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Oil Sands Environmental Management Bibliography

The Cumulative Environmental Management Association (CEMA)partnered with the Oil Sands Research and Information Network (OSRIN) to create the new Oil Sands Environmental Management Bibliography, which includes documents relevant to the environmental management of oil sands development in Alberta. The majority of the documents focus on the mineable oil sands in the Athabasca deposit, though some documents relate to in-situ developments. This bibliography was last updated in November 2014.

Watersheds in muskeg terrain: 1. The chemistry of water systems

Year of Publication: 1982

Abstract:
The Muskeg River basin has been the subject of a detailed, chemically based study of watersheds with extensive muskeg terrain. The objectives of this paper are to describe the chemical features of water from various components of the hydrologic cycle, and to interpret the groundwater and surface water processes in the watershed. Over a two-year period, it has been possible to characterize the variability in the major-ion chemistry of stream water, groundwater, muskeg water, and indirectly surface runoff. In most cases, waters are of the Ca2+Mg2+HCO−3-type but differ in that muskeg drainage and surface runoff are much more dilute than groundwaters from glacial drift units. Depending upon the time of year, stream water has a chemical composition that ranges between these groups. Streams in the Muskeg River basin are at baseflow only during the winter when there are no important sources of streamflow other than groundwater. At these times, the chemistry of the stream water and the average chemistry of groundwater from glacial drift units are nearly identical. Following spring snowmelt, drainage from muskeg is the main contributor to streamflow along with groundwater inflow. Stream water becomes chemically more similar to standing water in muskeg than to groundwater. During snowmelt runoff and other storm runoff periods, for example, September and October 1978, ion concentrations and specific conductance may be reduced further as direct precipitation and occasionally surface runoff contribute to streamflow.

Watersheds in muskeg terrain: 2. Evaluations based on water chemistry

Year of Publication: 1982

Abstract:
This paper discusses the application of data on stream water chemistry to regional groundwater evaluation, hydrograph separation, and evaluation of the effects of basin disturbance. We have selected for analysis the Firebag, Steepbank and Muskeg River basins, and Hartley and Thickwood Creek basins in northern Alberta, Canada. They cover slightly more than 9000 km2 within a region containing vast quantities of surface mineable, oil sand deposits. All basins are drift covered and underlain by bedrock that can range in age from Precambrian to Cretaceous. Comparison of chemical data for stream water from all basins with that for groundwater from Hartley Creek basin confirms that groundwater is a major source of streamflow in winter. Indications are that this groundwater inflow is almost entirely from glacial drift. Hydrograph separations based on chemical parameters indicate that during the spring and summer the proportion of groundwater in the streamflow is less than winter values with the largest contribution by far coming from the drainage of muskeg. Muskeg thus exerts important control on stream discharge and chemistry. If surface mining in these basins causes the removal of muskeg and replacement by mineral soil, stream discharge from affected areas will be less during summer and more during spring runoff and stormflow periods. As well, major-ion concentrations should be generally higher in the summer and fall months. However, the impact of local disturbances in a larger basin will be diminished downstream as waters from affected areas are mixed with other waters.

Watersheds in the Alberta Oil Sands Environmental Research Program study area: Drainage basin delineations watershed areas and stream profiles

Authors Froelich, C. R., & Lee G.
Year of Publication: 1980

Abstract:
This report contains watershed boundary delineations and associated drainage areas, and channel profiles on watersheds in the AOSERP study area. Included are watersheds larger than 50 km2 (20 mi2) tributary to the Athabasca River, and tributary sub-basins which contain standard hydrometric measurement sites. Also included are 15 sub-basins within the Muskeg River watershed at which monthly and bi-monthly discharge measurements were collected for one year as part of an intensive study. It has been necessary to include delineations to the sub-basin mouth and to the measurement site, since the latter must be located upstream of the former to avoid backwater effects. Mylar plates of individual watersheds (and township-range overlays) and one of all watersheds have been prepared for use in reports and/or slide presentations.

Wetland assessment in Alberta's oil sands mining area

Authors Rooney, R. C.
Year of Publication: 2011

Abstract:
Oil sands mining in Alberta will destroy tens of thousands of hectares of boreal habitat. This land will need to be reclaimed. Current closure plans call for the construction of shallow open water wetlands to cover about 10-30% of the reclaimed landscape. Already, several trial wetlands have been constructed by mine operators, but no large-scale wetland creation has been attempted. For wetland reclamation to be successful, clear targets and tools for wetland monitoring and assessment are needed. I characterized the local- and landscape-level environmental conditions and aquatic plant communities in naturally occurring, undisturbed shallow open water wetlands to serve as a reference for comparison with reclaimed wetlands. I developed two related tools to evaluate wetland condition; one focusing on levels of abiotic stress, another on biological integrity. Using these tools, I conclude that current constructed wetlands differ from reference sites in terms of aquatic plant community structure, nutrient levels, and exposure to contaminants like naphthenic acids. Using multivariate analyses, I identified seven distinct biotic assemblages, two of which might serve as targets for future reclamation. I modelled the relationship between local- and landscape-level variables and aquatic plant diversity to test hypotheses about the relative importance of relationships between environmental variables and species richness. I conclude that diversity is more strongly related to local variables than surrounding land use, but that land use does play a role, albeit one that changes with the spatial scale considered. My results can inform reclamation practices by setting clear goals for future projects and by providing tools to measure progress towards them.

