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WHAT IS SUSTAINABILITY IN THE CONTEXT OF MINERAL DEPOSITS?
Robert Bowell1
Sustainable development is a term that all too often has been hijacked within our society by politicians and business promoters eager to endorse their “green” credentials. Yet human society requires sustainable growth in order to continue. However, in the context of much of society’s mineral resources what does sustainability actually mean?
In the interest of complete disclosure, I have been a miner from the age of 16 and still own my own mining operations, so I am unapologetically promining. However, I also appreciate the planet we live on. The context and concept of mineral development being sustainable is one that intrigues me. By its very nature, mineral deposits are rarely “sustainable”. The activity of mining consumes a resource as the development progresses. At some point, a given mineral deposit will be physically or, more commonly, economically exhausted. Other than marine evaporates, guano phosphate and some soda ash deposits, mineral deposits are not renewed on a human timescale of true sustainability (Fig. 1).
This is nothing new. Georgius Agricola in his mid16th century book De Re Metallica [On the Nature of Metals (Minerals)] commented on the waste of resources in many of the mines around Freiberg, St Andreasberg and the Harz Mountains (Germany) and how they would cause problems for future generations. Yet, despite the consumption of resources, many mines continue for many generations. For example, the base metal–sulfide deposits of the Iberian Peninsula have been continuously mined for 5,000 years; the mines of Laviron in Greece were mined over a period of 3,000 years; and Bingham Canyon in Utah (USA), although just over a hundred years old, has seen the extraction of over 19 million tonnes of copper ore and continues to produce approximately 300,000 tons of copper, 500,000 ounces of gold, 4 million ounces of silver, 30 million pounds of molybdenum and 1 million tons of sulfuric acid every year! So, although not sustainable, certainly long lived (Fig. 2).
There is a growing interest in defining sustainability in the minerals industry. The papers in this volume highlight some of the research interest. Another recent and excellent publication on the topic focuses on the sustainability and historical development of global coal and copper resources, defined by the authors as “critical components in our species development” (Golding and Golding 2017).
1 SRK Consulting (UK) Limited 5th Floor, Churchill House, 17 Churchill Way Cardiff, CF10 2HH, Wales, UK E-mail: [email protected]
Despite often long and active periods of mining, most mines do not close as a result of the exhaustion of all ore. Mines close because the ore that is left costs more to extract at prevailing metal prices than will be realized in revenue. As many ore bodies reach this maturity or are abandoned, potential negative environmental impacts can and do occur.
It is conceivable that the mining legacies of previous generations can, through new technology, be considered as providing an alternative ore source, possibly in perpetuity: truly “sustainable mining”. A recent publication by Nordstrom et al. (2017) addressed the potential methods that could be applied to offset environmental impact mitigation and produce critically required metals from contaminated water discharged from mine sites. But is there really value in such an exercise?
An evaluation on mine waters discharged from Iron Mountain (California, USA) (Fig. 3) indicates “ore grade” concentrations up to 650 mg/L copper and 2,600 mg/L zinc in water with a pH less than 1.5 at a flow rate up to 50 L/s (Alpers et al. 2003). The calculated value of the water in terms of metals (primarily as copper and zinc) could be in excess of US$12,000 a day, making it a midsize basemetal producer. This water also has a wide range of other potentially valuable trace
Dr Robert Bowell, is a Corporate Consultant (Geochemistry) at SRK Consulting with 27 years’ experience. His background is in applied geology in tropical and deeply weathered terrains and mining consulting in the fields of due diligence, financial and technical audits, process chemistry, environmental geochemistry, environmental engineering and mineralogy. He specializes in the application of chemistry and mineralogy to solve engineering problems.
1811-5209/17/0297-$0.00 DOI: 10.2138/gselements.13.5.297
Figure 1 Hajipir Marine Chemical Operation (Northern India). This operation produces potash, halite and bromine by sea water evaporation and
chemical separation: production is over 130,000 t per year of product.
Figure 2 Bingham Canyon (Utah, USA). Open pit copper operation that covers some 9 km2 and has mined about two billion tons of material in over
100 years of operation.
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components as well (such as Ag, Pb, Cd, Li, Be, Ga, Ge, Sn, Te, Tl, and rareearth elements). However, the reality is that the total metal value can be very different from the economic value because it does not account for the cost of metal extraction, refining or transport. These costs can be on the order of 60% or more of total metal value. So, despite the attractive costs, if it costs $8,000 to $10,000 per day to recover these metals then the operation is less attractive as a commercial concern but could be driven by other factors, such as environmental cleanup.
Metal recovery from mine waters, such as at Iron Mountain, represents a potential source of revenue to offset water treatment costs and, in some places, may even represent an economic project in its own right.
A caveat exists, however: even if the “ore potential” can be proven and the technology can recover economic amounts of metal, there may still be little incentive to “remine” many old mining districts.
Companies that attempt such remining ventures may be held responsible for all past mining legacy, as well as any new disturbance. Furthermore, the mere mention of metal value from these old districts could result in legal action from property owners or bankruptcy trustees who will lay claim to any recovered value. It is quite conceivable that potentially “sustainable” developments could become unattainable simply due to legal quagmires. So, despite the potential for extractable minerals, in some cases they could become “legally offlimits”.
Nevertheless, in the current environment of highmetal demand and exhaustion of historically important metal sources, different sources of metals or technologies to extract metals will have to be found. This could be from mining deeper primary mineral resources, using new types of ore (such as bauxites) providing rareearth elements or returning to recover extractable minerals from abandoned mines. These challenges will require a good understanding of the mineralogy and geochemistry of the target metals and minerals in order to identify such “sustainable” opportunities. The geological community must be suitably trained and equipped to characterize such “sustainable” opportunities.
