Land-Use References

Year Title (Author, Description) File Download
2005

Integrated Landscape Management Tools for Sustainable Development Policy Making

Policy Research Initiative

Sustainable Development Briefing Note

Contact ALCES for Policy Research Initiative, 2005
2010

Integrated Place-Based Approaches for Sustainable Development

The Policy Research Institute

Place-based approaches address social, environmental or economic issues and thus offer the promise of operationalizing Sustainable Development (SD) principles. By focusing attention on policy issues as they play out in concrete geographic and community settings, place-based approaches provide a means to grasp complex and sometimes unexpected connections. This issue of Horizons provides a sense of the diversity of place-based approaches as they are applied in different policy areas, and identifies some of the lessons learned from an SD perspective.

Contact ALCES for The Policy Research Institute, 2010
2008

Lake Simcoe Basin’s Natural Capital: The Value of the Watershed’s Ecosystem Services

Sara J. Wilson

This study quantifies the natural capital value of the ecosystem goods and services provided by Lake Simcoe’s watershed, a section of which is located in Ontario’s Greenbelt. At a minimum estimated worth of $975 million per year, the services provided by the watershed are worth $2,780 to each of the 350,000 permanent residents annually. This study represents the first application of this methodology to a watershed in southern Ontario. Goods and services provided by ecosystems are traditionally undervalued as they go unmeasured by conventional economics. These benefits include storage of floodwaters by wetlands, air pollution absorption, climate regulation, pollination of crops and water filtration, resulting in clean air and water and safe and abundant local food sources. In order to measure the value of these benefits, this study first describes the watershed’s natural assets – that is, the extent of the forests, wetlands, grasslands, water bodies, agricultural lands and urban or built-up areas. Then, using market-determined values (e.g. the avoided increased costs of a man-made water filtration service as a proxy for the existing capabilities of a natural system to filter water), the study was able to quantify many of the goods and services that are provided by the watershed.

Contact ALCES for Sara J. Wilson, 2008
2003

Land Advocate: News for Canadians living with oil and gas production

Andrew Nikiforuk

A democratic voice for landowners and the land. An advocate for more 100,000 farmers, ranchers and landowners in Saskatchewan, Alberta and British Columbia. We'll separate the oil from the gas to give you the best and most informed perspective on what's right and what's wrong in the oil patch.

Contact ALCES for Andrew Nikiforuk, 2003
2012

Land and Water Impacts of Oil Sands Production in Alberta

Sarah Jordaan

Review of the Land and Water Impacts of Oil Sands Productions in Alberta

Contact ALCES for Sarah Jordaan, 2012
1999

Leverage Points: Places to intervene in a system

Donella H. Meadows

What you are about to read is a work in progress. It's not a simple, sure-fire recipe for finding leverage points. Rather, it's an invitation to think more broadly about the many ways there might be to get systems to change.

Contact ALCES for Donella H. Meadows, 1999
2009

Literature Review of Selected Best Management Practices Specific to Agricultural Practices in Red-Assiniboine River Watersheds

Stephanie Melles

Contact ALCES for Stephanie Melles , 2009
2013

Logging to Supply Timber vs. Logging to Supply Water Is there a Difference?

Nigel Douglas

In all of the long-drawn-out, at times acrimonious disputes over logging in Alberta’s southern Eastern Slopes, one question has continued to baffle observers. Why has the Alberta government, despite all of the mounting opposition, been so determined to push ahead with logging these precious watersheds when the economic benefits are so minimal and the environmental costs so high? One possible answer to that question has been hinted at in recent comments from government spokesmen in the media. What if the government is indeed logging full speed to maximize resource extraction from the forest, but the primary focus is not on the production of timber, but on the production of water? If you have a tunnel-vision focus on managing forests to supply one thing – be it timber or water – then other things, including wildlife and recreation are likely to suffer. This seems to be the case in Alberta.

Contact ALCES for Nigel Douglas, 2013
2012

Mayatan Lake State of the Watershed Report

Melissa Logan, P.Biol., Billie Milholland, B.A., and David Trew, P.Biol.

The purpose of this report is to summarize all available environmental information for Mayatan Lake and its surrounding watershed. This report also provides a benchmark against which future stewardship activities and best management practices aimed at maintaining and improving watershed health can be assessed. The information will provide landowners, stakeholders, Parkland County and the Mayatan Lake Management Association (MLMA) with the information needed to support sound management decisions and develop solutions to protect or enhance land and water resources in the watershed. It also serves as a localized component and example of NSWA’s larger basin planning initiative, the Integrated Watershed Management Plan for the North Saskatchewan River Basin.

Contact ALCES for Melissa Logan, P.Biol., Billie Milholland, B.A., and David Trew, P.Biol., 2012
2008

Modeling Cumulative Effects in Barren-ground Caribou Range: Proceedings of a Workshop in Yellowknife

Jan Adamczewski, John Nishi, Anne Gunn, Terry Antoniuk, Chris Johnson, Don Russell, Ted Blondin, All

In the early 2000s, most herds of barren-ground caribou in the Northwest Territories (NWT) were declining. The declines aroused considerable concern in NWT communities because caribou have been a resource of great value to people in the north for many generations. Possible explanations for the declines include a natural cycle, variation in weather and forage conditions, predation, hunting, disease, and industrial development. Of these factors, some are beyond immediate control, but effects due to direct human influence, like hunting and development, can be managed. The impact of development on caribou is usually not due to single roads, mines, cut-blocks or seismic lines, rather it is the cumulative effects of many habitat alterations over time that affect caribou numbers and distribution. Concerns over effects of development on caribou have been raised in environmental assessments and particularly by aboriginal groups for many years, but progress on assessing them has been limited. To be objective, assessment of cumulative effects must account for other factors, including hunting and natural variation in weather. Due to the need for overall knowledge of a caribou herd‟s complex ecology in assessing cumulative effects, biologists have turned to computer models to help track multiple variables and relationships, and to look at “what if” simulations. While these models cannot predict the future, they can help users understand how various factors interact and what likely consequences of particular management decisions might be. In the 2006-2010 NWT Caribou Management Strategy, a commitment was made by the Government of the Northwest Territories to developing a modeling approach that could assess development in its proper context of natural variation. In this report we summarized the presentations and participant responses at a public workshop held in February 2008, Yellowknife, NWT, on modeling cumulative effects in the range of the Bathurst herd. In addition, we report on progress towards a demonstration project initiated at the February 2008 workshop.

