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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.

Techno-economic and environmental assessments of replacing conventional fossil fuels: Oil sands industry case studies

Authors McKellar, J. M.
Year of Publication: 2012

Abstract:
Conventional fossil fuels are widely used, however there are growing concerns about the security of their supply, volatility in their prices and the environmental impacts of their extraction and use. The objective of this research is to investigate the potential for replacing conventional fuels in various applications, focusing on the Alberta oil sands industry. Such investigations require systems-level approaches able to handle multiple criteria, uncertainty, and the views of multiple stakeholders. To address this need, the following are developed: life cycle assessment (LCA) and life cycle costing models of polygeneration systems; a life cycle-based framework for multi-sectoral resource use decisions; and a method combining LCA and real options analyses to yield environmental and financial insights into projects. These tools are applied to options for utilizing oil sands outputs, both the petroleum resource (bitumen) and by-products of its processing (e.g., asphaltenes, coke), within the oil sands industry and across other sectors. For oil sands on-site use, multiple fuels are assessed for the polygeneration of electricity, steam and hydrogen, in terms of life cycle environmental and financial impacts; asphaltenes gasification with carbon capture and storage (CCS) is the most promising option, able to reduce greenhouse gas (GHG) emissions to 25% of those of current natural gas-based systems. Coke management options are assessed with the life cycle-based framework; the most promising options are identified as: Electricity generation in China through integrated gasification combined cycle; and, hydrogen production in Alberta, either for sale or use by the oil sands industry. Without CCS, these options have amortized project values ranging from $21 to $160/t coke. The application of the combined LCA and real options analyses method finds that uncertainty in natural gas and potential carbon prices over time significantly impacts decisions on coke management; the formulated decision tree identifies increases of 29% and 11% in the financial and GHG emissions performance, respectively, of the overall coke management project compared to pursuing the decision identified by the life cycle-based framework. While promising options for replacing conventional fossil fuels are identified through systems-level analyses, there are trade-offs to be made among the financial, risk and environmental criteria.

Techno-economics of CCS in oil sands thermal bitumen extraction: Comparison of CO2 capture integration options

Year of Publication: 2013

Abstract:
Canada's oil industry is a growing energy source, with proven reserves exceeding 174 billion barrels. The majority of the production is attributable to oil sands. Thermal bitumen extraction is the predominant production method, and is poised to grow at an annual rate of 23% to 2025. This has important long-term GHG emissions implications. To date, CO2 emissions mitigation efforts have overwhelmingly focused on implementing CCS in bitumen upgrading operations, rather than in thermal bitumen extraction processes. The paper covers the application of CO2 capture to the main thermal bitumen extraction process: SAGD (Steam-assisted gravity drainage). The paper presents four SAGD-oxy-fuel integration configurations and compares their techno-economics to a SAGD process featuring natural gas-fired co-generation without CO2 capture (reference case). Configuration one is a natural-gas fired co-generation boiler retrofitted for oxy-fuel operation. Configuration two is an oxy-fuel fluidized boiler using bitumen as fuel. The third configuration features a natural gas oxy-fuel boiler integrated with a cryogenic Air Separation Unit (ASU). The pressurized “waste” N2 is expanded in a turbine with additional heat integration. The fourth configuration features natural gas oxy-combustion with O2 from an Oxygen Transport Membrane (OTM) unit. Other integration concepts, including Chemical Looping combustion (CLC) are introduced. Because these concepts are in an earlier stage of development, the discussion covers their qualitative aspects and potential benefits over the previously mentioned cases.

Technology development

Authors Wells, P. S.
Year of Publication: 2011

Abstract:
Technological innovation has been a primary factor in the successes achieved in tailings handling within the oil sands industry in north-eastern Alberta. As a key driver of innovation for Suncor Energy, Inc., The author has been part of the team that stewarded several developments from conception through to full-scale implementation. This paper will present the conceptual shift in thinking which allowed for the introduction of key technologies including Tailings Reduction Operations (TRO).

Technology options and integration concepts for implementing CO2 capture in oil-sands operations

Year of Publication: 2012

Abstract:
The majority of the technology development for CO 2 capture and storage (CCS) is driven by the electric-utility industry, in which the emphasis is on large centralized units for electric-power generation with coal as the primary fuel. The implementation of CCS in oilsands operations has significant potential to provide meaningful carbon-emissions reductions. This paper presents various concepts for integrating leading CO 2-capture techniques to bitumen-extraction and -upgrading processes. The main carbon-capture technologies are reviewed, and their relative advantages and disadvantages for implementation in bitumen mining, thermal bitumen extraction, and bitumen upgrading are discussed, leading to a qualitative assessment of their suitability for each oil-sands process.

