Summary of the Workshop on Ecological Effects of Hydrocarbon Spills in Alaska

In any study of the effects of the introduction of an organic compound, such as oil, into a particular environment, such as the Arctic we should, at the outset separate two basic responses: the responses of those organisms (largely bacteria and fungi) to whom the oil is a nutrient to be attacked and...

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Published in:ARCTIC
Main Authors: Costerton, J.W., Brunskill, G.J., Hutchinson, T., Widden, P.
Format: Article in Journal/Newspaper
Language:English
Published: The Arctic Institute of North America 1978
Subjects:
Online Access:https://journalhosting.ucalgary.ca/index.php/arctic/article/view/65720
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author Costerton, J.W.
Brunskill, G.J.
Hutchinson, T.
Widden, P.
author_facet Costerton, J.W.
Brunskill, G.J.
Hutchinson, T.
Widden, P.
author_sort Costerton, J.W.
collection Unknown
container_issue 3
container_title ARCTIC
container_volume 31
description In any study of the effects of the introduction of an organic compound, such as oil, into a particular environment, such as the Arctic we should, at the outset separate two basic responses: the responses of those organisms (largely bacteria and fungi) to whom the oil is a nutrient to be attacked and eventually decomposed, from the responses of those organisms (largely plants and animals) to whom the oil is a physical and chemical agent of potential toxicity to be tolerated with varying degrees of success. . both groups really function as mixed populations that exhibit dynamic responses to environmental changes, such as oil spills, but our perception of the effects of these changes is largely population-oriented in the decomposers and species-oriented among higher organisms. . The actual removal of oil from the Arctic environment depends on a combination of physical weathering and microbial decomposition . Thus a general principle of microbial ecology is sustained here in that the addition of an organic material to a system stimulates the development of a specific microbial population capable of using that material as a nutrient. The rate of this decomposition process is of maximum importance and it obviously depends on the robustness of the initial microbial population and on nutrient limitation. . One of the special problems of the Arctic is the very slow rate at which these decomposer populations develop significant activities . and accessory nutrient supplementations may be required to achieve acceptable rates of hydrocarbon decomposition. A very important facet of oil degradation is the relative rates at which the different components of oil are broken down by bacteria and fungi. . There are many reasons why oil may be toxic to animals . Oil appears to constitute a fairly general "contact herbicide" whose direct application is most often toxic to plants. . plants vary in their sensitivity to this "contact herbicide" and sensitivity mapping . and bioassays of the sensitivity of specific plants under field ...
format Article in Journal/Newspaper
genre Arctic
Arctic
Alaska
genre_facet Arctic
Arctic
Alaska
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op_source ARCTIC; Vol. 31 No. 3 (1978): September: 153–411; 408-411
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spelling ftunivcalgaryojs:oai:journalhosting.ucalgary.ca:article/65720 2025-06-15T14:14:26+00:00 Summary of the Workshop on Ecological Effects of Hydrocarbon Spills in Alaska Costerton, J.W. Brunskill, G.J. Hutchinson, T. Widden, P. 1978-01-01 application/pdf https://journalhosting.ucalgary.ca/index.php/arctic/article/view/65720 eng eng The Arctic Institute of North America https://journalhosting.ucalgary.ca/index.php/arctic/article/view/65720/49634 https://journalhosting.ucalgary.ca/index.php/arctic/article/view/65720 ARCTIC; Vol. 31 No. 3 (1978): September: 153–411; 408-411 1923-1245 0004-0843 Animals Bacteria Biomass Biodegradation Environmental impacts Fertilizers Fungi Microbial ecology Oil spills Oil spill cleanup Plants (Biology) Soil microorganisms Toxicity Weathering Alaska info:eu-repo/semantics/article info:eu-repo/semantics/publishedVersion research-article 1978 ftunivcalgaryojs 2025-05-27T03:29:43Z In any study of the effects of the introduction of an organic compound, such as oil, into a particular environment, such as the Arctic we should, at the outset separate two basic responses: the responses of those organisms (largely bacteria and fungi) to whom the oil is a nutrient to be attacked and eventually decomposed, from the responses of those organisms (largely plants and animals) to whom the oil is a physical and chemical agent of potential toxicity to be tolerated with varying degrees of success. . both groups really function as mixed populations that exhibit dynamic responses to environmental changes, such as oil spills, but our perception of the effects of these changes is largely population-oriented in the decomposers and species-oriented among higher organisms. . The actual removal of oil from the Arctic environment depends on a combination of physical weathering and microbial decomposition . Thus a general principle of microbial ecology is sustained here in that the addition of an organic material to a system stimulates the development of a specific microbial population capable of using that material as a nutrient. The rate of this decomposition process is of maximum importance and it obviously depends on the robustness of the initial microbial population and on nutrient limitation. . One of the special problems of the Arctic is the very slow rate at which these decomposer populations develop significant activities . and accessory nutrient supplementations may be required to achieve acceptable rates of hydrocarbon decomposition. A very important facet of oil degradation is the relative rates at which the different components of oil are broken down by bacteria and fungi. . There are many reasons why oil may be toxic to animals . Oil appears to constitute a fairly general "contact herbicide" whose direct application is most often toxic to plants. . plants vary in their sensitivity to this "contact herbicide" and sensitivity mapping . and bioassays of the sensitivity of specific plants under field ... Article in Journal/Newspaper Arctic Arctic Alaska Unknown Arctic ARCTIC 31 3
spellingShingle Animals
Bacteria
Biomass
Biodegradation
Environmental impacts
Fertilizers
Fungi
Microbial ecology
Oil spills
Oil spill cleanup
Plants (Biology)
Soil microorganisms
Toxicity
Weathering
Alaska
Costerton, J.W.
Brunskill, G.J.
Hutchinson, T.
Widden, P.
Summary of the Workshop on Ecological Effects of Hydrocarbon Spills in Alaska
title Summary of the Workshop on Ecological Effects of Hydrocarbon Spills in Alaska
title_full Summary of the Workshop on Ecological Effects of Hydrocarbon Spills in Alaska
title_fullStr Summary of the Workshop on Ecological Effects of Hydrocarbon Spills in Alaska
title_full_unstemmed Summary of the Workshop on Ecological Effects of Hydrocarbon Spills in Alaska
title_short Summary of the Workshop on Ecological Effects of Hydrocarbon Spills in Alaska
title_sort summary of the workshop on ecological effects of hydrocarbon spills in alaska
topic Animals
Bacteria
Biomass
Biodegradation
Environmental impacts
Fertilizers
Fungi
Microbial ecology
Oil spills
Oil spill cleanup
Plants (Biology)
Soil microorganisms
Toxicity
Weathering
Alaska
topic_facet Animals
Bacteria
Biomass
Biodegradation
Environmental impacts
Fertilizers
Fungi
Microbial ecology
Oil spills
Oil spill cleanup
Plants (Biology)
Soil microorganisms
Toxicity
Weathering
Alaska
url https://journalhosting.ucalgary.ca/index.php/arctic/article/view/65720