Canadian Protected Areas Status Report 2006 to 2011: chapter 3


Chapter 3: Protected Areas Management

Context

With more than 6000 terrestrial and marine protected sites covering 10.0% of Canada's land area and 0.9% of its marine territory, it is important to ask how well these protected areas are being managed.

Once protected areas are established, organizations have the responsibility to develop management policies and guidance, carry out management planning, conduct scientific research and monitoring programs, and enforce rules and regulations.

As demonstrated in Chapter 2, protected area organizations in Canada aspire to complex management goals such as "maintaining ecological integrity," "conserving biodiversity" and/or "protecting ecological goods and services." Management becomes even more challenging in the face of surrounding land use pressures, climate change, invasive species and other threats. For example, protected areas managers are currently dealing with large infestations of mountain pine beetle in western parks, the restoration of fire and grazing to grasslands in the prairies, invasive species such as the Emerald Ash Borer in Ontario, and threats to nesting sites of the endangered piping plover on coastal beaches in Atlantic Canada. Given the range of issues in protected areas, it is increasingly clear that just leaving nature alone will not be adequate to conserve biodiversity and many of the other values associated with protected areas (Graber et al., 2009).

"We clearly need to put as much effort into achieving sound and effective management of protected areas as into setting up new areas."

- Hockings et al. (2006)

Science plays a crucial role in supporting protected areas management. It helps managers to understand the ecology and ecological integrity of their protected areas, the nature and extent of the real and anticipated impacts of various threats on that ecological integrity, and the best ways to prevent or respond to these impacts so that protected area objectives can best be achieved.

The CBD PoWPA addresses a number of topics relevant to protected areas management, including mitigation of negative threats, involvement of Aboriginal and local communities, financial sustainability, and management effectiveness.

This third chapter of the status report addresses such questions as:

Program  Of Work  On Protected Areas: Sample Goals  For Protected Areas Management

Goal 1.4: To substantially improve site-based protected area planning and management

Goal 1.5: To prevent and mitigate the negative impacts of key threats to protected areas

Goal 2.1: To promote equity and benefit-sharing

Goal 2.2: To enhance and secure involvement of indigenous and local communities and relevant stakeholders

Goal 3.1: To provide an enabling policy, institutional and socio-economic environment for protected areas

Goal 3.4: To ensure financial sustainability of protected areas and national and regional systems of protected areas

Goal 3.5: To strengthen communication, education and public awareness

Goal 4.2: To evaluate and improve the effectiveness of protected areas management

Goal 4.3: To assess and monitor protected area status and trends

Goal 4.4: To ensure that scientific knowledge contributes to the establishment and effectiveness of protected areas and protected area systems

See Appendix 2 for the complete list of PoWPA goals and Aichi Biodiversity Targets.

Policy Framework For Management Of Protected Areas

Two thirds of terrestrial protected area organizations (11 of 16) have policy frameworks for the management of their protected areas in place, 7 of which are being updated. Two other organizations have frameworks under development. Six of 9 MPA organizations also have such policy frameworks in place.

What Is A "Policy Framework" For The Management Of Protected Areas?

Policy frameworks are statements of intent that provide direction for the management of protected areas, and can include such elements as a philosophy of approach, guiding principles, and direction on when management plans should be prepared, what should be considered, and who should be involved.

For example, Parks Canada Agency's Guiding Principles and Operational Policies contain the National Parks Policy and National Marine Conservation Areas Policy. Overarching guiding principles for both include the following concepts:

For more information, see Parks Canada Guiding Principles and Operational Policies

The Fisheries and Oceans Canada-led National Framework for Establishing and Managing Marine Protected Areas applies to MPAs under the Oceans Act and is currently being updated. Steps 4 and 6 of the Framework concern the development of a management plan for the candidate MPA site, and the management of the MPA once designated, and include the following direction:

For more information, see National Framework for Establishing and Managing Marine Protected Areas

Management Plan Development And Implementation

Although protected area organizations in Canada have developed numerous management plans since 2005, management planning is not keeping pace with the designation of new protected areas. Approximately 18% of Canada's protected areas have up-to-dateTable Footnote17 management plans in place as of 2011, slipping from 25% in 2005.

