Response of soil bacterial community to biochar application in a boreal pine forest
Boreal forests commonly suffer from nitrogen deficiency due to low rate of nitrogen mineralization. Biochar may promote soil organic matter decomposition and accelerate nitrogen mineralization. In this study, Illumina NovaSeq sequencing combined with functional annotation of prokaryotic taxa (FAPROT...
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Published in | Journal of forestry research Vol. 34; no. 3; pp. 749 - 759 |
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Main Authors | , , , , , , , , |
Format | Journal Article |
Language | English |
Published |
Singapore
Springer Nature Singapore
01.06.2023
Springer Springer Nature B.V Department of Forest Sciences, University of Helsinki,Latokartanonkaari 7, P. O. Box 27, 00014 Helsinki, Finland Collaborative Innovation Center of Sustainable Forestry in Southern China, College of Forestry, Nanjing Forestry University, Nanjing 210037, China%Department of Forest Sciences, University of Helsinki,Latokartanonkaari 7, P. O. Box 27, 00014 Helsinki, Finland%Department of Environmental and Biological Sciences,University of Eastern Finland, Yliopistonranta 1 E,P. O. Box 1627, 70211 Kuopio, Finland%Collaborative Innovation Center of Sustainable Forestry in Southern China, College of Forestry, Nanjing Forestry University, Nanjing 210037, China |
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Online Access | Get full text |
ISSN | 1007-662X 1993-0607 |
DOI | 10.1007/s11676-022-01509-x |
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Abstract | Boreal forests commonly suffer from nitrogen deficiency due to low rate of nitrogen mineralization. Biochar may promote soil organic matter decomposition and accelerate nitrogen mineralization. In this study, Illumina NovaSeq sequencing combined with functional annotation of prokaryotic taxa (FAPROTAX) analysis was used to investigate the effect of biochar pyrolysis temperatures, the amount of applied biochar, and the period since the biochar application (2- and 3-year) on soil bacterial communities. The results show that biochar pyrolysis temperatures (500 °C and 650 °C) and the amount of applied biochar (0.5 kg m
−2
and 1.0 kg m
−2
) did not change soil properties. Nevertheless, the interaction of biochar pyrolysis temperature and the amount had significant effects on bacterial species richness and evenness (
P
< 0.05). The application of biochar produced at 500 °C had a lower abundance of Actinobacteria and Verrucomicrobia, while that produced at 650 °C had a higher abundance of
Conexibacter
and
Phenylobacterium.
When biochar produced at 650 °C was applied, applying 0.5 kg m
−2
had a higher abundance of
Cyanobacteria
,
Conexibacter
, and
Phenylobacterium
than that of 1.0 kg m
−2
(
P
< 0.05). Functionally, the abundance of the aromatic compound degradation group increased with the extension of application time and increase of pyrolysis temperature. The time since application played an important role in the formation of soil bacterial communities and their functional structure. Long-term studies are necessary to understand the consequence of biochar on bacterial communities in boreal forests. |
---|---|
AbstractList | Boreal forests commonly suffer from nitrogen deficiency due to low rate of nitrogen mineralization. Biochar may promote soil organic matter decomposition and accelerate nitrogen mineralization. In this study, Illumina NovaSeq sequencing combined with functional annotation of prokaryotic taxa (FAPROTAX) analysis was used to investigate the effect of biochar pyrolysis temperatures, the amount of applied biochar, and the period since the biochar application (2- and 3-year) on soil bacterial communities. The results show that biochar pyrolysis temperatures (500 °C and 650 °C) and the amount of applied biochar (0.5 kg m
−2
and 1.0 kg m
−2
) did not change soil properties. Nevertheless, the interaction of biochar pyrolysis temperature and the amount had significant effects on bacterial species richness and evenness (
P
< 0.05). The application of biochar produced at 500 °C had a lower abundance of Actinobacteria and Verrucomicrobia, while that produced at 650 °C had a higher abundance of
Conexibacter
and
Phenylobacterium.
