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Arciszewski TJ, Hazewinkel RRO, Dubé MG. A critical review of the ecological status of lakes and rivers from Canada's oil sands region. INTEGRATED ENVIRONMENTAL ASSESSMENT AND MANAGEMENT 2022; 18:361-387. [PMID: 34546629 PMCID: PMC9298303 DOI: 10.1002/ieam.4524] [Citation(s) in RCA: 4] [Impact Index Per Article: 2.0] [Reference Citation Analysis] [Abstract] [Key Words] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Received: 03/17/2021] [Revised: 09/19/2021] [Accepted: 09/20/2021] [Indexed: 05/05/2023]
Abstract
We synthesize the information available from the peer-reviewed literature on the ecological status of lakes and rivers in the oil sands region (OSR) of Canada. The majority of the research from the OSR has been performed in or near the minable region and examines the concentrations, flux, or enrichment of contaminants of concern (CoCs). Proximity to oil sands facilities and the beginning of commercial activities tend to be associated with greater estimates of CoCs across studies. Research suggests the higher measurements of CoCs are typically associated with wind-blown dust, but other sources also contribute. Exploratory analyses further suggest relationships with facility production and fuel use data. Exceedances of environmental quality guidelines for CoCs are also reported in lake sediments, but there are no indications of toxicity including those within the areas of the greatest atmospheric deposition. Instead, primary production has increased in most lakes over time. Spatial differences are observed in streams, but causal relationships with industrial activity are often confounded by substantial natural influences. Despite this, there may be signals associated with site preparation for new mines, potential persistent differences, and a potential effect of petroleum coke used as fuel on some indices of health in fish captured in the Steepbank River. There is also evidence of improvements in the ecological condition of some rivers. Despite the volume of material available, much of the work remains temporally, spatially, or technically isolated. Overcoming the isolation of studies would enhance the utility of information available for the region, but additional recommendations for improving monitoring can be made, such as a shift to site-specific analyses in streams and further use of industry-reported data. Integr Environ Assess Manag 2022;18:361-387. © 2021 The Authors. Integrated Environmental Assessment and Management published by Wiley Periodicals LLC on behalf of Society of Environmental Toxicology & Chemistry (SETAC).
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Affiliation(s)
- Tim J. Arciszewski
- Environmental Stewardship DivisionAlberta Environment and ParksCalgaryAlbertaCanada
| | | | - Monique G. Dubé
- Environmental Stewardship DivisionAlberta Environment and ParksCalgaryAlbertaCanada
- Present address: Cumulative Effects Environmental Inc.CalgaryAlbertaCanada
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Wong L, Noble B, Hanna K. Water Quality Monitoring to Support Cumulative Effects Assessment and Decision Making in the Mackenzie Valley, Northwest Territories, Canada. INTEGRATED ENVIRONMENTAL ASSESSMENT AND MANAGEMENT 2019; 15:988-999. [PMID: 31231934 DOI: 10.1002/ieam.4179] [Citation(s) in RCA: 0] [Impact Index Per Article: 0] [Reference Citation Analysis] [Abstract] [Key Words] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Received: 04/23/2019] [Revised: 05/15/2019] [Accepted: 06/17/2019] [Indexed: 06/09/2023]
Abstract
Project proponent- and government-led environmental monitoring are required to identify, understand, and manage cumulative effects (CE), yet such monitoring initiatives are rarely mutually supportive. Notwithstanding the need for a more integrated and complementary approach to monitoring, monitoring efforts are often less effective than intended for addressing CE. This paper examines current monitoring programs in the Mackenzie Valley, Northwest Territories, Canada, based on 7 attributes: consistency, compatibility, observability, detectability, adaptability, accessibility, and usability. Results indicate a tenuous link between and across proponent-led monitoring requirements under project-specific water licenses and government-led monitoring of regional baseline conditions. There is some consistency in what is monitored, but data are often incompatible, insufficient to understand baseline change, not transferable across projects or scales, inaccessible to end users, and ultimately unsuitable to understanding CE. Lessons from the Mackenzie Valley highlight the need for improved alignment of monitoring efforts across programs and scales, characterized by a set of common parameters that are most useful for early detection of cumulative change and supporting regulatory decisions at the project scale. This alignment must be accompanied by more open and accessible data for both proponents and regulators, while protecting the sensitivity of proprietary information. Importantly, there must be conceptual guidance for CE, such that the role of monitoring is clear, providing the types of CE questions to be asked, identifying the hypotheses to be tested, and ensuring timely and meaningful results to support regulatory decisions. © 2019 SETAC.