Among the 12 terrestrial organizations that reported in both 2005 and 2011, seven had increases in the total number of their protected areas that have management plans (PCA, BC, AB, SK, MB, QC and NL). However, management planning is lagging behind the designation of new protected areas (Figure 13).

Figure 13: Number of protected areas with up-to-date management plans compared with those without up-to-date plans and without plans, for 2005 and 2011

Numbers of total protected areas
Long description for Figure 13

A bar chart representing the number of protected areas with up-to-date management plans versus the total number of protected areas without up-to-date management plans in 2005 (first bar) and 2011 (second bar) in each province and territory and 4 federal departments (PCA, EC, AAFC, DFO; total of 8 bars); the vertical axis represents the total number of protected areas (from 0 to just over 2000).

Jurisdiction / year No. of protected areas with up-to-date plans No. of protected areas without up-to-date plans Total
BC 2005 573 262 835
BC 2011 481 539 1020
AB 2005 39 480 519
AB 2011 18 234 252
SK 2005 0 129 129
SK 2011 0 666 666
MB 2005 1 101 102
MB 2011 5 297 302
ON 2005 0 0 0
ON 2011 118 522 640
QC 2005 12 1084 1096
QC 2011 123 2277 2400
NB 2005 0 38 38
NB 2011 0 65 65
NS 2005 0 57 57
NS 2011 6 53 59
PE 2005 0 0 0
PE 2011 24 109 133
NL 2005 7 48 55
NL 2011 1 56 57
YT 2005 7 2 9
YT 2011 4 14 18
NT 2005 3 0 3
NT 2011 1 22 23
NU 2005 0 27 27
NU 2011 0 8 8
PCA 2005 25 17 42
PCA 2011 38 9 47
EC 2005 4 139 143
EC 2011 0 130 130
AAFC 2005 85 0 85
AAFC 2011 85 0 85
DFO 2005 5 0 5
DFO 2011 6 2 8

 

Tableau 11a : Terrestrial protected areas - Extent that management plans are in place and being implemented

Terrestrial protected areas - Provincial and territorial protected area agencies
Number of protected areas with management plans in place
Government
Organization
Number/
Total percent
Percent
BC
669/1 020
65.6 %
AB
60/252
23.8 %
SK
625/666
93.8 %
MB
9/302
3.0 %
ON
622/640
97.2 %
QC
207/2 400
8.6 %
NB
0/65
0.0 %
NS
14/59
23.7 %
PE
125/133
94.0 %
NL
17/60
28.3 %
YT
4/18
22.2 %
NT
3/23
13.0 %
NU
0/8
0.0 %
Terrestrial protected areas - Provincial and territorial protected area agencies
Number of protected areas with management plans less than 10 years old Extent that management
Government
Organization
Number/
Total percent
Percent
BC
481/1 020
47.2 %
AB
18/252
7.1 %
SK
0/666
0.0 %
MB
5/302
0.0 %
ON
118/640
18.4 %
QC
179/2 400
7.5 %
NB
0/65
0.0 %
NS
6/59
10.2 %
PE
24/133
18.0 %
NL
1/57
1.8 %
YT
4/18
22.2 %
NT
1/23
4.3 %
NU
0/8
0.0 %
Terrestrial protected areas - Provincial and territorial protected area agencies
Government
Organization
Extent that management actions are being implemented
BC
Not Known
AB
Partially
SK
Not Known
MB
Substantially
ON
Partially
QC
Not Known
NB
Not Known
NS
Not Known
PE
Not Known
NL
Not Known
YT
Not Known
NT
Not Known
NU
Not Known
Terrestrial protected areas - Federal protected area agencies
Number of protected areas with management plans in place
Government
Organization
Number/
Total percent
Percent
PCA
40/47
85.1 %
EC
13/130
10.0 %
AAFC
85/85
100 %
DFO
DNR
DNR
Terrestrial protected areas - Federal protected area agencies
Number of protected areas with management plans less than 10 years old Extent that management
Government
Organization
Number/
Total percent
Percent
PCA
38/47
80.9 %
EC
0/130
0.0 %
AAFC
85/85
100 %
DFO
DNR
DNR
Terrestrial protected areas - Federal protected area agencies
Government
Organization
Extent that management actions are being implemented
PCA
Substantially
EC
Not Known
AAFC
Fully
DFO
DNR

