OVERVIEW OF THE IMPACT OF MINING ON THE ... - IIED pubs

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low rainfall regions of the basin (where physical weathering processes predominate) have relatively low and/or localized impacts on the water resources. In contrast, mining operations located in the wetter regions of the basin where chemical weathering processes predominate tend to have far more extensive impacts. This seems to be due to the presence of ample moisture within the soil profile that enables continual chemical changes to take place and allows the water available to mobilize and transport the different contaminants that become available. A summarized overview of the actual and anticipated impacts of mining operations and mineral processing plants in each sub-catchment of the Zambezi basin is given in Table 3.41. This information provides a useful impression that could be used to focus water resource management plans and water quality management plans in the different component areas of the Zambezi basin. ccviii
4. <strong>THE</strong> LIMPOPO BASIN In order to provide a suitable background for subsequent descriptions of the impacts of mining on water resources in the Limpopo basin, this section starts with a brief overview of the catchment characteristics. This is then followed by condensed descriptions of the information relating to mining activities and their impacts in each sub-catchment. The Olifants basin is actually a sub-catchment of the Limpopo basin but has been treated separately in this report (see Section 5). As a result, the figures used in this report for the catchment area, runoff, and population of the Limpopo basin exclude the relevant details for the Olifants basin. 4.1 Introduction The Limpopo River is one of the most important rivers in southern Africa and its basin comprises portions of four SADC states (Botswana, Mozambique, South Africa and Zimbabwe; Table 4.1; Figure 1.1). The basin is located between 19.5 ° and 26.5 ° South latitude and between 25.5 ° and 34.5 ° East longitude, with a total basin area of approximately 282,000 km 2 , comprising roughly 9% of the total area of the four basin states. The area contributed to the basin by each state varies between 7.4% (Mozambique) and 12.8% (Botswana; Table 4.1). Table 4.1: Area statistics for the four SADC states comprising the Limpopo basin (excluding the Olifants subbasin, which is dealt with in Section 5). [Data obtained from Midgley et al. (1995), SARDC (1996) and Boroto & Görgens (1999)]. Country Total Area of Country (km 2 ) Country Area in Basin (km 2 ) ccix Proportion of Country Area (%) Proportion of Basin Area (%) Botswana 600,370 70,000 11.7 24.8 South Africa 1,219,912 102,900 8.4 36.5 Mozambique 801,590 59,000 7.4 20.9 Zimbabwe 390,759 49,900 12.8 17.8 Totals: 3,012,631 281,800 9.4 100.0 The Limpopo River has a relatively dense network of tributary streams and rivers, though most of these tributaries only have either seasonal or episodic flows. In historical times, the Limpopo River was considered to be a strong-flowing perennial river but is now regarded as a weakly perennial river where flows frequently cease and, during drought periods, no surface water is present over large stretches of the middle and lower reaches of the river.
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AN OVERVIEW OF THE IMPACT OF MINING
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AN OVERVIEW OF THE IMPACT OF MINING
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exploited, the size of the facility
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2.3.6 Stockpiling and transport of
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4.1.6 Mining and mineral processing
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LIST OF FIGURES Figure 1.1: Compari
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Table 1.6: Minimum annual productio
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Table 3.26: Mining operations in th
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ACKNOWLEDGEMENTS Several enthusiast
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1. INTRODUCTION AND BACKGROUND INFO
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Box 1.2). Each research team is req
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The MRC cannot be held responsible
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of amenity or deterioration in wate
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Typically, river flows in the count
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In simple terms, all of the propone
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shared by more than one country, es
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most appropriate technical or inves
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CAMEROUN GABON CENTRAL AFRICAN REPU
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1.6.1 Data on the location, nature,
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1997). In future studies, more atte
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Section 5 briefly reviews the water
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Mining methods vary widely and depe
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Removal and storage of ores and was
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These effects are usually ameliorat
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Water quality changes are widely co
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these substances are often mobilize
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The acidification of the water has
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and kinetic stability of the comple
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This process is carefully balanced
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neutralize each other - this situat
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(Chenje, 2000). Despite the recent
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Swaziland Water Environment Tanzani
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Draft Environmental Management Bill
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siting of works plan for approval t
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The draft policy encourages develop
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provides a definition but one which
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2.9.3.9 Zimbabwe Environmental Impa
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Sector Activity Industry °Chemical
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Cyanides and related compounds (CN)
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of Natural Resources and the South
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3.1.1 Geology, topography and soils
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Air temperatures across the Zambezi
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or fuelwood production. Similar pat
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Zambia. Clearly, some water quality
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3.2.1.6 Human impacts on water reso
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The Botswana segment of this area f
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3.4.1.4 Surface water users The onl
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3.5.1.2 Geology The Upper Karoo Bat
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3.5.6 Implications for water qualit
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3.6.4 Monitoring systems None. 3.6.
