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Frontiers of Environmental Science & Engineering

ISSN 2095-2201

ISSN 2095-221X(Online)

CN 10-1013/X

Postal Subscription Code 80-973

2018 Impact Factor: 3.883

Front. Environ. Sci. Eng.    2022, Vol. 16 Issue (11) : 145    https://doi.org/10.1007/s11783-022-1580-1
RESEARCH ARTICLE
Plastic materials and water sources actively select and shape wastewater plastispheres over time
Yu Xia1,2,3, Xuyang Zhang1, Miao Zhang1, Liming Chen1, Xiaotong Tang1, Yuhong Sun1, Xiang Li1,2,3()
1. School of Environmental Science and Engineering, Southern University of Science and Technology, Shenzhen 518055, China
2. State Environmental Protection Key Laboratory of Integrated Surface Water-Groundwater Pollution Control, School of Environmental Science and Engineering, Southern University of Science and Technology, Shenzhen 518055, China
3. Guangdong Provincial Key Laboratory of Soil and Groundwater Pollution Control, School of Environmental Science and Engineering, Southern University of Science and Technology, Shenzhen 518055, China
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Abstract

● Wastewater MPs exhibited resistomes and therefore health threats.

● High density of alkB gene indicates both HDPE and PET can be utilized by microbes.

● Plastics and waters actively selected and shaped the plastispheres over time.

● A broader phylogenetic spectrum of MHET-degrading microorganisms was annotated.

The daily use of plastics presents a serious pollution issue due to their extremely slow degradation. Microplastics and the biofilm that grows on plastics (i.e., the plastisphere) are important subsets of plastic wastes. Many studies have been conducted to reveal the structures of the plastispheres, the driving factors for the formation of the plastisphere, and the ability of the plastispheres to degrade plastics in a variety of water bodies. However, the plastispheres related to wastewater are understudied. In this study, we used a microcosmic strategy to study the evolution of the plastispheres associated with microplastics (MPs) over time in wastewater. We found that plastic materials and water sources did not actively select and shape the plastispheres at an early stage, but the active selection for a unique niche of the plastisphere occurred after 14 d of growth. In addition, we confirmed that the alkB gene was densely present, and metagenomics showed some additional chemical reactions, which suggests that MPs are consumed by the microbes in the plastispheres. Additionally, metagenomics identified some metagenome-assembled genomes (MAGs) associated with high-density polyethylene (HDPE) and polyethylene terephthalate (PET). The identification of HDPE-associated MAGs and PET-associated MAGs further supports the notion that the selection for a unique niche of the plastisphere is driven by plastic materials and water sources (in this study, after 14 d of growth). Our discoveries bring new views on the behavior of the wastewater-associated plastisphere, especially how long it takes a wastewater plastisphere to form.

Keywords Microplastics      Whole-genome metagenomic sequencing      Plastisphere      Plastic degradation      MHETase     
Corresponding Author(s): Xiang Li   
Issue Date: 10 June 2022
 Cite this article:   
Yu Xia,Xuyang Zhang,Miao Zhang, et al. Plastic materials and water sources actively select and shape wastewater plastispheres over time[J]. Front. Environ. Sci. Eng., 2022, 16(11): 145.
 URL:  
https://academic.hep.com.cn/fese/EN/10.1007/s11783-022-1580-1
https://academic.hep.com.cn/fese/EN/Y2022/V16/I11/145
Parameters Effluent parameters (mg/L) (average values)
XL FT
pH 7.04 6.81
SS 5 5
BOD5 1.5 2.1
COD 17 14
Total P 0.11 0.12
Ammonia-N 0.31 0.59
NO3-N 6.52 6.53
NO2-N 2.260 0.055
Total N 10.60 8.36
TDS 301 618
TS 307 633
Tab.1  Parameters of effluents discharged from studied wastewater treatment plants
Antibiotics FT XL HDPE PET
Aminoglycoside 0.006 0.018 0.019 0.017
Bacitracin 0.075 0.176 0.137 0.144
Beta-lactam 0.011 0.059 0.111 0.090
Chloramphenicol 0.008 0.003 0.002 0.003
Fosmidomycin 0.004 0.026 0.020 0.025
Kasugamycin 0.003 0.001 0.001 0.001
Macrolides, lincosamides, and streptogramins (MLS) 0.016 0.025 0.039 0.019
Multidrug 0.203 0.277 0.230 0.248
Quinolone 0.000 0.002 0.003 0.002
Rifamycin 0.001 0.002 0.000 0.001
Sulfonamide 0.004 0.003 0.003 0.002
Tetracycline 0.009 0.009 0.004 0.003
Trimethoprim 0.002 0.000 0.001 0.001
Unclassified 0.021 0.010 0.010 0.016
Vancomycin 0.002 0.001 0.000 0.001
Tab.2  Concentrations of ARGs (gene copies/cell) in samples of the plastisphere
Fig.1  qPCR measurements of the densities of the alkB and 16S rRNA genes. The x-axis shows the groups grouped on the basis plastic materials and water sources, and the y-axis shows the densities (gene copies/mm2) of the genes. The results of the heteroscedastic student’s t test (two-tailed) are annotated. *** represents p < 0.001, and ns represents “not significant”.
Fig.2  A maximum-likelihood phylogenetic tree of the bacterial MHETase identified in our metagenome and reference protein sequences.
Fig.3  The clustering of the operational taxonomic units (OTUs) of the plastisphere on the basis of the relative abundance of amplicon 16S rRNA samples. The temporal average relative abundance (ARA) of orders (ARA > 1%) is shown in (a). The principal component analysis (PCA) of the groups grouped on the basis of the combination of plastic materials, water sources, and incubation periods is shown in (b). The PCA of the groups grouped on the basis of the combination of plastic materials and incubation periods is shown in (c), and the PCA of the groups grouped on the basis of water sources and incubation periods is shown in (d).
Fig.4  A heatmap of the operational taxonomic units (OTUs) of the samples of microcosmic experiments. Only the OTU number that is greater than 800 is shown, and the value shows the sample replicates in the x-axis. YC-E6 and YLA114 belong to the class Methanomicrobia. Methanomicrobia are indicated in the y-axis by the red color.
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