Tableau 11b : Marine protected areas - Extent that management plans are in place and being implemented

Marine protected areas - Provincial and territorial protected area agencies
Number of protected areas with management plans in place
Government
Organization
Number/
Total percent
Percent
BC
Included in Terrestrial protected areas
Included in Terrestrial protected areas
MB
No information provided
No information provided
QC
14/466
3.0 %
NB
0/1
0.0 %
PE
-
-
NL
3/6
50 %
Marine protected areas - Provincial and territorial protected area agencies
Number of protected areas with management plans less than 10 years old Extent that management
Government
Organization
Number/
Total percent
Percent
BC
Included in Terrestrial protected areas
Included in Terrestrial protected areas
MB
No information provided
No information provided
QC
11/466
2.4 %
NB
0/1
0.0 %
PE
Included in Terrestrial protected areas
Included in Terrestrial protected areas
NL
0/6
0.0 %
Marine protected areas - Provincial and territorial protected area agencies
Government
Organization
Extent that management actions are being implemented
BC
Included in Terrestrial protected areas
MB
Not Known
QC
Not Known
NB
Not Known
PE
-
NL
Substantially
Marine protected areas - Federal protected area agencies
Number of protected areas with management plans in place
Government
Organization
Number/
Total percent
Percent
PCA
Included in Terrestrial protected areas
Included in Terrestrial protected areas
EC
Included in Terrestrial protected areas
Included in Terrestrial protected areas
MBO
6/8
75 %
Marine protected areas - Federal protected area agencies
Number of protected areas with management plans less than 10 years old Extent that management
Government
Organization
Number/
Total percent
Percent
PCA
Included in Terrestrial protected areas
Included in Terrestrial protected areas
EC
Included in Terrestrial protected areas
Included in Terrestrial protected areas
MBO
6/8
75 %
Marine protected areas - Federal protected area agencies
Government
Organization
Extent that management actions are being implemented
BC
Included in Terrestrial protected areas
AB
Included in Terrestrial protected areas
SK
Substantially

Managing For Ecological Integrity

Increasingly, Canadian organizations are adopting ecological integrity as a foundation for protected area management, with most organizations (13 of 16 terrestrial and 4 of 9 marine) reporting the concept incorporated within their operating principles. However, about one third of protected area organizations report measures in place to monitor ecological integrity, and about one half report having measures in place to manage for ecological integrity. These statistics indicate that although there has been some improvement since the last reporting period, a gap persists between intention and reality.

Parks Canada Agency: A Leader In Managing For Ecological Integrity

The expert Panel on Ecological Integrity released its report in 2000 entitled Unimpaired for Future Generations? Conserving Ecological Integrity in Canada's National Parks (Parks Canada Agency,2000a), and PCA continues to work to implement its recommendations. For example:

Ecological Integrity In Canada's Network Of Marine Protected Areas

A living guidance and best practices document is being developed to guide MPA network planning in Canada's oceans and Great Lakes.

The document adopts internationally recognized network design properties with the aim of enhancing the network's overall ecological integrity and coherence.

For example, having a well-connected network made up of adequate and viable MPAs ensures that MPAs have the size, spacing and management needed to maintain the ecological integrity of the feature(s) for which they were selected, and of the marine environment overall.

Table 12. Extent of monitoring of ecological integrity

Terrestrial
Marine
  • Full monitoring at all protected areas:
    • PCA, AAFC
  • Full monitoring at all protected areas:
    • PCA
  • Some monitoring at most proptected areas:
    • YT
  • Some monitoring at most proptected areas:
    • -
  • Some monitoring at some protected areas:
    • EC, SK, QC
  • Some monitoring at some protected areas:
    • EC, DFO
  • Sporadic monitoring:
    • NT, BC, ON,NB, NS, NL
  • Sporadic monitoring:
    • BC, QC, NL
  • Little or no monitoring:
    • NU, AB, MB, PE
  • Little or no monitoring:
    • MB,NB
  • Not applicable:
    • -
  • Not applicable:
    • PE

