| Subject | Mining, Mineral Extraction |
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| Text | Mining |
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The environmental effects of all types of mining, mineral extraction and quarrying in New Zealand are regulated through the Resource Management Act. Prior to 1991, mining activities were controlled through the Mining Act 1971, the Petroleum Act 1937, and the Coal Mines Act 1979. They were largely exempt from any local authority planning controls under the Town and Country Planning Act 1977, which has resulted in a number of environmental issues at problem sites which are still being dealt with today, after mining has ceased. The Crown Minerals Act 1991 deals with the management and extraction of Crown owned minerals. Through a system of Minerals Permits and Access Agreements, rights are allocated for mining and quarrying in return for the payment of royalties to the Crown. Minerals such as gold, silver, metals, fuel minerals (coal, gas and oil) industrial rocks and clays, stone used for building (schist, Oamaru Stone) are all classed as Crown-owned minerals, and are covered by the Act unless it can be determined that they are privately owned. A person or firm wishing to mine must obtain a mining permit from the Crown, which will set the amount of royalties to be paid. They must secure an access agreement with the landowner (if the land is not theirs), which will involve payment. They need to obtain any other necessary permits or authorities, e,g, authority to modify archaeological sites under the Historic Places Act 1993, the consent of the Minister of Conservation if the site is within the conservation estate, and building consents under the Building Act where structures are required. All mining operations require a resource consent. Gravel, sand, shingle and low-value rock of the type used in building construction, concrete and road building are not usually Crown-owned. Operations for quarrying and extracting these need a resource consent only. Environmental effects of mining Opencast mining results in large scale alteration to the landscape, with removal of vegetation, the need for restoration of landforms, and revegetation of large areas. Coal mining can result in acid drainage water, high levels of sediment and heavy metals entering streams and rivers. Cyanide and mercury are used in gold mining to extract gold from hard rock. Mining operations need to be engineered to contain these substances securely within the site, both during mine operations, and in the years after mining ceases. During the resource consent procedure, risks must be properly assessed and clearly communicated to communities. Measures to avoid, remedy or mitigate risks must be robust, and liability issues clarified. Bond payments are a common instrument used by local and regional authorities to deal with risks of this nature. Effective monitoring programmes are also essential. A useful summary of mining issues and impacts can be found in Chapter 10 of Forest and Bird’s ‘Handbook of Environmental Law’. (see reference list) Sustainable Management of Minerals |
| References |
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Harris, R.(ed)(2004) Handbook of Environmental Law Williams, D. A. R. (1997) Environmental and Resource Management Law, 2nd Edition Langer, E R. Davis, M. R. Ross, C. W. (1999) Rehabilitation of Lowland Native Forest After Mining in Westland PCE (1997) Long Term Management of the Environmental Effects of Tailing Dams. PCE (1992) Environmental Management of Coal Mining Barker, R and Hurley, G (1997) Mining and the Environment, 2nd ed. Mineral Resource Series No. 2. Bosselmann, K. and Grinlinton, D. (2002) Environmental Law for a Sustainable Society Journal ArticlesGibbs, M.(2003) The fate of existing mining privileges. Web-Based ResourcesSite:www.minerals.co.nz Site:www.crownminerals.govt.nz |
| Relevant Case Law |
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