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The assimilative capacity of the Athabasca River for organic compounds


Year: 1980

Abstract:
Understanding the functioning of the aquatic ecosystem within the mainstem Athabasca River is of paramount importance if protection against the input of contaminants from oil sands developments is to be afforded to the Athabasca River itself, the Peace-Athabasca Delta, and Lake Athabasca. The term assimilative capacity has been applied to denote the dynamic ability of aquatic ecosystems to remain viable and productive in the face of external factors (natural or anthropogenic). An implicit assumption within this definition is the fact that aquatic ecosystems possess the ability to change in response to external factors while maintaining their productivity and diversity. The rate and extent of this adaptive capability is the underlying process of assimilative capacity which must be understood and therefore examined.

The Athabasca fluting field, Alberta, Canada: Implications for the formation of large-scale fluting (erosional lineations)


Year: 2000

Abstract:
Current drumlin and fluting hypotheses, centred on processes of formation, erosion and deposition by subglacial deformation, accretion by lodgement, glacial erosion, and meltwater erosion and deposition, rarely receive comprehensive field testing. This paper documents the morphology, internal structure, and landscape associations of the Athabasca fluting field, Alberta, and discusses how well these characteristics are explained by postulated fluting forming processes. Fluting hypotheses are comprehensively tested by this approach and their rejection or acceptance are firmly based on field observation and knowledge of processes. Using multiple criteria, fluting is shown to be erosional and not to be a product of pervasive subglacial deformation or accretion by lodgement. Morphology, landscape associations, bed truncation, plus glaciofluvial lags and gravel on fluting ridges are inferred to support erosion by meltwater. Intact primary bedding, synsedimentary faults and injection structures very close to the landsurface, showing no sign of shear deformation, are used to reject erosion by subglacial deformation. Fluting is shown to be closely associated with tunnel channels and indicates that these channels were overtopped by broad floods that formed the fluting field and eroded anabranching tracts over the length of the Alberta Plains. Prior to fluting formation, sequences with melt-out and lodgement till, conduit sediment and boulder lags record net deposition over an extended time period. Diapirism prior to fluting formation marks a period of extreme pressure gradients which are related to bed separation. Following fluting formation, there was only minimal landscape modification, dominated by glaciofluvial and glaciolacustrine deposition, not glacial processes. This progression is presented as evidence for two very different glacial regimes separated by a short period with diapirism and extensive landscape modification by meltwater erosion. We note that the study area was glaciated only once, during the Late Wisconsinian, and it follows that glacial sedimentation and landscape modification were confirmed to this single glacial episode.

The Athabasca Watershed


Author(s): Council, T. A. W.

Year: 2015

Abstract:
The Athabasca River watershed is the area of land that captures all precipitation (rain, hail, and snow) that eventually drain into the Athabasca River. Together with the area of land within Alberta that drains into Lake Athabasca, they form the Athabasca watershed within Alberta. As water flows downhill over and through land our activities on land eventually affect rivers, streams, lakes, wetlands and ocean. Whatever we do upstream affects water and land downstream. Therefore, the watershed is the appropriate land unit for managing our activities so that the land, water, and wildlife remain healthy.

The Canadian oil sands development: Management of land, air and water resources


Author(s): Poveda, C. A.

Year: 2015

Abstract:
The Canadian oil sands -the third largest proven reserves of oil after Saudi Arabia and Venezuela- are located in Northern Alberta, Canada; these deposits of unconventional oil are an attractive investment for oil & gas developers and governments not only because of the size of the reserves but also the geopolitical stability of the region. Nevertheless, the development of the projects and current operations are facing opposition and struggling with a negative campaign around the world due in part to misinformation of the facts, lack of knowledge of the process throughout the projects life cycle, and years of stakeholder mismanagement. Indisputably, the development of the projects carries a series of impacts (environmental, social, economic, and health); developers and operators may dispute the intensity of the impacts but not the existence of them. The manuscript discusses the impacts on land, water and air resources based on indicators included in sustainability reports presented by oil sands developing and operating organizations. These reported statistics give a broader understanding of the current state of the Canadian oil sands and their development. The aim of the manuscript is to present these statistics four most common environmental impacts from oil sands development: greenhouse gas emissions, land use, water use, and tailing ponds.