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Affiliation(s)
- Lindsay Wong
- Department of Geography and Planning, University of Saskatchewan, Saskatoon, Saskatchewan, Canada
| | - Bram Noble
- Department of Geography and Planning, University of Saskatchewan, Saskatoon, Saskatchewan, Canada
| | - Kevin Hanna
- Center for Environmental Assessment Research, University of British Columbia, Vancouver, British Columbia, Canada
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Arciszewski TJ, Hazewinkel RR, Munkittrick KR, Kilgour BW. Developing and applying control charts to detect changes in water chemistry parameters measured in the Athabasca River near the oil sands: A tool for surveillance monitoring. ENVIRONMENTAL TOXICOLOGY AND CHEMISTRY 2018; 37:2296-2311. [PMID: 29744924 DOI: 10.1002/etc.4168] [Citation(s) in RCA: 4] [Impact Index Per Article: 0.7] [Reference Citation Analysis] [Abstract] [Key Words] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Received: 02/15/2018] [Revised: 03/23/2018] [Accepted: 05/07/2018] [Indexed: 05/05/2023]
Abstract
Control charting is a simple technique to identify change and is well suited for use in water quality programs. Control charts accounting for covariation associated with discharge and in some cases time were used to explore example and representative variables routinely measured in the Athabasca River near the oil sands area for indications of change. The explored variables include 5 major ions (chloride, sodium, sulfate, calcium, magnesium), 5 total metals (aluminum, iron, thallium, molybdenum, vanadium), and total suspended solids at two sites straddling the developments north of Fort McMurray. Regression equations developed from reference data (1988-2009) were used to predict observations and calculate residuals from later test data (2010-2016). Evidence of change was sought in the deviation of residual errors from the test period compared with the patterns expected and defined from probability distributions of the reference residuals using the odds ratio. In most cases, the patterns in test residuals were not statistically different from those expected from the reference period at either site, especially when data were examined annually. However, differences were found at both locations, more were found at the downstream site, and more differences emerged as data accumulated and were analyzed over time. In sum, the analyses at the downstream site suggest higher concentrations than predicted in most major ions, but the source of the changes is uncertain. In contrast, the concentrations of most metals at during the test period were lower than expected, which may be related to deposition patterns of materials or weathering of minerals during construction activities of the 2000s which influence the reference data used. The analyses also suggest alternative approaches may be necessary to understand change in some variables. Despite this, the results support the use of control charts to detect changes in water chemistry parameters and the value of the tool in surveillance phases of long-term and adaptive monitoring programs. Environ Toxicol Chem 2018;37:2296-2311. © 2018 SETAC.
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Affiliation(s)
- Tim J Arciszewski
- Canada's Oil Sands Innovation Alliance (COSIA), Calgary, Alberta, Canada
| | | | - Kelly R Munkittrick
- Canada's Oil Sands Innovation Alliance (COSIA), Calgary, Alberta, Canada
- Wilfrid Laurier University, Waterloo, Ontario, Canada
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Cronmiller JG, Noble BF. Integrating environmental monitoring with cumulative effects management and decision making. INTEGRATED ENVIRONMENTAL ASSESSMENT AND MANAGEMENT 2018; 14:407-417. [PMID: 29418066 DOI: 10.1002/ieam.4034] [Citation(s) in RCA: 1] [Impact Index Per Article: 0.2] [Reference Citation Analysis] [Abstract] [Key Words] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Received: 08/17/2017] [Revised: 11/26/2017] [Accepted: 02/04/2018] [Indexed: 06/08/2023]
Abstract
Cumulative effects (CE) monitoring is foundational to emerging regional and watershed CE management frameworks, yet monitoring is often poorly integrated with CE management and decision-making processes. The challenges are largely institutional and organizational, more so than scientific or technical. Calls for improved integration of monitoring with CE management and decision making are not new, but there has been limited research on how best to integrate environmental monitoring programs to ensure credible CE science and to deliver results that respond to the more immediate questions and needs of regulatory decision makers. This paper examines options for the integration of environmental monitoring with CE frameworks. Based on semistructured interviews with practitioners, regulators, and other experts in the Lower Athabasca, Alberta, Canada, 3 approaches to monitoring system design are presented. First, a distributed monitoring system, reflecting the current approach in the Lower Athabasca, where monitoring is delegated to different external programs and organizations; second, a 1-window system in which monitoring is undertaken by a single, in-house agency for the purpose of informing management and regulatory decision making; third, an independent system driven primarily by CE science and understanding causal relationships, with knowledge adopted for decision support where relevant to specific management questions. The strengths and limitations of each approach are presented. A hybrid approach may be optimal-an independent, nongovernment, 1-window model for CE science, monitoring, and information delivery-capitalizing on the strengths of distributed, 1-window, and independent monitoring systems while mitigating their weaknesses. If governments are committed to solving CE problems, they must invest in the long-term science needed to do so; at the same time, if science-based monitoring programs are to be sustainable over the long term, they must be responsive to the more immediate, often shorter term needs and CE information requirements of decision makers. Integr Environ Assess Manag 2018;14:407-417. © 2018 SETAC.
