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New Ajem 1210 Incorporating Indigenous values with ‘Western’ conservation values in sustainable biodiversity management A.J.J. Lynch, D.G. Fell and S. McIntyre-Tamwoy * iodiversity management in Australia is underlain In this United Nation’s declared Year of Biodiversity, it by legislative mechanisms such as the is important to take stock of and reassess commitments BEnvironment Protection and Biodiversity made at the 1992 Earth Summit in Rio and the Conservation Act 1999 (Cwlth) and policies such as the subsequent ratification in 1993 of the Convention on national Strategy for the Conservation of Australia’s Biological Diversity (CBD). These events were Biological Diversity and the international Convention on benchmarks in formalising the place of biological Biological Diversity. While these policy directives conservation globally and for instituting the term encompass a range of values and components of ‘biodiversity’ in the public, governmental and scientific ‘biodiversity’, on-ground planning and development sectors, and in international attitudes to conservation, assessments often focus only on threatened species and environmental management and sustainable development. ecosystems as defined in state and national legislation. The close and traditional dependence of many Indigenous In regions such as northern Cape York Peninsula, which communities on biological resources is also recognised in is managed by the resident Aboriginal and Torres Strait the CBD, along with the need to respect, preserve and Islander communities as Deed of Grant in Trust maintain traditional knowledge (see SCBD 2005, (DOGIT), planning for biodiversity management needs pp. 5-8). to acknowledge the high cultural values of such areas The Australian commitment as a signatory to the CBD and to encompass Indigenous values and perspectives. A was directly associated with the development of recent study assessed the significant species and habitats biodiversity-related national policy (e.g. the of the greater Lockerbie Scrub – the northernmost extent Intergovernmental Agreement on the Environment 19921; of rainforest in Australia and a region with high species the National Strategy for Ecologically Sustainable and ecosystem diversity. While it is acknowledged that Development 19922; the National Forest Policy Statement research into the cultural values of the plant species is (CoA 1992); the Strategy for the Conservation of preliminary, the minimal overlap between lists of flora Australia’s Biological Diversity (DEST 1996) and from Western (i.e. under legislative mechanisms) and legislation (various Acts and regulations encompassing Traditional Owner perspectives suggests that cultural conservation of species, ecosystems, and national and differences in values and perceptions may result in cultural assets, which later were amalgamated under the differing conservation management priorities. A more Commonwealth’s Environment Protection and holistic, integrative approach to local and national Biodiversity Conservation Act 1999, EPBC Act). Similar biodiversity management planning could accommodate policy and legislation mechanisms have been enacted multiple perspectives and enable greater environmental internationally, such as the Endangered Species Act 1973 and socio-cultural sustainability. in the United States, the UK Biodiversity Action Plan, the Birds Directive of 1979 and Habitats Directive of Keywords: Indigenous, Aboriginal, Gudang, biodiversity, 1992, which protect endangered species in European conservation, environmental management, cultural Union member states (McLean et al. 1999). Evaluation of values threats to species underlies decisions globally about species conservation listing and prioritisation, such as * Jasmyn Lynch is with the Centre for Environmental under the International Union for Conservation of Nature Management, School of Science and Engineering, University of Red List categories of extinction risk (IUCN 2001). Ballarat, PO Box 663, Ballarat Vic 3353; David Fell is at PO Box 337, Alstonville NSW 2477; and Susan McIntyre-Tamwoy is 1 See http://www.environment.gov.au/about/esd/publications/igae/index.html with the School of Arts and Social Sciences, James Cook (viewed 26 September 2010). University, PO Box 6811, Cairns Qld 4870. Email: 2 See http://www.environment.gov.au/about/esd/publications/strategy/ [email protected]. index.html (viewed 26 September 2010). 244 AUSTRALASIAN JOURNAL OF ENVIRONMENTAL MANAGEMENT—Volume 17 The role of Indigenous communities in Australian Both Indigenous and Western approaches to environmental management has developed inconsistently environmental management could be perceived as between regions, but Indigenous land and sea resource use frameworks but focused on different management activities in northern Australia have environmental aspects and timescales. Jackson (2005, p. proliferated since the mid-1980s (Hill et al. 2008). 