Citation:

The Chipewyan-Cree-Métis interaction sphere and the fur trade political economy: Archaeological, ethnohistorical and ethnographic approaches


Year: 2012

Abstract:
The goal of this paper is to understand the development of economic and so- cial interactions between several different societies, or cultural-ethnic groups, occupying the same regional environment and involved in a common political economy. Toward this end, Chipewyan, Cree, Métis and Euro-Canadian rela- tionships and conflicts in central subarctic Canada will illustrate the complexi- ties and subtleties of intergroup dynamics emerging over a two-century span from the late 18th to the mid-20th centuries. Particular emphasis in this paper will be given to the period between the 1890s and 1950s. We began grappling with these issues over 30 years ago, for which we developed a particular style or genre of ethnoarchaeology which involves a syn- ergistic blend of historical archaeology, archival ethnohistory, and ethnography. First, we will provide a brief overview of some of the key findings and inter- pretations of our research1. Second, the occasion of the Tromsø conference of- fers an opportunity to rethink Chipewyan-Cree-Métis relations and, perhaps, to reassess their theoretical relevance for discussions of “interaction spheres,” networks, and identity in archaeology and anthropology generally.

The distribution foraging behaviour and allied activities of the white pelican in the Athabasca oil sands area


Author(s): Ealey, D. M.

Year: 1979

Abstract:
From mid to late summer 1977 an investigation was made of the distribution and foraging of White Pelicans in the Birch Mountains. This study was linked with a breeding investigation undertaken at the pelican rookery as part of the Alberta Oil Sands Environmental Research Program. Aerial surveys, ground observations, prey analysis and prey sampling were conducted. Pelicans were observed to regularly use foraging/loafing areas up to 69 km from the rookery. Timing of diurnal arrivals and departures from all locations showed that the birds belonged to the same population. A shift in concentrations of the pelicans was detected over the summer. Reasons for this shift were advanced. Trends in diurnal and seasonal activities were determined for the pelicans away from the rookery. Basic behavior seemed comparable to that observed at the rookery. The behavioural observations indicated the importance of foraging areas and loafing bars. Habitat features varied considerably for these locations but basic criteria were established for each. The locations of the foraging/loafing areas were determined for lakes in an intensive study area. The diet of juvenile pelicans included brook stickleback, northern pike and lake whitefish. The total fish consumption of the Birch Mountains population of White Pelicans was estimated at between 19.7 and 24.8 tonnes during the 1977 season. It is recommended that this investigation of distribution and foraging of White Pelicans be continued.

The effect of elevation and fish predation on the distribution of Chaoborus in Rocky Mountain Lakes: Paleolimnological applications


Author(s): Lamontagne, S.

Year: 1993

Abstract:
Cabin, Celestine and Caledonia lakes, Jasper National Park, contain naturally reproducing populations of rainbow trout (Oncorhynchus mykiss) and lake chub (Couesius plumbeus), but whether these populations are native was not known. I used subfossil Chaoborus) mandibles retrieved from sediment cores to determine if planktivorous fish were present in these lakes prior to this century. I determined that C. (subgenus Chaoborus) americanus is the only species found in fishless lakes, while C. (C.) flavicans is only found in lakes containing fishes. The genus Chaoborus also had a restricted distribution along the elevation-temperature gradient of mountain lakes. Cabin and Celestine lakes were fishless prior to this century. In these lakes, C. americanus was present prior to this century but was eliminated when fish were first stocked. C. flavicans has replaced C. americanus in Celestine Lake but Chaoborus are presently rare in Cabin Lake. The occurrence of C. flavicans throughout the Caledonia Lake core suggests that this lake had native fish(es) prior to this century. Paleolimnological analysis supports the hypothesis of the past occurrence of the Athabasca rainbow trout (O. mykiss athabascae) in Caledonia Lake. (Abstract shortened by UMI.)

The environmental hydrogeology of the oil sands lower Athabasca area, Alberta


Author(s): Miall, A. D.

