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File Report 116

Case, R., L. Buckland and M. Williams. 1996. The status and management of the Bathurst caribou herd, Northwest Territories, Canada. 34 pp.

ABSTRACT

This report outlines the goals and objectives used by the Department of Renewable Resources for management of the Bathurst caribou herd during the past 10 years.  The report also summarizes available data on ecology, discusses various uses of the herd, addresses potential impacts of industrial and recreational development, and describes management options for achieving goals and objectives.  In 1988, a draft Bathurst Caribou Management Plan was widely circulated among interest groups and the public, and public meetings were held throughout the Bathurst caribou range to discuss management options.  This draft plan and comments received resulted in the management program described in this report.

The Bathurst caribou herd is the largest in the NWT and is accessible to more people than other NWT herds.  Bathurst caribou presently occupy a range of approximately 250,000 km2.  In 1990, herd size was estimated at 352,000 caribou age one year and older.  At the present time the herd is at a density of 2 caribou/ km2 over the entire range.

The Bathurst herd and range appear to be in very good condition.  Recruitment has been high for several years and hunter kill has been relatively low.  Hunter harvest is a major source of mortality for the Bathurst herd.  General Hunting License holders make up the bulk of the hunting population, followed by Resident, Non-resident and Non-resident alien hunters.  The total harvest of Bathurst caribou (including commercial harvest) is estimated to be between 14,500 and 18,500.  It is felt that the herd can sustain this level of harvest.  The wolf is the only major predator of barren-ground caribou and is one of the main factors affecting natural mortality rates and, therefore, population growth.  Disease and parasitism are believed to be relatively unimportant at this time, although insect harassment may contribute to poorer fall condition and possibly reduced fertility.  Inter- and intra-specific competition do not appear to significantly influence population growth.  No data exist to suggest that weather has been a significant or direct cause of mortality on the Bathurst range.  Fire is a significant factor affecting the distribution of plant species and succession of the forests on the Bathurst range, but fire has had no detectable affect on caribou productivity.  Through their influence on range quality and, therefore, caribou distribution, forest fires may affect the availability of caribou to some users.

Industrial activities on the Bathurst range include mine sites, mineral exploration camps, winter access roads and air strips.  Individually, most of the potential and proposed developments are expected to have limited impact on the herd; however, development needs to be addressed on a regional and cumulative basis.

A main management objective for the Bathurst herd is to maintain a population level high enough to sustain a harvest of at least 16,000 annually.  A population of between 300,000 and 600,000 has been identified as the range which will meet this objective.  The total allowable harvest based on current information and the 1990 population estimate is approximately 23,000 caribou.  A calving ground survey to estimate the number of caribou in the herd is recommended for 1996.

It is intended that this report be the basis for future discussions on the management of the Bathurst caribou herd.  It is recommended that a management plan for the Bathurst herd be developed in consultation with all stakeholders following the calving ground survey in 1996.

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