• 微生物组学专题 • 下一篇
张蕾1,2(
), 杜尧1, 周颖雯1, 张议文1, 李露1, 王战1, 李尚耘1, 何晓青1(
)
收稿日期:2025-06-12
出版日期:2025-11-24
通讯作者:
何晓青,女,博士,教授,研究方向 :生态系统微生物组;E-mail: lenahe@bjfu.edu.cn作者简介:张蕾,女,博士研究生,研究方向 :水生态环境系统;E-mail: pooh00winnie@sina.com基金资助:
ZHANG Lei1,2(
), DU Yao1, ZHOU Ying-wen1, ZHANG yi-wen1, LI lu1, WANG zhan1, LI shang-yun1, HE Xiao-qing1(
)
Received:2025-06-12
Published:2025-11-24
摘要:
微生物在水生态系统中扮演着关键角色,推动物质循环和能量流动。它们在不同类型水体中展现出独特的群落结构和功能。 目的 此研究深入剖析北京市五大水系微生物多样性、群落稳定性和网络复杂性,解析五大水系微生物碳氮磷硫相关功能。 方法 通过宏基因组测序技术,对以北京五大水系微生物群落展开研究。 结果 蓟运河水系微生物群落Shannon和Simpson指数最高,但稳定性最低;永定河相反,结果支持“多样性-稳定性”假说。研究量化并比较了五大水系循环代谢功能,发现蓟运河在多个代谢通路中的丰度最高。两种核心属丰度与多样性、功能基因丰度呈正相关,与微生物群落稳定性与网络复杂性呈负相关。 结论 五大水系微生物共有属和特有属驱动群落多样性模式和功能潜力。此研究为构建健康可持续的水生态系统奠定了坚实基础。
张蕾, 杜尧, 周颖雯, 张议文, 李露, 王战, 李尚耘, 何晓青. 北京五大水系共有与特有微生物属对群落多样性及碳氮磷硫循环功能的驱动作用[J]. 生物技术通报, doi: 10.13560/j.cnki.biotech.bull.1985.2025-0611.
ZHANG Lei, DU Yao, ZHOU Ying-wen, ZHANG yi-wen, LI lu, WANG zhan, LI shang-yun, HE Xiao-qing. The Driving Effects of Shared and Specific Microbial Genera in the Five Major Water Systems of Beijing on Community Diversity and the Cycling Functions of Carbon, Nitrogen, Phosphorus, and Sulfur[J]. Biotechnology Bulletin, doi: 10.13560/j.cnki.biotech.bull.1985.2025-0611.
图1 采样点分布图图片来源于2010-2012年北京市第一次水务普查结果。BYR:北运河;CBR:潮白河;DQR:大清河;JYR:蓟运河;YDR:永定河。下同
Fig. 1 Sampling point distributionThe picture is sourced from the results of the first water conservancy census of Beijing conducted between 2010 and 2012. BYR: BeiYun River; CBR: ChaoBai River; DQR: DaQing River; JYR: Jiyun River; YDR: YongDing River. The same below
图2 微生物多样性与群落组成A:门水平、属水平相对丰度;B:α多样性指数;C:PCoA分析;D:AVD指数;E:微生物群落稳定性指数与Shannon指数、Simpson指数关系
Fig. 2 Microbial diversity and community compositionA: Relative abundance at the phylum level and genus level; B: Alpha diversity index; C: PCoA analysis; D: AVD index; E: Relationship between microbial stability index and Shannon index, Simpson index
图3 五大水系水体微生物属水平共现网络与基石物种A:五大水系水体微生物属水平共现网络;B:五大水系水体微生物基石物种;C-F:五大水系中基石物种数量、丰度,网络模块化,网络复杂性的比较;G:基石物种数量与网络复杂性的回归关系
Fig. 3 Co-occurrence network of microbial genus and keystone in five major water systemsA: Horizontal co-occurrence network of microbial genus in five major water systems. B: Keystone of microorganisms in five major water systems. C-F: Comparison of Keystone numbers, abundance, Network Modularity, and Network Complexity in the Five Major Water Systems; G: The regression relationship between the numbers of keystone and network complexity
图4 环境因素及其与群落关系A:环境因素差异图;B:环境因素与群落RDA分析
Fig. 4 Relationships of environmental factors and communityA: Difference of environmental factors. B: RDA analysis of environmental factors and community
图5 N、P、C、S循环差异A: KEGG二级功能类别代谢通路;B:N、P、C、S代谢通路差异;C:蓟运河与其他四个水系代谢通路的差异及占比