138) argued against this on the basis that Indigenous Indigenous Australian communities are involved in values are not purely utilitarian but related to broader biodiversity and cultural heritage management through humanitarian ‘notions of sociality, sacredness, identity formalised land and sea management programs, including and life-giving’. However, Strang (1997) claimed that the Indigenous Protected Area program. They have Aboriginal management was highly practical, well responsibility through land claims under the Native Title organised, and coupled regular resource use with Act 1993 (Cwlth) for 12.1 per cent of the country management of the physical environment (including the (National Native Title Tribunal 2010)3, predominantly in use of spiritual increase rituals) to maximise and control remote areas (Altman et al. 2009) with limited resource availability and stability. Places were valued alternatives for effective land management arrangements. according to their resources, which is consistent with It should be noted, however, that, for some IPAs, cultural Western perspectives. heritage is considered a primary value with biodiversity Further, both Indigenous and Western environmental values as secondary (see DEWR 2007). management approaches have impacted on landscapes Nevertheless, and despite the acknowledgement of its and biotic assemblages. Lewis (1989) argued that importance in the CBD, Indigenous Traditional Aborigines and other foraging societies had varied and Ecological Knowledge (TEK) is frequently viewed as pronounced effects on most world environments, with inferior to ‘Western’ scientific approaches – as being Aboriginal setting of habitat fires as particularly intuitive, informal, less reliable and less accessible – and ecologically significant in Australia. Russell-Smith et al. its use remains elusive (Huntington 2000; Smallacombe (1997) supported that many elements of traditional et al. 2007). In contrast, scientific approaches to burning patterns – including its ordered, directed manner conservation have been criticised for being reductionist – were common to pre-contact Aboriginal groups in and relying on objectification and specificity, while coastal northern Australia. Although describing the ignoring social factors, long timescales and differing impact of Aboriginal burning on biodiversity and on perspectives (Strang 1997, p. 266; Jackson 2005; species extinctions and diversification as ‘complex’ and Rotarangi & Russell 2009) – essentially hyper-focusing ‘contentious’, Bowman (1998) acknowledged that it must on some aspects while neglecting the broader have influenced vegetation structure and species ranges, interconnectedness and complexity of ecosystems and of and may have caused the extinction of some species with the human – nature relationship. fire-sensitive habitats, particularly during periods of climatic stress. Lack of burning by Europeans, however, However, there is an increasing call to recognise and may have caused severe declines in small-to-medium- integrate TEK and Western scientific knowledge into sized mammal populations, vegetation changes, and environmental management (Berkes et al. 2000; range contractions in conifers and some monsoon Huntington 2000; Ross & Pickering 2002). Western rainforest trees (Bowman 1998; Russell Smith et al. conservation management approaches and Indigenous 2004). environmental perspectives have been viewed as in conflict, but an alternative is to recognise the multiplicity Since European settlement, land clearance has exceeded of logics and practices underlying different knowledge ecological limits across most of the intensive land-use systems and to reframe the debate as a science and zone of Australia, and significantly compromised broad- traditional knowledge dialogue and partnership with co- scale landscape functions (Beeton & McGrath 2009). production of complementary knowledge for problem- There are now over 2800 threatened ecosystems in solving (Agrawal 1995; Berkes 2009). There are Australia (Cork et al. 2006), many of Australia’s substantial heterogeneities among Indigenous knowledge mammal species occur over less than 20 per cent of their systems and substantial similarities across the artificial original range, six per cent of marsupials and 14 per cent Indigenous – Western knowledge divide (Agrawal 1995). of rodents extant 200 years ago are extinct, while 76 3 Large areas of freehold land (5.7 million hectares) are also owned by Aboriginal corporations in urban, rural and remote Australia (in contrast to land claimed under Native Title) and granted through the Commonwealth’s Indigenous Land
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