Abstract

When Wabakimi Wilderness Park was created in 1983, conservation of woodland caribou (Rangifer tarandus caribou) was one of the primary considerations. Twelve years later, in April 1995, the Government of Ontario announced that the Park, measuring some 155 000 ha, was to be expanded into a ca. 890 000 ha protected area. This was done following 2.5 yr of deliberations of the Wabakimi Park Boundary Committee. The Committee tried to reach consensus on an expanded protected area by examining a variety of options in terms of criteria related to a range of key values, one of which was woodland caribou. The analysis procedure involved dividing the 1.25-million-ha study area into more than sixty "assessment units". These were defined primarily on the basis of approximate sub-watershed boundaries. Each assessment unit was ranked on a five-level scale with respect to goodness for each value, including seasonal caribou habitat. High-value habitats for wintering, calving, and migration dominated the assessment of habitat importance for caribou.The initial assessment phase included six park expansion concepts ranging in size from just over 200 000 ha to about 1 million ha. One of the concepts (about 750 000 ha), was based specifically on the caribou value. In the second phase, four refined options were examined, ranging from just under 600 000 to roughly a million ha. Two additional options were added to the four and submitted to the Ontario Ministry of Natural Resources for consideration. The Committee was, in the end, unable to reach full consensus on which of the final options to recommend. However, upon consideration of the Committee's final report and other input, the Ontario Government announced in April 1995 the more than five-fold expansion. The new protected area contains about 475 000 ha of high-value caribou habitat. Caribou were a key value in determining both the ultimate size and configuration of the expansion.

Highlights

  • Natural resources decision-making works best when it is comprised of a productive blend of rational analysis and bounded politics (Lee, 1993)

  • Most participants and observers would agree with the statement made by Paul Gagné, Avenor's C E O, at the April 1995 announcement of the proposed expansion of the Wabakimi protected area: "The expansion of Wabakimi will create a world-class park and ensure the continued protection of unique land forms and wildlife habitats indigenous to the region." We are happy to report that the expanded park was officially regulated in July 1997

  • Caribou habitat was one of eleven key values that commanded much attention during the deliberations of the W P B C. It was fortuitous from a park-expansion point of view that several park values overlapped spatially in roughly the same areas surrounding the former, 155 000-ha Wabagium

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Summary

Introduction

Natural resources decision-making works best when it is comprised of a productive blend of rational analysis and bounded politics (Lee, 1993). Analysis for decision-making normally consists of a protocol including: (a) identification of criteria and indicators by which potential solutions are to be judged; (b) creation of alternative potential solutions; (c) prediction of the state of each indicator under implementation of each alternative solution; and (d) evaluation of alternative solutions in terms of the predictions (Duinker & Baskerville, 1986). In 1992, the Ontario Ministry of Natural Resources (OMNR) established a public advisory committee - the Wabakimi Park Boundary. The Committee engaged in a 2.5-yr process that included both technical analysis and consensus building. Eleven values (criteria) were chosen for evaluation of boundary-expansion alternatives.

Lake Superior
Background to the Wabakimi Park Boundary Committee
Caribou in the Wabakimi area
Study Area
Conclusions
Human disturbance
Findings
Collaborative Approaches to Resolving Natural Resources
Full Text
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