The active methanotrophic community in a wetland from the High Arctic

Summary The dominant terminal process of carbon mineralization in most freshwater wetlands is methanogenesis. With methane being an important greenhouse gas, the predicted warming of the Arctic may provide a positive feedback. However, the amount of methane released to the atmosphere may be controll...

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Published in:Environmental Microbiology Reports
Main Authors: Graef, Christiane, Hestnes, Anne Grethe, Svenning, Mette Marianne, Frenzel, Peter
Format: Article in Journal/Newspaper
Language:English
Published: Wiley 2011
Subjects:
Online Access:http://dx.doi.org/10.1111/j.1758-2229.2010.00237.x
https://api.wiley.com/onlinelibrary/tdm/v1/articles/10.1111%2Fj.1758-2229.2010.00237.x
http://onlinelibrary.wiley.com/wol1/doi/10.1111/j.1758-2229.2010.00237.x/fullpdf
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spelling crwiley:10.1111/j.1758-2229.2010.00237.x 2024-09-15T18:27:19+00:00 The active methanotrophic community in a wetland from the High Arctic Graef, Christiane Hestnes, Anne Grethe Svenning, Mette Marianne Frenzel, Peter 2011 http://dx.doi.org/10.1111/j.1758-2229.2010.00237.x https://api.wiley.com/onlinelibrary/tdm/v1/articles/10.1111%2Fj.1758-2229.2010.00237.x http://onlinelibrary.wiley.com/wol1/doi/10.1111/j.1758-2229.2010.00237.x/fullpdf en eng Wiley http://onlinelibrary.wiley.com/termsAndConditions#vor Environmental Microbiology Reports volume 3, issue 4, page 466-472 ISSN 1758-2229 1758-2229 journal-article 2011 crwiley https://doi.org/10.1111/j.1758-2229.2010.00237.x 2024-08-27T04:27:20Z Summary The dominant terminal process of carbon mineralization in most freshwater wetlands is methanogenesis. With methane being an important greenhouse gas, the predicted warming of the Arctic may provide a positive feedback. However, the amount of methane released to the atmosphere may be controlled by the activity of methane‐oxidizing bacteria (methanotrophs) living in the oxic surface layer of wetlands. Previously, methanotrophs have been isolated and identified by genetic profiling in High Arctic wetlands showing the presence of only a few genotypes. Two isolates from Solvatnet (Ny‐Ålesund, Spitsbergen; 79°N) are available: Methylobacter tundripaludum (type I) and Methylocystis rosea (type II), raising the question whether the low diversity is a cultivation effect. We have revisited Solvatnet applying stable isotope probing (SIP) with 13 C‐labelled methane. 16S rRNA profiling revealed active type I methanotrophs including M. tundripaludum , while no active type II methanotrophs were identified. These results indicate that the extant M. tundripaludum is an active methane oxidizer at its locus typicus; furthermore, Methylobacter seems to be the dominant active genus. Diversity of methanotrophs was low as compared, e.g. to wetland rice fields in the Mediterranean. This low diversity suggests a high vulnerability of Arctic methanotroph communities, which deserves more attention. Article in Journal/Newspaper Ny Ålesund Ny-Ålesund Spitsbergen Wiley Online Library Environmental Microbiology Reports 3 4 466 472
institution Open Polar
collection Wiley Online Library
op_collection_id crwiley
language English
description Summary The dominant terminal process of carbon mineralization in most freshwater wetlands is methanogenesis. With methane being an important greenhouse gas, the predicted warming of the Arctic may provide a positive feedback. However, the amount of methane released to the atmosphere may be controlled by the activity of methane‐oxidizing bacteria (methanotrophs) living in the oxic surface layer of wetlands. Previously, methanotrophs have been isolated and identified by genetic profiling in High Arctic wetlands showing the presence of only a few genotypes. Two isolates from Solvatnet (Ny‐Ålesund, Spitsbergen; 79°N) are available: Methylobacter tundripaludum (type I) and Methylocystis rosea (type II), raising the question whether the low diversity is a cultivation effect. We have revisited Solvatnet applying stable isotope probing (SIP) with 13 C‐labelled methane. 16S rRNA profiling revealed active type I methanotrophs including M. tundripaludum , while no active type II methanotrophs were identified. These results indicate that the extant M. tundripaludum is an active methane oxidizer at its locus typicus; furthermore, Methylobacter seems to be the dominant active genus. Diversity of methanotrophs was low as compared, e.g. to wetland rice fields in the Mediterranean. This low diversity suggests a high vulnerability of Arctic methanotroph communities, which deserves more attention.
format Article in Journal/Newspaper
author Graef, Christiane
Hestnes, Anne Grethe
Svenning, Mette Marianne
Frenzel, Peter
spellingShingle Graef, Christiane
Hestnes, Anne Grethe
Svenning, Mette Marianne
Frenzel, Peter
The active methanotrophic community in a wetland from the High Arctic
author_facet Graef, Christiane
Hestnes, Anne Grethe
Svenning, Mette Marianne
Frenzel, Peter
author_sort Graef, Christiane
title The active methanotrophic community in a wetland from the High Arctic
title_short The active methanotrophic community in a wetland from the High Arctic
title_full The active methanotrophic community in a wetland from the High Arctic
title_fullStr The active methanotrophic community in a wetland from the High Arctic
title_full_unstemmed The active methanotrophic community in a wetland from the High Arctic
title_sort active methanotrophic community in a wetland from the high arctic
publisher Wiley
publishDate 2011
url http://dx.doi.org/10.1111/j.1758-2229.2010.00237.x
https://api.wiley.com/onlinelibrary/tdm/v1/articles/10.1111%2Fj.1758-2229.2010.00237.x
http://onlinelibrary.wiley.com/wol1/doi/10.1111/j.1758-2229.2010.00237.x/fullpdf
genre Ny Ålesund
Ny-Ålesund
Spitsbergen
genre_facet Ny Ålesund
Ny-Ålesund
Spitsbergen
op_source Environmental Microbiology Reports
volume 3, issue 4, page 466-472
ISSN 1758-2229 1758-2229
op_rights http://onlinelibrary.wiley.com/termsAndConditions#vor
op_doi https://doi.org/10.1111/j.1758-2229.2010.00237.x
container_title Environmental Microbiology Reports
container_volume 3
container_issue 4
container_start_page 466
op_container_end_page 472
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