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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.

Reclaiming Homeland. Envisioning research on traditional knowledge in reclamation. Volume 2: Technical report

Authors
Year of Publication: 2013

Abstract:
Reclamation is the creation of a healthy environment that can support various land uses after mining is complete. The project will be the first step in informing the development of traditional use-indicators for the Criteria and Indicator Framework for Oil Sands Mine Reclamation Certification. The proposed approach for conducting this project is based on methods developed by the RWG as part of the Biodiversity Traditional Knowledge Study; the updated Traditional Knowledge Research Guidelines issued by the TKWG in 2013; and methods used in Sustainable Forest Management Systems in other regions of Canada. A collaborative, team-based approach will be used to conduct the project. The joint Task Group will be comprised of members of the Aboriginal Coordinating Committee (ACC), Traditional Knowledge Working Group (TKWG), and the Reclamation Working Group (RWG).

Reclamation and vegetation of surface mined areas in the Athabasca tar sands

Year of Publication: 1977

Abstract:
One of the major environmental problems which arises with surface mining of the oil sands in the Fort McMurray-Fort MacKay area of Alberta is the permanent loss of the natural vegetation and the drastic change in the soils that supported it. It has been estimated that with a production target of one million barrels of crude oil per day approximately two thousand acres of land will have to be cleared every year. Most of the disturbed areas eventually must be vegetated again; these include the overburden piles and the tailings sand. In vegetating such areas several problems such as salinity, oil, low fertility, erosion and unfavorable soil reaction have to be contended with. There has been some success in the general vegetation program on the Great Canadian Oil Sands Ltd. lease, but the problems listed above still have to be studied and solutions for them found. Surface mining of the Alberta oil sands requires the clearing of natural vegetation from thousands of acres of land. Under other circumstances these cleared areas should present few problems for revegetation programs, but major problems arise in mined areas and in areas where mine wastes are deposited. The wastes include tailings sand, overburden materials (which may contain oil-bearing materials and may present salinity and alkalinity problems), and coke and sulfur (by-products of the upgrading process which could damage vegetated areas through wind-blown dust deposits). A likely problem in the future is the damage that would be caused over wide areas to the soil and vegetation by the sulfur dioxide emissions from the processing plants. The only operating plant in the area, Great Canadian Oil Sands Ltd. (GCOS), has embarked on a program to vegetate the tailings pond dike, whose outer shell consists of tailings sand, and also the overburden piles. Investigations carried out over a one-year period examined some of the materials at hand and techniques available for solving some of the existing known problems in vegetating the mine wastes. A number of plant species, both cultivated and native, were grown in growth chambers on the waste materials to determine the performance of the species under different salinity, soil reaction, fertility, soil mix, and oil conditions. A second major study, a field trial on an already vegetated area on the GCOS tailings pond dike, was conducted to determine responses of the already established vegetative cover to different fertility levels, and to determine the fate of added fertilizer nutrients. The materials used in preparing various \"soil mixes\" were characterized chemically and biologically.

Reclamation for afforestation by suitable native and introduced tree and shrub species

