EJB Electronic Journal of Biotechnology ISSN: 0717-3458
 
© 2002 by Universidad Católica de Valparaíso -- Chile
 
BIOTECHNOLOGY ISSUES FOR DEVELOPING COUNTRIES

Present and future of bioleaching in developing countries

 

Fernando Acevedo
Escuela de Ingeniería Bioquímica
Universidad Católica de Valparaíso
Avenida Brasil 2147, Valparaíso. Chile
Tel: 56-32-273644
Fax: 56-32-273803
E-mail: facevedo@ucv.cl

Financial support: FONDECYT Grant 1020768.

Keywords: Acidithiobacillus, bacterial leaching, bio oxidation, heap leaching, tank leaching, Thiobacillus.

Abstract

Nowadays bioleaching occupies an increasingly important place among the available mining technologies. Today bioleaching is no longer a promising technology but an actual economical alternative for treating specific mineral ores. An important number of the current large-scale bioleaching operations are located in developing countries. This situation is determined by the fact that several developing countries have significant mineral reserves and by the characteristics of bioleaching that makes this technique especially suitable for these countries because of its simplicity and low capital cost requirement.

The current situation of commercial-size bioleaching operations and ongoing projects in developing countries is presented and discussed with especial reference to copper and gold mining. It is concluded that this technology can significantly contribute to the economic and social development of these countries.

Introduction

In our days, at the beginning of the XXI century, bioleaching occupies an increasingly important place among the available mining technologies. The situation is now quite different than was 25 years ago, when the first international meeting on the subject took place in Socorro, New Mexico (Murr et al. 1978), initiating the now traditional International Biohydrometallurgy Symposia. Today bioleaching is no longer a promising technology but an actual economical alternative for treating specific mineral ores.

Examination of the current large-scale bioleaching operations reveals that an important number of them are located in developing countries. This is not purely accidental but the necessary result of two important factors: for one thing,  many developing countries have significant mineral reserves and mining constitutes one of their main sources of income; on the other hand, bioleaching is a technique especially suitable for developing countries because of its simplicity and low capital cost requirement (DaSilva, 1981; DaSilva, 1982; Gentina and Acevedo, 1985; Warhurst, 1985; Acharya, 1990; Acevedo et al. 1993). This is the case for countries like Chile, Indonesia, Mexico, Peru and Zambia. As can be seen in Table 1, these developing countries share over 50% of the world copper production.

Table 1. World copper production (thousands of tonnes)a.

Country
1998
1999
2000

Australia

607.0

711.0

829.0

Canada

705.8

620.1

634.2

Chile

3,6869

4,391.6

4,602.0

China

486.0

520.0

588.5

Indonesia

809.1

790.3

1,005.5

Mexico

384.3

381.2

344.6

Peru

483.3

563.3

553.9

Poland

436.2

463.6

463.2

Russia

518.0

510.0

510.0

United States

1,860.0

1,601.0

1,480.0

Zambia

378.8

271.0

320.1

Others

1,932.7

1,915.9

1,912.7

World

12,288.1

12,712.0

13,243.7

a USGS Minerals Yearbook at http://minerals.usgs.gov/minerals/pubs/commodity/myb

 

In the case of gold mining, Brazil, Chile, Ghana, Indonesia, Papua New Guinea, Peru and Uzbekistan rank among the 13 top producer countries with 33% of the world production, as shown in Table 2.

Table 2. World gold production (tonnes)a.

Country
1998
1999
2000

Australia

310,1

301.1

296.4

Brazil

49.6

52.6

52.0

Canada

165.6

157.6

153.8

Chile

45.0

45.7

54.1

China

178.0

173.0

180.0

Ghana

72.5

79.9

72.1

Indonesia

124.0

127.1

124.6

Papua New Guinea

64.1

61.3

74.0

Peru

94.2

128.5

132.6

Russia

114.9

125.9

140.0

South Africa

464.7

451.3

430.8

United States

366.6

341.0

353.0

Uzbekistan

80.0

85.0

85.0

World

2,510.0

2,550.0

2,550.0

  a USGS Minerals Yearbook at http://minerals.usgs.gov/minerals/pubs/commodity/myb

 

Historical development

It is recognized that microorganisms have contributed to the solubilisation of metal sulphides since ancient times and that Romans benefited from their action long before Christ. It has been pointed out that the copper mine of Río Tinto in Spain was probably the first large-scale operation in which microorganism played a major role (Brierley, 1978; Brierley, 1982).

The role that microorganisms play in this process was demonstrated only in 1947 when Colmer and Hinkle isolated from acid mine waters bacteria belonging to the Thiobacillus genus (Le Roux, 1970). Later, Thiobacillus ferrooxidans (Temple and Colmer, 1951) and Thiobacillus thiooxidans (Temple and Delchamps, 1953)were isolated and characterised. Thiobacillus ferrooxidans has been recently reclassified as Acidithiobacillus ferrooxidans (Kelly and Wood, 2000).