Contact ALCES for Jan Adamczewski, John Nishi, Anne Gunn, Terry Antoniuk, Chris Johnson, Don Russell, Ted Blondin, All, 2008
2011

Modeling Rangeland Community Structure in ALCES Southern Alberta Sustainability Strategy (SASS)

Barry Adams and Brad Stelfox

Rangeland communities are not constant in structure (physiognomy), but change through time as they grow older, or when they are disturbed by various natural processes including fire, drought, and herbivory. Unlike forest communities, rangelands do not have to be reset to the youngest seral stage when they are affected by a natural disturbance. Instead, structural change varies depending on the intensity of the disturbance. The purpose of modeling rangeland in SASS is to simulate and compare rangeland structure under various future land use and development scenarios, and to use these results in modeling changes to wildlife habitat values. Modeling in SASS is at a regional scale and is over a 50-year time period. The study area is more or less comprised of the South Saskatchewan watershed, which is about 20% of the total area of Alberta.

Contact ALCES for Barry Adams and Brad Stelfox, 2011
2007

Modelling potential effects of angling on recovery of westslope cutthroat trout (Oncorhynchus clarkii lewisi) in Alberta

Michael Sullivan

Alberta’s native form of cutthroat trout, westslope cutthroat trout (Oncorhynchus clarkii lewisi), was listed in 2006 as a threatened species under the federal Species at Risk Act. Amongst other legal requirements, this action requires that an assessment of threats be conducted to determine what activities are acceptable and unacceptable with respect to the maintenance and recovery of populations of these fish. Sport angling for cutthroat trout and other species is a popular activity throughout this fish’s habitat in Alberta and has the potential to harm this species’ recovery. To investigate this potential harm, the possible effects of a variety of angling scenarios (e.g., different levels of angler effort and regulations) on stream populations of cutthroat trout were simulated using a population dynamics computer model. The results of these simulations suggested that recovery of depressed cutthroat trout populations could occur under scenarios of limited and low angler effort, and no directed harvest (i.e., catch-and-release angling). Once recovered, however, healthy populations of westslope cutthroat trout may be maintained with catch-and-release angling with moderate fishing effort. Angling regulations that allow harvest of cutthroat trout are unlikely to either maintain or recover most populations unless angler effort is controlled. Incidental mortality (either through accidental hooking mortality or illegal harvest through misidentification of trout species) in these simulations was an important factor in population maintenance and recovery. This suggests that minimizing these sources of mortality may be an important management concern for this species.

Contact ALCES for Michael Sullivan, 2007
2012

Models and Data: What are they saying about cumulative effects on wildlife species important to the community of Fort McKay

Lorne Gould

Wildlife is an integral part of the Fort McKay’s culture. Since the start of development (late 1960s) there has been a transformation of traditional lands from boreal forest and wetlands into oil sands development (open pit mines, in situ operations, and associated infrastructure). The environmental impact assessments (EIAs) prepared by oil sands operators and proponents repeatedly claim that these developments will have little impact on wildlife populations and their habitats because reclamation will return the land to a productive state. Fort McKay Community members are skeptical of future reclamation success and believe that development already has negatively impacted certain wildlife populations. The Fort McKay also has concerns about the project by project review process and the assessment of cumulative effects. This report provides brief summaries of studies that show cumulative effects on wildlife important to the Fort McKay. This report also presents wildlife data from EIAs and the findings of a recent study on wildlife habitat models used in the oil sands region. Four wildlife species; moose, beaver, fisher/marten, and Canada lynx are emphasized because of their cultural importance. The moose and beaver are considered Cultural Keystone species for the Fort McKay Community (Garibaldi 2006). Canada lynx, fisher, and marten are furbearers vital to the Fort McKay’s traditional economy. Fisher and marten are lumped together because of the difficultly in differentiating their snow tracks in the field. Sources of information for this report are as follows: 􀁸 Results of the Fort McKay Specific Assessment (FMSA); 􀁸 Results of modeling completed for the Lower Athabasca Regional Plan (LARP) and Terrestrial Ecosystem Management Framework (TEMF); 􀁸 Aerial surveys completed by the Alberta Sustainable Resource Development (ASRD); 􀁸 Wildlife data collected in the oil sands region in support of environmental impact assessments; 􀁸 Population viability analysis (PVA) modelling reports completed in the oil sands region; and 􀁸 Analysis of habitat models used in the oil sands region completed by CEMA. In 2011, 1.7 million barrels of bitumen were produced in the oil sands region of Alberta. This quantity is expected to reach 3.5 million barrels per day by 2020 (Alberta Government 2012). We summarize modeling results that predict impacts from oil sands development. We also provide information that shows how the present project by project EIA process is failing to assess cumulative effects on wildlife. We provide recommendations that will reduce impacts and allow for the future recovery of wildlife in the Fort McKay’s Traditional Territory.

Contact ALCES for Lorne Gould, 2012
2009

Moose Alces alces behaviour related to human activity

WIEBKE NEUMANN

The spatiotemporal dynamics of human activity requires a better understanding of the ecological effects on wildlife. This thesis focuses on the behavioural response of a harvested species, moose (Alces alces), to dynamic human activities e.g. hunting and recreation, and to static influences like roads, using experimental and descriptive approaches. Potentially lethal (hunting) and non-lethal (hiking, snowmobiling) activities provoked short-lived increases in moose movement activity and caused spatial displacement. The data suggests a uniform response towards unexpected disturbance and that moose are sensitive to human proximity. Hunting clearly provoked the strongest response. Moose approached by a hunting dog commonly fled, suggesting adjustments in anti-predator behaviour towards a nonnative predator. This may lead to predator facilitation where wolves and human predation co-exist, because the moose’s behavioural response towards one predator possibly increases the predation risk by the other. Unexpectedly, hiking and motordriven (snowmobiling) recreational activity caused a comparable change in moose behaviour. The short-lived response towards dynamic human activities indicates a rather minor impact on moose total energy budget from a single disturbance. Moose seldom crossed roads, but did increasingly so during migration. Roadcrossing sites were aggregated, suggesting well established travel routes and corridors for migratory moose. Moose did not cross roads more often during hunting season. In general, moose little utilized habitats in proximity to roads. Moose-vehicle collisions did not occur where and when moose most commonly cross roads. My results suggest a higher risk to human safety during times of poor visibility and close to urban areas, but not necessarily in the vicinity of forests. For wildlife subject to intensive harvest and sensitive to human proximity, I emphasize the need to include animal behavioural, landscape ecological, political as well as socio-economical aspects for future research concerning human-wildlife interactions. I also recommend future research to combine wildlife movement data from active tracking sensors such as GPS-collars together with collision data to improve conclusions about wildlife movement corridors and traffic risk zones.

