Domesticating aquatic plants in hydroponic systems to demonstrate and advance phytoremediation of the artificial sweetener acesulfame.


Journal

The Science of the total environment
ISSN: 1879-1026
Titre abrégé: Sci Total Environ
Pays: Netherlands
ID NLM: 0330500

Informations de publication

Date de publication:
20 Sep 2023
Historique:
received: 28 02 2023
revised: 08 06 2023
accepted: 08 06 2023
medline: 10 7 2023
pubmed: 13 6 2023
entrez: 12 6 2023
Statut: ppublish

Résumé

Artificial sweeteners (ASs) are ubiquitously detected in the global water system, among which acesulfame (ACE) is an emerging contaminant for its chemical and biological stability and unsatisfying removal by conventional or advanced treatment technologies. Phytoremediation is an effective and sustainable in-situ remediation technology that this study is the first to explore ACE removal by aquatic plants. The emergent plants, Scirpus Validus (S. validus), Phyllostachys heteroclada Oliver (P. heteroclada) and Acorus tatarinowii (A. tatarinowii) showed superior removal capability than eleven floating plants, and demonstrated high phytoremediation efficiencies (PEs) of up to 75 % after 28 d domestication. ACE removal by the three emergent plants increased during domestication, as the PEs after 28 d domestication were 5.6-6.5 times of 7 d domestication. Notably, the half-life of ACE was decreased from 20.0 to 33.1 d to 1.1-3.4 d in the plant-hydroponic system, compared with 481.0-1152.4 d in control water without plants. Moreover, A. tatarinowii demonstrated the highest removal capacity for ACE with 0.37 mg/g fresh biomass weight (FW), higher than S. validus (0.27 mg/g FW) and P. heteroclada (0.20 mg/g FW). It is worth noting that a mass balance analysis demonstrated that plant transpiration and plant uptake account for about 6.72 %-18.54 % and 9.69 %-21.67 % ACE removal, while hydrolysis only accounted for about 4 % and photolysis was negligible. The rest ACE may be used as a carbon source by endophytic bacteria and root microorganisms of plants. In addition, increased temperature, pH, and illumination intensity had a significant effect on phytoremediation. In the selected experimental range, the increase of temperature from 15 °C to 35 °C, illumination intensity from 1500 lx to 6000 lx, and pH from 5 to 9 generally accelerated the PEs of ACE during the domestication process. Though the mechanism still requires further investigation, the results provide scientific and feasible data for removal of ACE from water by diverse plants for the first time, and also revealed insights for in-situ treatment of ACE.

Identifiants

pubmed: 37308013
pii: S0048-9697(23)03429-0
doi: 10.1016/j.scitotenv.2023.164806
pii:
doi:

Substances chimiques

Sweetening Agents 0
acetosulfame MA3UYZ6K1H
Thiazines 0
Water Pollutants, Chemical 0

Types de publication

Journal Article

Langues

eng

Sous-ensembles de citation

IM

Pagination

164806

Informations de copyright

Copyright © 2023. Published by Elsevier B.V.

Déclaration de conflit d'intérêts

Declaration of competing interest The authors declare the following financial interests/personal relationships which may be considered as potential competing interests: Weiwei Bi reports a relationship with Zhejiang University of Technology that includes: employment.

Auteurs

Xiaoyan Ma (X)

College of Civil Engineering, Zhejiang Key Laboratory of Civil Engineering Structures & Disaster Prevention and Mitigation Technology, Zhejiang University of Technology, Hangzhou 310023, China.

Sinong Huang (S)

College of Civil Engineering, Zhejiang Key Laboratory of Civil Engineering Structures & Disaster Prevention and Mitigation Technology, Zhejiang University of Technology, Hangzhou 310023, China.

Yuhong Jin (Y)

College of Civil Engineering, Zhejiang Key Laboratory of Civil Engineering Structures & Disaster Prevention and Mitigation Technology, Zhejiang University of Technology, Hangzhou 310023, China.

Hui Liao (H)

College of Civil Engineering, Zhejiang Key Laboratory of Civil Engineering Structures & Disaster Prevention and Mitigation Technology, Zhejiang University of Technology, Hangzhou 310023, China.

Shaoning Chen (S)

College of Life Science and Medicine, Zhejiang Sci-Tech University, Hangzhou, Zhejiang 310018, China.

Hong Wang (H)

College of Civil Engineering, Zhejiang Key Laboratory of Civil Engineering Structures & Disaster Prevention and Mitigation Technology, Zhejiang University of Technology, Hangzhou 310023, China.

Weijie Zhang (W)

College of Civil Engineering, Zhejiang Key Laboratory of Civil Engineering Structures & Disaster Prevention and Mitigation Technology, Zhejiang University of Technology, Hangzhou 310023, China.

Yifei Wu (Y)

College of Civil Engineering, Zhejiang Key Laboratory of Civil Engineering Structures & Disaster Prevention and Mitigation Technology, Zhejiang University of Technology, Hangzhou 310023, China.

Weiwei Bi (W)

College of Civil Engineering, Zhejiang Key Laboratory of Civil Engineering Structures & Disaster Prevention and Mitigation Technology, Zhejiang University of Technology, Hangzhou 310023, China. Electronic address: weiweibi@zjut.edu.cn.

Xueyan Li (X)

School of Environmental Science and Engineering, Suzhou University of Science and Technology, Suzhou 215009, China.

Andrea M Dietrich (AM)

Civil and Environmental Engineering, Virginia Polytechnic Institute and State University, Blackburg, VA 24061, USA.

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Classifications MeSH