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3.7.2 Mining and mineral processing
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3.8.1.5 Water management systems Th
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3.9.1.2 Geology This sub-catchment
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3.9.5 Water quality data None avail
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Z-87 Mulobezi Amethyst Operating Ve
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3.11.1.6 Human impacts on water res
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3.12.1.2 Geology This sub-catchment
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• Increased quantities of suspend
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Determinant Fischer’s Farm Raglan
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3.13.1.4 Surface water users There
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The Nampundwe pyrite mine poses a r
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Z-90 Chisuki Mica, Tin, Tantalite O
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along the major roads between Chiru
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3.16.1 General description 3.16.1.1
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Z-17 Jessie Gold Starting Very Smal
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Small intrusions of Greenstone form
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Several stretches of streams and ri
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3.18.1.5 Water management systems T
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3.18.6 Implications for water quali
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3.20 The Mazowe (Mozambique) sub-ca
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3.20.4 Monitoring systems This area
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The only settlements of any size ar
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3.23.1 General description 3.23.1.1
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3.23.4 Monitoring systems None. 3.2
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• Non-point impact from minefield
Page 157 and 158: This is Zones G1-G6, B1-B3, S1-S6,
Page 159 and 160: The catchment falls mainly under th
Page 161 and 162: The two lone water quality data poi
Page 163 and 164: • Non-point domestic effluent, ru
Page 165 and 166: Land use comprises the Siabuwa, Oma
Page 167 and 168: 3.28 The Ume sub-catchment 3.28.1 G
Page 169 and 170: 3.28.4 Monitoring systems None. 3.2
Page 171 and 172: 3.29.1.4 Surface water users The Ci
Page 173 and 174: Thristle Etna Gold 6.7 Medium Tiger
Page 175 and 176: Sanyati, all may well contribute or
Page 177 and 178: 3.30.1.5 Water management systems T
Page 179 and 180: This is Zone Z1 of Area C (ZSG, 198
Page 181 and 182: 3.31.5 Water quality data Only one
Page 183 and 184: 3.32.2 Mining and mineral processin
Page 185 and 186: Land use above the Zambezi Escarpme
Page 187 and 188: Extensive alluvial mining of gold t
Page 189 and 190: The major settlements are the metro
Page 191 and 192: 3.34.6 Implications for water quali
Page 193 and 194: • Urban run off, urban areas of C
Page 195 and 196: 3.36.1.4 Surface water users The to
Page 197 and 198: 3.37.1.1 Hydrology This is Zones M1
Page 199 and 200: The catchment falls under the Harar
Page 201 and 202: 3.37.3 Alluvial mining Alluvial min
Page 203 and 204: widely intruded by Mashonaland Dole
Page 205 and 206: 3.38.4 Monitoring systems ZINWA is
Page 207: 3.39.2 Mining and mineral processin
Page 211 and 212: Mountains. Most of the basin consis
Page 213 and 214: the City of Pretoria and the northe
Page 215 and 216: continues to flow in the deeper all
Page 217 and 218: Each basin state maintains its own
Page 219 and 220: Land use in the upper parts of the
Page 221 and 222: the Limpopo River some 100 kilometr
Page 223 and 224: None obtainable in time for this re
Page 225 and 226: 4.4.2 Mining and mineral processing
Page 227 and 228: In the Botswana sector of the sub-c
Page 229 and 230: 4.5.5 Water quality data None avail
Page 231 and 232: 4.6.5 Water quality data None avail
Page 233 and 234: Table 4.9: Mining operations in the
Page 235 and 236: 4.7.4 Monitoring systems ZINWA is c
Page 237 and 238: There is exploration for diamonds (
Page 239 and 240: There is exploration, mainly for di
Page 241 and 242: 4.10.2 Mining and mineral processin
Page 243 and 244: Hwange National Park (ZSG, 1998). A
Page 245 and 246: 4.12.1.3 Pedology, agriculture and
Page 247 and 248: 4.13 The Marico sub-catchment 4.13.
Page 249 and 250: • Major non-point impact of agric
Page 251 and 252: Several thermal springs are located
Page 253 and 254: • Disposal of large volumes of li
Page 255 and 256: D7-13 Premier Diamond - kimberlite
Page 257 and 258: 4.15.1 General description 4.15.1.1
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4.15.2 Mining and mineral processin
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Most of the clayey loam soils in th
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4.17 The Theuniskloof sub-catchment
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4.17.4 Monitoring systems The Depar
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4.18.1.4 Surface water users All of
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Water quality data for three sites
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supplies in the sub-catchment, the
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4.20.1.2 Geology Like the Mogalakwe
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• Minor non-point impact from non
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4.21 The Nzhelele sub-catchment 4.2
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4.22.1.3 Pedology, agriculture and
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Code Number Name of Mine Commodity
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5. THE OLIFANTS CATCHMENT In order
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Soil formations across the Olifants
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indices of per capita agricultural
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professional capacity within the me
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• Dark grey to blackish, mottled
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5.2.5 Water quality data No specifi
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Several towns (e.g. Witbank and Mid
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The following mining operations are
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5.3.6 Implications for water qualit
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5.4.1.3 Pedology, agriculture and l
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K 5.5 5 4.5 Cl 380 350 200 F 1.0 1.
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local geological formations. High c
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The South African Department of Wat
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pH 8.5 8.3 8.8 8.7 8.8 8.9 TDS 439
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Soils in the sub-catchment can be d
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No information is available on the
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In its upper reaches, the sub-catch
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The Phalaborwa Water Board has been
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m 3 /day) water abstractions, and m
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In the south-west of the sub-catchm
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• Minor non-point impact of agric
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(Figure 4.2). The tributaries of th
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5.9.1.6 Human impacts on water reso
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y the upper Klaserie River. Recent
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5.10.6 Implications for water quali
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In Mozambique, the Mozambican Depar
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Acid mine drainage (AMD) represents
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• Antimony, cadmium and tin conta
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• Decreased light penetration to
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6.1.8 “Peripheral” or indirect
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Worldwide, the general public has e
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2. That copies of this report shoul
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Banks, D., P.L. Younger, R.T. Arnes
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CSIR (1993). An Environmental Impac
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Fuggle, R.F. & M.A. Rabie (1996). E
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Love, D. & D.K. Hallbauer (2000). M
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Pettersson, U.T. & J. Ingri (2000b)
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Turton, A.R. (1999b). Water scarcit
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World Bank (1998). World Developmen
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