Table 13. Measures are in place to manage ecological integrity

Terrestrial
Marine
  • Yes:
    • PCA, AAFC
  • Yes:
    • PCA
  • Partially:
    • YT, BC, SK, MB, ON,NB, NS
  • Partially:
    • BC, MB
  • In development:
    • None
  • In development:
    • -
  • No:
    • EC, NT, NU, AB, QC, PE, NL
  • No:
    • DFO, EC, QC,NB, NL
  • Not applicable:
    • PE
  • Not applicable:
    • -

Threats To Canada's Protected Area

Most organizations conduct some assessment of principal threats, and report "incompatible use outside of protected areas" and "climate change" as the most serious threats to the ecological integrity of terrestrial protected areas. It was more difficult to pinpoint the most serious threats for MPAs.Table Footnote18

Table 14. Principal threats to Canada's terrestrial protected areas

Principal threats 2000-2005
Principal threats 2006-2011
  1. Incompatible land uses adjacent to protected areas
  2. Habitat fragmentation
  3. Invasive species
  4. Increasing visitor use
  1. Climate change
  2. Cumulative impacts
  3. Incompatible land uses adjacent to protected areas
  4. Population declines
  5. Invasive species

The State Of Climate Change Adaptation In Canada's Protected Areas Sector (From Lemieux et al., 2011)

"Although there is much uncertainty about the timing, extent, and manner in which ecosystems and other protected areas assets (e.g., recreational opportunities) might respond to evolving climatic conditions, it is critically important that natural asset management agencies begin to identify, assess, and implement adaptation options that could reduce the vulnerability of Canada's protected areas (and their constituent biodiversity) to climate change... Considering the short-term projections of species turnover and loss resulting from climate change, the potential for non- linear ecological responses (in other words, ecological surprises), the length of time required for species and ecosystem response to management interventions, and the relatively slow process of implementing new policies within protected areas agencies, the time to begin developing proactive and integrative climate change adaptation strategies is now."

Table 15. Organizational characterization of terrestrial threat management

Threats: 1. Climate change

Examples of management measures
Factors affecting capacity to manage

Designation of additional protected areas; securing land for connecting corridors; ecological monitoring; guidance on sea-level rise; planting of tree species better adapted to anticipated conditions

Lack of knowledge, land use competition makes designation and securing corridors difficult; outdated management plans; lack of capacity and funding for research and management; management priority focused on more immediate threats; climate change acceleration

Threats: 2. Cumulative impacts

Examples of management measures
Factors affecting capacity to manage

Permits and management guidelines for activities in/ near protected areas; integrated land use planning; environmental impact/review processes

Outdated management plans; lack of capacity and funding to monitor permits and contribute to planning and review processes; lack of knowledge and experience

Threats: 3. Incompatible uses adjacent to protected areas

Examples of management measures
Factors affecting capacity to manage

Establishment of larger protected areas to buffer impacts; partnerships to acquire private lands; permits for activities in/near protected areas; monitoring, communication and outreach with surrounding users; voluntary stewardship agreements; planning (zoning); integrated land use planning; environmental review process

Limited land availability or simple mechanism or funding to acquire buffers; lack of influence on external land uses; sharing of legislative responsibilities between government authorities; limited capacity to monitor permits or contribute to planning and review processes

Threats: 4. Population declines

Examples of management measures
Factors affecting capacity to manage

Designation of additional protected areas; medical interventions to address disease; habitat inventory; population monitoring; visitor access controls

Lack of staff time and funding; conflicts between industry and conservation interests; external conditions beyond control of protected area staff; lack of visitor cooperation

Threats: 5. Invasive species

Examples of management measures
Factors affecting capacity to manage

Management guidelines restricting introductions; mitigative measures added to permits; control measures to kill them and prevent spreading (physical removal, prescribed burning, pesticides, use of other living organisms); partnerships with other departments or jurisdictions directly responsible for invasive species

Extent of issue largely unknown; biology and demographics of invasive species; lack of capacity and funding to conduct research and enforce permits, monitor establishment, and implement controls, develop partnerships; limited technical capacity to monitor and deal with invasive species; expense and difficulty of access to invasive species

Management Challenges In Canada's Protected Areas: Some Examples From 2006-2011

Although these threats are significant, organizations are implementing measures to address some of them. The main factors affecting capacity to manage threats include lack of influence on land uses and activities beyond protected area borders, lack of capacity and funding, and inadequate scientific understanding of an issue or the technical capacity to deal with it. For each of the top five issues, examples of management measures and factors affecting capacity to manage are presented in Table 15.

