Ecotoxicological effects of fluvial eroded bitumen sediments from the Alberta oil sands to model aquatic species

Detalhes bibliográficos
Autor(a) principal: Cardoso, Diogo N.
Data de Publicação: 2023
Outros Autores: Gonçalves, Sandra F., Silva, Ana Rita R., Soares, Amadeu M. V. M., Wrona, Frederick J., Loureiro, Susana
Tipo de documento: Artigo
Idioma: eng
Título da fonte: Repositório Científico de Acesso Aberto de Portugal (Repositórios Cientìficos)
Texto Completo: http://hdl.handle.net/10773/37061
Resumo: To fully understand the ecological and cumulative effects of mining activities on the surrounding aquatic systems of the Canadian oil sands region, it is essential to understand the consequences of exposure to bitumen-containing soils/sediment from natural geomorphological processes. Both physical and chemical stress on aquatic biota can potentially result from exposure to natural bitumen, resulting from hillslope erosional processes and slumping of bankside soils into the rivers, affecting both riverbed habitat and water quality. The magnitude and duration of bitumen-containing soil's fluvial soils/erosional input into receiving watersheds depends on the interannual variability in the regional hydroclimatology and related seasonal and extreme flow events. The primary objective of this study was to evaluate the potential ecotoxicological effects associated with erosional input of riverbank bitumen soils using controlled exposures. A series of integrated, laboratory-based ecotoxicological bioassays were conducted using organisms with different ecological and functional traits (Daphnia magna (Cladocera), Physa acuta (Gastropoda), and Aliivibrio fischeri (Bacteria)). All model organisms were exposed to elutriates produced from natural bitumen from four different regional rivers: fresh bitumen from shoreline outcrops at the Steepbank River upper and lower reaches (STB-CF and STB-MF, respectively) and the lower-Ells River (EL-MF) and aged, fluvially processed/weathered bitumen from the shoreline of the Athabasca River (ATB-MF). All tested organisms responded negatively to STB-MF and EL-MF elutriates. Low toxicity was also observed in the STB-CF and ATB-MF samples. These results follow the chemical analysis of the parental material and elutriates, where higher levels of metals, polycyclic aromatic compounds and naphthenic acids were detected in the EL-MF sample. In summary, this study shows that eroded and transported bitumen-containing soils and sediments could be a natural source of contaminant exposure to aquatic biota. This fluvial pathway should be considered when assessing background toxicity and the toxicological and ecological effects of oil sands mining activities.
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spelling Ecotoxicological effects of fluvial eroded bitumen sediments from the Alberta oil sands to model aquatic speciesBitumen elutriate toxicityNatural contaminationWeathered bitumenFluvial erosionTo fully understand the ecological and cumulative effects of mining activities on the surrounding aquatic systems of the Canadian oil sands region, it is essential to understand the consequences of exposure to bitumen-containing soils/sediment from natural geomorphological processes. Both physical and chemical stress on aquatic biota can potentially result from exposure to natural bitumen, resulting from hillslope erosional processes and slumping of bankside soils into the rivers, affecting both riverbed habitat and water quality. The magnitude and duration of bitumen-containing soil's fluvial soils/erosional input into receiving watersheds depends on the interannual variability in the regional hydroclimatology and related seasonal and extreme flow events. The primary objective of this study was to evaluate the potential ecotoxicological effects associated with erosional input of riverbank bitumen soils using controlled exposures. A series of integrated, laboratory-based ecotoxicological bioassays were conducted using organisms with different ecological and functional traits (Daphnia magna (Cladocera), Physa acuta (Gastropoda), and Aliivibrio fischeri (Bacteria)). All model organisms were exposed to elutriates produced from natural bitumen from four different regional rivers: fresh bitumen from shoreline outcrops at the Steepbank River upper and lower reaches (STB-CF and STB-MF, respectively) and the lower-Ells River (EL-MF) and aged, fluvially processed/weathered bitumen from the shoreline of the Athabasca River (ATB-MF). All tested organisms responded negatively to STB-MF and EL-MF elutriates. Low toxicity was also observed in the STB-CF and ATB-MF samples. These results follow the chemical analysis of the parental material and elutriates, where higher levels of metals, polycyclic aromatic compounds and naphthenic acids were detected in the EL-MF sample. In summary, this study shows that eroded and transported bitumen-containing soils and sediments could be a natural source of contaminant exposure to aquatic biota. This fluvial pathway should be considered when assessing background toxicity and the toxicological and ecological effects of oil sands mining activities.Elsevier2025-03-01T00:00:00Z2023-03-01T00:00:00Z2023-03-01info:eu-repo/semantics/publishedVersioninfo:eu-repo/semantics/articleapplication/pdfhttp://hdl.handle.net/10773/37061eng0048-969710.1016/j.scitotenv.2022.160592Cardoso, Diogo N.Gonçalves, Sandra F.Silva, Ana Rita R.Soares, Amadeu M. V. M.Wrona, Frederick J.Loureiro, Susanainfo:eu-repo/semantics/embargoedAccessreponame:Repositório Científico de Acesso Aberto de Portugal (Repositórios Cientìficos)instname:Agência para a Sociedade do Conhecimento (UMIC) - FCT - Sociedade da Informaçãoinstacron:RCAAP2024-02-22T12:11:29Zoai:ria.ua.pt:10773/37061Portal AgregadorONGhttps://www.rcaap.pt/oai/openaireopendoar:71602024-03-20T03:07:43.548760Repositório Científico de Acesso Aberto de Portugal (Repositórios Cientìficos) - Agência para a Sociedade do Conhecimento (UMIC) - FCT - Sociedade da Informaçãofalse
dc.title.none.fl_str_mv Ecotoxicological effects of fluvial eroded bitumen sediments from the Alberta oil sands to model aquatic species
title Ecotoxicological effects of fluvial eroded bitumen sediments from the Alberta oil sands to model aquatic species
spellingShingle Ecotoxicological effects of fluvial eroded bitumen sediments from the Alberta oil sands to model aquatic species
Cardoso, Diogo N.
