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Effect of luminescent materials on the biochemistry, ultrastructure, and rhizobial microbiota of Spirodela polyrhiza.
Li, Qi; Lan, Yiyang; Yang, Yixia; Kang, Shiyun; Wang, Xin; Jiang, Jiarui; Liu, Shengyue; Wang, Qianchao; Zhang, Weizhen; Zhang, Liping.
Afiliação
  • Li Q; College of Ecology and Environment, Chengdu University of Technology, Chengdu, 610059, PR China. Electronic address: liqi21@cdut.edu.cn.
  • Lan Y; College of Ecology and Environment, Chengdu University of Technology, Chengdu, 610059, PR China.
  • Yang Y; College of Ecology and Environment, Chengdu University of Technology, Chengdu, 610059, PR China.
  • Kang S; College of Ecology and Environment, Chengdu University of Technology, Chengdu, 610059, PR China.
  • Wang X; The Chinese University of Hong Kong, Shenzhen, 518172, PR China.
  • Jiang J; College of Ecology and Environment, Chengdu University of Technology, Chengdu, 610059, PR China.
  • Liu S; College of Ecology and Environment, Chengdu University of Technology, Chengdu, 610059, PR China.
  • Wang Q; Keymed Biosciences Inc, Chengdu, 610059, PR China.
  • Zhang W; College of Ecology and Environment, Chengdu University of Technology, Chengdu, 610059, PR China.
  • Zhang L; The Chinese University of Hong Kong, Shenzhen, 518172, PR China. Electronic address: lipingzhang0599@163.com.
Plant Physiol Biochem ; 207: 108427, 2024 Feb.
Article em En | MEDLINE | ID: mdl-38367389
ABSTRACT
Fluorescent materials and technologies have become widely used in scientific research, and due to the ability to convert light wavelengths, their application to photosynthetic organisms can affect their development by altering light quality. However, the impacts of fluorescent materials on aquatic plants and their environmental risks remain unclear. To assess the effects of luminescent materials on floating aquatic macrophytes and their rhizosphere microorganisms, 4-(di-p-tolylamino)benzaldehyde-A (DTB-A) and 4-(di-p-tolylamino)benzaldehyde-M (DTB-M) (emitting blue-green and orange-red light, respectively) were added individually and jointly to Spirodela polyrhiza cultures and set at different concentrations (1, 10, and 100 µM). Both DTB-A and DTB-M exhibited phytotoxicity, which increased with concentration under separate treatment. Moreover, the combined group exhibited obvious stress relief at 10 µM compared to the individually treated group. Fluorescence imaging showed that DTB-A and DTB-M were able to enter the cell matrix and organelles of plant leaves and roots. Peroxidation induced cellular damage, contributing to a decrease in superoxide dismutase (SOD) and peroxidase (POD) activities and malondialdehyde (MDA) accumulation. Decomposition of organelle structures, starch accumulation in chloroplasts, and plasmolysis were observed under the ultrastructure, disrupting photosynthetic pigment content and photosynthesis. DTB-A and DTB-M exposure resulted in growth inhibition, dry weight loss, and leaf yellowing in S. polyrhiza. A total of 3519 Operational Taxonomic Units (OTUs) were identified in the rhizosphere microbiome. The microbial communities were dominated by Alphaproteobacteria, Oxyphotobacteria, and Gammaproteobacteria, with the abundance and diversity varied significantly among treatment groups according to Shannon, Simpson, and Chao1 indices. This study revealed the stress defense response of S. polyrhiza to DTB-A and DTB-M exposures, which provides a broader perspective for the bioremediation of pollutants using aquatic plants and supports the further development of fluorescent materials for applications.
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Texto completo: 1 Base de dados: MEDLINE Assunto principal: Benzaldeídos / Araceae Idioma: En Ano de publicação: 2024 Tipo de documento: Article

Texto completo: 1 Base de dados: MEDLINE Assunto principal: Benzaldeídos / Araceae Idioma: En Ano de publicação: 2024 Tipo de documento: Article