Stress response to nanoplastics with different charges in Brassica napus L. during seed germination and seedling growth stages

Tao Li, Xiufeng Cao, Rui Zhao, Zhaojie Cui

PDF(5270 KB)
PDF(5270 KB)
Front. Environ. Sci. Eng. ›› 2023, Vol. 17 ›› Issue (4) : 43. DOI: 10.1007/s11783-023-1643-y
RESEARCH ARTICLE
RESEARCH ARTICLE

Stress response to nanoplastics with different charges in Brassica napus L. during seed germination and seedling growth stages

Author information +
History +

Highlights

● Higher concentrations of PS, PS-NH2 and PS-SO3H inhibited seed germination.

● PS, PS-NH2 and PS-SO3H influenced seedling growth in a dose-dependent manner.

● PS, PS-NH2 and PS-SO3H reduced essential nutrients uptake and plant quality.

● PS, PS-NH2 and PS-SO3H increased antioxidant enzyme activities and MDA content.

● Nanoplastic toxicity was related to surface charges.

Abstract

Nanoplastic pollution has become a significant problem in farmland systems worldwide. However, research on the effects of nanoplastics (NPs) with different charges on field crops is still limited. In our study, NPs with different charges, including unmodified polystyrene nanoplastics (PS), positively charged polystyrene nanoplastics (PS-NH2), and negatively charged polystyrene nanoplastics (PS-SO3H), were investigated for their impacts on seed germination and seedling growth of rape. The results showed that seed water uptake (after 12 h), seed germination, seed vigour, and relative root elongation were all significantly reduced under exposure to NPs (200 mg/L). Similarly, remarkable decreases in plant biomass (root weight, shoot weight), growth (root length, plant height), photosynthesis ability (chlorophyll a, chlorophyll b, carotenoids), essential nutrient uptake (Fe, Mn, Zn, Cu), and plant quality (soluble protein, soluble sugar, crude fibre content) of rape seedlings were also observed after exposure to NPs. Among the three kinds of NPs, PS-NH2 showed stronger effects. Moreover, superoxide dismutase, peroxidase, and catalase activities of rape seedlings were changed, and the content of malondialdehyde was significantly increased under exposure to NPs. Furthermore, positively charged PS-NH2 showed stronger effects on the phenotype, physiology, biochemistry, nutrient uptake, and plant quality of rape. Notably, a comprehensive toxicity evaluation revealed that PS-NH2 had the strongest toxicity to rape. The present study provides important implications for the interaction and risk assessment of NPs and crops in soil-plant systems.

Graphical abstract

Keywords

Nanoplastics / Rape (Brassica napus L.) / Physiology and biochemistry / Nutrient absorption / Plant quality / Toxicity

Cite this article

Download citation ▾
Tao Li, Xiufeng Cao, Rui Zhao, Zhaojie Cui. Stress response to nanoplastics with different charges in Brassica napus L. during seed germination and seedling growth stages. Front. Environ. Sci. Eng., 2023, 17(4): 43 https://doi.org/10.1007/s11783-023-1643-y

