Skógræktarritið - 15.05.2001, Qupperneq 196

Skógræktarritið - 15.05.2001, Qupperneq 196
to weigh different options on how to react, and to evaluate the urgency of the requirement foraction (Fues 1998: 41, BUNDand Misereor 1996: 38). • Indicators offer a common con- ceptual framework, which facil- itates decision making and consensus finding to the per- sons taking part in the process (Fues 1998: 42). • Indicators are absolutely nec- essary in order to find out whether policy is working and to measure progress (Gouzée etal. 1995: 24). A second literature search shows limitations of indicators: • indicators are used abusively if they are regarded as indepen- dent values and if the basic relationship to the regarded circumstances remains uncon- sidered (Fues 1998: 41). • "While indicators certainly help to focus on the key issues and highlight some significant trends, they do not by any means give the whole story. They are by their nature simpli- fications. They also relate only to areas which can be readily quantified and aggregated in a meaningful way to give nation- al statistics." (Dept. of Environment 1996: 2) • "The power implicit in the indi- cators used for decision mak- ing will lead to the selection of unsuitable indicators or their misapplication." (WWF and NEF 1994b: 2) A survey among the members of the German and the Finnish commissions of sustainable development showed that the majority of the interviewed experts expressed the opinion that indicators are suitable to illustrate long-term development or the dimension of a problem to decision makers as well as to the public. indicators allow national and global comparability and support international reporting. Indicators are suitable to make decision-making visible, to moni- tor progress of policy implemen- tation and to point out calls for action. Further on it was men- tioned that indicators can serve the process of target-setting. About one third of the inter- viewed experts expressed the opinion, that indicators are not objective mirrors of reality and that they cannot reflect values nor clarify qualitative phenome- na or changes. Conclusions Since the Rio Conference, there has been a big effort in develop- ing criteria and indicators for the assessment of sustainable devel- opment (Essmann and Linser 1997; SRU 1998). |ust a few of those indicator systems are actu- ally in use. Some are too com- prehensive, have no underlying database, are superficial or high- ly aggregated and therefore unin- telligible. Indicators of sustain- able development that are based on a theoretical background (Linser, 1999) and an extensive statistical database can provide solid bases for decision-making at all levels and contribute to sustainable development. Most of the already developed indicator systems focus on the measurement and implementa- tion of ecological targets and thus only represent one aspect of sustainable development. Azar et al. (1996), BUND and Misereor (1996) and Walz (1997) criticize the strong emphasis on indica- tors of environmental status, while the interactions of society and ecological systems are insuf- ficiently considered. Therefore, it is especially important, that cri- teria and indicators are devel- oped for all three dimensions of sustainability. This requires a collective interaction of the rep- resentatives of the social, ecolog- ical and economic fields. The forest sector has always been a leader concerning sus- tainability, due to the fact that the origin of this concept goes back to forest management at the beginning of the 18^ centu- ry. In 1992, immediately after Rio, the development of criteria and indicators for sustainable forest management started enthusiastically, for example, within the Helsinki process (Schneider, 1995, p.184), the Montreal process (Kronauer, 1996, p. 1063) and the Tarapoto process (Schneider, 1997). Mistakes and diffi'culties occurred, but the will to improve can be seen everywhere. During revision of existing indicator sys- tems, all three dimensions of sustainability have to be given the sameweight. Furthermore, concepts have to be elaborated in a participatory approach. With regard to this background, a new, common definition of sustainable forest management was laid down in Resolution HI at the Third Ministerial Conference on the Protection of Forests in Europe in Lisbon, 1998: "sustainable forest management is tfie stewardsfiip and use offorests and forest lands in a way, and at a rate, tfiat maintains tfieir bio- diversity, productivity, regeneration capacity, vitality and tfieir potential to fulfil, nowand in thefulure, relevant ecological, economic and social func- tions, at local, national, and global lev- els, and that does not cause damage to other ecosystems". 194 SKÓGRÆKTARRITIÐ 2001 l .tbl.
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