…For example, in the Diavik project, Canada, where a similar climate to this site is experienced, waste rock was grouped into three different types based on total sulphur values (i.e., Type I-< 0.04% S; Type II-0.04 to 0.008% S; Type III-> 0.08%) as documented in [41]. Such an approach could be adapted for this site, with ARDI, Hy-GI and total sulphur values instead used: Type IV: total S: >1%; ARDI score: >30/50; Hy-GI: <500 Highest risk/rapid AMD Type IV materials are the highest risk on-site, and therefore would be nominated for immediate segregation as described in [42,43]. Alternatively, if an encapsulation design is preferred, then their placement within the centre of a pile would be appropriate as described in [44].…”
Section: Waste Mangement Planningmentioning
confidence: 99%