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Affiliation(s)
- Joshua G Cronmiller
- Department of Geography and Planning, University of Saskatchewan, Saskatoon, Saskatchewan, Canada
| | - Bram F Noble
- Department of Geography and Planning, University of Saskatchewan, Saskatoon, Saskatchewan, Canada
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Arciszewski TJ, Munkittrick KR, Kilgour BW, Keith HM, Linehan JE, McMaster ME. Increased size and relative abundance of migratory fishes observed near the Athabasca oil sands. Facets (Ott) 2017. [DOI: 10.1139/facets-2017-0028] [Citation(s) in RCA: 14] [Impact Index Per Article: 2.0] [Reference Citation Analysis] [Abstract] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Indexed: 11/22/2022] Open
Abstract
Responses to chemical and physical stressors are commonly expected among organisms residing near the Athabasca oil sands. Physiological effects have been observed in fishes during field studies; but further effects associated with development are not clear or consistent among species. For instance, data from a fish fence in 2009 show declines in the relative abundances of some species, including Arctic grayling ( Thymallus arcticus). In contrast, increases were seen in white sucker ( Catostomus commersoni). This divergence suggests incomplete understanding of the status of fishes residing near the oil sands. However, an important challenge limiting understanding is the lack of reliable baseline or reference data. To overcome this challenge, we used iterative normal ranges and a historical data set (electrofishing surveys done from 1987 to 2014) to determine if changes have occurred in fishes captured in the lower Athabasca River. These analyses revealed clear increases in the lengths of white sucker and walleye ( Sander vitreus) and their relative abundances during the spawning season. The occurrence of these changes may be associated with overwintering location, but reduced fishing pressure in Lake Athabasca, eutrophication, or a cumulative effect may explain the form of changes detected in this study.
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Affiliation(s)
- Tim J. Arciszewski
- Canada’s Oil Sands Innovation Alliance (COSIA), Calgary, AB T2P 3R7, Canada
| | | | | | - Heather M. Keith
- Hatfield Consultants Partnership, North Vancouver, BC V7P 0A3, Canada
| | | | - Mark E. McMaster
- Environment and Climate Change Canada (ECCC), Burlington, ON L7S 1A1, Canada
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Dubé MG, Duinker P, Greig L, Carver M, Servos M, McMaster M, Noble B, Schreier H, Jackson L, Munkittrick KR. A framework for assessing cumulative effects in watersheds: an introduction to Canadian case studies. INTEGRATED ENVIRONMENTAL ASSESSMENT AND MANAGEMENT 2013; 9:363-369. [PMID: 23553957 DOI: 10.1002/ieam.1418] [Citation(s) in RCA: 9] [Impact Index Per Article: 0.8] [Reference Citation Analysis] [Abstract] [Key Words] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Received: 11/19/2012] [Revised: 12/31/2012] [Accepted: 03/19/2013] [Indexed: 06/02/2023]
Abstract
From 2008 to 2013, a series of studies supported by the Canadian Water Network were conducted in Canadian watersheds in an effort to improve methods to assess cumulative effects. These studies fit under a common framework for watershed cumulative effects assessment (CEA). This article presents an introduction to the Special Series on Watershed CEA in IEAM including the framework and its impetus, a brief introduction to each of the articles in the series, challenges, and a path forward. The framework includes a regional water monitoring program that produces 3 core outputs: an accumulated state assessment, stressor-response relationships, and development of predictive cumulative effects scenario models. The framework considers core values, indicators, thresholds, and use of consistent terminology. It emphasizes that CEA requires 2 components, accumulated state quantification and predictive scenario forecasting. It recognizes both of these components must be supported by a regional, multiscale monitoring program.
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Affiliation(s)
- Monique G Dubé
- Canadian Rivers Institute, University of New Brunswick, Alberta, Canada.
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