Authors Selner, J., & Thompson R.
Year of Publication: 1977

Abstract:
During 1976, a variety of methods and materials were used in the search for afforestation practices that will assist in the establishment of a self sustaining vegetation cover compatible with land use objectives for the Alberta oil sands area. The project study area is located on the Great, Canadian Oil Sands Company Ltd. Mining lease and all test plots were situated on tailings sand (tailings,dike) or overburden material (waste dump no. 7). Twenty four species of trees and shrubs and 23 clones of poplars were tested for their rec1amation suitability. In general the poplars showed greater survival and growth than the other species used. Conclusions about individual species will not be made because the significance of one seasons observations on long lived plants is questionable until more long term observations have been made. The most productive of the eight planting sites used was on the tailings dike where a l0 cm layer of peat was mixed with the tailings sand. Perhaps the most beneficial property of the peat is that it increases the moisture holding capacity of the sand. Although a Swedish planting mattock was, used to plant seedlings, about: 1500 Manitoba maple (Acer negundo (Britt.) Sarg.) were planted with a planting bar to assess the effectiveness of a faster planting method. No significant difference resulted from' the use of these two tools but it is suspected other factors such as seedling condition and time of planting masked any difference that might have occurred. Both coniferous and deciduous seeds were used on a seed bed of tai1ings sand and peat mixed together. The intention was to estab1ish the potential of direct seeding of woody species for revegetation on the tailings dike Jack pine (Pinus banksiana Lamb.) was the most successful species to germinate and survive. Rodent damage, high soil surface temperature, erosion and proper species selection are some of the problems which have to be solved if direct seeding is going to be useful. Plots of Basford willow (Salix fragi1is var. 'Basfordiana' Redher) were set up on the tailings dike to examine what effect position on the dike's slope might have on seedling performance. While performance did vary along the slope the variance was not consistent between plots. Eight hundred cuttings of native balsam poplar (Populus balsamifera L.) were planted and it would seem the larger, more deeply planted cuttings sprouted the best. The performance of cuttings was poor compared to seedlings. In the fall, approximately 2000 container seedlings were planted to compare their success to spring planted seedlings. This planting time is being investigated as an alternative to the often busy spring season, and it also allows the seedlings to take advantage of favourable early spring growing conditions.

Reclamation for aspen revegetation in the Athabasca oil sands: Understanding soil water dynamics through unsaturated flow modelling

Year of Publication: 2012

Abstract:
Reclamation of mined areas in the Athabasca oil sands region is required by law, with the ultimate goal of revegetating to species characteristic of predisturbance native plant communities. To develop adequate reclamation strategies, an analysis of soil water dynamics is of utmost importance, as is understanding the impact of the thickness of the reclamation cover. In this work, soil water dynamics and fluxes at the water table were simulated for three reclamation scenarios and compared with the fluxes obtained for natural conditions assuming that aspen is the target reclamation species. According to the simulations, a reclamation thickness between 0.5 and 1.0 m can be used to provide water for revegetation. The numerical simulations show that the reclaimed landscapes have fluxes at the water table that exhibit less fluctuation than natural conditions. To limit the interaction between the water table and atmospheric fluxes, and to limit upward flux, the water table should be deeper than 2.0 m on reclaimed landscapes that use aspen for revegetation, particularly when reclamation takes place during a dry climatological cycle.

Reclamation of an oil sand tailings storage facility: Vegetation and soil interactions

Authors Burgers, T. D.
Year of Publication: 2005

Abstract:
A thesis submitted to the Faculty of Graduate Studies and Research in partial fulfillment of the requirements for the degree of Master of Science in Land Reclamation and Remediation, Dept. of Renewable Resources, University of Alberta. Thesis (M. Sc.)--University of Alberta, 2005. Includes bibliographical references.

Reclamation of peat-based wetlands affected by Alberta Canada's oil sands development

Year of Publication: 2013

Abstract:
The ability to construct or reclaim functional peat-based wetlands as a replacement for those lost to development activity is uncertain. Oil sands development in northern Alberta, Canada will ultimately result in the removal of over 85 km2 of peat-based wetlands. To examine potential replacement of these lost peatlands we compared four treatments assigned to 16 known-age wetlands where we followed plant community, carbon dynamics, water quality, invertebrates and top predators for 5 years. Key questions followed by a synopsis of findings include: (1) Will wetland communities become more natural with age? – Yes, however industrial effluents of salinity and napthenates will slow succession and may truncate development compared to natural systems; (2) Can community succession be accelerated? – Yes, the addition of carbon-rich soils can facilitate development in some zones but cautions are raised about a “green desert” of vigorous plant stands with low insect and vertebrate diversity; (3) Is productivity sustainable? – Maybe, limitations of water chemistry (salinity and napthenates) and hydrologic regime appear to play large roles; (4) Will production support top predators? Sometimes; insectivorous birds, some small fish and a few amphibians persisted under all except the most saline and napthenate-enriched sites; (5) What is the role of the compromised water quality in reclamation? – Reduced diversity of plants, insects and vertebrates, reduced plant physiological efficiency and thus slower rates of reclamation. It is axiomatic and well demonstrated throughout Europe that it is easier and more cost effective to protect peatlands than it is to reclaim or create them. This is complicated, though, where mineral or property values soar to over $1 million per hectare. Industrial planners, governments and the public need to understand the options, possibilities, time frames and costs of peatland replacement to make the best land use decisions possible. Our research provides a quantifiable scientific basis for forecasting the future functions, conditions and replacement value of wetlands lost to development, while providing a basis for reclamation recommendations.