Some specific examples of management challenges in Canada's protected areas during the reporting period 2006-2011 are described above.

Science And Research In Support Of Protected Areas Management

Overall, terrestrial and marine organizations rated the availability and quality of scientific and other information in support of protected areas management as "limited to good." Table Footnote19

Organizations reported that the most readily available and highest quality information pertains to "adjacent (human) land use activities" and "natural resource inventories," with about three quarters of terrestrial organizations rating the availability and quality of these resources as "good" or "excellent." In addition to these types of information, marine organizations rated as "high" the availability and quality of information on community structure and function.

"It is now clear that science must and can play a fundamental role in maintaining ecological integrity."

-Parks Canada Agency, 2000b

Improving Knowledge For Management Decisions: A Sample Of Projects 2006-2011

Trends In Funding For Protected Areas

Terrestrial organizations in Canada spent on average about $6.00 per ha per year on protected areas, down from about $22.00 in 2005, although expenditures for individual organizations range from less than a dollar per ha to almost $30.00. Financial resources for Fisheries and Oceans Canada's MPA programs amount to roughly 1% of the amount spent on terrestrial protected areas programs.

"Doing Less With  Less":  The Impact Of Budget Shorthfalls On Fulfilling The Parks Mandate In Ontario

Excerpt from a case study featured in Doing Less with Less: How shortfalls in budget, staffing and in-house expertise are hampering the effectiveness of Ontario Ministry of the Environment and Ontario Ministry of Natural Resources (Office of the Environmental Commissioner of Ontario, 2007)

"The public has a strong and emotional connection to Ontario's parks, conservation reserves and wilderness areas; even those residents that aren't regular park visitors expect the system (of both operating and non-operating parks) to be protected and properly maintained. Unfortunately, the parks system has been underfunded for many years, to the point where the ministry has not been able to meet its legislated responsibilities, or to provide adequate services to the public. [Ministry of Natural Resources (MNR)] does not have the capacity to manage the system, which is growing in size and complexity. Over the past few years, the number and area of protected areas has grown substantially, and new parks legislation has added a new scientific mandate and more rigorous requirements. At the same time, the amount of money allocated from general revenues to protected areas has been cut repeatedly. While park revenues have increased, they have not been sufficient to offset the combination of severe cuts in government funding, the dramatic growth of the parks system and the expanded responsibilities of MNR."

For more information, see PDF file.

Management Effectiveness Evaluation

Less than half of Canada's protected area organizations evaluate management effectiveness. Seven terrestrial and four marine organizations employ a wide range of approaches to management effectiveness evaluation.

Management Effectiveness In Protected Areas

"Protected areas will only be able to significantly contribute to biodiversity conservation if they are managed effectively. Standardised repeat assessments of management effectiveness have become a powerful tool to support adaptive and effective management of protected areas over time. They help to ensure that protected areas meet their conservation objectives and deliver the desired conservation outcomes."

-World Conservation Monitoring Centre

What Is Management Effectiveness Evaluation?

The IUCN defines management effectiveness evaluation as the assessment of how well protected areas are being managed-primarily the extent to which management is protecting values and achieving goals and objectives.

The term management effectiveness reflects three main "themes" in protected area management:

-Hockings et al., 2006 (retrieved August, 2013). For more information, see PDF file.

International Efforts On Protected Area Management Effectiveness Evaluation

The IUCN World Commission for Protected Areas released the second edition of a framework for management effectiveness (Hockings et al., 2006) to provide a consistent basis for designing assessment systems, provide guidance about what to assess and broad criteria for assessment. Based on this Framework, different systems that apply a range of evaluation 'tools' can be used to conduct evaluations at different scales and depths.

For more information, see PDF file.