Year: 2013

Abstract:
Shallow fresh groundwater and deep saline groundwater are used together with surface water in the extraction of bitumen from the Athabasca Oil Sands both in the surface mining and in situ operations. However, increasing efficiencies in processing technologies have reduced water use substantially, and currently at least 75% of the water used in most operations is recycled water. Much concern has been expressed regarding contamination of surface waters by seepage from tailings ponds, but hydrogeological studies indicate that this is not happening; that seepage capture design is effective. Oil sands mining and in situ project licensing and operation regulations include Environmental Impact Assessments that mandate considerable hydrogeological measurement and monitoring work. However, little of this is independently evaluated for accuracy or synthesized and interpreted for the public. Recent changes in Alberta environmental regulation, including the establishment of the Alberta Environmental Monitoring Management Board (in October 2012) are expected to bring new transparency to environmental management of Oil Sands operations.

The fish and fisheries of the Athabasca River basin: Status and environmental requirements


Year: 1984

Abstract:
The information presented here reviews what is currently known of fish ecology and production of the Athabasca Basin, and includes discussions of fish production, sport and commercial use of fish populations, and alternative opportunities for recreational fishing in the rivers of the Athabasca Basin. Fisheries management objectives for the basin rivers and data gaps in existing knowledge of fish and fisheries are also discussed. In addition, water quality criteria for the protection of fish and aquatic life have been referenced, and, where possible, stream flows which affect fish populations have been included. The Athabasca Basin accounts for 23% of the land area of Alberta. For the purposes of this report, the basin has been divided into 10 sub-basins: four mainstem sub-basins, and six tributary sub-basins. The mainstems of the principal rivers of the 10 sub-basins provide approximately 4,390 km of fish habitat which can be roughly divided as providing 1,500 km (34%) coldwater habitat (supporting mainly trout and whitefish), 2,250 km (51%) warmwater habitat (supporting mainly pike, walleye, and goldeye), and 640 km (15%) transition zone intermediate between the two. Both commercial and recreational fisheries occur within the Athabasca Basin. The commercial fish catch represents a substantial proportion of the overall harvest and total market value of the Alberta commercial fishery. The recreational fishery occurs mainly in rivers and streams, though some lakes and reservoirs provide alternate opportunities. In 1980/81, approximately 9% (26,346) of Alberta's licensed anglers resided and fished within the Athabasca Basin. The opportunities provided to sport fishermen by the basin rivers have local, regional and in some cases, national significance. The Athabasca River rises high in the Rocky Mountains, and terminates at the delta created by the Peace and Athabasca rivers at the western extreme of Lake Athabasca. Over its length, the Athabasca River grows from a torrential high-mountain stream to a silt-laden major river at its delta, and its basin encompasses virtually every temperate stream type. In its upstream reaches, the Athabasca River flows generally northeast, steadily increasing in volume as it receives flows from the Berland, McLeod, Pembina, Lesser Slave, Lac La Biche, and Calling rivers. Further downstream, in the vicinity of a series of rapids, the river receives flows from the Pelican and Horse rivers. Near Fort McMurray, the Athabasca forms a confluence with the Clearwater River, and turns to flow north through the Athabasca Oi1 Sands region. Within the oil sands, the Athabasca River receives flows from many rivers and streams, including the Steepbank, Muskeg, Mackay, Ells, Firebag, and Richardson rivers. Reaching the Peace-Athabasca Delta near Embarras Portage, the Athabasca River subsequently forms part of the Mackenzie drainage, which empties into the Beaufort Sea. Flowing through diverse and widely differing terrain, including remote alpine areas, populated urban settings, and the 1argest open-pit oil sands mining sites in the world, the Athabasca Basin is made up of a corresponding variety of waterbodies. Within the basin, each sub-basin has characteristic fish-producing capabilities, which are largely determined by the conditions which contribute to its environment. The primary features of each sub-basin and the characteristics of its lakes and rivers are summarized.

The fur trade of Fort Chipewyan on Lake Athabaska, 1778-1835


Author(s): Parker, J. M. P.

Year: 1967

Abstract:
Masters thesis, examining the establishment of the fur trade at Lake Athabaska with Fort Chipewyan as its focus.

The future of oil sands production in Alberta


Author(s): Khan, M. A.