What investors need to know about reclamation risks in the oil sands.

Authors Barrios, P.
Year of Publication: 2010

Abstract:
The development of Canada’s oil sands has attracted considerable attention in Canada and elsewhere in the last few years, mainly due to the impact of oil sands projects on the local environment, and the fact that they constitute an important source of Canada's greenhouse gas emissions.1 Among the impacts of oil sands projects on the local environment, land reclamation deserves special attention by investors, as there are many uncertainties regarding the effectiveness of current approaches to reclamation (in particular of wetlands and of tailings, the waste stream that results from oil sands mining), and new technologies remain unproven. These uncertainties indicate that reclamation may prove much more costly and difficult to achieve than anticipated. Oil sands operators are required to reclaim disturbed land to an “equivalent land capability,” which is defined as the ability of the land to support uses that are similar but not necessarily identical to those that existed before mining.2 Despite companies’ assurances that disturbed lands will be reclaimed to viable ecosystems, after nearly fifty years of mining, only 0.2% of disturbed land has been certified as reclaimed by the government of Alberta (companies claim to have reclaimed 13.6% of the disturbed land, but it is unclear whether they meet regulatory requirements to obtain a reclamation certificate), and no tailings pond has been reclaimed to date.3 Suncor projects to finalise the reclamation of Pond 1 in 2010, but the process will consume virtually no “mature fine tailings,” the portion of the mining waste stream that has proven most difficult to reclaim (see section 2.1 for details). In an effort to help our clients assess the risks associated with land reclamation, in May 2009 SHARE initiated a dialogue with five Canadian companies involved in mining projects in Alberta’s oil sands region. Considering the specific features of different projects, we inquired about each company’s success in the area of tailings and land reclamation, and steps taken to mitigate key risks associated with reclamation. This briefing note summarizes those discussions, highlighting areas where greater information will be required if shareholders are to be able to thoroughly assess the value of their investments. While most questions are relevant to mining operations (notably, in situ projects do not create tailings), the issue of wetland restoration and compensation may be relevant to all projects, and therefore merits consideration by all investors.

What's your hurry Fort McMurray? The physical development of the oil sands town

Authors James, S. A.
Year of Publication: 1980

Abstract:
Undergraduate thesis. Examines the planning processes involved in directing Fort McMurray's growth and looks at the resultant problems, many of which are common to all isolated resource boom towns.

When worlds collide? Hearings vs. media in making meaning for Alberta's oil sands

Authors Lefsrud, L. M.
Year of Publication: 2014

Abstract:
Although resources are central in many organizational theories, we tend to overlook the social processes by which these become defined, infused with value, and made usable by rules. Thus I ask: How has a once legitimate and unquestioned energy source – the Alberta oil sands – become problematized? Neither the nature of this resource nor the decision processes for development have fundamentally changed over the past 50 years. Yet, the meanings of this previously taken-for-granted resource have become so contested within and between the regulatory development hearings and public media more broadly, such that industry self-regulation and international rulings are being transformed. To unpack the processes by which stakeholders construct and contest these meanings, I draw on an extended case study of Alberta’s oil sands. I start by examining macro-level evolution of meaning in global media, then macro- to micro-level meanings between hearings and the surrounding media, and lastly on interactive macro- to micro-level contestations as discursive stakeholders agentically leverage across these arenas. During field emergence, oil (and tar as its descriptive synonym) was the uncontested resource of interest in this discursive field. Our interest in it increased exponentially, along with its value on the world market. This changed in 2008 and onwards, when water (and tar as the newly pejorative variation of ‘oil’) became a central resource in the discussion. The refocusing was catalyzed by the 1600 duck deaths on Syncrude’s tailings ponds and by increasing concerns amongst Aboriginal peoples about contamination of the Athabasca River. This shift in the discussion represents an effort to balance the technical utility of oil with the life affirming essence of water, from a broader constituency of discursive stakeholders. My cross-arena rhetorical analysis illustrates how discursive stakeholders use different rhetorical tools to position and counter-position themselves against their opponents, differently in public media versus hearings, to influence the regulatory outcomes. This demonstrates that, when faced with decades of institutional intransigence, interstices between discursive fields can reveal hypocrisies and give challengers leverage points for change.