Technology requirements for mineable oil sands by the year 2010

Authors Yildrim, E.
Year of Publication: 1992

Abstract:
Alberta's reserves of conventional erode oil, natural gas, heavy oil and oil sands represent more than 90% of Canada's total energy reserves in these categories. Of these. heavy oil and oil sands. constitute more than 60% of Alberta's total. Current forecast point out a decline in conventional reserves as production exceeds new discoveries. This trend is expected to continue with fewer and smaller prospects remaining to be discovered. The decline in conventional reserves, however, could be made up by an orderly development of oil sands and heavy oil projects. Based on the magnitude of the unconventional reserves, (approximately 300 billion tonnes bitumen in place), one could observe that the prospects for maintaining Canada's energy self-sufficiency are contingent on the production of heavy hydrocarbons from oil sands and heavy oil. The development of new surface mineable oil sands projects require large capital investment and their operations are labour intensive. Therefore, the total cost of synthetic crude production from new projects is not competitive with the most conventional production operations. However, oil sands have no exploration costs and present minimal exploration risks. In addition, the experience gained in oil sands operations during the last two decades has reduced actual production costs by one-half; but, the cost discrepancy between the conventional oil and synthetic crude oil, is significant enough to justify serious R&D efforts in oil sands. This paper points out the importance of oil sands for the future energy supply in Canada and identifies the R&D as the key to further commercial development of this valuable resource. The paper proposes a methodology and a set of criteria for determining technology requirements and ranking them. Finally, it provider a select list of areas for technology development and offers a series of practical recommendations.

Telemetry receiver site investigation for the lower Athabasca River radio telemetry remote monitoring station network

Authors
Year of Publication: 2007

Abstract:
This document provides a description of the assessment of proposed receiver locations for the Lower Athabasca River Removte Monitoring Station Network. They were found to be suitable, with no vegetation, geographical or hydraulic features that would impose restrictions on the use of radio telemetry equipment for tracking fish.

Temporal changes and effects of amendments on the occurrence of sheathing (ecto-) mycorrhizas of conifers growing in oil sands tailings and coal spoil

Year of Publication: 1991

Abstract:
The effects of peat, mineral fertilizer and sewage sludge on tree growth and mycorrhizal status were monitored after planting replicate enclosures containing oil sands tailings with container-grown jack pine (Pinus banksiana Lamb.) and subalpine coal mine spoil with white spruce (Picea glauca (Moench) Voss). Growth was generally better on coal spoil than oil sands tailings. Adding sewage sludge greatly increased growth of jack pine and both sewage sludge and peat improved the growth of white spruce. Populations of sheating mycorrhizas on “egressed” roots were monitored for 10 years by direct observation and isolation techniques. The proportions of short roots of jack pine that were mycorrhizal ranged from 5 to 25% in Year 1, from 24 to 74% in Year 2 and from 29 to 91% in Year 4; their development was highest in the peat treatment and lowest in the fertilizer and unamended “control” treatments. Mycorrhizas of white spruce developed much more rapidly in coal mine spoil than those of jack pine in oil sands tailings: ∼90% of short roots were mycorrhizal in coal spoil after 2 years irrespective of treatment. Thelephora terrestris was the dominant fungus on pine for the first 4 years except when growing with peat amendments when E-strain (Complexipes) dominated. Later Suillus spp. became more important, until after 10 years 32% of mycorrhizas were formed by Suillus. The early stage fungi, E-strain and T. terrestris, persisted and formed 23 and 17% of mycorrhizas after 10 years, respectively. In contrast to events on pines in oil sands tailings, E-strain fungi formed nearly all spruce mycorrhizas for the first 2 years; it was not until seedlings were 4 years old that E-strain began to be replaced by Amphinema byssoides (Fr.) J. Erikss. By Year 7 A. byssoides dominated all treatments (62–90%), but thereafter its abundance decreased. In Year 10, the dominant fungi on spruce were A. byssoides (19%), Hebeloma (19%), E-strain (25%) and Tomentella spp. (14%). These temporal changes suggest that the fungi forming mycorrhizas with jack pine and white spruce are subject to replacement in an ordered sequence that was not significantly affected by soil amendments or vigor of the host. Relatively few fungi were involved and late stage fungi were absent. The symbiotic mycoflora was species poor even after 10 years. The spectrum of fungi encountered is thought to be typical of mycorrhizas developing in non-forest soils. Populations of sheating mycorrhizas on “egressed” roots were monitored for 10 years by direct observation and isolation techniques. The proportions of short roots of jack pine that were mycorrhizal ranged from 5 to 25% in Year 1, from 24 to 74% in Year 2 and from 29 to 91% in Year 4; their development was highest in the peat treatment and lowest in the fertilizer and unamended “control” treatments. Mycorrhizas of white spruce developed much more rapidly in coal mine spoil than those of jack pine in oil sands tailings: ∼90% of short roots were mycorrhizal in coal spoil after 2 years irrespective of treatment. Thelephora terrestris was the dominant fungus on pine for the first 4 years except when growing with peat amendments when E-strain (Complexipes) dominated. Later Suillus spp. became more important, until after 10 years 32% of mycorrhizas were formed by Suillus. The early stage fungi, E-strain and T. terrestris, persisted and formed 23 and 17% of mycorrhizas after 10 years, respectively. In contrast to events on pines in oil sands tailings, E-strain fungi formed nearly all spruce mycorrhizas for the first 2 years; it was not until seedlings were 4 years old that E-strain began to be replaced by Amphinema byssoides (Fr.) J. Erikss. By Year 7 A. byssoides dominated all treatments (62–90%), but thereafter its abundance decreased. In Year 10, the dominant fungi on spruce were A. byssoides (19%), Hebeloma (19%), E-strain (25%) and Tomentella spp. (14%). These temporal changes suggest that the fungi forming mycorrhizas with jack pine and white spruce are subject to replacement in an ordered sequence that was not significantly affected by soil amendments or vigor of the host. Relatively few fungi were involved and late stage fungi were absent. The symbiotic mycoflora was species poor even after 10 years. The spectrum of fungi encountered is thought to be typical of mycorrhizas developing in non-forest soils.