Contact ALCES for WIEBKE NEUMANN, 2009
2006

New Tools for New Times

Casey Vander Ploeg

The livability and economic prowess of our large cities is of fundamental importance to western Canada’s quality of life and long-term prosperity. The fate of our large cities is a key determinant of the future of our democracy, economy, and way of life. Understanding the constellation of issues that must be addressed for our cities to reach their potential and compete with the great cities of the world is the goal of the Canada West Foundation’s Western Cities Project. The project has been providing decision-makers and the public with timely and accessible information about urban issues and putting forward practical recommendations for addressing urban public policy challenges since 2000. With the generous support of the Cities of Calgary, Edmonton, Regina, Saskatoon, Vancouver, and Winnipeg, we have embarked on a new phase of the project that runs until the end of 2008. This new phase will include groundbreaking work on street level social problems, innovative options for funding urban infrastructure, the economies of western Canada's big cities, public transit, the connections between inner city areas and suburban areas, and the intergovernmental relationships that cut across these and other issues.

Contact ALCES for Casey Vander Ploeg, 2006
2012

Nighttime lights as proxy for the spatial growth of dense urbanized areas

Nicola Pestalozzi

Nighttime lights constitute a very appealing database that can be used to measure various different aspects of the human footprint on the planet. The amount of research and the number of publications around this dataset confirm this, offering a broad spectrum of applications that involve economics, energy, society and environment. I chose to use them to study the spatial extension and the relative distribution of settlements around the Earth and their evolution over time. I analyzed the DMSP-OLS ‘stable lights’ database of the NGCD consisting in a catalog of world images of the last 19 years. I discovered that the mean center of lights is moving steadily to South-East. This reflects the extreme growth experienced by the urban centers in the developing countries, especially in Asia. I further developed a version of the Gini coefficient to compare the statistical spatial dispersion of nighttime lights, unexpectedly finding that all the countries show a very similar inequality value, quickly converging to the same coefficient by raising the lower threshold of light detection. Further, I analyzed the evolution of the lit area at a country level and in the largest urban agglomerations, finding that whereas most developing countries and cities are experiencing an incredible spatial growth in illumination, some ‘historical’ conurbations present rather constant or even decreasing emissions. This could be a signal of success of the light pollution abatement programs launched in the last years.

Contact ALCES for Nicola Pestalozzi, 2012
2006

Phosphorus Sources and Sinks in Watersheds: A Review

Sandi Riemersma, Joanne Little, Gerald Ontkean, and Tanya Moskal-Hébert

Many regions around the world are concerned with phosphorus (P) and the risk it poses to water quality. Phosphorus is the limiting nutrient in most freshwater systems and, when in excess, it can accelerate eutrophication. Many countries have adopted some form of phosphorus management strategy to reduce the risk of phosphorus entering surface water from agricultural land. In Alberta, the Soil Phosphorus Limits Project was initiated in 1999 to develop soil phosphorus limits that will maintain or improve surface water quality by minimizing phosphorus loading from agricultural soils. With laboratory work complete, micro-watershed studies have recently been initiated to identify the relationship between dissolved phosphorus (DP) and soil test phosphorus (STP). However, on a larger scale there are a variety of phosphorus sources and sinks within watersheds that influence the phosphorus content of surface water. A key question is what proportion of phosphorus in surface water can be attributed to agricultural land, and what factors govern inconsistencies in the various sources and sinks. To better understand this complex issue, a review of literature pertaining to phosphorus sinks and sources was conducted. Research carried out in Alberta and elsewhere that attempted to integrate phosphorus fluxes on a watershed scale was assessed, and its implications on the Soil Phosphorus Limits Project discussed.

Contact ALCES for Sandi Riemersma, Joanne Little, Gerald Ontkean, and Tanya Moskal-Hébert, 2006
2008

Potential of Rangelands to Sequester Carbon in Alberta

Eric Bremer

Contact ALCES for Eric Bremer, 2008
2010

Predicting deerevehicle collisions in an urban area

Rob Found, Mark S. Boyce

Collisions with deer and other large animals are increasing, and the resulting economic costs and risks to public safety have made mitigation measures a priority for both city and wildlife managers. We created landscape models to describe and predict deer-vehicle collision (DVCs) within the City of Edmonton, Alberta. Models based on roadside characteristics revealed that DVCs occurred frequently where roadside vegetation was both denser and more diverse, and that DVCs were more likely to occur when the groomed width of roadside right-of-ways was smaller. No DVCs occurred where the width of the vegetation-free or manicured roadside buffer was greater than 40 m. Landscape-based models showed that DVCs were more likely in more heterogeneous landscapes where road densities were lower and speed limits were higher, and where non-forested vegetation such as farmland was in closer proximity to larger tracts of forest. These models can help wildlife and transportation managers to identify locations of high collision frequency for mitigation. Modifying certain landscape and roadside habitats can be an effective way to reduce deer-vehicle collisions.

Contact ALCES for Rob Found, Mark S. Boyce, 2010
2007

Protecting Water, Producing Gas: Minimizing the Impact of Coalbed Methane and Other Natural Gas Production on Alberta’s Groundwater

Mary Griffiths

Contact ALCES for Mary Griffiths, 2007
2008

Quantification of Extinction Risk: IUCN’s System for Classifying Threatened Species

G. Mace, N. Collar, K. Gaston, C. Milner-Gulland, and S. Stuart

The International Union for Conservation of Nature (IUCN) Red List of Threatened Species was increasingly used during the 1980s to assess the conservation status of species for policy and planning purposes. This use stimulated the development of a new set of quantitative criteria for listing species in the categories of threat: critically endangered, endangered, and vulnerable. These criteria, which were intended to be applicable to all species except microorganisms, were part of a broader system for classifying threatened species and were fully implemented by IUCN in 2000. The system and the criteria have been widely used by conservation practitioners and scientists and now underpin one indicator being used to assess the Convention on Biological Diversity 2010 biodiversity target. We describe the process and the technical background to the IUCN Red List system. The criteria refer to fundamental biological processes underlying population decline and extinction. But given major differences between species, the threatening processes affecting them, and the paucity of knowledge relating to most species, the IUCN system had to be both broad and flexible to be applicable to the majority of described species. The system was designed to measure the symptoms of extinction risk, and uses 5 independent criteria relating to aspects of population loss and decline of range size. A species is assigned to a threat category if it meets the quantitative threshold for at least one criterion. The criteria and the accompanying rules and guidelines used by IUCN are intended to increase the consistency, transparency, and validity of its categorization system, but it necessitates some compromises that affect the applicability of the system and the species lists that result. In particular, choices were made over the assessment of uncertainty, poorly known species, depleted species, population decline, restricted ranges, and rarity; all of these affect the way red lists should be viewed and used. Processes related to priority setting and the development of national red lists need to take account of some assumptions in the formulation of the criteria.