Wildlife habitat mapping SEWG (South) study area

Year of Publication: 2006

Abstract:
This report was intended to present objectives, methods and example results for the classification and mapping of wildlife habitat for the southern AVI portion of the RMWB. The report also provides recommendations for product utility and for extending similar mapping to the northern area of the RWMB that does not currently support AVI. GIS map and attribute files and meta-data summary previously submitted to SEWG under contracts 2002-0004 and 2002-0005.

Wildlife habitat requirements summaries for selected wildlife species in Alberta

Year of Publication: 1985

Abstract:
This manual attempts to summarize and highlight information to assist in defining species habitat relationships relevant to Alberta environments and for a number of Alberta wildlife species. The degree of specificity of the summaries, in part or whole, varies according to the background information available. Information must often be extrapolated from studies outside Alberta, or from specific regions in Alberta; this should be taken into consideration when applying this information. The summaries have been reviewed by species experts and their comments have been incorporated. Habitat distribution maps follow the summaries; a comparative Wildlife Habitat Region map for Alberta is provided. It is hoped this manual will serve as an information base, and as a reference guide for habitat mapping and evaluation activities. The summaries are being used as an integral part in the development of habitat interpretation models which attempt to establish quantifiable value relationships between landscape features and species life requisites. These models will allow the classification of habitat suitability for a particular region on a species basis. The background information provided in the summaries supports the relative values assigned within the models for a particular habitat region. Wildlife requires a number of life support requisites for survival and reproduction. Habitat features that will supply food, cover, and space will determine a species' presence or absence from an area, as well as influencing the relative abundance of a species. Food (vegetative or animal matter, water, and trace minerals) should provide all the nutritional requirements necessary for growth and development, maintenance and reproduction. Cover may be required for thermal, reproductive, escape, resting and roosting purposes. A number of landscape components, such as vegetation, land forms, topography, and aquatic forms, may serve these functions. Space is the area or range an animal requires to satisfy these basic requirements during its lifetime. The habitat requirements of a species vary seasonally, and with sex, age, and reproductive status. As well, many habitat components (vegetation, snow cover) undergo dramatic seasonal changes or gradual successional changes that will temporally influence the suitability of a region. Disturbance phenomena, natural as wildfires or human-induced as timber harvest, may also have a significant effect on habitat suitability. Effects may be species-specific or species-general, and harmful or beneficial to varying degrees. Species characteristics will determine the components of the habitat essential to its existence. Species plasticity influences the range of habitat conditions that a species can adapt to. Sage grouse, for example, are dependent on expanses of sagebrush and cannot exist elsewhere. Elk, in contrast, are a generalistic species able to utilize a wide variety of habitats under varying conditions. Before accurate evaluations of wildlife habitat of such species can be made, an adequate information base of their habitat needs, and the factors influencing these needs, is required.

Wildlife movement and habitat connectivity monitoring guidelines for the Regional Municipality of Wood Buffalo - Task 1: Literature review

Authors
Year of Publication: 2009

Abstract:
Habitat loss and fragmentation are the most commonly cited threats to species extinction and loss of biodiversity. In the Rural Municipality of Wood Buffalo, Oil Sands development, in combination with other land use activities, may contribute to habitat fragmentation. The ability of wildlife species to effectively use habitat patches may depend on adequate connectivity between these patches. In addition, many wildlife species have daily, home range, seasonal or long-distance dispersal movement requirements. Planning development to retain adequate habitat connectivity through the landscape may minimize development impacts on wildlife species in this region. The Sustainable Ecosystems Working Group of the Cumulative Environmental Management Association would like to incorporate connectivity criteria/guidelines into the assessment of wildlife habitat quality. The following report details specific habitat, migration and dispersal requirements, which relate to connectivity, of the key indicator species which are the focus of this task. This document provides a review and synthesis of the available information on wildlife movement and connectivity requirements in the Rural Municipality of Wood Buffalo for several indicator species. Indicator species included in this document are: • Moose • Black Bear • Wolf • Canada Lynx • Fisher • Woodland Caribou • Old Growth Forest Birds/Bats For each of the indicator species identified above, studies done to date were summarized to provide species-specific connectivity and movement requirements, including scale(s) of movement (e.g., short movements to meet daily foraging requirements versus longer movements between seasonal ranges). In addition, the zones of influence and disturbance coefficients used in past Oil Sands environmental assessments were also summarized.