Terrain sensitivity classification methodology

Year of Publication: 1981

Abstract:
Presents a technique for classification of the landscape into areas of similar inherent sensitivity.

Terrestrial ecosystem management framework for the Regional Municipality of Wood Buffalo

Authors
Year of Publication: 2008

Abstract:
The goal of this project was to finalize the Terrestrial Ecosystem Management Framework. This project was commissioned for a consultant to facilitate the consensus-based stakeholder decision-making required to complete the Terrestrial Ecosystem Management Framework and to run the models that were required to support those decisions.

Test of a bird deterrent device at a tailings pond, Athabasca oil sands, 1974

Year of Publication: 1976

Abstract:
Between 26 August and 30 October 1974, a reflector device was tested as a deterrent to birds at a small tailings pond (Lower Camp Tailings Pond) located on Syncrude's lease 17, approximately 40 km (25 mi) north of Fort McMurray, Alberta. This tailings pond provided a situation analogous (though on a smaller scale) to that expected to occur at the Mildred Lake Tailings Pond that will be constructed on lease 17. The discovery of two bitumen-covered ducks and the remains of approximately 25 other birds along the shore of the small tailings pond on 6 August 1974, indicated that birds had died at this pond. Accordingly, the results of this study also provided information on the extent to which this tailings pond was hazardous to water-associated birds. The results of this study indicated that the reflector device did not sufficiently deter shorebirds and passerines from landing along the shoreline of this pond. Few ducks and no geese were observed to land at this pond; consequently, it was not possible to determine the effectiveness of reflectors as a deterrent to these birds. Analysis of the data did indicate that such birds might be deterred by reflectors. Because few ducks or coots and no geese landed at the small tailings pond, the hazard of this pond was considered small to such birds. Evidence did indicate, however, that the risk of contacting bitumen was great for any such birds that did land on the tailings pond. Shorebirds readily landed on the shore of this pond and were observed to pick up bitumen on their feet and legs. The hazard to these birds was considered small – although some shorebirds are known to have died at this pond. The hazard of this pond to passerines was also considered small.

Testate amoebae (protozoa) and microbial communities as bioindicators in wetlands impacted by oil sands processed materials (OSPM)

