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富营养化对海草生态系统沉积物、海水和叶际微生物群落结构的影响。

Impacts of eutrophication on microbial community structure in sediment, seawater, and phyllosphere of seagrass ecosystems.

作者信息

Deng Wenchao, Chen Shunyang, Chen Shiquan, Xing Bingpeng, Chan Zhuhua, Zhang Yao, Chen Bin, Chen Guangcheng

机构信息

Third Institute of Oceanography, Ministry of Natural Resources, Xiamen, China.

Observation and Research Station of Coastal Wetland Ecosystem in Beibu Gulf, Ministry of Natural Resources, Beihai, China.

出版信息

Front Microbiol. 2024 Aug 14;15:1449545. doi: 10.3389/fmicb.2024.1449545. eCollection 2024.

DOI:10.3389/fmicb.2024.1449545
PMID:39206368
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC11350616/
Abstract

INTRODUCTION

Seagrass-associated microbial communities play a crucial role in the growth and health of seagrasses. However, like seagrass meadows, seagrass-associated microbial communities are often affected by eutrophication. It remains unclear how eutrophication influences the composition and function of microbial communities associated with different parts of seagrass.

METHODS

We employed prokaryotic 16S rRNA gene high-throughput sequencing combining microbial community structure analysis and co-occurrence network analysis to investigate variances in microbial community compositions, potential functions and complexities across sediment, seagrass leaves, and seawater within different eutrophic areas of two adjacent seagrass meadows on Hainan Island, China.

RESULTS

Our results indicated that microbial diversity on seagrass leaves was significantly lower than in sediment but significantly higher than in seawater. Both sediment and phyllosphere microbial diversity showed no significant difference between the highly eutrophic and less eutrophic sites in each lagoon. However, sediment microbial diversity was higher in the more eutrophic lagoon, while phyllosphere microbial diversity was higher in the less eutrophic lagoon. Heavy eutrophication increased the relative abundance of phyllosphere microorganisms potentially involved in anaerobic metabolic processes, while reducing those responsible for beneficial functions like denitrification. The main factor affecting microbial diversity was organic carbon in seawater and sediment, with high organic carbon levels leading to decreased microbial diversity. The co-occurrence network analysis revealed that heavy eutrophication notably reduced the complexity and internal connections of the phyllosphere microbial community in comparison to the sediment and seawater microbial communities. Furthermore, ternary analysis demonstrated that heavy eutrophication diminished the external connections of the phyllosphere microbial community with the sediment and seawater microbial communities.

CONCLUSION

The pronounced decrease in biodiversity and complexity of the phyllosphere microbial community under eutrophic conditions can lead to greater microbial functional loss, exacerbating seagrass decline. This study emphasizes the significance of phyllosphere microbial communities compared to sediment microbial communities in the conservation and restoration of seagrass meadows under eutrophic conditions.

摘要

引言

与海草相关的微生物群落对海草的生长和健康起着至关重要的作用。然而,与海草草甸一样,与海草相关的微生物群落也经常受到富营养化的影响。目前尚不清楚富营养化如何影响与海草不同部位相关的微生物群落的组成和功能。

方法

我们采用原核生物16S rRNA基因高通量测序,结合微生物群落结构分析和共现网络分析,研究了中国海南岛两个相邻海草草甸不同富营养化区域内沉积物、海草叶片和海水中微生物群落组成、潜在功能及复杂性的差异。

结果

我们的结果表明,海草叶片上的微生物多样性显著低于沉积物中的,但显著高于海水中的。每个泻湖内,高富营养化和低富营养化地点的沉积物和叶际微生物多样性均无显著差异。然而,在富营养化程度较高的泻湖中,沉积物微生物多样性较高,而在富营养化程度较低的泻湖中,叶际微生物多样性较高。重度富营养化增加了叶际微生物中可能参与厌氧代谢过程的相对丰度,同时减少了负责反硝化等有益功能的微生物的相对丰度。影响微生物多样性的主要因素是海水和沉积物中的有机碳,高有机碳水平导致微生物多样性降低。共现网络分析表明,与沉积物和海水微生物群落相比,重度富营养化显著降低了叶际微生物群落的复杂性和内部连接性。此外,三元分析表明,重度富营养化减少了叶际微生物群落与沉积物和海水微生物群落的外部连接。

结论

富营养化条件下叶际微生物群落生物多样性和复杂性的显著降低会导致更大的微生物功能丧失,加剧海草衰退。本研究强调了在富营养化条件下海草草甸保护和恢复中,叶际微生物群落相对于沉积物微生物群落的重要性。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/5698/11350616/3e3c8efda487/fmicb-15-1449545-g009.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/5698/11350616/3fe452d33fc2/fmicb-15-1449545-g001.jpg
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https://cdn.ncbi.nlm.nih.gov/pmc/blobs/5698/11350616/ffd0e519eeba/fmicb-15-1449545-g007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/5698/11350616/d74f08cb2bfd/fmicb-15-1449545-g008.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/5698/11350616/3e3c8efda487/fmicb-15-1449545-g009.jpg
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https://cdn.ncbi.nlm.nih.gov/pmc/blobs/5698/11350616/b7f1b09098df/fmicb-15-1449545-g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/5698/11350616/8b625205bac7/fmicb-15-1449545-g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/5698/11350616/ffd0e519eeba/fmicb-15-1449545-g007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/5698/11350616/d74f08cb2bfd/fmicb-15-1449545-g008.jpg
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