Contact ALCES for G. Mace, N. Collar, K. Gaston, C. Milner-Gulland, and S. Stuart, 2008
2002

Quantifying barrier effects of roads and seismic lines on movements of female woodland caribou in northeastern Alberta

Simon J. Dyer, Jack P. O’Neill, Shawn M. Wasel, and Stan Boutin

Linear developments such as roads, seismic lines, and pipeline rights-of-way are common anthropogenic features in the boreal forest of Alberta. These features may act as barriers to the movement of threatened woodland caribou (Rangifer tarandus caribou). Thirty-six woodland caribou were captured and fitted with global positioning system collars. These collared caribou yielded 43 415 locations during the 12-month study period. We compared rates of crossing roads and seismic lines with rates at which caribou crossed simulated roads and seismic lines created using ArcInfo GIS. Seismic lines were not barriers to caribou movements, whereas roads with moderate vehicle traffic acted as semipermeable barriers to caribou movements. The greatest barrier effects were evident during late winter, when caribou crossed actual roads 6 times less frequently than simulated road networks. Semipermeable barrier effects may exacerbate functional habitat loss demonstrated through avoidance behaviour. This novel approach represents an important development in the burgeoning field of road ecology and has great potential for use in validating animal-movement models.

Contact ALCES for Simon J. Dyer, Jack P. O’Neill, Shawn M. Wasel, and Stan Boutin, 2002
2009

Quantifying land use of oil sands production: a life cycle perspective

Sarah M Jordaan, David W Keith and Brad Stelfox

Methods for the inclusion of land use in life cycle assessment are not well established. Here, we describe an approach that compares land disturbance between spatially compact and diffuse activities that contribute to the life cycle of a single product, in this case synthetic crude from Alberta’s oil sands. We compare production using surface mining and in situ extraction technologies. In situ technologies disturb less land per unit of production than surface mining, but the spatial footprint of in situ production is more dispersed—increasing landscape fragmentation—and in situ production requires more natural gas which increases land use due to gas production. We examine both direct and peripheral land use of oil sands development by quantifying land disturbance using a parameterized measure of fragmentation that relies on ‘edge effects’ with an adjustable buffer zone. Using a life cycle perspective, we show that the land area influenced by in situ technology is comparable to land disturbed by surface mining when fragmentation and upstream natural gas production are considered. The results suggest that land disturbance due to natural gas production can be relatively large per unit energy. This method could be applied to other energy developments, for example, a comparison between coal mining and natural gas production when both fuels are used to generate electricity.

Contact ALCES for Sarah M Jordaan, David W Keith and Brad Stelfox, 2009
2009

Regional Strategic Environmental Assessment in Canada: Principles and Guidance

Canadian Council of Ministers of the Environment

Contact ALCES for Canadian Council of Ministers of the Environment, 2009
2006

Relationships between Soil and Runoff Phosphorus in Small Alberta Watersheds

Joanne Little, Sheilah Nolan, Janna Casson, and Barry Olson

Field-scale relationships between soil test phosphorus (STP) and flow-weighted mean concentrations (FWMCs) of dissolved reactive phosphorus (DRP) and total phosphorus (TP) in runoff are essential for modeling phosphorus losses, but are lacking. The objectives of this study were (i) to determine the relationships between soil phosphorus (STP and degree of phosphorus saturation (DPS)) and runoff phosphorus (TP and DRP) from field-sized catchments under spring snowmelt and

Contact ALCES for Joanne Little, Sheilah Nolan, Janna Casson, and Barry Olson, 2006
1995

Relationships Between Stand Age, Stand Structure, and Biodiversity in Aspen Mixedwood Forests in Alberta

J.B. Stelfox (editor)

Resource managers and the environmental community are concerned that intensive clearcut logging of Alberta's aspen-dominated boreal mixedwood forests at 60–70 year rotations may alter the age class structure of the forest landscape and result in a change in forest structure and biota. In response to these concerns, we described forest structure and composition of plant and animal communities in young (20–30 years), mature (50–65 years) and old (120+ years) aspen mixedwood stands of fire origin in Alberta. The information collected in this study will serve as a reference against which structure and biota in harvested forests can be compared.

Contact ALCES for J.B. Stelfox (editor), 1995
2004

RESPONSE OF A WINTERING MOOSE POPULATION TO ACCESS MANAGEMENT AND NO HUNTING – A MANITOBA EXPERIMENT

Vince Crichton, Trevor Barker, and Doug Schindler

We report on an experiment undertaken in eastern Manitoba beginning in 1996, in which a moose population wintering in 62 km2 (24.2 mi2)was protected from hunting until September 2003. At the time of closure, it is speculated that about 37 (0.6/km2 (1.5/mi2)) moose wintered in the area based on aerial surveys and considering visibility bias. The closure was supported by the Eastern Region Committee for Moose Management, which is comprised of Manitoba Conservation staff, First Nation representatives from local communities, local hunting organizations, and other interest groups such as Tembec Manitoba Incorporated and the Manitoba Model Forest. Road access to the area was curtailed by using locked gates, millstones, and V-plowing a portion of the road in 2002. The area was surveyed from a helicopter on March 4, 2003, and 107 moose were counted in the closed area and again, based on visibility bias, it is speculated that about 142 moose (2.3/km2 (5.8/mi2 )) were present. This experiment clearly demonstrates that moose will respond positively to access management and no hunting, and that V-plowing roadbeds is a useful technique for controlling access. The cost associated with such plowing varies from about $500-$1,500/km depending on material contained in the roadbed.

Contact ALCES for Vince Crichton, Trevor Barker, and Doug Schindler, 2004
2007

Review of Alberta Environment’s Ecosystem Goods and Services Assessment - Southern Alberta Phase 2 Report