In the period of 1950 to 1980, bioleaching was thought mostly as an appropriate technology for the recovery of copper and other metals from damps and low-grade ores. Probably the most important operations in those days were in the copper mines of Río Tinto, Spain and Cananea, Mexico. Río Tinto had a dump bioleaching operation, that produced 8,000 tonnes of copper per year, while Cananea produced 9,000 tonnes/year in its dump and in-situ operations (Gentina and Acevedo, 1985).

Although not completely successful, the pilot operation at Toromocho, Peru, can be cited as an important contribution to the development of bioleaching technology. In the mid-seventies, heaps and dumps up to 36 thousand tones of ore of 0,4% Cu were operated and evaluated. Although the copper recovery was lower than expected, the economic evaluation of a full-scale operation was positive (Zegarra, 1979; Warhurst, 1985).

A major multidisciplinary and multiinstitutional Chilean project on bacterial leaching of copper ore is also considered a landmark in bioleaching technology. The project, funded by the Chilean government and the United Nations Development Program - UNDP, started in 1985 with the participation of scientists and engineers from universities, research institutes and mining companies. Their activities covered a wide spectrum of topics, from basic biological aspects to the operation of small pilot heaps (Badilla-Ohlbaum et al. 1991). Its contribution to basic and applied knowledge in the area was recognised by the United Nations Industrial Development Organization- UNIDO (Anonymous, 1987).

A breakthrough in bioleaching practice was the establishment of the first copper mine exploited solely by bacterial technology. This goal was achieved in Minera Pudahuel in Chile, when in the mid-eighties they switch from a mixed acid and bacterial leaching to full heap bacterial leaching of an ore containing 1 to 2% copper, rendering 14,000 tonnes of fine copper per year (Acevedo et al. 1993). The process consisted in crushing, agglomeration, heap bioleaching, solvent extraction and electrowinning. It is worth noting that Pudahuel's biotechnology was totally developed in Chile.

Current bioleaching operations and projects in developing countries

Soon after the start-up of the Pudahuel process, several other copper bioleaching operations were established in Chile, as shown in Table 3.

Table 3. Copper bioleaching operations in Chile.

Mine

Production, tonnes/year

Heap leaching

Lo Aguirre

14,000

Quebrada Blanca

75,000

Cerro Colorado

100,000

Zaldívar

150,000

Iván-Zar

12,000

Andacollo-Cobre

21,000

Dump leaching

Chuquicamata

over 15,000

Los Bronces

n.d

Zaldívar

n.d

 
n.d: no data available  

A number of copper bioleaching projects are at this time under study and development. Perhaps the most meaningful one is being carried on jointly by the Chuquicamata Division of CODELCO (Chilean National Copper Corporation) and BHP Billiton. This project aims to the large-scale operation of a plant for the bioleaching of copper concentrates in continuous stirred tank reactors using thermophilic microorganisms. The project involves the construction of a US$ 60 million large pilot plant able to produce 20,000 tonnes of copper cathodes/year (Anonymous, 2002a; Anonymous, 2002b).

Another exciting experience is being carried on in Mexico. Peñoles S.A., in association with Mintek, has been able to produce several tonnes of copper cathodes in their demonstration plant in Monterrey. The plant is an integrated tank bioleaching, solvent extraction, electrowinning facility capable of producing 500 kg of copper per day (Anonymous, 2001a).

Bioleaching is also successfully applied in gold mining, when the metal is covered with a film of insoluble metal sulphides that difficult the extraction of gold with cyanide solutions. In this case, the sulphide film must be removed in order to obtain satisfactory gold recoveries, and bioleaching is presently the alternative of choice for such pre-treatment step. Ten large-scale gold biooxidation facilities are known to operate today, four of them located in developing countries, as shown in Table 4.

Table 4. Large-scale gold concentrates biooxidation plants in developing countriesa.

Plant

Capacity

Commisioned

São Bento, Brazil

150 tonnes gold concentrate/d

1990

Ashanti, Ghana

1.000 tonnes gold concentrate/d

1994

Sansu, Ghana

1.000 tonnes gold concentrate/d

1994

Tamboraque, Peru

260.000 tonnes zinc flotation tailings

1999

  a Acevedo, 2000

A series demonstration plant was commissioned on February 2002 in the Hutti Gold Mines in the Karnataka state in India. The plant was designed for treating gold and silver bearing concentrates, but it can be used for the bioleaching of copper, zinc, nickel and other base-metal concentrates  (Anonymous, 2002c). Another ongoing project is a heap bioleaching plant to treat zinc sulphide concentrates that is being developed in the Kumba's Rosh Pinah mine in Namibia (Anonymous, 2001b).

Looking forward

The current panorama of bioleaching in developing countries is encouraging. It is expected that in the coming years several new commercial-size bioleaching plants will be installed. It is likely that heap leaching will continue to be the choice for low-grade ores and tailings, while tank bioleaching technology will probably increase its application for gold, copper and other base-metal concentrates. The use of thermophilic bacteria and archea will be a major contribution, increasing the leaching rates and metal recoveries and allowing for the treatment of recalcitrant ores such as chalcopyrite.

Developing countries should increase their efforts in research and development in bioleaching technology, as they have comparative and competitive advantages in this area. International cooperation should also be considered in the establishment of new operations that can significantly contribute to the economic and social development of these countries.

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