The global study into management effectiveness evaluation (Leverington et al., 2010) was conducted between late 2005 and 2010. The study aimed to strengthen the management of protected areas by compiling the existing work on management effectiveness evaluation, review and summarize methodologies, find patterns and common themes in evaluation results, and investigate the most important factors leading to effective management.

Programme of Work on Protected Areas Target 1.4 states that all IUCN protected areas should have effective management by 2012. Decision X/31.19 invites Parties to "continue to expand and institutionalize management effectiveness assessments to work towards assessing 60 per cent of the total area of protected areas by 2015 using various national and regional tools and report the results into the global database on management effectiveness maintained by the World Conservation Monitoring Centre".

For more information, see Leverington et al., 2010 (Management effectiveness evaluation in protected areas-a global study).

State Of Protected Areas Reporting

About half of protected area organizations - 8 of 16 terrestrial organizations and 5 of 9 marine organizations-confirm that they assess and report on the state of their protected areas on a systematic basis either alone or more broadly through state of the environment reporting.

At the present time, eight protected area organizations (PCA, AAFC, BC, SK, MB, ON, QC and PE) implement measures in order to report on a regular basis on the state of their protected areas reporting. For all of these organizations except Agriculture and Agri-Food Canada, BC and MB such reporting is entrenched in legislation. For EC and YT, measures to require protected areas reporting are sporadic. This compares to only three organizations that legislated such reporting in 2005. On the marine side, Parks Canada Agency, Fisheries and Oceans Canada, British Columbia, Manitoba and Quebec report on the state of their protected areas, with all but Manitoba complying with a legislative or policy requirement to do so.

Nunavut's ongoing legislative review recommends that state of parks reporting be included in the new Territorial Parks Act. British Columbia is in the process of developing a more comprehensive annual report that would feature information from the long-term ecological monitoring framework, and the threat assessments in the B.C. Parks Conservation Risk Assessment would provide information to assess and report on the state of protected areas. British Columbia is in the process of developing a more comprehensive annual report that would feature this type of information.

Within Fisheries and Oceans Canada bioregions, Marine Protected Area Advisory Committees share progress reports with the broader stakeholder community, and review annual work plans and performance reports.

Assessments Of Benefits Of Protected Areas

In addition to biodiversity conservation, organizations increasingly promote protected areas for their benefits to local, regional and national economies, cultural heritage conservation, human health and well-being, climate change adaptation and mitigation, clean water and other ecological services, and scientific research and education. A number of studies during 2006-2011 highlight the specific value of protected areas for a range of benefits.

Economic impact studies conducted on Canada's national, provincial and territorial protected areas concluded that they are vital contributors to tourism and the economy. Spending by governments and by the visitors that come to protected areas has a substantial and recurring impact, producing tax revenue for governments, creating jobs, and generating income for local businesses, particularly in rural and remote areas of Canada (CPC, 2011b). A study of Prairie Farm Rehabilitation Area-managed community pastures revealed annual benefits of almost $55 million (Kulshreshtha et al., 2008) (Table 16).

Race Rocks Ecological Reserve: Education And Research On The Local And Global Levels

Race Rocks Ecological Reserve was established in 1980 under British Columbia's Ecological Reserve Act. Located in the strong tidal currents of Juan de Fuca Strait, the rocks lie where nutrient-rich coastal waters mix with oceanic influences. The site is unique in rarity, abundance and diversity of benthic invertebrates and reef fish, and is a meeting and breeding place for marine mammals and seabirds.

MPA status has focused government and public attention to protect nature through access management, best practices for allowable activities and harvest restrictions. Local tourism and marine educators visit Race Rocks to provide their clients with direct observations of nature. Ecological and geophysical scientists have conducted research in the reserve. Restricted access for harvesting and time- series environmental data has established Race Rocks as an ecological benchmark site.

In addition, Race Rocks Ecological Reserve is virtually accessible to the world over the Internet. Interactive cameras and webcasts both on land and underwater provide education and research opportunities for people around the globe.

For more information, see Race rocks site.