Bitumen elutriate toxicity
Natural contamination
Weathered bitumen
Fluvial erosion
title_short Ecotoxicological effects of fluvial eroded bitumen sediments from the Alberta oil sands to model aquatic species
title_full Ecotoxicological effects of fluvial eroded bitumen sediments from the Alberta oil sands to model aquatic species
title_fullStr Ecotoxicological effects of fluvial eroded bitumen sediments from the Alberta oil sands to model aquatic species
title_full_unstemmed Ecotoxicological effects of fluvial eroded bitumen sediments from the Alberta oil sands to model aquatic species
title_sort Ecotoxicological effects of fluvial eroded bitumen sediments from the Alberta oil sands to model aquatic species
author Cardoso, Diogo N.
author_facet Cardoso, Diogo N.
Gonçalves, Sandra F.
Silva, Ana Rita R.
Soares, Amadeu M. V. M.
Wrona, Frederick J.
Loureiro, Susana
author_role author
author2 Gonçalves, Sandra F.
Silva, Ana Rita R.
Soares, Amadeu M. V. M.
Wrona, Frederick J.
Loureiro, Susana
author2_role author
author
author
author
author
dc.contributor.author.fl_str_mv Cardoso, Diogo N.
Gonçalves, Sandra F.
Silva, Ana Rita R.
Soares, Amadeu M. V. M.
Wrona, Frederick J.
Loureiro, Susana
dc.subject.por.fl_str_mv Bitumen elutriate toxicity
Natural contamination
Weathered bitumen
Fluvial erosion
topic Bitumen elutriate toxicity
Natural contamination
Weathered bitumen
Fluvial erosion
description To fully understand the ecological and cumulative effects of mining activities on the surrounding aquatic systems of the Canadian oil sands region, it is essential to understand the consequences of exposure to bitumen-containing soils/sediment from natural geomorphological processes. Both physical and chemical stress on aquatic biota can potentially result from exposure to natural bitumen, resulting from hillslope erosional processes and slumping of bankside soils into the rivers, affecting both riverbed habitat and water quality. The magnitude and duration of bitumen-containing soil's fluvial soils/erosional input into receiving watersheds depends on the interannual variability in the regional hydroclimatology and related seasonal and extreme flow events. The primary objective of this study was to evaluate the potential ecotoxicological effects associated with erosional input of riverbank bitumen soils using controlled exposures. A series of integrated, laboratory-based ecotoxicological bioassays were conducted using organisms with different ecological and functional traits (Daphnia magna (Cladocera), Physa acuta (Gastropoda), and Aliivibrio fischeri (Bacteria)). All model organisms were exposed to elutriates produced from natural bitumen from four different regional rivers: fresh bitumen from shoreline outcrops at the Steepbank River upper and lower reaches (STB-CF and STB-MF, respectively) and the lower-Ells River (EL-MF) and aged, fluvially processed/weathered bitumen from the shoreline of the Athabasca River (ATB-MF). All tested organisms responded negatively to STB-MF and EL-MF elutriates. Low toxicity was also observed in the STB-CF and ATB-MF samples. These results follow the chemical analysis of the parental material and elutriates, where higher levels of metals, polycyclic aromatic compounds and naphthenic acids were detected in the EL-MF sample. In summary, this study shows that eroded and transported bitumen-containing soils and sediments could be a natural source of contaminant exposure to aquatic biota. This fluvial pathway should be considered when assessing background toxicity and the toxicological and ecological effects of oil sands mining activities.
publishDate 2023
dc.date.none.fl_str_mv 2023-03-01T00:00:00Z
2023-03-01
2025-03-01T00:00:00Z
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dc.identifier.uri.fl_str_mv http://hdl.handle.net/10773/37061
url http://hdl.handle.net/10773/37061
dc.language.iso.fl_str_mv eng
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dc.relation.none.fl_str_mv 0048-9697
10.1016/j.scitotenv.2022.160592
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dc.publisher.none.fl_str_mv Elsevier
publisher.none.fl_str_mv Elsevier
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