Nanoplastic aggravates CH4 and N2O emission in plant-soil system

Shuyang Li , Huaijia Xin , Yajun Wang , Qinghua Ji , Yaohui Bai , Huijuan Liu , Jiuhui Qu

Front. Environ. Sci. Eng. ›› 2025, Vol. 19 ›› Issue (11) : 146

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Front. Environ. Sci. Eng. ›› 2025, Vol. 19 ›› Issue (11) : 146 DOI: 10.1007/s11783-025-2066-8
RESEARCH ARTICLE

Nanoplastic aggravates CH4 and N2O emission in plant-soil system

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Abstract

As nanoplastics continue to accumulate in natural wetland ecosystems, it remains unclear whether and how the effects of nanoplastics on the emission of methane (CH4) and nitrous oxide (N2O). Here we constructed a simulated natural wetland and introduced polystyrene nanoplastics (PS-NPs) to investigate the effects and potential mechanisms on CH4 and N2O emissions. The results indicated that PS-NPs can increase CH4 emissions by 20% to 100% and N2O emissions by approximately 100%. Analysis of the microbial community and plant functional characteristics in soils showed that PS-NPs inhibited plant growth and photosynthesis, and weakened plant stress resistance. Changes in plant functional characteristics affect the oxygen production capacity and secretion content of plant roots, which further affect the microbial community structure and metabolic activity of rhizosphere soil, enhancing methanogenesis and denitrification processes during the carbon and nitrogen cycles, resulting in increased CH4 and N2O emissions. Therefore, the continuous accumulation of PS-NPs is an important factor in changing the carbon sink function of wetlands. This study underscores the importance of controlling plastics pollution for the emission of greenhouse gases.

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Keywords

Wetland ecosystems / Nanoplastics / Greenhouse gases / Rhizosphere microbial communities

Highlight

● PS-NPs significantly increase CH4 and N2O emissions in simulated wetland.

● PS-NPs inhibit plant growth and photosynthesis, weakening stress resistance.

● Rhizosphere microbial shifts enhance methanogenesis and denitrification.

● PS-NPs alter root exudates, supplying carbon for CH4 production.

● Nanoplastics convert wetland carbon sinks to enhanced greenhouse gases sources.

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Shuyang Li, Huaijia Xin, Yajun Wang, Qinghua Ji, Yaohui Bai, Huijuan Liu, Jiuhui Qu. Nanoplastic aggravates CH4 and N2O emission in plant-soil system. Front. Environ. Sci. Eng., 2025, 19(11): 146 DOI:10.1007/s11783-025-2066-8

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References

[1]

Bosse U, Frenzel P. (1997). Activity and distribution of methane-oxidizing bacteria in flooded rice soil microcosms and in rice plants (Oryza sativa). Applied and Environmental Microbiology, 63(4): 1199–1207

[2]

Bridgham S D, Cadillo-Quiroz H, Keller J K, Zhuang Q L. (2013). Methane emissions from wetlands: biogeochemical, microbial, and modeling perspectives from local to global scales. Global Change Biology, 19(5): 1325–1346

[3]

Bridgham S D, Megonigal J P, Keller J K, Bliss N B, Trettin C. (2006). The carbon balance of North American wetlands. Wetlands, 26(4): 889–916

[4]

CubaschUWuebblesDChenDFacchiniM CFrameDMahowaldNWintherJ G (2013). Introduction. In: Stocker T F, Qin D, Plattner G K, Tignor M, Allen S K, Boschung J, Nauels A, Xia Y, Bex V, Midgley P M, eds. Climate Change 2013: The Physical Science Basis. Contribution of Working Group I to the Fifth Assessment Report of the Intergovernmental Panel on Climate Change. Cambridge: Cambridge University Press, 119–158

[5]

Fujii H, Chinnusamy V, Rodrigues A, Rubio S, Antoni R, Park S Y, Cutler S R, Sheen J, Rodriguez P L, Zhu J K. (2009). In vitro reconstitution of an abscisic acid signalling pathway. Nature, 462(7273): 660–664

[6]

Geyer R, Jambeck J R, Law K L. (2017). Production, use, and fate of all plastics ever made. Science Advances, 3(7): e1700782

[7]

Greenup A L, Bradford M A, Mcnamara N P, Ineson P, Lee J A. (2000). The role of Eriophorum vaginatum in CH4 flux from an ombrotrophic peatland. Plant and Soil, 227(1−2): 265–272

[8]

Harshvardhan K, Jha B. (2013). Biodegradation of low-density polyethylene by marine bacteria from pelagic waters, Arabian Sea, India. Marine Pollution Bulletin, 77(1−2): 100–106

[9]

Hernandez M E, Beck D A C, Lidstrom M E, Chistoserdova L. (2015). Oxygen availability is a major factor in determining the composition of microbial communities involved in methane oxidation. PeerJ, 3: e801

[10]

Holzapfel-Pschorn A, Conrad R, Seiler W. (1985). Production, oxidation and emission of methane in rice paddies. FEMS Microbiology Letters, 31(6): 343–351

[11]

Huang W, Xia X H. (2024). Element cycling with micro(nano)plastics. Science, 385(6712): 933–935

[12]

Intrator N, Jayakumar A, Ward B B. (2024). Aquatic nitrous oxide reductase gene (nosZ) phylogeny and environmental distribution. Frontiers in Microbiology, 15: 1407573

[13]

Jiang S Q, Lu H T, Xie Y Y, Zhou T R, Dai Z Q, Sun R K, He L, Li C Y. (2025). Toxicity of microplastics and nano-plastics to coral-symbiotic alga (Dinophyceae symbiodinium): evidence from alga physiology, ultrastructure, OJIP kinetics and multi-omics. Water Research, 273: 123002