Management and Solutions in Environmental Science

Alberta Environment (AENV) requested that Management and Solutions in Environmental Science (MSES) review and assess their Ecosystem Goods and Services Assessment Report (EGS Assessment). The peer review provides comments on the main elements of the EGS Assessment. We base our review on the stated goal of the Ecosystem Services Project, namely that the “ultimate aim is … to deliver the right information to policy developers and decision makers…”. Specifically, MSES evaluates the overall framework of the EGS Assessment, addresses the questions posed by AENV, and provides recommendations for further discussion. The following overarching comments or points are made on the EGS Assessment. More detailed responses to specific questions can be found in the body of our report. A list of recommendations for consideration is also provided. 1. The EGS Assessment presents a useful framework for assessing goods and services that are provided by landscape parameters, which are composed of a mosaic of habitats and a diversity of wildlife that uses them. However, for discussion we would like to highlight the anchoring question of this work: “How do ecosystem services support the maintenance of natural and anthropogenic assets?” . A service supporting an asset is only meaningful from an anthropogenic economic perspective, wherein a service is maintained strictly for its value to humans. From a natural ecosystem perspective, is it not the asset that supports the service rather than the other way around? The wording of the question has a major impact on how one views the direction of dependencies. The way that all spreadsheet tables are set up in the document suggests that a service maintains an asset. Using a cow and produced milk as an example, the milk is the result of the condition of the cow: no cow – no milk; poor cow – little milk; good cow – plenty of milk. The authors of the report ask questions from an economic perspective (translated): how does the milk support the maintenance of the cow? Therefore, all spreadsheet tables must be read from assets to services. However, ecological systems include parameters that may or may not fit neatly into human economic systems. For example, “How do Prairie Wetlands maintain the service of water regulation?” While sometimes there are feedbacks from the services to the assets, this important point of critique has a large impact on the overall assessment. In addition to summing-up and reporting the services, the values of the assets (which, in part, should consider asset condition) should be summed-up also. 2. The world’s ecosystem services have been under-valued by several orders of magnitude. Many current economists’ approaches to put dollar values to natural assets are highly inadequate. Civilizations died out (e.g. Sumerians in Mesopotamia) because one single element of the ecosystem (soil) was degraded (salinization) to such an extent that food production was severely decimated. In the given example, what was the value of the soil? Is the value of the soil in this example not close to infinite? This idea is corroborated by Costanza et al. (1997), who state that in one sense the total value of ecosystem services to the economy is infinite. 3. In addition to the problem of evaluating an economic service provided by natural assets, there is an emotional or spiritual service that is extremely difficult to express in monetary terms; the human perception of well-being provided by the surroundings. For example, what would the quality of our lives be without rivers and lakes? Or with only polluted rivers and lakes? Natural assets provide services that we need for our spiritual survival as a whole. 4. While the authors have undertaken a literature review (200 titles), it is not necessarily exhaustive. It is likely that there are many more publications that could be reviewed with potential findings that could be incorporated into the southern Alberta EGS Assessment framework. The EGS Assessment is very important and complex, and additional work is required to fill in many of the existing gaps. 5. One of the objectives of the assessment is to “Provide an understanding of the value of high quality ecosystems in relation to economic production in southern Alberta,…”(pg 5). Figure 3-1 of the report (pg 12) presents a conceptual framework of the function of ecosystem services. However, the figure does not carry a clear message, as it does not provide specific details or an explanation of the different types of arrows. No other framework of value assessment of ecosystems is provided. De Groot et al. (2002) in Barg and Swanson (2004) provide one such figure (see Figure 1, this report) that could be used as a starting point for the framework (written for Agriculture and Agri-Food Canada). A clear division of ecological, socio-cultural and economic values could facilitate the value assessment of ecosystem services in southern Alberta.

Contact ALCES for Management and Solutions in Environmental Science, 2007
2007

Road Sediment Production and Delivery: Processes and Management

Lee MacDonald and Drew B.R. Coe

Unpaved roads are often considered to be the predominant sediment source in forested catchments. In steep, wet climates roads can cause a 10- to 300-fold increase in the landslide erosion rate, and this increase is due to the effects of roads on hillslope flow paths and the structural integrity of hillslopes. The proportion of sediment that is delivered to the stream will generally be very high for road-induced failures in hollows and inner gorge landforms, and much lower for planar hillslope failures. The pulsed input of sediment from roadinduced landsliding can greatly alter stream channel habitat and morphology. Unpaved roads can increase sediment production rates by more than an order of magnitude as a result of road surface erosion. The high surface erosion rate stems from the generation of surface runoff from the highly compacted road travelway, the lack of surface cover, and the availability of fine sediment due to traffic and road maintenance procedures such as grading. Sediment delivery to streams occurs primarily at road-stream crossings and secondarily by road-induced gullies. The proportion of the road network that is connected to the stream network is primarily a function of mean annual precipitation (R2=0.9), and is increased by about 40% in the absence of any engineered drainage structures. The chronic input of the fine sediment from roads can have adverse effects on freshwater aquatic ecosystems as well as coral reefs. Our present understanding of road surface erosion processes is good, but our models to predict road surface erosion and landsliding are much better for relative than absolute predictions. Climate change can greatly increase road-induced landslides and road surface erosion by increasing the magnitude of large storm events and increasing the amount of rain relative to snow. Extensive field surveys also show that relatively few road segments typically generate most of the road-related increases in sediment yields. Road surface erosion, the risk of road-induced landslides, and road sediment delivery can be greatly decreased by improved road designs and maintenance practices. Hence the greatest needs are to develop and provide land managers with the tools for identifying high-risk segments, and then to make the necessary investments in road reconstruction and restoration.

Contact ALCES for Lee MacDonald and Drew B.R. Coe, 2007
2007

Scenario analysis in environmental impact assessment: Improving explorations of the future

Peter Duinker and Lorne Greig

Scenarios and scenario analysis have become popular approaches in organizational planning and participatory exercises in pursuit of sustainable development. However, they are little used, at least in any formal way, in environmental impact assessment (EIA). This is puzzling because EIA is a process specifically dedicated to exploring options for more-sustainable (i.e., less environmentally damaging) futures. In this paper, we review the state of the art associated with scenarios and scenario analysis, and describe two areas where scenario analysis could be particularly helpful in EIA: (a) in defining future developments for cumulative effects assessment; and (b) in considering the influence of contextual change, e.g. climate change, on impact forecasts for specific projects. We conclude by encouraging EIA practitioners to learn about the promise of scenario-based analysis and implement scenario-based methods so that EIA can become more effective in fostering sustainable development. Environmental Impact Assessment Review 27 (2007)

Contact ALCES for Peter Duinker and Lorne Greig, 2007
2011

Scenario Analysis to Identify Viable Conservation Strategies in Paraguay’s Imperiled Atlantic Forest

Carlson, M. J., R. Mitchell, and L. Rodriguez

A common challenge facing land use planning is assessment of the future performance of land use options. The challenge can be acute in developing regions where land use is expanding rapidly and funding and data needed for planning are scarce. To inform land use planning for a biosphere reserve located in Paraguay’s Atlantic forest region, a scenario analysis explored the relative merits of conventional and conservation agricultural practices, sustained yield forestry, and protection. Simulations compared the long-term impacts on land cover, biotic carbon, and income of the area’s residents. Ecological and economic decline were projected under conventional practices. Protection and forestry scenarios achieved only small relative improvements to ecological indicators at the cost of reduced economic performance. By addressing the underlying issue of land degradation, conservation agriculture including no-tillage was the most successful land use strategy both ecologically and economically. Identification of conservation agriculture as the most promising land use strategy prioritizes issues that must be addressed to achieve sustainability, most importantly the provision of education and funding to smallholder farmers. We conclude that scenario analysis offers a flexible strategy to integrate available data for the purpose of informing land use planning in data-limited regions such as Paraguay’s Atlantic forest.

