section5-03a

Throughway Management

Minimize Environmental Impacts of Highways

Many of Canada’s national parks are transected by highways. These routes contribute to habitat fragmentation, direct and indirect wildlife mortality, and pollution. In 2000, the Panel on the Ecological Integrity of Canada’s National Parks highlighted this stressor. In response Parks Canada committed to developing a reporting and associated performance measurement framework to monitor and mitigate the impacts of through highways in national parks.

The framework, shown in Table 35, was completed in 2006 and is now being implemented in the 16 national parks that have through highways. Through the ecological integrity monitoring and reporting program, each national park identifies and addresses specific impacts of these highways, which include wildlife mortality, barrier effects on animal movement, invasive alien plants and road salt.

Table 35: Framework For Reporting On Ecological Impacts of Highways
Indicator

Measures

Highway construction and maintenance

Number of projects subject to environmental assessment and approval.

Viability of wildlife populations

Number of road kill by type of animal

Habitat connectivity

Number of animals using passages by age, gender

Pollution of Ecologically Sensitive Areas

Number of approved Salt Management Plans
Salt usage
Number of Parks with identified areas vulnerable to road salt

Vegetation (Quality of Roadside habitat)

Kilometres of highway with native vegetation restored or exotic plant species removed

Specific attention is being paid to wildlife mortality (10 parks), barrier effects on animal movement (11 parks), invasive alien plants (11 parks) and road salt (7 parks). Every year, the Agency reports on selected measures.

Table 36 summarizes ecological indicators of highways in national parks. Eighty per cent of these incidents resulted in confirmed mortalities, while ninety-five per cent involved big game species such as deer, wolf and bear. Though it is too early to examine trends in highway collisions, it is clear that parks differ in the intensity of this stress on wildlife populations as shown in Table 37.

Table 36: Ecological Indicators of Highways in National Parks

National Park

Wildlife Collisions

Habitat Fragmentation

Invasive Alien Vegetation

Road Salts

Banff

o

o

o

o

Cape Breton Highlands

o

o

o

o

Forillon

o

o

o

o

Fundy

?

o

x

?

Gros Morne

o

o

o

?

Jasper

o

o

o

o

Kootenay

o

o

o

?

Kouchibouguac

o

o

o

o

L’Anse aux Meadows*

?

?

?

?

Mt. Revelstoke and Glacier

o

o

o

o

Pacific Rim

o

o

o

x

Prince Albert

o

x

x

x

Riding Mountain

o

o

o

o

Terra Nova

o

o

o

o

Waterton Lakes

o

?

o

?

Yoho

o

o

o

?

Key:     o = Known impact     ? = Impact unknown     x = No impact
* L’Anse aux Meadows is a national historic site.

Table 37: Number of Wildlife Collisions on Through Highways in 2005 and 2006

National Park

2005

2006

Banff

23

19

Forillon

2

5

Jasper

104

128

Kootenay

42

62

Kouchibouguac

3

6

Prince Albert

5

7

Riding Mountain

12

7

Terra Nova

5

6

Waterton Lakes

9

12

Yoho

22

20

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