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UCREFRP
UCREFRP Catalog Number
8152
Author
Olver, C. H., B. J. Shuter and C. K. Minns.
Title
Toward a Definition of Conservation Principles for Fisheries Management.
USFW Year
1995.
USFW - Doc Type
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<br />1586 <br /> <br />Leopold (1939) suggested that economic biology, with its <br />focus on providing a competitive advantage to "useful" <br />species, needed to be replaced by an ecological approach <br />that conceived of the biota as a single system, the land <br />organism, "so complex, so conditioned by interwoven <br />cooperations and competitions, that no man can say where <br />utility begins or ends." The purpose of conservation was to <br />perpetuate the health of this system. Health was simply <br />"the capacity of the land for self-renewal" and conservation <br />"our effort to understand and preserve this capacity" <br />(Leopold 1949). <br />Leopold based his view of conservation on two com- <br />plementary principles: first, that humanity is best served by <br />preserving the natural life support systems of the planet; sec- <br />ond, that indigenous ecological systems have intrinsic <br />value that must be respected. He built an ecological ratio- <br />nale for his views that avoided the largely untenable sen- <br />timentalism of the Romantics and the strictly anthropo- <br />centric utilitarianism of the advocates of wise use. His <br />ideas found eloquent advocates in Canada (e.g., Clarke <br />1963; Coventry 1963). <br />The evolutionary-ecological land ethic of Leopold is <br />grounded in an intimate appreciation of the interconnected <br />structures and functions of ecosystems and their vulnera- <br />bility to unguarded tinkering. Since Leopold's time, the <br />land ethic has evolved into the concept of the ecosystem <br />approach (Christie et al. 1986), which aims to balance eco- <br />logical, economic, and social objectives and recognizes <br />that human uses must be reconciled with intrinsic and nec- <br />essary ecosystemic functions and structures. <br />Miller (1986), Regier and Bronson (1992), and others <br />have further attempted to recognize and codify the range of <br />thinking exemplified by the preservationist and utilitarian <br />attitudes. Miller (1986) describes the divergent viewpoints <br />that are generally represented in environmental disputes as <br />technocratic (=utilitarian) and humanistic (=preservationist). <br />These are ideological perspectives that cannot be resolved <br />by scientific validation and rational debate. <br />Both the preservationist and utilitarian approaches to <br />conservation have weaknesses. Both represent anthro- <br />pocentric views of ecosystems. The former focuses on <br />meeting the aesthetic and spiritual needs of humans while <br />the latter focuses on meeting their material needs. Extreme <br />preservationist attitudes promote intrinsic valuation of <br />resources and view wild ecosystems as temporally static, <br />rather than naturally dynamic. Extreme utilitarian attitudes <br />promote monetary valuation of resources and view ecosys- <br />tems as collections of organisms that can be arranged and <br />rearranged at will. Science cannot be used to determine <br />how resources should be valued in either case; however, sci- <br />ence can provide objective validation of those assump- <br />tions about the real world that underlie any particular val- <br />uation procedure. Current ecological science presents a <br />view of ecosystems (e.g., Pimm 1991: systems of inter- <br />acting biological populations, characterized by temporal <br />variation in abundance and species composition that are <br />constrained by past and present environmental conditions <br />and competitive-predatory linkages) that is quite incom- <br />patible with either of the ideological positions outlined <br />above. <br /> <br />Can. J. Fish. Aquat. Sci. Vol. 52, 1995 <br /> <br />In the modern parlance of resource management, the <br />terms sustainable development, sustainable use, and Con- <br />servation are often used interchangeably in ways that are <br />strongly influenced by the wise-use ethic of Pinchot. The <br />original definition of sustainable development, "development <br />that meets the needs of the present without compromis- <br />ing the ability of future generations to meet their Own <br />needs" (World Commission on Environment and Devel- <br />opment 1987), is really wise use with a longer time hori- <br />zon. A recent redefinition ("improving the quality of human <br />life while living within the carrying capacity of supporting <br />ecosystems" World Conservation Union, United Nations <br />Environment Programme, and World Wide Fund for Nature <br />1991) moves a bit towards Leopold's position by explicitly <br />recognizing the existence of ecological limits on use. Sus- <br />tainable use ("use of an organism, ecosystem or other <br />renewable resource at a rate within its capacity for renewal" <br />World Conservation Union, United Nations Environment <br />Programme, and World Wide Fund for Nature 1991) focuses <br />directly on use, but recognizes that limits on use should <br />be based on resource renewal rates rather than existing <br />inventory levels. <br />Several recent definitions of conservation also have a <br />strong utilitarian focus. In 1980, the World Conservation <br />Strategy of the International Union for the Conservation <br />of Nature and Natural Resources (1980) defined conser- <br />vation as "the management of human use [our italics] of the <br />biosphere so that it may yield the greatest sustainable ben- <br />efit to present generations while maintaining its potential <br />to meet the needs and aspirations of future generations." In <br />1991, conservation was defined as "the management of <br />human use [our italics] of organisms or ecosystems to <br />ensure such use is sustainable. Besides sustainable use, <br />conservation includes protection, maintenance, rehabilita- <br />tion, restoration, and enhancement of populations and <br />ecosystems'; (World Conservation Union, United Nations <br />Environment Programme, and World Wide Fund for Nature <br />1991 ). <br />The principal focus of all these definitions is resource <br />use. There are many reasons for rejecting use, or wise use <br />as the main focus for a new definition of conservation: <br />(i) It emphasizes the economic aspects of biology and thus <br />it fosters over-valuation of those natural entities that are of <br />direct use to man; (ii) It ignores intrinsic values by dis- <br />counting the complex interrelations between "useful" and <br />"nonuseful" organisms that characterize ecosystem function; <br />as Leopold (1949) noted, "One basic weakness in a con- <br />servation system based wholly on economic motives is <br />that most members of the land community have no eco- <br />nomic value" but they are "(as far as we know) essential to <br />its healthy functioning"; (iii) Wise use is often seen as <br />synonymous with multipurpose use or multiple use that <br />"usually involves an interminable succession of piecemeal <br />additions of new more intensive uses through time and a <br />stepwise ecological shift away from the initial wild state" <br />(Francis et al. 1979); and (iv) It signifies continued reliance <br />on an anthropocentric philosophy which holds that "only <br />people possess intrinsic value, while nature possesses <br />merely instrumental value" (Callicott 1991). <br />
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