[14]

Jiang X F, Chen H, Liao Y C, Ye Z Q, Li M, Klobučar G. (2019). Ecotoxicity and genotoxicity of polystyrene microplastics on higher plant Vicia faba. Environmental Pollution, 250: 831–838

[15]

King G M. (1990). Regulation by light of methane emissions from a wetland. Nature, 345(6275): 513–515

[16]

Lehner R, Weder C, Petri-Fink A, Rothen-Rutishauser B. (2019). Emergence of nanoplastic in the environment and possible impact on human health. Environmental Science & Technology, 53(4): 1748–1765

[17]

Li T, Cao X F, Zhao R, Cui Z J. (2023). Stress response to nanoplastics with different charges in Brassica napus L. during seed germination and seedling growth stages. Frontiers of Environmental Science & Engineering, 17(4): 43

[18]

Ma Y X, Huang J, Han T W, Yan C N, Cao C, Cao M F. (2021). Comprehensive metagenomic and enzyme activity analysis reveals the negatively influential and potentially toxic mechanism of polystyrene nanoparticles on nitrogen transformation in constructed wetlands. Water Research, 202: 117420

[19]

Meng K, Harkes P, Huerta Lwanga E, Geissen V. (2024). Microplastics exert minor influence on bacterial community succession during the aging of earthworm (Lumbricus terrestris) casts. Soil Biology and Biochemistry, 195: 109480

[20]

Mo X H, Wang M K, Zeng H, Wang J J. (2023). Rhizosheath: distinct features and environmental functions. Geoderma, 435: 116500

[21]

Porra R J, Thompson W A, Kriedemann P E. (1989). Determination of accurate extinction coefficients and simultaneous equations for assaying chlorophylls a and b extracted with four different solvents: verification of the concentration of chlorophyll standards by atomic absorption spectroscopy. Biochimica et Biophysica Acta (BBA) - Bioenergetics, 975(3): 384–394

[22]

Reay D S, Davidson E A, Smith K A, Smith P, Melillo J M, Dentener F, Crutzen P J. (2012). Global agriculture and nitrous oxide emissions. Nature Climate Change, 2(6): 410–416

[23]

Seeley M E, Song B, Passie R, Hale R C. (2020). Microplastics affect sedimentary microbial communities and nitrogen cycling. Nature Communications, 11(1): 2372

[24]

Serrano-Silva N, Sarria-GuzmÁn Y, Dendooven L, Luna-Guido M. (2014). Methanogenesis and methanotrophy in soil: a review. Pedosphere, 24(3): 291–307

[25]

Spanò C, Muccifora S, Ruffini Castiglione M, Bellani L, Bottega S, Giorgetti L. (2022). Polystyrene nanoplastics affect seed germination, cell biology and physiology of rice seedlings in-short term treatments: evidence of their internalization and translocation. Plant Physiology and Biochemistry, 172: 158–166

[26]

Su X X, Yang L Y, Yang K, Tang Y J, Wen T, Wang Y M, Rillig M C, Rohe L, Pan J L, Li H. . (2022). Estuarine plastisphere as an overlooked source of N2O production. Nature Communications, 13(1): 3884

[27]

Sun X D, Yuan X Z, Jia Y B, Feng L J, Zhu F P, Dong S S, Liu J J, Kong X P, Tian H Y, Duan J L. . (2020). Differentially charged nanoplastics demonstrate distinct accumulation in Arabidopsis thaliana. Nature Nanotechnology, 15(9): 755–760

[28]

Wagner S, Reemtsma T. (2019). Things we know and don’t know about nanoplastic in the environment. Nature Nanotechnology, 14(4): 300–301

[29]

Wang C Q, Kuzyakov Y. (2024). Rhizosphere engineering for soil carbon sequestration. Trends in Plant Science, 29(4): 447–468

[30]

Wu H, He B B, Chen B C, Liu A. (2024). Toxicity mechanisms of photodegraded polyvinyl chloride nanoplastics on pea seedlings. Frontiers of Environmental Science & Engineering, 18(4): 49

[31]

Xu M L, Ma W Q, Yao Y, Xu Q, Du W C, Yin Y, Ji R, Wang X Z, Guo H Y. (2024). Investigation of the effects of polyethylene microplastics at environmentally relevant concentrations on the plant-soil-microbiota system: a two-year field trial. Science of the Total Environment, 954: 176341

[32]

Yang X Y, He Q, Guo F C, Sun X H, Zhang J M, Chen M L, Vymazal J, Chen Y. (2020). Nanoplastics disturb nitrogen removal in constructed wetlands: responses of microbes and macrophytes. Environmental Science & Technology, 54(21): 14007–14016

[33]

Yuan W K, Zhou Y F, Liu X N, Wang J. (2019). New perspective on the nanoplastics disrupting the reproduction of an endangered fern in artificial freshwater. Environmental Science & Technology, 53(21): 12715–12724

[34]

Zhang S Y, Wang H, Liu M M, Yu H W, Peng J F, Cao X F, Wang C R, Liu R P, Kamali M, Qu J H. (2022). Press perturbations of microplastics and antibiotics on freshwater micro-ecosystem: case study for the ecological restoration of submerged plants. Water Research, 226: 119248

[35]

Zhou C Q, Lu C H, Mai L, Bao L J, Liu L Y, Zeng E Y. (2021). Response of rice (Oryza sativa L.) roots to nanoplastic treatment at seedling stage. Journal of Hazardous Materials, 401: 123412

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