Reclamation of soils contaminated by sodium chloride

Authors De Jong, E.
Year of Publication: 1982

Abstract:
Soil samples contaminated in the laboratory with a Nacl solution were leached with water after various amendments had been added. with no amendments added, percolation rates were reduced more on a light-textured Dark Brown chernozemic A than on a medium-textured Black chernozemic A. Undisturbed B horizon cores showed a smaller decrease in percolation rate than the A horizons, but natural gypsum or carbonates were of no benefit in maintaining percolation through the unamended contaminated subsoils. Percolation g"n".uily increased as more ca-amendment was added to the contaminated A horizons, but rate of (surface-applied) amendment had no effect on the percolation throush the B horizon cores. Gypsum mixed into the contaminated soll was much more-eflective than gypsum applied on the surface; adding NH1NO, to the gypsum had no effect. The efficiency of incorporated amendments decreased in the order: gypsum > MgSO, > Ca(NO,)r. Surface-applied Ca(NOr). was a better amendment than mixed-in Ca(NO.,)r. kaching losses decreased in the order: Cl > Na > Mg > Ca > K. Initial losses of Cl, Na, Mg and Ca were faster than expected from the rule of thumb that one pore volume of water reduces the salt content by about one-half. Subsequently, losses were much slower than in the rule of thumb as most of the remaining cations are in exchangeable form.

Reclamation of wetland habitat in the Alberta oil sands: Generating assessment targets using boreal marsh vegetation communities

Authors Raab, D. J.
Year of Publication: 2010

Abstract:
Thousands of hectares of wetlands are being destroyed by oil sands mining in Alberta, and the industry must undertake wetland reclamation to compensate for these losses. Wetland vegetation has developed at some previously mined sites, however reclamation is thus far exploratory, and limited in extent. To inform reclamation practices and assist compliance monitoring I examined vegetation communities in 25 natural boreal wetlands and 20 oil sands reclaimed wetlands, developed a Vegetation-based Index of Biological Integrity (vIBI) to quantify the ecological health of wetlands, and identified possible physical and chemical barriers to reclamation. The vIBI identified 6 reclaimed wetlands in fair to good health, however reclaimed wetlands have different vegetation communities, do not produce the same level of aboveground biomass, and have lower levels of sediment nutrients than natural wetlands. To reclaim healthy wetlands, planning should focus on establishing appropriate species, and alleviate nutrient and sediment deficiencies.

Reclamation to native forest ecosystems in the oil sands region

Authors Tuttle, S.
Year of Publication: 1997

Abstract:
Suncor's reclamation goal is to achieve maintenance-free, self-sustaining ecosystems with capability equivalent to their pre-disturbed condition. Ecosystem re-establishment includes the following steps: (1) soil reconstruction, (2) revegetation, and (3) growth of primary vegetation communities. To assess the sustainability of re-established ecosystems, vegetation and soil characteristics are monitored each year. This method of reclamation and tree planting results in a diverse herbaceous cover developing within a year of soil amendment application, providing erosion protection along with a source of cover and food for wildlife. Results to date have proven to be very positive, since reconstructed soils have been shown to be equivalent to or better than original soils. Also, reclamation sites are developing into sustainable ecological units comparable to nearby natural forest areas

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