Year: 2007

Abstract:
The oil sands are an enormous Canadian resource. The ultimate volume of crude bitumen in place is estimated to be some 400 billion cubic meters with 12 percent or 49 billion cubic meters estimated to be ultimately recoverable. Canada's resources of crude bitumen occur entirely within the province of Alberta and are found in sand and carbonate sedimentary formations in three regions defined as the Athabasca, Cold Lake, and Peace River. To mine and extract these resources, dragline or shovel and truck processes are used. Lower steam to oil ratio and artificial lift can help in finding out an optimum condition for extracting bitumen. Though it minimizes the recovery process but at the same time will reduce cost. Upgrading process is complex and need to be develop according to the composition of oil sands formation. As the resources in Canada for extracting conventional crude oil are declining; there is need for development of the existing technology for extracting heavy oil and oil sands. Advance development made in directional drilling and Measurement While Drilling (MWD) technologies leads to further develop in-situ production technologies for instance Steam Assisted Gravity Drainage (SAGD). These advances in technologies will help in improving well bore reservoir contact and sweep efficiencies ensuring minimum production costs. Environmental concerns increase with the use of mining oil sands by in-situ methods. The main issues are habitat fragmentation, surface and ground water quality, air emissions and land disturbance.

The hydrogeology of the Athabasca oil sands area Alberta


Year: 1979

Abstract:
The area of study includes most of the Athabasca Oil Sands deposit and extends from Tp77 to Tp100, and R1 to R25 west of the fourth meridian: a total of about 67,260 sq. km (25,970 sq. mi). Holocene and Cretaceous clastic rocks unconformably overlie Devonian nonclastic rocks resting on Precambrian basement. Regional dip is toward the southwest. A major fault passing north-northwestward under Fort McMurray is hypothesized, with a downthrow west of about 273 ft (83 m); it appears to be of post-Devonian age. Partial solution of Prairie Evaporite Formation salts extends about 16 km (10 mi) west of the fault; to the east solution is almost complete. Collapse features are particularly notable at the Cretaceous-Devonian contact. West of the fault, three hydrostratigraphic units are defined: 1.The K-O hydrostratigraphic unit, consisting of Holocene and Cretaceous sediments, is characterized by alternating vertical and horizontal groundwater flow controlled by zones of low and high hydraulic conductivity, respectively. Unsaturated zones extend up to 10 km(6 mi) from outcrop into the units of high hydraulic conductivity. Total dissolved solids contents in groundwaters are usually less than 10,000 mg/L and commonly less than 5000 mg/L 2.The D-2 hydrostratigraphic unit, consisting essentially of Upper Devonian strata, has dominantly horizontal groundwater flow towards a zone of hydraulic heads located roughly coincident with the fault at elevations generally equal to those of the Athabasca River. Total dissolved solids concentrations are usually less than 40,000 mg/L, but are higher to the southwest and in the north-center of the area. 3.The D-1 hydrostratigraphic unit, consisting of the Methy, McLean River, and La Loche Formations that underlie the Elk Point evaporites, has horizontal groundwater flow toward the fault zone. Freshwater hydraulic heads west of the fault are approximately at land surface, but decline eastward to the elevations of major rivers. Total dissolved solids concentrations exceed 200,000 mg/L west of the fault. The D-1 and D-2 hydrostratigraphic units merge east of the fault. Groundwater flows west towards the fault, with total dissolved solids concentrations seldom exceeding 50,000 mg/L. On a regional basis, the oil sands have a finite hydraulic conductivity commonly of 10-6 to 10-4 cm/sec. Surface mining ventures will generally require that the oil sands and underlying aquifers be depressurized. Hydrogeological conditions will affect depressurization:1.pumping volumes will vary widely; 2.in produced water, total dissolved solids may range up to 300,000 mg/L; 3.hydrogen sulphide gas contents will vary greatly;4.induced infiltration from the Beaverhill Lake Formation or the Athabasca River may occur;5.collapse features and faults caused by evaporite solution may have affected the oil sands sufficiently that loss of pressures and fluids could occur in in situ operations. Structural conditions are suitable for injection of waste liquids into the D-2 hydrostratigraphic unit only west of the limits of evaporite solution. Waste injection into the Beaverhill Lake Formation may be possible where the overlying Woodbend Group is sufficiently thick.

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