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Lac la Biche Lake


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Lakeland County AB
Canada

Royal Society’s oil sands study ignores First Nations knowledge; Portrays incomplete and inaccurate picture of the destructive developments says Beaver Lake Cree Nation


Year: 2010

Abstract:
Dec. 17, 2010 ( Indigenous People's Issues Today delivered by Newstex) Alberta: Royal Society's Oil Sands Study Ignores First Nations Knowledge; Portrays Incomplete And Inaccurate Picture Of The Destructive Developments Says Beaver Lake Cree Nation Royal Society's oil sands study ignores First Nations knowledge; portrays incomplete and inaccurate picture of the destructive developments says Beaver Lake Cree Nation A new 438-page study of Alberta's tar sands by a team at the Royal Society makes many strong criticisms of the tar sands developments but lacks of respect and regard for traditional knowledge, says the Chief and Council of Beaver...

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 influence of trophic state, thermal structure and winterkill on littoral macroinvertebrate communities in boreal plain lakes


Author(s): Langlois, P. W.

Year: 2000

Abstract:
Littoral macroinvertebrates were sampled from seven lakes varying in trophic state and thermal structure in north-central Alberta's Boreal Mixedwood ecoregion. Across the seven lakes, macroinvertebrate taxonomic richness was inversely related to total phosphorus concentration, and community diversity was positively related to thermal stability. Macroinvertebrate communities in less nutrient-rich, thermally stratified lakes, generally had higher relative biomass and density of amphipods and lower relative biomass and density of dipterans than communities in nutrient-rich, polymictic lakes. Total macroinvertebrate biomass was positively associated with total phosphorus concentration in stratified lakes only, suggesting that factors such as low dissolved oxygen availability negatively influence community structure in polymictic lakes. In the four study lakes with pike ( Esox lucius ) and perch (Perca flavescens ) assemblages, including one that experienced a winterkill during the study, the density of Gammarus sp. and Hyallela sp. varied inversely with fish density (either measured or projected) over time, suggesting that benthivorous fish may directly influence the density of larger, common macroinvertebrate prey. Observed relationships between littoral macroinvertebrate community structure, total phosphorus concentration, and water column thermal stability suggest that enhanced eutrophication or climatic warming could negatively affect benthic food webs in boreal lakes.

The role of landscape factors, predation, and demography in the ecology of anurans in boreal Alberta


Author(s): Eaton, B. R.

Year: 2004

Abstract:
I examined basic anuran biology, and responses to habitat disturbance and predators, in Alberta, concentrating on the province's boreal mixedwood ecoregion. Using landscape data for a 504 km2 area, I found that loss of small wetlands increased the distance between remaining water bodies, potentially exceeding the movement capabilities of most wood frogs (Rana sylvatica ). Using movement cost maps derived from slope, habitat, and moisture data, I found that most upland portions of the study area were potentially appropriate for wood frog use and travel. I used fish and anuran abundance estimates from 12 lakes over five years to examine relationships between these groups. Severe fish winterkills were often followed by large anuran recruitment events; young-of-the-year wood frog abundance was related most strongly to changes in abundance of small-bodied fish species, whereas toad (western, Bufo boreas , and Canadian, B. hemiophrys ) abundance was related to changes in populations of large-bodied fish species. I ran whole-pond experiments over 2 years to examine interactions between anuran larvae and small-bodied fish species. Wood frog larval activity and survival to metamorphosis were dramatically reduced in the presence of fathead minnow ( Pimephales promelas ) and brook stickleback (Culaea inconstans ); western toad larvae were unaffected by fish presence. Growth rates, longevity, and size at age of anurans often vary across latitude. Using skeletochronology, I examined these parameters for Canadian toads at four sites in three ecoregions across an 850 km latitudinal gradient from Brooks to Fort McMurray, Alberta. I also examined variation in age and size structure across three sites at a local scale. Growth rate, adjusted for length of active season, was higher at the two northern sites. Growth rates were similar at three boreal sites that were within 10 km of each other, but size structure of toad populations at these sites varied. Longevity varied from seven to 12 years across sites. Results of my research on the ecology of northern anuran populations can be used in conservation efforts focused on these species in western Canada.

The role of silica depletion in the eutrophication of Lac La Biche, Alberta


Author(s): Crowe, A. M.

Year: 2006

Abstract:
Eutrophication of aquatic systems can induce silica (Si) depletion through enhanced production and sedimentation of diatoms. This may shift the phytoplankton assemblage to include increasing proportions of non-siliceous taxa such as potentially nuisance Cyanobacteria. I examined the role of Si depletion in the eutrophication of Lac la Biche, a large lake in northern Alberta. Paleolimnological analyses indicate that while Lac la Biche has undergone eutrophication since the mid-20 th century, there is no evidence for either Si depletion or Si mediated shifts in the relative proportion of diatoms and Cyanobacteria. However, I show through nutrient amendment experiments that Si depletion can be induced seasonally under specific nutrient regimes. Further, Si amendment significantly increased the proportion of diatoms relative to Cyanobacteria. I conclude that with ongoing eutrophication and anticipated declines in Si loading to aquatic systems associated with drought and climate warming, Si depletion may become increasingly important in structuring phytoplankton communities.

Traditional knowledge of surface water - groundwater interactions in the Lower Athabasca Region


Author(s): Strand, J., & Light J.

Year: 2013

Abstract:
This report describes the study undertaken by SNC-Lavalin Environment (SLE) c to identify locations where there are potential interactions between surface water and groundwater. The study was done in the late summer and fall of 2012 and included interviews with 62 participants from First Nations and Metis groups located throughout the LAR. The interviews were conducted by two researchers from SLE with the assistance of community based researchers employed by CEMA. Interviews were conducted in Fort Chipewyan, Fort McKay, Fort McMurray (at the CEMA offices and at the Nistawoyou Friendship Centre, at Anzac, and at Lac La Biche.

Traditional land use assessment


Year: 2007

Abstract:
While the Kirby project is located within the Regional Municipality of Wood Buffalo, its footprint impacts on the traditional territories of a number of Aboriginal communities both within and beyond the boundaries of the municipality. At the time of writing, interviews had been held with Heart Lake First Nation, Chipewyan Prairie Dene First Nation, and the Métis holder of trapline #2361, resident at Winefred Lake. Interviews with other Aboriginal communities were in the process of being arranged. The scope of this report was framed by one central question: What effects could existing and approved developments, the project, and planned developments have on traditional land use? Data gathered for the report came from a literature review of previous community and industry-initiated traditional land use studies, as well as interviews with Heart Lake First Nation Elders and an interview with the Métis holder of RFMA #2361. Data was then analysed qualitatively and quantitatively, with an assessment of the extent of temporary and/or permanent loss of land. The study also contains a reclamation assessment in which the potential for the re-establishment of traditional plant and animal harvesting was determined using ecosite phases and habitat suitability indices for the closure landscape of the project. The baseline study includes summary information on historical and current traditional land use of the study area. A study of existing and approved development impacts includes a quantitative analysis of existing disturbances to RFMAs by listing type of disturbance and the number of hectares that disturbance occupies. Also provided is a linkage analysis, which highlights the key concerns of interviewed trappers and Heart Lake First Nation Elders, and then determines whether the linkage (or concern) is valid or invalid based on proposed project designs and operational plans. Valid linkages are then examined qualitatively, drawing on biophysical assessments for the project. Issues and concerns identified in the literature review and interviews are summarized for each community. Finally, changes to traditional land use are considered in the context of project-specific effects and cumulative effects.

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