British Columbia Mine Reclamation Symposium

Balancing focal species, recreation and biodiversity in mountain coal mine closure planning : Alberta, Canada Kansas, J.L.; Symbaluk, M.D.


Coal extraction in the Coal Branch region of Alberta, Canada has occurred since 1911 with surface mining dominating as of the 1940s. Coal mining in this mountain/foothills landscape now occurs in a multiple land use context along with oil and gas exploration and production, timber harvest, aggregate mining, big game hunting/guiding/outfitting, fur trapping, recreational All Terrain Vehicle (ATV) use, fishing, camping and other outdoor recreational pursuits. Currently, there are three surface coal mines in various stages of active mining, reclamation and closure in the upper elevations of the Coal Branch region. Mining has taken place within an increasingly stringent regulatory framework. In the mid-1990s, application was made for the Cheviot mine project. It’s close proximity to Jasper National Park and heightened cumulative effects assessment requirements resulted in a ground-breaking series of public hearings, legal proceedings and two federal-provincial Joint Review Panels. Focal wildlife species, with particular emphasis on large carnivores (grizzly bears) and ungulates (elk, bighorn sheep), were a major aspect of the Cheviot environmental impact assessments and subsequent research/monitoring. The Cheviot mine was approved in 2004 with the first of a series of mine licenses required through the phased mine development. A land use planning process (LUP) is on-going for the end land use closure planning of two older coal mines (Luscar and Gregg River) located near the Cheviot Mine. This process is being informed by on-going ecological research and monitoring at all three mines. The issues and discussions surrounding the LUP are in turn informing the Cheviot Mine permit application process. Three over-arching end land use goals dominate the current mine closure planning debate. They include: 1) maintaining and enhancing focal species habitat and populations as per the original Cheviot project mandate; 2) preserving either pre-disturbance or modified recreational land use opportunities; and, 3) approximating pre-disturbance native biological diversity conditions. This paper discusses challenges and lessons learned over a 15-year period concerning the balancing of these three primary end land use goals.

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