Wind-wave-induced suspension of mine tailings in disposal ponds - a case study

Year of Publication: 1991

Abstract:
Linear wave theory and wave hindcasting are applied to derive an expression for the depth of water needed to prevent the wind-wave-induced suspension of sediments in mine tailings ponds. The depth is expressed as a function of four factors: the threshold velocity, the wind velocity, the fetch over which the wind blows, and a factor based on the statistical distribution of wave heights. This study was motivated by the need to determine the thickness of water required to prevent the suspension of sludge solids in existing and proposed tailings ponds at Syncrude Canada Ltd.'s oil sands plant. Although data relevant to this problem are used to provide a specific example, the results are applicable whenever sediment suspension is caused by fetch-limited, deep water, wind waves. The results should be of particular use when the available data set is limited, e.g., for proposed tailings ponds. Key words: linear wave theory, wave hindcasting, wind-wave-induced suspension, threshold velocity, sludge capping, reclamation ponds, mine tailings ponds.

Winter and summer hydrometric surveys and modeling in the Athabasca Delta - hydrodynamic & habitat modeling report

Authors
Year of Publication: 2009

Abstract:
AMEC was retained by CEMA in February 2008 as the prime consultant on a team with Northwest Hydraulic Consultants to execute a detailed bathymetric and hydrometric survey at key locations in the Athabasca River delta. The summer survey was conducted in the 2008 open water season (AMEC-nhc, 2008a) while the winter survey was conducted in February 2008 (AMEC-nhc, 2008b). The surveys focused on four sites within the delta. This report presents the results of a hydrodynamic and fish habitat modeling exercise for Site 2 and Site 4 using the River2D hydrodynamic model. HYDRODYNAMIC MODELING Model boundaries were selected which encompassed all the topographic data in each segment which typically included the top of bank line and one additional survey point taken approximately 10 m inland from the top of bank. The upstream boundary at Site 4 was extended about 400 m upstream of the survey data to allow the model to simulate the velocity distribution measured at Section 4-1Q. The final open water simulations were carried out with bed roughness values of 50, 80, 100 and 120 mm with a bed roughness of 80 mm providing the best overall fit to the observed water surface elevation data. The final under ice simulations were carried out for ice roughness values of 80, 120, 160, 200 and 240 mm with an ice roughness of 160 mm providing the best overall fit to the observed water surface elevation data. Under both open water and under ice conditions, the modeled water surface elevations were found to be insensitive to the roughness values selected but were sensitive to the water level assigned to the downstream boundary. The simulated velocities matched the measured velocities reasonably well under both open water and under ice conditions. FISH HABITAT MODELING Outflow boundary rating curves at Site 2 and Site 4 were developed using an average Lake Athabasca water level computed based on lake level records between 1998 and 2006. Using the open water outflow rating curves, a total of 116 different river discharges at Site 2 and 112 different river discharges at Site 4 were selected to represent both extreme low flow conditions and extreme high (but confined within the channel) flow conditions. Using the under ice outflow rating curves, a total of 20 different river discharges each at Site 2 and Site 4 were selected to represent both extreme low flow conditions and extreme high (but confined within the channel) flow conditions. River2D models were generated for each of the above open water and under ice modeling conditions. For each open water River2D model, the total available wetted area was computed as were the weighted useable area (WUA) values for a total of ten different fish species/life stage combinations. For each under ice River2D model, the total available wetted area was computed as were the weighted useable area (WUA) values for a total of three different fish species/life stage combinations.

Winter avifauna of Lease 17, a preliminary survey

Authors Gill, D.
Year of Publication: 1979

Abstract:
During the periods 27 January, 3-6 February and 10-13 February 1977, a preliminary survey was conducted on Syncrude Lease 17 to gain the following information on wintering birds: species presence during mid winter; abundance of each species within representative habitats; and numbers of birds present in undisturbed, lightly disturbed, and highly disturbed habitats. To accomplish these objectives, transect and flight surveys were established, together with listening posts, in three sample plots that are representative of the five major habitat types on Lease 17 (trembling aspen, black spruce, mixedwood, and riparian habitats, and the main cleared area). A total of 14 species was observed on the study plots in 72 separate sightings. The gray jay was the most common species (57 sightings), followed by hoary and common redpolls (33 sightings), willow ptarmigan (24 sightings}, boreal chickadee (10 sightings), black-capped chickadee (six sightings), hairy woodpecker (five sightings), downy woodpecker (four sightings), ruffed grouse and common raven (three sightings each), goshawk and black-backed three-toed woodpecker (two sightings each}, and sharp-tailed grouse and snowy owl (one sighting each). One additional species, the house sparrow, was seen near the extraction plant. The number of avifauna sightings made in each habitat type were: main cleared area 46, mixedwood 37, trembling aspen 34, black spruce 22, and riparian 12. In undisturbed habitats 37 sightings of birds were made, while in lightly disturbed and highly disturbed habitats 45 and 69 sightings, respectively, were counted.

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