Table 16 : Studies/literature reviews of protected areas benefits from 2006 to 2011

The Economic Impact of Canada's National, Provincial and Territorial Parks in 2009 (CPC, 2011b)

Spending associated with national, provincial and territorial parks in 2009:

  • Added $4.6 billion to Canada's Gross Domestic Product;
  • Generated $2.9 billion in labour income (the equivalent of over 64 000 full time jobs); and
  • Provided $337.1 million in tax revenue to governments.

For more information, see PDF file.

Economic Impact of Parks Canada (The Outspan Group Inc., 2011)

Spending associated with National Parks, National Historic Sites and National Marine Conservation areas in 2008-2009:

  • Added $3.0 billion to Canada's Gross Domestic Product;
  • Generated $1.9 billion in labour income; and
  • Provided $217.9 million in tax revenue to governments.

For more information, see Parks Canada -Economic Impact.

Distribution of Public and Private Benefits on Federally Managed Community Pastures in Canada (Kulshreshthaet al., 2008)

For all the Prairie Farm Rehabilitation Administration-managed community pastures, annual benefits to society (including patrons of the community pastures) are estimated at $54.9 million, yielding a ratioof benefits to costs of 2.5 to 1.

For more information, see PDF file.

Marine Protected Areas and MPA Networks: The Benefits and Costs to the Fishing Industry (Draft) (Fisheries and Oceans Canada, 2010)

The following benefits to fish harvesters of MPA establishment have been well documented in the scientific literature:

  • increased size, abundance and diversity of fish (including other marine organisms);
  • stability for fish harvesters through replenishment of stocks;
  • protection of marine habitats and biophysical processes;
  • improved ecological resilience to resist or recover from disturbances;
  • fostered sustainable tourism including activities such as recreational fishing, scuba diving and kayaking;
  • buffering of coastal communities from storm impacts; and
  • protection of spiritual or cultural heritage value such as archaeological sites, shipwrecks and traditional use areas.

For more information, see PDF file.

Human health and well-being motivations and benefits associated with protected area experiences: an opportunity for transforming policy and management in Canada (Lemieux et al., 2012)

The perceived benefits received from the experiences were substantial. Visiting protected areas can be considered a highly positive life experience, and the greatest well-being benefits were perceived tobe psychological/emotional, social, cultural and environmental.

Visitation to parks was perceived to have important benefits for child development, especially in terms of physical development, social knowledge and competency, and cognitive learning and language.

For more information, see PDF file.

"My Head Is Breathing Out Here"

Alberta reports that persons with disabilities have expressed an increase in self-confidence and a positive sense of interdependence through programs such as "Push to Open Nature." Canmore Nordic Centre Provincial Park has identified benefits to athletes who train in a natural setting versus a more urban setting. New Canadian participants in a "Nature as a Second Language" program have recognized that their experiences in parks helped them relax and feel more welcome in their new homeland. One participant commented: "I feel like my head is breathing out here."

Aboriginal Participation In Protected Area Management

Almost all of Canada's protected area organizations are pursuing forms of Aboriginal cooperative management, particularly in the northern territories and in provinces that have vast and remote northern areas.

Quebec Partnership With Indigenous People For The Development And Management Of Northern Parks

A necessary adaptation to respect differences

The Quebec government recognizes the rights of indigenous people on territory covered by agreements, treaties and conventions. National (provincial) Parks that are located on the territory covered by the Convention of the James Bay and Northern Quebec Agreement (JBNQA) give beneficiaries certain rights, ensuring the Inuit and Cree can continue traditional activities such as hunting, fishing, trapping and establishment of camps. This facilitates the acceptance of park projects as they do not interfere with the rights of indigenous peoples.

Within the territories under the JBNQA in Quebec, parks not only protect a territory, but they help to preserve traditional activities while at the same time sharing this way of life with visitors.

Shared vision with partners in Aboriginal communities

The Quebec government ensures the involvement of the community by entrusting the operation of parks to the Kativik Regional Government (KRG) and the corresponding Cree community for each park in the area covered by the JBNQA.

Today, Pingualuit National Park (established in 2004) and the National Park Kuururjuaq (created in 2009) are operated by the KRG, and many employees come from host villages. There are 6 permanent and several part-time jobs that are generated within each of the national parks, and a team of 10 administrative employees. Local knowledge is emphasized in the activities and services offered in these parks.

