Table 4.
Overview of in vivo studies of the immunotoxic effects of nano- and microplastics in vertebrates. *This has been calculated by the authors based on Bachmanov AA et al. Behav Genet 2002 [73]
| Reference | Nano-microplastics | Dosage | Duration of exposure | Route of exposure | Species | Observed immunotoxic effects |
|---|---|---|---|---|---|---|
| Nanoplastics | ||||||
|
Greven et al., Environ. Toxicol. Chem. 2016 [111] |
Polystyrene 41 nm |
0.025–0.05-0.1- 0.2 μg/μL |
2 h | Tank water |
Fathead minnows (Pimephales promelas) |
Neutrophil function in vitro assays Dose dependent ↑myeloperoxidase activity and neutrophil extracellular trap release |
|
Brandts et al., Genomics. 2018 [112] |
Polymethylmethacrylate ~ 45 nm |
0.02–0.2-2-20 mg/L | 96 h | Tank water |
European sea bass (Dicentrarchus Labrax) |
Plasma ↓ esterase activity (biomarker of oxidative stress) (0.02 and 0.2 mg/L) |
| Microplastics | ||||||
|
Greven et al., Environ. Toxicol. Chem. 2016 [111] |
Polycarbonate 158.7 nm |
0.025–0.05-0.1- 0.2 μg/μL |
2 h | Tank water |
Fathead minnows (Pimephales promelas) |
Neutrophil function in vitro assays Dose dependent ↑ myeloperoxidase activity, neutrophil extracellular trap release, and oxidative burst |
|
Asmoniate et al., Environ. Sci.Technol.2018 [79] |
Polystyrene 100–400 μm |
10 mg /fish/day | 4 weeks | Food |
Rainbow trout (Oncorhynchus mykiss) |
No variation of immune parameters: serum lysosyme activity blood immune cells counts |
|
Banaee et al., Chemosphere 2019 [113] |
Isolated from body scrub (likely polyethylene) No data on size |
250 and 500 μg/L | 30 days | Tank water |
Common carp (Cyprinus carpio) |
Plasma ↓total immunoglobulin ↓alternative complement activity ↓ complement C3 ↓complement C4 ↓lysozyme activity ↓acetylcholinesterase activity ↓γ-glutamyl-transferase activity ↑ lactate deshydrogenase activity ↑alkaline phosphatase activity |
|
Espinosa et al., Fish Shellfish Immunol. 2017 [114] |
Polyvinyl chloride 40–150 μm |
100–500 mg/kg of food |
15, 30 days |
Food |
Gilthead seabream (Sparus aurata) |
↑ head-kidney leucocyte phagocytic capacity (15 days only) |
|
Espinosa et al., Environ. Pollut. 2018 [115] |
Polyvinyl chloride - Polyethylene 40–150 μm |
1–10-100 mg/mL |
1 h 24 h |
Tank water |
European sea bass (Dicentrarchus Labrax) Gilthead seabream (Sparus aurata) |
Head-kidney leucocytes European sea bass PVC: ↓phagocytic capacity (all dosages, 1 h and 24 h) PE: ↑ respiratory burst (100 mg/mL, 24 h) Gilthead seabream PVC: ↓phagocytic ability, ↑ respiratory burst (100 mg/mL, 24 h) PVC and PE: ↑ Nrf2 expression (100 mg/mL, 1 h) |
|
Espinosa et al., Fish Shellfish Immunol. 2019 [88] |
Polyvinyl chloride - Polyethylene 40–150 μm |
100–500 mg/kg of food |
3 weeks | Food |
European sea bass (Dicentrarchus Labrax) |
Cellular innate immune parameters in head kidney leucocytes PVC: ↑ phagocytic capacity at both dosages ↑ respiratory burst activity at 100 mg/kg PE: ↑ respiratory burst activity at both dosages |
|
Limonta et al., Sci rep 2019 [90] |
Irregularly shaped high density polyethylene and polystyrene particles |
100 and 1000 μg/L |
20 days | Food |
Zebrafish (Danio rerio) |
↓ liver leukotriene B4 receptor (ltb4r) and interferon induced transmembrane protein 1 (ifitm1) expression |
|
Li et al., Chemosphere. 2020 [93] |
Polyethylene 10–150 μm |
2–20-200 μg/g ~ 0.0004, 0.004 and 0.04 μg/kg bw/day* |
5 weeks | Food |
C57BL/6 mice (Mus musculus) |
At 20 and 200 μg/g: serum:↑ IL1α, ↓G-CSF spleen:↓Treg cells, ↑Th17 cells |
|
Park et al., Toxicology Letters 2020 [116] |
Polyethylene irregular micropsheres 16.9 ± 1.9 μm |
0.125, 0.5 and 2 mg/day/mouse ~ 5, 20 an 80 μg/kg bw/day* |
90 days | Gavage |
ICR mice (Mus musculus) |
In dams: ↑ blood neutrophils ↑ blood IgA levels In dams and offspring: alteration of spleen lymphocytes |