References

[1]
Bosker T , Bouwman L J , Brun N R , Behrens P , Vijver M G . (2019). Microplastics accumulate on pores in seed capsule and delay germination and root growth of the terrestrial vascular plant Lepidium sativum. Chemosphere, 226: 774–781
CrossRef Pubmed Google scholar
[2]
Cao X , Cui X , Xie M , Zhao R , Xu L , Ni S , Cui Z . (2022). Amendments and bioaugmentation enhanced phytoremediation and micro-ecology for PAHs and heavy metals co-contaminated soils. Journal of Hazardous Materials, 426: 128096
CrossRef Pubmed Google scholar
[3]
Cui X, Geng Y, Li T, Zhao R, Li X, Cui Z (2021). Field application and effect evaluation of different iron tailings soil utilization technologies. Resources, Conservation and Recycling, 173: 105746
CrossRef Google scholar
[4]
Das S , Mukherjee A , Sengupta G , Singh V K . (2020). Nano-materials as photocatalysts for pegradation of environmental pollutants. ScienceDirect, 371–401
[5]
de Souza Machado A A , Lau C W , Kloas W , Bergmann J , Bachelier J B , Faltin E , Becker R , Görlich A S , Rillig M C . (2019). Microplastics can change soil properties and affect plant performance. Environmental Science & Technology, 53(10): 6044–6052
CrossRef Pubmed Google scholar
[6]
Dong Y , Song Z , Liu Y , Gao M . (2021). Polystyrene particles combined with di-butyl phthalate cause significant decrease in photosynthesis and red lettuce quality. Environmental pollution, 278: 116871
CrossRef Pubmed Google scholar
[7]
Gao J (2006). Experimental Guidance for Plant Physiology. Beijing: Higher Education Press (in Chinese)
[8]
Lambert S , Wagner M . (2016). Characterisation of nanoplastics during the degradation of polystyrene. Chemosphere, 145: 265–268
CrossRef Pubmed Google scholar
[9]
Li C , Gao Y , He S , Chi H , Li Z , Zhou X , Yan B . (2021a). Quantification of nanoplastic uptake in cucumber plants by pyrolysis gas chromatography/mass spectrometry. Environmental Science & Technology Letters, 8(8): 633–638
CrossRef Google scholar
[10]
Li S , Guo J , Wang T , Gong L , Liu F , Brestic M , Liu S , Song F , Li X . (2021c). Melatonin reduces nanoplastic uptake, translocation, and toxicity in wheat. Journal of Pineal Research, 71(3): e12761
CrossRef Pubmed Google scholar
[11]
Li S , Wang T , Guo J , Dong Y , Wang Z , Gong L , Li X . (2021b). Polystyrene microplastics disturb the redox homeostasis, carbohydrate metabolism and phytohormone regulatory network in barley. Journal of Hazardous Materials, 415: 125614
CrossRef Pubmed Google scholar
[12]
Lian J , Liu W , Meng L , Wu J , Chao L , Zeb A , Sun Y . (2021). Foliar-applied polystyrene nanoplastics (PSNPs) reduce the growth and nutritional quality of lettuce (Lactuca sativa L.). Environmental pollution, 280: 116978
CrossRef Pubmed Google scholar
[13]
Lian J , Wu J , Xiong H , Zeb A , Yang T , Su X , Su L , Liu W . (2020). Impact of polystyrene nanoplastics (PSNPs) on seed germination and seedling growth of wheat (Triticum aestivum L.). Journal of Hazardous Materials, 385: 121620
CrossRef Pubmed Google scholar
[14]
Lian Y , Liu W , Shi R , Zeb A , Wang Q , Li J , Zheng Z , Tang J . (2022). Effects of polyethylene and polylactic acid microplastics on plant growth and bacterial community in the soil. Journal of Hazardous Materials, 435: 129057
CrossRef Pubmed Google scholar
[15]
Liu C , Yang Z , Hu Y . (2015). Drought resistance of wheat alien chromosome addition lines evaluated by membership function value based on multiple traits and drought resistance index of grain yield. Field Crops Research, 179: 103–112
CrossRef Google scholar
[16]
Liu J , Yin P , Zhao L . (2018). Adverse effect of nano-TiO2 on the marine macroalgae Gracilaria lemaneiformis (Gracilariales, Rhodophyta): growth and antioxidant activity. RSC Advances, 8(51): 29172–29178
CrossRef Pubmed Google scholar
[17]
Ng E L , Huerta Lwanga E , Eldridge S M , Johnston P , Hu H W , Geissen V , Chen D . (2018). An overview of microplastic and nanoplastic pollution in agroecosystems. Science of the Total Environment, 627: 1377–1388
CrossRef Pubmed Google scholar
[18]
Nizzetto L, Futter M, Langaas S (2016). Are agricultural soils dumps for microplastics of urban origin? Environmental Science & Technology, 50(20): 10777–10779
CrossRef Pubmed Google scholar
[19]
Ren Z , Gui X , Xu X , Zhao L , Qiu H , Cao X . (2021). Microplastics in the soil-groundwater environment: Aging, migration, and co-transport of contaminants: a critical review. Journal of Hazardous Materials, 419: 126455
CrossRef Pubmed Google scholar
[20]
