Cumulative access in Canada’s forest ecozones By: Peter Lee, Matthew Hanneman, Jeannette Gysbers, and Ryan Cheng This is the second of several publicatons in celebration of Global Forest Watch Canada’s 10th anniversay year and in celebration of the International Year of Biodiversity. It summarizes the results of several years of mapping anthropogenic disturbances as seen by Landsat satellite imagery. This bulletin accompanies Global Forest Watch Canada’s (GFWC) geospatial dataset (Canada Access – Combined) and high resolution maps in PNG, TIFF and JPEG formats which are available at http://www.globalforestwatch.ca/datawarehouse/datawarehouse.htm and http://www.globalforestwatch.ca, respectively. _________________________________________________________________________________________ What is Cumulative Access? How was the Cumulative Access dataset created? Cumulative access is the combined land surface anthropogenic disturbances caused mainly by industrial activities, which include, but are not limited to, roads, mines, clearcuts, wellsites, pipelines, transmission lines, and agricultural clearings. GFWC’s Cumulative Access dataset is a by-product of our work on another GFWC project, Canada’s Intact Forest Landscapes. In order to map Canada’s intact forest landscapes, GFWC first mapped all anthropogenic disturbances as Global Forest Watch Canada (GFWC) has analyzed the already mapped in readily available and reliable existing extent to which Canada’s forest ecozones have been datasets (especially roads datasets) and as seen on Landimpacted by significant human activities. GFWC’s cumu- sat images. All resulting features were mapped as either lative access layer was compiled primarily by analyzing linear or polygon features. Then, using Geographic InLandsat (TM and ETM) satellite images for the period formation Systems software, GFWC applied buffers to 1988 to 2006. these disturbance datasets. A zone of influence of 500 metres was applied to local roads (i.e. subdivision roads in a city or gravel roads in rural areas), airports, mines, pipelines, powerlines, reservoirs, and clearcuts. A zone ________________________________________________________________________________________ Citation: Lee PG, Hanneman M, Gysbers JD, Cheng R. 2010. Cumulative access in Canada’s forest ecozones. Edmonton, Alberta: Global Forest Watch Canada 10th Anniversary Publication #2. 7 pp. Available at: www.globalforestwatch.ca. 1 of influence of 1,000 metres was applied to the TransCanada Highway and other principal roads. The width of the zone of influence was considered conservative, given that many studies have shown that the effects of disturbance greatly exceed 1,000 metres for birds, predators, and ungulates, as well as smaller wildlife. For example, one Ontario government study on wildlife areas used 5- and 10-kilometre buffers. Applying these buffers also helped to mask errors related to orthorectification problems with Landsat satellite imagery. Although this Cumulative Access dataset was not specifically developed as a stand-alone dataset, GFWC is making it available due to increasing requests by government agencies and academics and due to its apparent usefulness for some kinds of analysis (e.g., see: A. Schindler, D.W. Comprehensive conservation planning to protect biodiversity and ecosystem services in Canadian boreal regions under a warming climate and increasing exploitation. Biol. Conserv. (2010), doi:10.1016/j.biocon.2010.04.003; B. Environment Canada. 2008. Scientific Review for the Identification of Critical Habitat for Woodland Caribou (Rangifer tarandus caribou), Boreal Population, in Canada. August 2008. Ottawa: Environment Canada. 72 pp. plus 180 pp Appendices.) The resulting layers of buffered features were combined to create an anthropogenic disturbance layer. These areas were then removed from further consideration as intact forest landscapes. Additionally, residual areas smaller than 5,000 hectares for the boreal/taiga ecozones and smaller than 1,000 hectares for the temperate forest ecozones were removed according to the threshold sizes selected. What are some of the limitations of the Cumulative Access dataset? GFWC recommends that users of the dataset become familiar with its creation and resulting limitations for various desired uses. GFWC notes that there are several limitations, including: • The anthropogenic disturbances were mapped from Landsat images of a variety of dates, although the general period of consistency is in the 1999-2002 range. • Landsat images are considered to be medium resolution, therefore fine-scale anthropogenic disturbances were not detected and mapped. • The 1,000 metre (for primary highways) and 500 metre (for all other anthropogenic disturbances) buffering that was applied to all linear and polygonal features results in a coarse-level dataset that may not be appropriate for some analysis. • Areas shown as having no cumulative access and that are smaller than 5,000 ha for the boreal/taiga ecozones and smaller than 1,000 ha for temperate forest ecozones may in fact contain cumulative access. These smaller areas may have been missed in the mapping as they were not the focus of the original intact forest landscape mapping project. Further details of the methodology are contained within GFWC’s publication: Lee P, JD Gysbers, and Stanojevic Z. 2006. Canada’s Forest Landscape Fragments: A First Approximation (A Global Forest Watch Canada Report). Edmonton, Alberta: Global Forest Watch Canada. 