Fig. 5 N, P, C, S metabolic function gene differencesA: Gene abundance of KEGG level 2. B: N, P, C, S metabolic pathway difference. C: The differences and proportions of functional abundance between the Jiyun River and the other four water systems
| 代谢通路 | CBR | YDR | BYR | DQR | JYR |
|---|---|---|---|---|---|
| Dissimilatory nitrate reduction | 422.79 | 247.63 | 2 786.18 | 2 890.77 | 6 224.69 |
| Assimilatory nitrate reduction | 990.38 | 449.19 | 290.15 | 155.49 | 134.04 |
| Denitrification | 233.61 | 140.39 | 2 177.48 | 1 459.56 | 2 160.70 |
| Nitrification | 245.79 | 156.91 | 2 121.28 | 2 006.09 | 4 362.90 |
| NAD(P)H-quinone oxidoreductase | 462.55 | 458.80 | 257.05 | 156.50 | 115.64 |
| Cytochrome c oxidase, cbb3-type | 897.19 | 927.77 | 1 850.30 | 2 485.02 | 3 608.05 |
| Cytochrome bd ubiquinol oxidase | 532.99 | 552.14 | 847.88 | 1 420.04 | 2 034.80 |
| Cytochrome bc1 complex | 391.10 | 430.96 | 615.08 | 482.83 | 788.79 |
| Type I Secretion | 682.30 | 674.28 | 1 254.54 | 1 204.90 | 1 919.10 |
| Type II Secretion | 467.52 | 402.35 | 833.83 | 1 154.43 | 1 975.22 |
| Type Ⅳ Secretion | 76.85 | 41.50 | 305.24 | 259.93 | 570.08 |
| Dissimilatory arsenic reduction | 1 828.24 | 1 665.47 | 2 420.37 | 2 477.97 | 3 164.24 |
| Wood-Ljungdahl pathway | 1.66 | 5.58 | 18.66 | 7.19 | 1.24 |
| 3-Hydroxypropionate Bicycle | 175.76 | 156.06 | 249.41 | 311.52 | 365.87 |
| Methanogenesis | 0.29 | 1.07 | 8.69 | 4.32 | 0.86 |
| Fermentation to formate | 835.57 | 912.58 | 1 807.42 | 2 220.91 | 3 230.39 |
| Fermentation to acetate | 121.18 | 38.19 | 40.19 | 52.43 | 134.20 |
| Fermentation to ethanol | 4 361.11 | 3 558.31 | 5 402.47 | 7 320.00 | 9 378.01 |
| Assimilatory sulfate reduction | 1 737.97 | 1 300.54 | 1 950.72 | 2 666.15 | 4 417.41 |
| Thiosulfate oxidation by SOX complex | 740.87 | 836.35 | 1 336.70 | 1 437.95 | 1 992.74 |
| Alternative thiosulfate oxidation | 116.09 | 99.34 | 65.60 | 175.63 | 16.84 |
| Thiosulfate oxidation | 1 147.70 | 1 337.66 | 2 122.03 | 2 691.99 | 3 134.51 |
| Thiosulfate disproportionation | 7.59 | 9.01 | 38.47 | 26.03 | 7.27 |
| Sulfide oxidation | 2.29 | 21.31 | 21.10 | 46.31 | 35.72 |
| DMS oxidation | 75.27 | 71.31 | 120.72 | 185.39 | 191.44 |
表1 N、P、C、S代谢通路差异
Table 1 N, P, C, S metabolic pathway difference
| 代谢通路 | CBR | YDR | BYR | DQR | JYR |
|---|---|---|---|---|---|
| Dissimilatory nitrate reduction | 422.79 | 247.63 | 2 786.18 | 2 890.77 | 6 224.69 |
| Assimilatory nitrate reduction | 990.38 | 449.19 | 290.15 | 155.49 | 134.04 |
| Denitrification | 233.61 | 140.39 | 2 177.48 | 1 459.56 | 2 160.70 |
| Nitrification | 245.79 | 156.91 | 2 121.28 | 2 006.09 | 4 362.90 |
| NAD(P)H-quinone oxidoreductase | 462.55 | 458.80 | 257.05 | 156.50 | 115.64 |