When biochar produced at 650 °C was applied, applying 0.5 kg m
−2
had a higher abundance of
Cyanobacteria
,
Conexibacter
, and
Phenylobacterium
than that of 1.0 kg m
−2
(
P
< 0.05). Functionally, the abundance of the aromatic compound degradation group increased with the extension of application time and increase of pyrolysis temperature. The time since application played an important role in the formation of soil bacterial communities and their functional structure. Long-term studies are necessary to understand the consequence of biochar on bacterial communities in boreal forests. Boreal forests commonly suffer from nitrogen deficiency due to low rate of nitrogen mineralization.Bio-char may promote soil organic matter decomposition and accelerate nitrogen mineralization.In this study,Illumina NovaS eq sequencing combined with functional annotation of prokaryotic taxa(FAPROTAX)analysis was used to investigate the effect of biochar pyrolysis temperatures,the amount of applied biochar,and the period since the biochar application(2-and 3-year)on soil bacterial communities.The results show that biochar pyrolysis temperatures(500℃and 650℃)and the amount of applied biochar(0.5 kg m-2 and 1.0 kg m-2)did not change soil properties.Neverthe-less,the interaction of biochar pyrolysis temperature and the amount had significant effects on bacterial species richness and evenness(P<0.05).The application of biochar pro-duced at 500℃had a lower abundance of Actinobacteria and Verrucomicrobia,while that produced at 650℃had a higher abundance of Conexibacter and Phenylobacterium.When biochar produced at 650℃was applied,applying 0.5 kg m-2 had a higher abundance of Cyanobacteria,Conexibacter,and Phenylobacterium than that of 1.0 kg m-2(P<0.05).Functionally,the abundance of the aromatic compound degradation group increased with the extension of application time and increase of pyrolysis temperature.The time since application played an important role in the formation of soil bacterial communities and their functional structure.Long-term studies are necessary to understand the consequence of biochar on bacterial communities in boreal forests. Boreal forests commonly suffer from nitrogen deficiency due to low rate of nitrogen mineralization. Biochar may promote soil organic matter decomposition and accelerate nitrogen mineralization. In this study, Illumina NovaSeq sequencing combined with functional annotation of prokaryotic taxa (FAPROTAX) analysis was used to investigate the effect of biochar pyrolysis temperatures, the amount of applied biochar, and the period since the biochar application (2- and 3-year) on soil bacterial communities. The results show that biochar pyrolysis temperatures (500 °C and 650 °C) and the amount of applied biochar (0.5 kg m−2 and 1.0 kg m−2) did not change soil properties. Nevertheless, the interaction of biochar pyrolysis temperature and the amount had significant effects on bacterial species richness and evenness (P < 0.05). The application of biochar produced at 500 °C had a lower abundance of Actinobacteria and Verrucomicrobia, while that produced at 650 °C had a higher abundance of Conexibacter and Phenylobacterium. When biochar produced at 650 °C was applied, applying 0.5 kg m−2 had a higher abundance of Cyanobacteria, Conexibacter, and Phenylobacterium than that of 1.0 kg m−2 (P < 0.05). Functionally, the abundance of the aromatic compound degradation group increased with the extension of application time and increase of pyrolysis temperature. The time since application played an important role in the formation of soil bacterial communities and their functional structure. Long-term studies are necessary to understand the consequence of biochar on bacterial communities in boreal forests. Boreal forests commonly suffer from nitrogen deficiency due to low rate of nitrogen mineralization. Biochar may promote soil organic matter decomposition and accelerate nitrogen mineralization. In this study, Illumina NovaSeq sequencing combined with functional annotation of prokaryotic taxa (FAPROTAX) analysis was used to investigate the effect of biochar pyrolysis temperatures, the amount of applied biochar, and the period since the biochar application (2- and 3-year) on soil bacterial communities. The results show that biochar pyrolysis temperatures (500 °C and 650 °C) and the amount of applied biochar (0.5 kg m.sup.