REFERENCESAlpers CN, Nordstrom DK, Spitzley J (2003) Extreme acid mine drainage from
a pyritic massive sulfide deposit: the Iron Mountain endmember. In: Jambor JL, Blowes DW, Ritchie AIM (eds), Environmental Aspects of Mine Wastes. Mineralogical Association of Canada, Short Course 31, pp 407430
Golding B, Golding SD (2017) Metals, Energy and Sustainability: The Story of Doctor Copper and King Coal. Springer International Publishing, 196 pp
Nordstrom DK, Bowell RJ, Campbell KM, Alpers CN (2017) Challenges in recovering resources from acid mine drainage. In: Wolkersdorfer C, Sartz L, Sillanpää M, Häkkinen A. (eds) Mine Water and Circular Economy. Proceedings of the 2017 International Mine Water Association Conference held 2530 June 2017 in Lappeenranta, Finland. International Mine Water Association, pp 11381147
Figure 3 Mine-water discharge from Iron Mountain (California, USA). The pH of the water ~1.5; copper content in this water is ~0.5–0.6 g/L; zinc
content is ~2 g/L.
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Introduction
The Kyrgyz Republic has a long history
of mineral exploration, commencing in
the 1930s and continuing during the
former Soviet times, up until 1991. A
number of large mercury, antimony, and
fluorite deposits occur in the southwest
part of the country, some of which were
substantial underground and open-pit
mines. The terrane is undulating and
is not exposed to a severe winter cli-
mate. All of the mining districts are eas-
ily accessible via a paved highway from
the provincial capital of Osh, which is
the second largest city in the Kyrgyz
Republic (Fig. 1). Gold exploration in
the region during the past two decades
has identified numerous deposits, now
recognized as Carlin type (Yakubchuk et
al., 2002; Seltmann et al., 2004; Rickle-
man et al., 2011). Limited work by Bar-
rick and Phelps Dodge in the late 1990s
confirmed the presence of Carlin-type
mineralization, and subsequent drilling
by ASX-listed Manas Resources between
2005 and 2010 discovered the Shambe-
sai and Obdilla gold deposits (www.
manasresources.com). Field visits and
sampling, conducted by the authors
in October 2016, of the main mer-
cury and antimony mining districts at
Khaidarkhan, Kadamzhai, Chauvai, and
Chonkoy (Fig. 1) further highlighted the
exploration potential of the southwest
part of the Kyrgyz Republic for signifi-
cant Carlin-type gold deposits.
Regional Setting
The Kyrgyz Republic may be conve-
niently divided into three E-W–trend-
ing tectonic units: the Northern,
Middle, and Southern Tien Shan. The
southwest part of the country com-
prises the western portion of the South-
ern Tien Shan and is mainly composed
of middle to late Paleozoic fore-arc
accretionary complex, which was sub-
jected to intense folding
Advancing Science and Discovery
JULY 2017
NUMBER 110
NEWSLETTERwww.segweb.org
to page 14 . . .†Corresponding author:
e-mail, [email protected]
The Carlin-Type Hg, Sb, As, Au, F, Tl Deposits
of the Southwest Kyrgyz Republic
Douglas Kirwin (SEG 1997 F),† Alexander Becker (SEG 2017), Iaroslav Bandurak, and
Brian Lueck (SEG 2014), Geological Consultants
SEG
2017 Conference
See p. 25–36 for details
CUGB
Ore Deposits of Asia: China and Beyond
September 17–20, 2017 Beijing, ChinaO
seg2017.org
FIGURE 1. Location of the Hg, Sb, As, Au, F, and Tl districts, southwest Kyrgyz Republic.
INTRODUCTIONNovember 2016 marked the 25th anniversary of the announcement of the discovery of diamonds in the Lac de Gras region of the Northwest Territories (NWT) of Canada. This is an anniversary that deserves great celebra-tion. From 1998 through 2015, it is estimated that Canada produced 172,700,000 carats of diamonds with a value of approximately CDN $29 billion (Natural Resources Canada, 2016). The discovery of diamonds in the NWT and the subsequent exploration, mining, and business success is an inspiring story to those of us in the exploration and mining business. The combination of vision, commitment, hard work, application of sound scientific principles, timely investment, and supportive government and communities can have a positive transfor-mational effect on a region and a country. This paper summarizes the formation and develop-ment of the diamond business in Canada.
Most of the world’s natural diamonds have been produced from mines exploiting kimber-lite volcanic complexes, with the remainder coming from lamproite volcanic complexes and alluvial and marine gravel deposits and conglomerates.
Advancing Science and Discovery
JANUARY 2017 NUMBER 108
NEWSLETTERwww.segweb.org
to page 12 . . .†E-mail, [email protected]
The Canadian Diamond Business: 25 Years and Going StrongBrooke Clements (SEG 1990),† JBC Ventures Ltd., North Vancouver, BC, Canada
SEG
2017 Conference
See p. 27–38 for details
CUGB
Ore Deposits of Asia: China and BeyondSeptember 17–20, 2017 Beijing, China
O
seg2017.org
FIGURE 1. Major North American kimberlite and lamproite districts. Refer to page 12 for the names of numbered districts.
LegendDiamond MinesPost-1990 DiscoveriesKimberlite DistrictsLamproite DistrictsInterpreted Archean Basement > 2.5 billion yearsInterpreted Proterozoic Basement > 1.5 billion years
Interested in Ore Deposits?
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