Contact ALCES for Carlson, M. J., R. Mitchell, and L. Rodriguez, 2011
2003

Scenario Planning: a Tool for Conservation in an Uncertain World

Garry Peterson, Graeme Cumming, and Stephen Carpenter

Conservation decisions about how, when, and where to act are typically based on our expectations for the future. When the world is highly unpredictable and we are working from a limited range of expectations, however, our expectations will frequently be proved wrong. Scenario planning offers a framework for developing more resilient conservation policies when faced with uncontrollable, irreducible uncertainty. A scenario in this context is an account of a plausible future. Scenario planning consists of using a few contrasting scenarios to explore the uncertainty surrounding the future consequences of a decision. Ideally, scenarios should be constructed by a diverse group of people for a single, stated purpose. Scenario planning can incorporate a variety of quantitative and qualitative information in the decision-making process. Often, consideration of this diverse information in a systemic way leads to better decisions. Furthermore, the participation of a diverse group of people in a systemic process of collecting, discussing, and analyzing scenarios builds shared understanding. The robustness provided by the consideration of multiple possible futures has served several groups well; we present examples from business, government, and conservation planning that illustrate the value of scenario planning. For conservation, major benefits of using scenario planning are (1) increased understanding of key uncertainties, (2) incorporation of alternative perspectives into conservation planning, and (3) greater resilience of decisions to surprise.

Contact ALCES for Garry Peterson, Graeme Cumming, and Stephen Carpenter, 2003
2010

Science for a Changing Far North. The Report of the Far North Science Advisory Panel

The Far North Science Advisory Panel

This report describes the vast and largely intact ecological systems of the Far North, and recommends a conservation-matrix approach for land use planning. It recommends landscape-level planning, with benchmark areas and specific features of interest set aside from development, while other areas are designated for active management, and the landscape overall is planned for continuity and resilience of ecological function. Adaptive management provides a means of evaluating management strategies as climate change and economic development proceed. It will require sustained commitment to the collection and sharing of information about the Far North, including scientific and aboriginal traditional knowledge.

Contact ALCES for The Far North Science Advisory Panel, 2010
2008

Sediment Production and Delivery from Forest Roads and Off-Highway Vehicle Trails in the Upper South Platte River Watershed, Colorado

Matthew J. Welsh

Sediment is a principal cause of impairment to surface water quality. Erosion is a particularly important environmental issue in the Upper South Platte River (USPR) watershed of Colorado because it is the primary source of drinking water for Denver, has a high-value fishery, and several stream reaches are impaired by high levels of sediment. Unpaved roads are often considered a dominant source of sediment in forested watersheds, and off-highway vehicle (OHV) trails are another potentially important but largely unquantified sediment source. The objectives of this study were to: (1) quantify sediment production and delivery from forest road and OHV trail segments in the USPR watershed; (2) test the accuracy of WEPP:Road, SEDMODL2, and two empirical models for predicting sediment production from roads and OHV trails; and (3) compare sediment production, sediment delivery, and sediment yields from forest roads and OHV trails. Rainfall, site characteristics, and sediment production were measured on 14-22 native surface road segments from 2001 to 2006, and these data were used to test the accuracy of WEPP:Road and SEDMODL2. Empirical models for predicting storm-based and annual sediment production were developed from the first four years of data; the last two years of data were used for model testing. Similar measurements on 5-10 OHV trail segments from 2005 to 2006 were used to test WEPP:Road and SEDMODL2. Sediment delivery was assessed by detailed surveys along 17 km of roads and 10 km of OHV trails. In 2006 mean sediment production from the 10 OHV trail segments was 18.5 kg m-2 yr-1, or six times the mean value from the 21 road segments. The percentage of OHV trails connected to streams was 24%, or 70% higher than for roads, largely because more OHV trails were in the valley bottoms. None of the models accurately predicted sediment production from roads or OHV trails, but the performance of SEDMODL2 was greatly improved by calibrating the geology and traffic factors to the study area. SEDMODL2 also could be improved by adjusting the slope factor, better accounting for rill density on native surface roads, and making the rainfall factor dependent on rainfall erosivity rather than rainfall depth. WEPP:Road could be improved by making sediment production decrease rather than increase with higher soil rock content, and increasing the effect of a categorical change from no traffic to low traffic. Road density in the study area is 0.6 km km-2, or three times the density of OHV trails. Multiplying unit area sediment production normalized by summer erosivity times the density, mean active width, and percent connectivity indicates that roads and OHV trails are respectively delivering approximately 1.1 Mg km-2 and 0.8 Mg km-2 of sediment to the stream network per year. Sediment delivery to streams can be reduced by locating roads and OHV trails out of valley bottoms and off steep hillslopes, decreasing segment lengths, and reducing segment slopes.

Contact ALCES for Matthew J. Welsh, 2008
1990

Sediment Production from Forest Roads with Wheel Ruts

Randy b. Foltz and Edward R. Burroughs, Jr.

Artificial rainfall was applied to two sets of paired plots 30.5 m long by 1.52 m wide, each set on a different soil type. One plot in each set contained a wheel rut while the other did not. Measurements of water and sediment yield on rutted plots showed sediment production declined with cumulative runoff while unrutted plots did not show a significant sediment depletion. This difference was a result of concentrated flow versus sheet flow.

Contact ALCES for Randy b. Foltz and Edward R. Burroughs, Jr., 1990
2012

Shell Jackpine Mine Expansion Project

Oil Sands Environmental Coalition

The Panel’s responsibilities to determine if the Project is in the public interest and determine if it will create significant adverse effects, is onerous. We believe it would assist the Panel in discharging its responsibility to protect the public interest and make its assessment of the residual impacts, if it ensured that mitigation will, in fact, be implemented and knew the status of its previous recommendations, and commitments made by the proponent on which the Panel and ERCB relied upon – particularly as it relates to Shell’s projects and the projects in the Muskeg River basin.

Contact ALCES for Oil Sands Environmental Coalition, 2012
2012

Social-Ecological Thresholds in a Changing Boreal Landscape: Insights from Cree Knowledge of the Lesser Slave Lake Region of Alberta, Canada

Parlee, B. L., K. Geertsema, and Lesser Slave Lake Indian Regional Council

Drawing on the traditional ecological knowledge (TEK) of the Lesser Slave Lake Cree, this paper shares understanding of how resource development has affected water, fish, forests, and wildlife as well as the well-being of Cree communities in the Lesser Slave Lake region of Alberta, Canada. In addition to descriptive observations of change, the narratives point to social-ecological thresholds or tipping points in the relationship of Cree harvesters to local lands and resources. Specifically, the study speaks to the echoing effects of ecological loss and degradation on traditional livelihood practices over the last 100 years highlighting the complexity of cumulative effects as well as the challenges of balancing resource development in the region with alternative land uses including those valued by Alberta’s Aboriginal peoples.