Year of Publication: 2010

Abstract:
Microbial communities in wetlands are the foundation on which all higher trophic levels in the ecosystem depend. Generally, bacteria, fungi, and algae are regarded as the predominant components of wetland microbial communities. Among the different groups of protozoa occurring in wetlands, testate amoebae have been shown to represent up to 25% of total microbial biomass in wetlands, especially peatlands. Testate amoebae have the added advantage over most other microbial groups in that they can be readily identified to the species level, even after the death of the organism, and there is a growing knowledge base of their ecology in northern wetlands. Recent studies have shown them to be sensitive to hydrology and hydrogeochemistry. There have been no previous investigations of testate amoebae in OSPM wetlands. Testate amoebae from OSPM wetlands show differences in species composition and abundance in natural (peatlands and marshes) and created wetlands (marshes and open water wetlands), including both OSPM-affected and non-OSPM affected wetlands. Testate amoebae abundance appears to be limited in OSPM-affected wetlands compared to non-OSPM sites. Genera such as Difflugia may be attributed to OSPM-affected mineral wetlands while genera such as Nebela may be indicative of non-OSPM mineral wetlands. Total microbial biomass for bacteria, fungi and testate amoebae are greatest for peatland sites compared to mineral wetland sites; biomass numbers may be slightly greater in non-OSPM wetlands compared to OSPM wetlands but needs further confirmation. Testate amoebae show considerable potential as bioindicators given their limited occurrence in OSPM wetlands and greater occurrence in non-OSPM wetlands, especially in comparison to other more dominant components of the microbial community such as the bacteria and fungi. Studies on bacteria revealed clear functional and genetic differences respectively between OSPM and non-OSPM wetlands. Community level physiological profiling (CLPP) with BIOLOGTM Ecoplates revealed a trend in which communities in OSPM sites were most similar to each other, followed by those in natural sites, and communities in reference wetlands were variable. The vegetated areas of a wetland displayed increased functional richness and diversity compared to non-vegetated areas. Analyses using the genetic approach, denaturing gradient gel electrophoresis (DGGE), applied to the total bacterial community, revealed the highest number of operational taxonomic units in OSPM samples. When DGGE was applied to the bacterial subgroups, γ-Proteobacteria and Actinomycetes, the distinction between site type was more evident than when a total bacterial approach was taken. Within OSPM wetlands, γ- Proteobacteria populations were varied while Actinomycetes were similar across sites. Given that CLPP and DGGE could distinguish between communities based on site type, both may be useful for monitoring microbial communities in Athabasca wetlands throughout reclamation. In particular, BIOLOGTM is a simple technique that might be a practical tool for monitoring microbial communities and group-specific DGGE analyses are recommended for future research. This was the first study of testate amoebae and the first to attempt to characterize and quantify biomass of components of the microbial community in OSPM wetlands; further work on a larger field data set is needed to confirm the trends and implications of the results revealed in this study. We focused primarily on the total bacteria, fungi and testate amoebae components of the microbial community; future studies should include other components such as the micro-algae, ciliates, archaea, as well as other specific bacterial groups such as cyanobacteria.

Testate amoebae as a performance indicator of ecosystem establishment in wetlands impacted by oil sands processed materials

Authors Legg, A. M.
Year of Publication: 2009

Abstract:
Mining for oil sands in the Athabasca Basin in northeastern Alberta is rapidly expanding. As economics continue to drive growing mining practices, waste management, reclamation and bio-monitoring strategies are becoming increasingly important. This project aims to determine the practicality of testate amoebae assemblages as an indicator of microbial community health and ecosystem establishment in wetlands impacted by oil sand processed materials (OSPM). Testate amoebae are unicellular, shelled protists that live in abundance in soils, leaf litter and in fresh water habitats. This group of protists forms shells (or tests) which makes them relatively easy to identify. Ecological studies have shown they occupy specific niches controlled by environmental parameters such as pH and moisture variables. These features make testate amoebae excellent bioindicators, and this project explores the potential of applying testate amoebae bioindicators in wetlands affected by OSPM. Using compound and epifluorescent microscopy techniques, testate amoebae species assemblages were identified and tabulated from a series of wetlands with different impacts by oil sands processed materials. Bacterial and fungal proportions were characterized to compare with the testate amoebae and identify possible links within the microbial community. A total of 44 species of testate amoebae were encountered in 24 wetlands, with Centropyxis platystoma and Centropyxis aculeata being the most common taxa. Natural peatland sites, not affected by OSPM contained the most diverse assemblage of testate amoebae containing Arcella, Assulina, Centropyxis, Englypha, and Heleopera. Open-water iii wetlands not impacted by OSPM were less diverse than peatland sites, but maintained between two and 12 taxa per site. Open-water sites amended with OSPM contained fewer taxa (between 0 and 4 taxa at any given site) and fewer individuals than any other site type, with Difflugia being most common. Bacteria contributed an average of 65% of the microbial community in open-water sites and an average of 80% in peatland sites. Peatland sites were significantly different (P<0.05) from all other site types in terms of testate amoebae, bacteria, and fungal biomass. This study demonstrated that differences exist in testate amoebae assemblages between site types do exist, this study establishes the fact that testate amoebae are too few (<1% of biomass), and not in sync with the other microbial facets studied (bacteria and fungi) limiting their use as bioindicators of microbial community establishment in wetlands impacted by oil sands processed materials. However the predominance of bacteria in all site types calls attention to their vital role in these sites and their importance in further research in oil sands reclamation.

