Chinese mitten crab (Eriocheir sinesis) |
Polystyrene microplastics (5 μm) |
Reduced diversity of gut microbiota
The relative abundance of Firmicutes and Bacteroidetes decreased, and the relative abundance of Fusobacteria and Proteobacteria increased
|
[93] |
Marine medaka (Oryzias melastigma) |
Polystyrene micro- and nanoplastics (45 μm and 50 nm) |
Increased α-diversity of gut microbiota in the exposed group
The relative abundance of Bacteroidetes and Vicingus decreased
The relative abundance of Lewinella, Pseudomonas, Thalassospira, and Parahaliea increased
|
[94] |
Larval zebrafish |
Polystyrene microplastics (1–4 μm) |
Firmicutes, Bacteroidetes, Proteobacteria, and Verrucomicrobia changed significantly at the gate level
At the genus level, the relative abundance of Aeromonas, Shewanella, Microbacterium, Nevskia, and Methyloversatilis increased significantly, while the relative abundance of Pseudomonas, Ralstonia, and Stenotrophomonas decreased significantly
|
[95] |
Collembolans |
Polyvinyl chloride microplastics |
Increased gut microbiota diversity
The relative abundance of Bacteroidetes decreased, and the relative abundance of Firmicutes increased
|
[96] |
Mouse |
Polyethylene microplastics (10–150 μm) |
Increased diversity of gut microbiota
The relative abundance of Staphylococcus increased, and the relative abundance of Parabacteroides decreased
|
[78] |
Mouse |
Polystyrene micro- and nanoplastics (50 μm and 0.5 μm) |
At the gate level, the relative abundance of Firmicutes and α-Protebacteri was reduced
A total of 6 and 8 bacterial species were altered by exposure to 0.5 and 50 μm micro- and nanoplastics, respectively, at the genus level
|
[77] |
Mouse |
Polystyrene microplastics (5 μm) |
|
[26] |