Contact ALCES for Parlee, B. L., K. Geertsema, and Lesser Slave Lake Indian Regional Council, 2012
1999

Soil Carbon Sequestration and Land-Use Change: Processes and Potential

W. M. Post, and K. C. Kwon

When agricultural land is no longer used for cultivation and allowed to revert to natural vegetation or replanted to perennial vegetation, soil organic carbon can accumulate by processes that essentially reverse some of the effects responsible for soil organic carbon losses from when the land was converted from perennial vegetation.We discuss the essential elements of what is known about soil organic matter dynamics that may result in enhanced soil carbon sequestration with changes in land-use and soil management.We review literature that reports changes in soil organic carbon after changes in land-use that favor carbon accumulation. This data summary provides a guide to approximate rates of SOC sequestration that are possible with management, and indicates the relative importance of some factors that influence the rates of organic carbon sequestration in soil. There is a large amount of variation in rates and the length of time that carbon may accumulate in soil that are related to the productivity of the recovering vegetation, physical and biological conditions in the soil, and the past history of soil organic carbon inputs and physical disturbance. Maximum rates of C accumulation during the early aggrading stage of perennial vegetation growth, while substantial, are usually much less than 100 g C m  y   . Average rates of accumulation are similar for forest or grassland establishment: 33.8 g C m y    and 33.2 g C m  y   respectively. These observed rates of soil organic C accumulation, when combined with the small amount of land area involved, are insufficient to account for a significant fraction of the missing C in the global carbon cycle as accumulating in the soils of formerly agricultural land.

Contact ALCES for W. M. Post, and K. C. Kwon, 1999
2003

Spatial Analysis of Rural Residential Expansion in South-Western Alberta

Miistakis Institute for the Rockies

Contact ALCES for Miistakis Institute for the Rockies, 2003
2011

Synthesis of Habitat Models used in the Oil Sands Region

Judy E. Muir, M.Sc., R.P.Bio. Virgil C. Hawkes, M.Sc., R.P.Bio., Krysia N. Tuttle, M.Sc. and Tony Mo

This project assessed the current state of habitat models used in oil sands region EIA and closure planning to meet the following objectives: 1. Determine which habitat models are used in EIAs and closure planning, and how these models were used; 2. Determine what linkages exist between the habitat model predictions in the EIAs and closure plans; 3. Determine which habitat models have been validated, and of these, describe and evaluate the validation procedures that were used on each model with recommendations for improvement if needed; and 4. Recommend procedures to validate non-validated models. These four objectives were addressed through the completion of four tasks: 1. Review and summarize EIA species habitat models used in the oil sands regions for Environmental Impact Assessments (EIAs) for oil sands project applications and for other projects such as wildlife habitat mapping. 2. Review and summarize how regional wildlife habitat mapping data, EIA habitat model data, and habitat models, are used to develop oil sands closure plans conducted by SEWG or for the Lower Athabasca Regional Plan (LARP) 3. Summarize the validation methods and status of existing validated models 4. Provide recommendations for validation procedures of non-validated models

Contact ALCES for Judy E. Muir, M.Sc., R.P.Bio. Virgil C. Hawkes, M.Sc., R.P.Bio., Krysia N. Tuttle, M.Sc. and Tony Mo, 2011
2011

The Anthropocene: From Global Change to Planetary Stewardship

Will Steffen, A ° sa Persson, Lisa Deutsch, Jan Zalasiewicz, Mark Williams, Katherine Richardson, Ca

Over the past century, the total material wealth of humanity has been enhanced. However, in the twentyfirst century, we face scarcity in critical resources, the degradation of ecosystem services, and the erosion of the planet’s capability to absorb our wastes. Equity issues remain stubbornly difficult to solve. This situation is novel in its speed, its global scale and its threat to the resilience of the Earth System. The advent of the Anthropence, the time interval in which human activities now rival global geophysical processes, suggests that we need to fundamentally alter our relationship with the planet we inhabit. Many approaches could be adopted, ranging from geoengineering solutions that purposefully manipulate parts of the Earth System to becoming active stewards of our own life support system. The Anthropocene is a reminder that the Holocene, during which complex human societies have developed, has been a stable, accommodating environment and is the only state of the Earth System that we know for sure can support contemporary society. The need to achieve effective planetary stewardship is urgent. As we go further into the Anthropocene, we risk driving the Earth System onto a trajectory toward more hostile states from which we cannot easily return.

Contact ALCES for Will Steffen, A ° sa Persson, Lisa Deutsch, Jan Zalasiewicz, Mark Williams, Katherine Richardson, Ca, 2011
2011

The Challenge of Developing Social Indicators for Cumulative Effects Assessment and Land Use Planning

Mitchell, R. E., and J. R. Parkins

This paper provides a synopsis on social indicators as relevant to cumulative effects assessment and land use planning. Although much has been done to better understand the social dimensions of environmental assessment, empirical work has been lacking on social indicators that could be used either as measurable inputs or outputs for cumulative effects assessment and land use planning in different kinds of communities and regions. Cumulative effects models currently in practice often fail to address deeper issues of community and regional well-being. Against this gap, social scientists are being asked to make reliable generalizations about functional, measurable relationships between certain social indicators and land use change or scenarios. To address this challenge, the Alberta Research Council held a two-day workshop in 2005 with social scientists. The workshop resulted in a list of prioritized social indicators that could be included in cumulative effects modeling/assessments and land use planning. The top five social indicators included population growth rate, education attainment, self-assessed quality of life, equity, i.e., distribution of benefits, and locus of control. Although consensus on social indicators and social thresholds for cumulative effects models was not reached, the insight gained from the workshop will help inform future cumulative effects assessment and land use planning.

Contact ALCES for Mitchell, R. E., and J. R. Parkins, 2011
1997

The effects of Linear Developments on Wildlife: A Review of Selected Scientific Literature.

Jalkotzy, M. G., Ross, P. I., and Nasserden, M. D.

This report is a reference to be used when information is required regarding the effects of linear development on wildlife. It is divided into a number of sections. The basis of the literature review was an electronic search of biological and related electronic databases. The scope of this research is detailed in Section 2. Since the basis for understanding the effects of linear developments on wildlife is the ecology of landscapes, Sections 3 provides an introduction to the basic concepts of landscape ecology and Section 4 outlines the major functions of disturbance corridors. The effects of linear developments on wildlife can be divided into 6 major groupings, and these are outlined in Section 5. Section 6 examines the effects of linear corridors from the perspective of corridor type. Sections 5 and 6 are meant to be brief overviews of their respective topics. Section 7 forms the bulk of the report and examines, in detail, the effects of linear developments on different wildlife species and species groups. Large mammals are dealt with at the species level, whereas medium-sized carnivores are dealt with as a group, as are birds. The final section, Section 8, briefly reviews mitigative measures currently in use.