The proposed national park Tursujuq is the result of a concerted effort between the Government of Quebec, the Inuit and the Cree, who participated in all stages of park planning. Community support and understanding of the local context are being sought. Respect for cultures, protection of natural heritage park, and employment and training are under discussion.

Collaborative Opportunities Associated With Protected Areas 2006-2011

From case studies featured in
Aboriginal Peoples and Canada's Parks and Protected Areas
(Canadian Parks Council, 2011)

Katannilik Park Knowledge Camp: With 60% of its population under the age of 25, Nunavut is by far the "youngest" province or territory in Canada. Both challenges and opportunities exist in developing programs and activities for youth, particularly in smaller communities. Nunavut Parks has developed a "Knowledge Camp" for Katannilik Territorial Park, to establish connections between youth and Elders, and extend traditional knowledge and skills through generations. Opportunities to develop similar camps in other territorial parks in Nunavut are being explored. For more information, see PDF file.

Grizzly Bear Viewing in Ni'iinlii'Njik (Fishing Branch)-A cooperative Eco-Tourism Venture with the Vuntut Gwitchin First Nation, Vuntut Development Corporation, Yukon Parks and Bear Cave Mountain Eco-Adventures: The case study of Ni'iinlii'Njik illustrates the positive role that land claims can have in conservation and the effectiveness of partnership in management especially as it relates to the developing of a new, highly specialized activity within the eco-tourism industry. With effectively managed viewing opportunities, public appreciation of grizzly bears and bear ecology may increase, tourism activity could provide economic benefits, while at the same time protecting the bears and their habitat. For more information, see PDF file.

Tsleil Waututh Nation and BC Parks-Collaborative Management of Say Nuth Khaw YumHeritage Park/Indian Arm Provincial Park: A collaborative management agreement signed between the Tsleil-Waututh Nation and the Province of British Columbia forms the foundation of a relationship that has brought both parties forward in a spirit of cooperation and mutual respect. Under the agreement, both the Tsleil-Waututh Nation and the province (represented by BC Parks) are active participants in the planning, management and operations of the park. In September 2006, the Tsleil-Waututh Nation and B.C. Parks celebrated the completion of the Bioregional Inventory Atlas and the end of Phase 1. The second stage of the planning process is currently focused on drafting the Park Management Plan. For more information, see PDF file.

AkKutiliuk-Making a Path: Torngat Mountains National Park Reserve of Canada: During the summer of 2006, the first official operating season for this park, Parks Canada Agency organized a base camp on Shuldham Island in Saglek Bay at the southern entrance to the Park Reserve. One of the objectives of the base camp, which was managed by Inuit from Nain, was to explore ways to maximize the presence of Inuit in the park and to ensure the participation of Inuit in park management by merging agendas and objectives of Parks Canada Agency and Inuit as the first step to a productive and long-term cooperative management relationship. For more information, see PDF file.

Local Communities And Protected Areas Management

Most organizations continue to work with communities on management decisions concerning their local protected areas.

Local Community Participation In ProtectedArea Management Decisions-Organizational Comments

Nunavut: "In the past, park establishment and management stakeholders have involved community committees adjacent to the parks including representatives from the Hamlet, Tourism Associations, Hunters and Trappers Associations, Elders and Youth, Heritage Societies, and Community Land and Resource Committees."

Alberta: "An online consultation and notification process called 'Involving Albertans' was developed in 2009 to provide further opportunities to provide feedback and input into management decisions of all types... Opportunities for public involvement are provided on designation of new parks or addition of lands to existing parks, boundary amendments, facility development and park management. Locally held consultation mechanisms such as open houses, information sessions or public/stakeholder meetings are also used wherever warranted."

Manitoba: "Community participation in management decisions varies by site... Local communities with Resource Co-Management Boards participate in protected area management decisions for sites falling within their Resource Management Areas (RMAs). The Resource Co-Management Boards review and provide recommendations on all proposed activities within the RMA, which includes those protected areas located within the RMA. The boards are made up of members from the First Nation and the Government of Manitoba."

Footnotes

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2017-09-10