Testing of seed pre-germination treatments for selected native shrub species. Preliminary phase

Year of Publication: 1983

Abstract:
The results of preliminary experiments on pre-germination treatment methods for nine selected native woody plant species are presented. The species investigated include Amelanchier alnifolia (saskatoon), Arctostaphylos uva-ursi (bearberry), Elaeagnus commutata (silverberry), Juniperus communis (common juniper), Rosa acicular is (prickly rose), Rosa woodsii (Fendler woods rose), Rubus parviflorus (thimbleberry), Rubus strigosus (wild red raspberry) and Shepherdia canadensis (russet buffalo berry). These studies represent a portion of a program to evaluate, select and test native trees and shrubs for disturbed land reclamation in the Rocky Mountain Eastern Slopes of Alberta.

Textural interfaces affected the distribution of roots water and nutrients in some reconstructed forest soils in the Athabasca oil sands region

Year of Publication: 2014

Abstract:
Re-constructed soils in the reclaimed landscape in the Athabasca oil sands region (AOSR) usually consist of an upper amendment layer (cover soil) and a substrate layer below. The cover soil used is typically peat-mineral mix (PMM) and the substrate can be materials such as tailings sand (TS) and fine-textured overburden (OB) materials. Abrupt changes in soil properties between the cover soil and the lower substrate layer create the so-called textural interface that can restrict water and nutrient movement and subsequently affect root growth. To assess the effect of the textural interface on the distribution of roots, water, and nutrients, we collected soil samples from the 10–5, 5–2, and 2–0 cm layers above and 0–2, 2–5, and 5–10 cm layers below the interface (zero at the interface) from nine sites each of PMM/TS and PMM/OB that were planted to lodgepole pine (Pinus contorta) and white spruce (Picea glauca) trees, respectively. Fine root (<2 mm) biomass (FRB) decreased logarithmically (p < 0.01) through the interface. The greatest decrease was found between 5–2 and 2–0 cm above the interface in TS due to lack of capillary rise of water and at the interface in OB due to compaction of fine-textured OB material. Based on stepwise regression analysis, volumetric water content and NH4-N or DON explained the variation of FRB in TS while electrical conductivity (EC) was the main parameter explaining FRB in OB. Our results indicate that management practices need to consider the influence of textural discontinuity or textural interface on the distribution of fine roots, water and nutrients and for water and N availability in TS and salt stress in OB as potential limiting factors for improving tree growth in the reclaimed/reconstructed landscape in the AOSR.

The 1977 Fort McMurray AOSERP moose census: Analysis and interpretation of results

Year of Publication: 1978

Abstract:
A stratified random sampling procedure involving a helicopter census of square-mile (2.6 km2) quadrats in a 648 mi2 (1,678 km2) pilot area in the AOSERP study area was continued in February 1977. The census produced a weighted mean estimate of 0.49 moose/mi2 (0.19/km2), or a study area estimate of 320 moose ± 29 percent. This was not significantly different from the population of 363± 30 percent estimated in 1976. The 1977 moose population of 320 moose was contained in an estimated 196 groups distributed on 23 percent of the square-mile study area quadrats at the time of census. Analysis of front and back observer data indicated a visibility bias in the 1977 census of approximately 50 percent. Adequate visibility bias models are required to provide biologically meaningful and statistically reliable estimates on any future moose censuses of the area.

The 1981 snowpack survey in the AOSERP study area

Authors Murray, W. A.
Year of Publication: 1981

Abstract:
Snow samples were collected in the Athabasca Oil Sands region of northeastern Alberta in mid-January and late February 1981. The snow depth was measured and snow cores were taken at .60 sites around the oil sands plants. Snow sample collectors were set out at six of the sites in mid-January and removed in late February. Quantitative chemical analyses of the samples were carried out by a commercial laboratory. Duplicate samples from nine of the sites were analyzed as an independent cross-check. Concentrations of the major ions (SO4, NO3, Cl-, NH4, K+, H+, Na+, Mg++, ca++) as well as the insoluble (AI, Mn, Ti, V) and soluble (Al, Fe, Ni, V) constituents were determined. Snowpack loadings were computed from the measured concentrations, snowmelt volume, and the area sampled. The amounts of sulphate and nitrate deposited in the snow within 25 km of the oil sands plants have increased by 88 and 27% respectively, since the previous study in 1978. The amounts of insoluble particulates have decreased markedly

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