Contact ALCES for Jalkotzy, M. G., Ross, P. I., and Nasserden, M. D., 1997
2009

THE IMPLICATIONS OF ALTERNATIVE GROWTH PATTERNS ON INFRASTRUCTURE COSTS

IBI Group

EXECUTIVE SUMMARY Purpose of Report Calgary has seen record levels of growth over the last few years and population and economic growth is expected to continue in the future. Over the next 60 years the population in the city itself is expected to grow from approximately 1 million to 2.3 million persons, with another 0.5 million people in the surrounding region. This level of growth offers the opportunity, and the need, to shape the future land use and transportation patterns of Calgary. Plan It Calgary has commissioned this study to assist in development of an integrated plan for land use and transportation. It examines the infrastructure implications of two growth patterns. The Dispersed Scenario reflects current trends and the continuation of current city policies, while the new Recommended Direction intensifies jobs and population in specific areas of the city, and links them with high-quality transit services. The types of infrastructure investigated in this report are transportation (roads and transit), water and sewer services, police, fire, parks, recreation centres and schools. Key Findings • The land required for Plan It Calgary’s Recommended Direction is 25% smaller than the Dispersed Scenario (which reflects current policy and trends). • The cost to build Recommended Direction is 33% less expensive than the Dispersed Scenario. • The Recommended Direction would be less expensive to operate and maintain over the next 60 years than the Dispersed Scenario. • The cost to build, maintain and replace aging streets has the largest impact when comparing costs between the two growth patterns. Reduced greenfield growth in the Recommended Direction will result in a 36% cost savings for new streets compared to the Dispersed Scenario, and will also reduce maintenance and replacement costs. • Enhanced Primary Transit service proposed in the Recommended Direction would actually be less expensive to build than extending transit to suburban communities in the Dispersed Scenario. Increased transit ridership in Recommended Direction, which provides double the service compared to the Dispersed Scenario, means that it would cost approximately the same to operate transit in both growth patterns. • Reduced greenfield growth in Recommended Direction will result in a 55% cost savings for water and wastewater systems compared to the Dispersed Scenario. There would be no net difference in costs for the existing parts of Calgary since replacement of water and wastewater systems will be required as infrastructure ages. Significant intensification of existing areas and growth in new greenfield communities could both trigger the need to upgrade existing systems.

Contact ALCES for IBI Group, 2009
1982

The Sediment Delivery Problem

D.E. Walling

The linking of on-site rates of erosion and soil loss within a drainage basin to the sediment yield at the basin outlet, and improved knowledge and representation of the associated processes of sediment delivery, represent a major research need within the field of erosion and sedimentation and also an important scale problem in drainage basin studies. This paper reviews the limitations of the sediment delivery ratio concept by considering the problems of temporal and spatial lumping and its blackbox nature. Some recent advances in our understanding of the sediment delivery system and its modelling are described and the lack of empirical investigations is highlighted. The significance of recent concern for the role of sediments in the transport of nutrients and contaminants to sediment delivery studies is introduced, and the need for further work in this field is emphasized.

Contact ALCES for D.E. Walling, 1982
2010

Triage for conserving populations of threatened species: The case of woodland caribou in Alberta

Richard R. Schneider, Grant Hauer, W.L. (Vic) Adamowicz, Stan Boutin

Prioritization of conservation efforts for threatened and endangered species has tended to focus on factors measuring the risk of extirpation rather than the probability of success and cost. Approaches such as triage are advisable when three main conditions are present: insufficient capacity exists to adequately treat all patients, patients are in a critical state and cannot wait until additional capacity becomes available, and patients differ in their likely outcome and/or the amount of treatment they require. The objective of our study was to document the status of woodland caribou (Rangifer tarandus) herds in Alberta, Canada, with respect to these three conditions and to determine whether a triage approach might be warranted. To do this we modeled three types of recovery effort – protection, habitat restoration, and wolf control – and estimated the opportunity cost of recovery for each herd. We also assessed herds with respect to a suite of factors linked to long-term viability. We found that all but three herds will decline to critical levels (<10 animals) within approximately 30 years if current population trends continue. The opportunity cost of protecting all ranges by excluding new development, in terms of the net present value of petroleum and forestry resources, was estimated to be in excess of 100 billion dollars (assuming no substitution of activity outside of the ranges). A habitat restoration program applied to all ranges would cost several hundred million dollars, and a provincial-scale wolf control program would cost tens of millions of dollars. Recovery costs among herds varied by an order of magnitude. Herds also varied substantially in terms of their potential viability. These findings suggest that woodland caribou in Alberta meet the conditions whereby triage should be considered as an appropriate conservation strategy.

Contact ALCES for Richard R. Schneider, Grant Hauer, W.L. (Vic) Adamowicz, Stan Boutin , 2010
2011

Warning Signs Mitigate Deer–Vehicle Collisions in an Urban Area

Rob Found, Mark S. Boyce

Increasing collisions with deer (Odocoileus spp.) and other large animals, and the rise in associated public safety risks and economic costs, have made mitigation strategies a priority for both transportation and wildlife managers. Deer-crossing warning signage is one of the oldest forms of mitigating deer–vehicle collisions (DVCs), but despite their low cost and logistical simplicity, the effectiveness of standard-sized permanent warning signage at reducing DVCs has not previously been adequately determined. We used historical DVC data, based on deer carcass retrieval, to identify and target areas and periods of high collision frequency. We installed warning signs at these high collision frequency locations and then compared DVCs to un-signed control locations. The total number of DVCs at signed hotspots was significantly different in the year after the signs were installed, compared to the 3 prior years (F13 ¼ 4.99, P ¼ 0.004). Although the single year of posttreatment data means the long-term efficacy of warning signage remains unknown, we showed that in the first year after installation, deer-crossing signs targeting high collision locations can be effective at reducing DVCs.

Contact ALCES for Rob Found, Mark S. Boyce, 2011
2006

Water Quality Study of Waiparous Creek, Fallentimber Creek and Ghost River

Daniel Andrews

Increased usage of the Ghost -Waiparous basin for random camping and off-highway vehicles (OHVs) has raised concerns among stakeholders that these activities are affecting water quality in the Ghost, Waiparous and Fallentimber Rivers. This report to Alberta Environment attempts to determine whether there is a linkage between these activities and water quality in these three rivers and documents baseline water quality prior to the implementation of an access management plan by the Alberta Government.

Contact ALCES for Daniel Andrews, 2006
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