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Tailings stored in dams and impoundments are theoretically

supposed to remain forever, but in reality many storage facilities

fail. When mines were small-scale operations, the storage of

tailings was not given a lot of consideration and waste was

stored poorly or just dumped into valleys or rivers (and there

are many old abandoned mine sites that cause environmental

damage today as tailings do not necessarily become “safer”

with time). Improved technology has made it economical to

mine progressively lower grade ores, resulting in larger mines

and the production of more and more tailings that need to

be permanently quarantined from the environment. A review

of major tailings dam failures in the period 1910 to 2010 by

Bowker and Chambers (2015) found a trend towards failures of

increasing magnitude and negative impact, and concluded that

the scale of future disasters could require cleanup operations

that were beyond the economic capacity of mining companies.

Some of the largest mines in the world, and consequently

the largest waste dumps, are found in mountain regions and

statistically it appears that some of these storage dams will fail

in the future (Morgenstern et al 2015). The 2015 dam collapse

at the Germano iron ore mine located in ranges of Minas Gerais

in southeastern Brazil, illustrates the social, environmental and

economic impact of a giant dam failure. The collapse flooded

the village of Bento Rodrigues killing 19 people and spreading

toxic red mud for more than 700 km across two states (Hatje

Examples of some existing best practice guidelines, documents and initiatives related

to mining waste

“Reference document on Best Available Techniques

for Management of Tailings and Waste-Rock in Mining

Activities”:

In 2009, after an accident in Baia Mare

(2000), Romania, the European Commission released

this document, which as the name suggests describes

best available techniques for mining of the metals, coal

and selected industrial minerals. It includes rock-waste

management and tailings management (European

Commission, 2009)

“Safety guidelines and good practices for tailings

management facilities”:

The United Nations Economic

Commission (UNECE) for Europe issued this report in 2010

to supporting policymakers and the business sector in

enhancing awareness and the sharing of experience and

good practices among the competent authorities, operators

and the public. Another aim of this document is the better

harmonization of the regulations and requirements

concerning the safety of tailings management facilities

(TMF) in the ECE region (UNECE, 2014)

“Best Practice in Environmental Management of

Uranium Mines”:

the International Atomic Energy Agency

(IAEA) released this document in 2010 with the objective to

provide both operators and regulators with guidelines and

examples of the implementation of the principles of best

practice to the uranium mining and processing industry.

(IAEA, 2010)

International Council on Mining and Metals (ICCM):

ICMM

is an international organisation whose goal is to improve

the social and environmental performance of the mining

and metals industry. ICCM brings together 23 mining and

metals companies and 34 regional commodities associations,

identifying common challenges and working to establish a

safer and more sustainable industry. (ICMM, 2016)

2016). If a failure of this magnitude occurred high up in the

mountains the consequences could be even more devastating

and geographically extensive.

Perpetual waste: Waste generated after the

mine has closed

Mine restoration in mountain areas is difficult due to the steep

slopes, often thin, poor topsoil and high intensity rainfall events.

In addition, disturbed areas can be very extensive - open pit mines

constitute some of the largest man-made structures. Some mine

sites are just abandoned, with no attempt at restoration – this is

especially common inareas that haveexperienced informalmining,

in developing countries and or mines in developed countries that

operated prior to effective environmental legislation. Without

restoration, abandoned mine sites experience long-term erosion

and leaching from tailings impoundments and waste rock dumps.

Hard rock mines (associated with ores containing sulphides and

minerals like gold, silver, iron, copper, zinc, nickel, tin and lead) can

also be a source of environmentally damaging acid mine drainage.

Long after the economic minerals have been exhausted, acidic

waste can still be generated from the mine, stored tailings and

exposed rock. When iron sulphide minerals, common in many

mineral deposits, are exposed to air and water, they react to form

sulfuric acid and dissolved iron (the iron can precipitate, forming