-2 and 1.0 kg m.sup.-2) did not change soil properties. Nevertheless, the interaction of biochar pyrolysis temperature and the amount had significant effects on bacterial species richness and evenness (P < 0.05). The application of biochar produced at 500 °C had a lower abundance of Actinobacteria and Verrucomicrobia, while that produced at 650 °C had a higher abundance of Conexibacter and Phenylobacterium. When biochar produced at 650 °C was applied, applying 0.5 kg m.sup.-2 had a higher abundance of Cyanobacteria, Conexibacter, and Phenylobacterium than that of 1.0 kg m.sup.-2 (P < 0.05). Functionally, the abundance of the aromatic compound degradation group increased with the extension of application time and increase of pyrolysis temperature. The time since application played an important role in the formation of soil bacterial communities and their functional structure. Long-term studies are necessary to understand the consequence of biochar on bacterial communities in boreal forests. Boreal forests commonly suffer from nitrogen deficiency due to low rate of nitrogen mineralization. Biochar may promote soil organic matter decomposition and accelerate nitrogen mineralization. In this study, Illumina NovaSeq sequencing combined with functional annotation of prokaryotic taxa (FAPROTAX) analysis was used to investigate the effect of biochar pyrolysis temperatures, the amount of applied biochar, and the period since the biochar application (2- and 3-year) on soil bacterial communities. The results show that biochar pyrolysis temperatures (500 °C and 650 °C) and the amount of applied biochar (0.5 kg m⁻² and 1.0 kg m⁻²) did not change soil properties. Nevertheless, the interaction of biochar pyrolysis temperature and the amount had significant effects on bacterial species richness and evenness (P < 0.05). The application of biochar produced at 500 °C had a lower abundance of Actinobacteria and Verrucomicrobia, while that produced at 650 °C had a higher abundance of Conexibacter and Phenylobacterium. When biochar produced at 650 °C was applied, applying 0.5 kg m⁻² had a higher abundance of Cyanobacteria, Conexibacter, and Phenylobacterium than that of 1.0 kg m⁻² (P < 0.05). Functionally, the abundance of the aromatic compound degradation group increased with the extension of application time and increase of pyrolysis temperature. The time since application played an important role in the formation of soil bacterial communities and their functional structure. Long-term studies are necessary to understand the consequence of biochar on bacterial communities in boreal forests. |
Audience | Academic |
Author | Li, Xiao-li Heinonsalo, Jussi Berninger, Frank Köster, Kajar Palviainen, Marjo Sun, Hui Pumpanen, Jukka Ge, Yan Zhou, Xuan |
AuthorAffiliation | Collaborative Innovation Center of Sustainable Forestry in Southern China, College of Forestry, Nanjing Forestry University, Nanjing 210037, China%Department of Forest Sciences, University of Helsinki,Latokartanonkaari 7, P. O. Box 27, 00014 Helsinki, Finland%Department of Environmental and Biological Sciences,University of Eastern Finland, Yliopistonranta 1 E,P. O. Box 1627, 70211 Kuopio, Finland%Collaborative Innovation Center of Sustainable Forestry in Southern China, College of Forestry, Nanjing Forestry University, Nanjing 210037, China;Department of Forest Sciences, University of Helsinki,Latokartanonkaari 7, P. O. Box 27, 00014 Helsinki, Finland |
AuthorAffiliation_xml | – name: Collaborative Innovation Center of Sustainable Forestry in Southern China, College of Forestry, Nanjing Forestry University, Nanjing 210037, China%Department of Forest Sciences, University of Helsinki,Latokartanonkaari 7, P. O. Box 27, 00014 Helsinki, Finland%Department of Environmental and Biological Sciences,University of Eastern Finland, Yliopistonranta 1 E,P. O. Box 1627, 70211 Kuopio, Finland%Collaborative Innovation Center of Sustainable Forestry in Southern China, College of Forestry, Nanjing Forestry University, Nanjing 210037, China;Department of Forest Sciences, University of Helsinki,Latokartanonkaari 7, P. O. Box 27, 00014 Helsinki, Finland |