Rocha R J M, Rodrigues A C M, Campos D, Cícero L H, Costa A P L, Silva D A M, Oliveira M, Soares A M V M, Patrício Silva A L (2020). Do microplastics affect the zoanthid Zoanthus sociatus? Science of the Total Environment, 713: 136659
CrossRef Pubmed Google scholar
[21]
Saharan V , Kumaraswamy R V , Choudhary R C , Kumari S , Pal A , Raliya R , Biswas P . (2016). Cu-chitosan nanoparticle mediated sustainable approach to enhance seedling growth in maize by mobilizing reserved food. Journal of Agricultural and Food Chemistry, 64(31): 6148–6155
CrossRef Pubmed Google scholar
[22]
Salazar-Cubillas K , Dickhoefer U . (2021). Estimating the proportion of in situ rumen-undegraded crude protein from chemical crude protein and fiber fractions in tropical forage grasses and legumes. Animal Feed Science and Technology, 282: 115122
CrossRef Google scholar
[23]
Sun X D , Yuan X Z , Jia Y , Feng L J , Zhu F P , Dong S S , Liu J , Kong X , Tian H , Duan J L , Ding Z , Wang S G , Xing B . (2020). Differentially charged nanoplastics demonstrate distinct accumulation in Arabidopsis thaliana. Nature Nanotechnology, 15(9): 755–760
CrossRef Pubmed Google scholar
[24]
van Weert S , Redondo-Hasselerharm P E , Diepens N J , Koelmans A A . (2019). Effects of nanoplastics and microplastics on the growth of sediment-rooted macrophytes. Science of the Total Environment, 654: 1040–1047
CrossRef Pubmed Google scholar
[25]
Wei X F , Bohlén M , Lindblad C , Hedenqvist M , Hakonen A . (2021). Microplastics generated from a biodegradable plastic in freshwater and seawater. Water Research, 198: 117123
CrossRef Pubmed Google scholar
[26]
Xiang X , Chen Z , Ren D , Xu J , Li X , Ye Z , Chen N , Chen Q , Ma S . (2020). Shape engineering of polystyrene particles from spherical to raspberry-like to hollow flower-like via one-step non-surfactant self-templating polymerization of styrene in ethanol-water mixtures. RSC Advances, 10(19): 11535–11542
CrossRef Pubmed Google scholar
[27]
Yang W , Gao P , Ma G , Huang J , Wu Y , Wan L , Ding H , Zhang W . (2021). Transcriptome analysis of the toxic mechanism of nanoplastics on growth, photosynthesis and oxidative stress of microalga Chlorella pyrenoidosa during chronic exposure. Environmental pollution, 284: 117413
CrossRef Pubmed Google scholar
[28]
Yin L , Wen X , Huang D , Du C , Deng R , Zhou Z , Tao J , Li R , Zhou W , Wang Z , Chen H . (2021). Interactions between microplastics/nanoplastics and vascular plants. Environmental pollution, 290: 117999
CrossRef Pubmed Google scholar
[29]
Yu G , Huang S , Luo X , Zhao W , Zheng Z . (2022). Single and combined toxicity effects of nanoplastics and bisphenol F on submerged the macrophyte Hydrilla verticillata. Science of the Total Environment, 814: 152564
CrossRef Pubmed Google scholar
[30]
Yuan H , Liu Q , Guo Z , Fu J , Sun Y , Gu C , Xing B , Dhankher O P . (2021). Sulfur nanoparticles improved plant growth and reduced mercury toxicity via mitigating the oxidative stress in Brassica napus L. Journal of Cleaner Production, 318: 128589
CrossRef Google scholar
[31]
Zadeh L . (1965). Fuzzy sets. Information and Control, 8(3): 338–353
CrossRef Google scholar
[32]
Zhang H , Liang J , Luo Y , Tang N , Li X , Zhu Z , Guo J . (2022). Comparative effects of polystyrene nanoplastics with different surface charge on seedling establishment of Chinese cabbage (Brassica rapa L.). Chemosphere, 292: 133403
CrossRef Pubmed Google scholar
[33]
Zhang K , Wang Y , Mao J , Chen B . (2020). Effects of biochar nanoparticles on seed germination and seedling growth. Environmental pollution, 256: 113409
CrossRef Pubmed Google scholar
[34]
Zhu J , Wang J , Zhan X , Li A , White J , Gardea-Torresdey J L , Xing B . (2021). Role of charge and size in the translocation and distribution of zinc oxide particles in wheat cells. ACS Sustainable Chemistry & Engineering, 9(34): 11556–11564
CrossRef Google scholar

Acknowledgements

This work was financially supported by the National Natural Science Foundation of China (Nos. U20A20115 and 42007112) and the Major Technology Innovation Project of Shandong Province (No. 2020CXGC011403). The authors would like to thank all the anonymous referees for their constructive comments and suggestions.

Electronic Supplementary Material

Supplementary material is available in the online version of this article at https://doi.org/10.1007/s11783-023-1643-y and is accessible for authorized users.

RIGHTS & PERMISSIONS

2023 Higher Education Press
AI Summary AI Mindmap
PDF(5270 KB)

Accesses

Citations

Detail

Sections
Recommended

/