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Microplastics affect the ecological stoichiometry of plant, soil and microbes in a greenhouse vegetable system.
Palansooriya, Kumuduni Niroshika; Zhou, Ying; An, Zhengfeng; Cai, Yanjiang; Chang, Scott X.
Affiliation
  • Palansooriya KN; State Key Laboratory of Subtropical Silviculture, College of Environment and Resources, College of Carbon Neutrality, Zhejiang A&F University, Hangzhou 311300, China; Department of Renewable Resources, University of Alberta, Edmonton T6G 2E3, Canada.
  • Zhou Y; State Key Laboratory of Subtropical Silviculture, College of Environment and Resources, College of Carbon Neutrality, Zhejiang A&F University, Hangzhou 311300, China.
  • An Z; Department of Renewable Resources, University of Alberta, Edmonton T6G 2E3, Canada.
  • Cai Y; State Key Laboratory of Subtropical Silviculture, College of Environment and Resources, College of Carbon Neutrality, Zhejiang A&F University, Hangzhou 311300, China. Electronic address: yjcai@zafu.edu.cn.
  • Chang SX; State Key Laboratory of Subtropical Silviculture, College of Environment and Resources, College of Carbon Neutrality, Zhejiang A&F University, Hangzhou 311300, China; Department of Renewable Resources, University of Alberta, Edmonton T6G 2E3, Canada. Electronic address: sxchang@ualberta.ca.
Sci Total Environ ; 924: 171602, 2024 May 10.
Article in En | MEDLINE | ID: mdl-38461987
ABSTRACT
Microplastic (MP) pollution is a growing global issue due to its potential threat to ecosystem and human health. Low-density polyethylene (LDPE) MP is the most common type of plastics polluting agricultural soils, negatively affecting soil-microbial-plant systems. However, the effects of LDPE MPs on the carbon (C) nitrogen (N) phosphorus (P) of soil-microbial-plant systems have not been well elucidated. Thus, we conducted a pot experiment with varying LDPE MP concentrations (w/w) (control without MPs; 0.2 % MPs (PE1); 5 % MPs (PE2); and 10 % MPs (PE3)) to study their effects on soil-microbial-plant C-N-P stoichiometry. Soil CN ratio increased 2.3 and 3.4 times in PE2 and PE3, respectively. Soil CP ratio increased 2.2 and 3.6 times in PE2 and PE3, respectively. Soil microbial CN ratios decreased by 46.2 % in PE1, while CP ratios decreased by 59.2, 38.6, and 67.9 % in PE1, PE2, and PE3, respectively. Soil microbial NP ratio decreased in PE1 (17.2) and PE3 (59.1 %). MPs increased shoot C content and CN ratios, particularly at the 5 % MP addition rate. MP addition altered dissolved organic C, N, and P concentrations, depending on the MP addition rate. Microbial community responses to MP exposure were complex, leading to variable effects on different microbial groups at different MP addition rates. Structural equation modeling showed that MP addition had a direct positive effect (ß = 0.96) on soil C-N-P stoichiometry and a direct negative effect (ß = -1.34) on microbial C-N-P stoichiometry. These findings demonstrate the complex interactions between MPs, soil microorganisms, and nutrient dynamics, highlighting the need for further research to better understand the ecological implications of MP pollution in terrestrial ecosystems.
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Full text: 1 Collection: 01-internacional Database: MEDLINE Main subject: Vegetables / Microbiota Limits: Humans Language: En Journal: Sci Total Environ Year: 2024 Document type: Article Affiliation country: Canada

Full text: 1 Collection: 01-internacional Database: MEDLINE Main subject: Vegetables / Microbiota Limits: Humans Language: En Journal: Sci Total Environ Year: 2024 Document type: Article Affiliation country: Canada