Author_xml | – sequence: 1 givenname: Yan surname: Ge fullname: Ge, Yan organization: Collaborative Innovation Center of Sustainable Forestry in Southern China, College of Forestry, Nanjing Forestry University – sequence: 2 givenname: Xiao-li surname: Li fullname: Li, Xiao-li organization: Collaborative Innovation Center of Sustainable Forestry in Southern China, College of Forestry, Nanjing Forestry University – sequence: 3 givenname: Marjo surname: Palviainen fullname: Palviainen, Marjo organization: Department of Forest Sciences, University of Helsinki – sequence: 4 givenname: Xuan surname: Zhou fullname: Zhou, Xuan organization: Department of Environmental and Biological Sciences, University of Eastern Finland – sequence: 5 givenname: Jussi surname: Heinonsalo fullname: Heinonsalo, Jussi organization: Department of Forest Sciences, University of Helsinki – sequence: 6 givenname: Frank surname: Berninger fullname: Berninger, Frank organization: Department of Environmental and Biological Sciences, University of Eastern Finland – sequence: 7 givenname: Jukka surname: Pumpanen fullname: Pumpanen, Jukka organization: Department of Environmental and Biological Sciences, University of Eastern Finland – sequence: 8 givenname: Kajar surname: Köster fullname: Köster, Kajar organization: Department of Environmental and Biological Sciences, University of Eastern Finland – sequence: 9 givenname: Hui surname: Sun fullname: Sun, Hui email: hui.sun@njfu.edu.cn organization: Collaborative Innovation Center of Sustainable Forestry in Southern China, College of Forestry, Nanjing Forestry University, Department of Forest Sciences, University of Helsinki |
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Keywords | Boreal pine forests Bacterial communities Community function Biochar application |
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PublicationTitle | Journal of forestry research |
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PublicationYear | 2023 |
Publisher | Springer Nature Singapore Springer Springer Nature B.V Department of Forest Sciences, University of Helsinki,Latokartanonkaari 7, P. O. Box 27, 00014 Helsinki, Finland Collaborative Innovation Center of Sustainable Forestry in Southern China, College of Forestry, Nanjing Forestry University, Nanjing 210037, China%Department of Forest Sciences, University of Helsinki,Latokartanonkaari 7, P. O. Box 27, 00014 Helsinki, Finland%Department of Environmental and Biological Sciences,University of Eastern Finland, Yliopistonranta 1 E,P. O. Box 1627, 70211 Kuopio, Finland%Collaborative Innovation Center of Sustainable Forestry in Southern China, College of Forestry, Nanjing Forestry University, Nanjing 210037, China |
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Snippet | Boreal forests commonly suffer from nitrogen deficiency due to low rate of nitrogen mineralization. Biochar may promote soil organic matter decomposition and... Boreal forests commonly suffer from nitrogen deficiency due to low rate of nitrogen mineralization.Bio-char may promote soil organic matter decomposition and... |
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SubjectTerms | Abundance Actinobacteria Annotations application timing Aromatic compounds Bacteria biochar Biomedical and Life Sciences Boreal forests Carbon content Charcoal Coniferous forests Cyanobacteria Forestry Life Sciences Mineralization Nitrogen Organic matter Original Paper Phenylobacterium Pyrolysis soil Soil bacteria Soil formation Soil microbiology Soil microorganisms Soil organic matter Soil properties Soil temperature Soils Species richness Taiga temperature Trees Verrucomicrobia |
Title | Response of soil bacterial community to biochar application in a boreal pine forest |
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