Table 2.
Study participants | Locations | Technique of analysis | Polymer types | Reference |
---|---|---|---|---|
Three meconium, six infants, and ten adult faeces | New York | Mass spectrometry | Polyethylene terephthalate and polycarbonate | Zhang et al. (2019) |
Faeces of patients with inflammatory bowel disease and healthy people | China | Raman spectroscopy | Polyethylene terephthalate and polyamide | Yan et al. (2022a) |
Faeces of eight healthy volunteers aged 33 to 65 years | Europe and Asia | Fourier transform infrared spectroscopy | Polypropylene and polyethylene terephthalate | Schwabl et al. (2019) |
Sputum of 22 patients suffering from different respiratory diseases | China | Fourier transform infrared spectroscopy | Polyurethane polyester, chlorinated polyethylene, and alkyd varnish | Huang et al. (2022a) |
8000 samples of saliva from adult | Iran | Raman spectroscopy | Not detected | Abbasi and Turner (2021) |
Bronchoalveolar lavage fluid from 44 adult patients undergoing a bronchoscopy | Europe | Fourier transform infrared spectroscopy | Microfibres (rayon/viscose polyester cellulose and cotton) | Baeza-Martinez et al. (2022) |
Blood samples from 22 healthy volunteers | Netherlands | Fourier transform infrared spectroscopy | Polyethylene terephthalate, polyethylene, and polymers of styrene | Leslie et al. (2022) |
Placenta from healthy women and have a vaginal delivery | Italy | Raman microspectroscopy | Polypropylene | Ragusa et al. (2021a) |
Placental tissue and meconium specimens during two caesarean sections for breech deliveries | Austria | Fourier transform infrared spectroscopy | Polyethylene, polypropylene, polystyrene, and polyurethane | Braun et al. (2021b) |
The widespread contamination of microplastics is a concerning issue.