| Cytochrome c oxidase, cbb3-type | 897.19 | 927.77 | 1 850.30 | 2 485.02 | 3 608.05 |
| Cytochrome bd ubiquinol oxidase | 532.99 | 552.14 | 847.88 | 1 420.04 | 2 034.80 |
| Cytochrome bc1 complex | 391.10 | 430.96 | 615.08 | 482.83 | 788.79 |
| Type I Secretion | 682.30 | 674.28 | 1 254.54 | 1 204.90 | 1 919.10 |
| Type II Secretion | 467.52 | 402.35 | 833.83 | 1 154.43 | 1 975.22 |
| Type Ⅳ Secretion | 76.85 | 41.50 | 305.24 | 259.93 | 570.08 |
| Dissimilatory arsenic reduction | 1 828.24 | 1 665.47 | 2 420.37 | 2 477.97 | 3 164.24 |
| Wood-Ljungdahl pathway | 1.66 | 5.58 | 18.66 | 7.19 | 1.24 |
| 3-Hydroxypropionate Bicycle | 175.76 | 156.06 | 249.41 | 311.52 | 365.87 |
| Methanogenesis | 0.29 | 1.07 | 8.69 | 4.32 | 0.86 |
| Fermentation to formate | 835.57 | 912.58 | 1 807.42 | 2 220.91 | 3 230.39 |
| Fermentation to acetate | 121.18 | 38.19 | 40.19 | 52.43 | 134.20 |
| Fermentation to ethanol | 4 361.11 | 3 558.31 | 5 402.47 | 7 320.00 | 9 378.01 |
| Assimilatory sulfate reduction | 1 737.97 | 1 300.54 | 1 950.72 | 2 666.15 | 4 417.41 |
| Thiosulfate oxidation by SOX complex | 740.87 | 836.35 | 1 336.70 | 1 437.95 | 1 992.74 |
| Alternative thiosulfate oxidation | 116.09 | 99.34 | 65.60 | 175.63 | 16.84 |
| Thiosulfate oxidation | 1 147.70 | 1 337.66 | 2 122.03 | 2 691.99 | 3 134.51 |
| Thiosulfate disproportionation | 7.59 | 9.01 | 38.47 | 26.03 | 7.27 |
| Sulfide oxidation | 2.29 | 21.31 | 21.10 | 46.31 | 35.72 |
| DMS oxidation | 75.27 | 71.31 | 120.72 | 185.39 | 191.44 |
图6 五大水系中的共有属和特有属A:共有属和特有属的筛选;B:五大水系碳氮磷硫代谢的影响因素;C:共有属、特有属与环境因素的关系;D:共有属、特有属与Shannon指数、微生物群落稳定性指数、NST指数的关系;E:共有属、特有属与五大水系碳氮磷硫循环的关系
Fig. 6 Shared and specific genus in five major water systemsA: Screening of common and specific genus B: The influencing factors of carbon, nitrogen, phosphorus, and sulfur metabolism in the five major water systems. C: The relationship between common genera, endemic genera, and environmental factors; D: The relationship between common genera, endemic genera, Shannon index, microbial stability index, and NST index; E: The relationship between common genera, endemic genera, and carbon, nitrogen, phosphorus, and sulfur metabolism in the five major water systems
图7 探究影响元素循环的重要因素A:核心属与元素循环的Mantel test检验;B:核心属和代谢功能的回归分析;C:微生物多样性与代谢功能的回归分析;D:两个核心类群与微生物多样性和群落稳定性对功能循环的贡献
Fig. 7 Explores the important factors influencing functional circulationA: Mantel test of core genus and metabolic functions; B: Regression analysis of core genus and metabolic functions; C: Regression analysis of microbial diversity and metabolic functions; D: Contribution of two core taxa and microbial diversity and microbial stability to functional cycling
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