97 pp. (Available at: http://www.globalforestwatch.ca/FLFs/download.htm). Why is GFWC making this by-product dataset available? GFWC’s policy is to make geospatial datasets readily and publicly available, and where reasonable, free-of-charge. Reasons for this policy include: • To encourage others, particularly in governments and industry, to do the same. • To be transparent and to enhance credibility of GFWC products by allowing others to use and comment on our datasets. • To encourage others to conduct additional and new analysis, using GFWC’s datasets, in order to improve Canada’s sustainable forest management decisions. 2 Maps of Cumulative Access British Columbia, Ontario and Québec – contain almost 77% of Canada’s accessed forest ecozone area. The map, Cumulative Anthropogenic Access in Canada’s Forest Ecozones, provides a national picture of the cumulative extent of industrial access within Canada’s forest ecozones. The map, Watersheds of Canada Forest Ecozones by Percent Accessed, provides a national picture of the cumulative extent of industrial access within Canada’s watersheds. The map, Ecosdistricts of Canada Forest Ecozones by Percent Accessed, provides a national picture of the cumulative extent of industrial access within Canada’s ecodistricts. Table 1 presents the area and percentage results of access by forest ecozone as well as nationally. The results indicate that just over 21 percent of the total area of Canada’s forest ecozones is accessed. From a regional perspective, the most accessed are the eastern Atlantic Maritime and the Mixed Wood ecozones, with each being more than 75% accessed. The Boreal Plains and the Montane Cordillera ecozones are also significantly accessed at 45% and 40%, respectively. The most northern and remote forest ecozones (the Boreal Cordillera, the Taiga Shield, the Taiga Cordillera and the Hudson Plains) each have less than 5% cumulative access. Table 2 provides statistics on the percentage of accessed forest ecozone by Province. Four jurisdictions – Alberta, The three maritime provinces (New Brunswick, Prince Edward Island and Nova Scotia) each have over 70% of their forest ecozones accessed. Alberta is the fourth most accessed province at 47%. Six jurisdictions – British Columbia, Ontario, Québec, Saskatchewan, Newfoundland and Labrador, and Manitoba – each have between 10% and 33% of their forest ecozone area accessed. The Northwest Territories, Yukon and Nunavut each have less than 5% of their forest areas accessed. Table 1. Cumulative access by forest ecozone. Province/Territory Area Accessed Province Area 76.4 Boreal Cordillera 2,236,683 47,071,039 4.8 Boreal Plain 33,355,347 74,062,933 45 Boreal Shield 45,948,003 188,640,692 24.4 600,800 37,565,744 1.6 Mixed Wood Plains Hudson Plains 8,536,603 11,339,105 75.3 Montane Cordillera 19,811,286 48,975,931 40.5 5,689,362 20,873,620 27.3 Pacific Maritime 499,065 26,695,320 1.9 Taiga Plains Taiga Cordillera 9,620,222 65,773,771 14.6 Taiga Shield 3,915,278 139,314,737 2.8 % Accessed Alberta 23,837,235 50,672,649 47 31,385,860 94,709,033 33.1 5,909,506 57,883,340 10.2 New Brunswick 5,911,681 7,299,874 81 Newfoundland and Labrador 4,512,746 39,022,812 11.6 Northwest Territories 4,243,873 95,539,825 4.4 Nova Scotia 3,948,814 5,562,603 71 Nunavut Ontario Prince Edward Island 1,258 10,786,309 0 25,727,265 98,953,976 26 437,852 593,012 73.8 30,875,057 130,430,760 23.7 Saskatchewan 6,730,055 41,158,212 16.4 Yukon 2,090,600 47,851,969 4.4 145,611,802 680,464,374 21.4 Quebec Total % Accessed 20,151,483 British Columbia Manitoba Ecozone Area 15,399,153 Table 2. Cumulative access in forest ecozones by jurisdiction. Province/Territory Area Accessed Atlantic Maritime 3 Reviews of Cumulative Access Dataset A key principle of Global Forest Watch Canada is that transparency and accountability are essential for developing improved forest management. In the interest of promoting open, public, and transparent information policies, most Global Forest Watch Canada projects include a review process and the publication of a summary of the major comments provided by the reviewers, including how these comments were addressed. Resulting from these various direct and indirest reviews were a few important comments: Categorization -- The dataset would be much more useful if the anthropogenic disturbances were categorized (e.g., cutblock, mine site, agricultural clearing, road, pipeline, seismic line). GFWC agrees with this comment. However, that was not the purpose of its derivation and compilation. This dataset was handled differently than most of our reviewed products in that it was not specifically developed as a stand-alone dataset. It was developed as a byproduct of our Intact Forest Landscape mapping. The Cumulative Access dataset is somewhat of the inverse of the Intact Forest Landscape dataset. Time-stamp -- The dataset should have been timestamped so that changes over time could be monitored. The various draft iterations of the Intact Forest Landscape datasets were sent out by invitation to academic experts as well as to representatives from government, industry, ENGOs, and First Nations groups. In total, the various iterations were sent to hundreds of experts and stakeholders. Over 50 reviewers responded with comments. Buffering by 500 and 1,000 metres -- The dataset would be more useful if it was not buffered by 500 metres. There were two other reviews for the Cumulative Access dataset that were more direct. For examples: • A. Schindler, D.W. Comprehensive conservation planning to protect biodiversity and ecosystem services in Canadian boreal regions under a warming climate and increasing exploitation. Biol. Conserv. (2010), doi:10.1016/j.biocon.2010.04.003. The Cumulative Access dataset was published in this paper. • Environment Canada. 2008. Scientific Review for the Identification of Critical Habitat for Woodland Caribou (Rangifer tarandus caribou), Boreal Population, in Canada. August 2008. Ottawa: Environment Canada. 72 pp. plus 180 pp Appendices. The Cumulative Access dataset was used to establish the correlation between woodland caribou herd health and levels of anthorpogenic disturabnces within herd ranges. The dataset used hundreds of Landsat images over many years. The vast majority of the dataset does generally date from the 1999-2001 period, with some regional areas uo to 2006. GFWC agrees with this comment. However, the buffering was applied as some of the compiled sub-datasets were from the early 2000s and used many Landsat images that were not orthorectified to a high level of geographic positioning accuracy. Buffering by 500 metres for most distruabnces and 1,000 for p[rimary highways masked many of these problems. Name of Dataset -- Use of the word “access” in cumulative access is not appropriate. Should be termed “disturbance” as several of your items are not related to access per se (clearcuts, mines. Etc) Although the title of the dataset may be problematic for some, we did not want to use the word “disturbance” as it is problematic for others, based on earlier consultations. The rationale for using “access” was to provide an appropriate decriptor of the human, mainly industrial, disutrbances of the landscape that could be seen in medium-resolution satellite (i.e., Landsat), soe of which are long term distruabnces, such as in the case of paved roads, and some of which are mostly temporary, such as in the case of many cutblocks. The word “access” to GFWC implies both these ephemeral and more permanent areas of the landscape that have a visible human footprint. Who is Global Forest Watch Canada? Global Forest Watch Canada (GFWC) is an organization whose role is to support the stewardship and conservation of Canada’s remaining forests, by providing decision makers and civil society with timely, accurate information on their location, state, and change. In particular, this mission includes monitoring development activities occurring within and around Canada’s forests, which influence the current and future conditions of these ecosystems as well as the people who live within them. We contribute to a shift toward greater ecological sustainability in the management of natural areas by creating a compelling visual picture and analysis of current conditions, historical changes and future trends. Our vision is that Canada’s forests will be increasingly well-managed through better information that supports improved decision-making and, thereby, will provide a full range of benefits for both present and future generations. Global Forest Watch Canada provides access to more complete information about development activities in Canada’s forests and their environmental impacts. We are convinced that providing greater information about Canada’s forests will lead to better decision-making on forest management and use, which ultimately will result in forest management regimes that provide a full range of benefits for both present and future generations. Find out more/contact us: Website: www.globalforestwatch.ca Email: info@globalforestwatch.ca Phone: 780-422-5989 Mailing Address: 10337 146 St, Edmonton AB T5N 3A3