Effects of nanoplastics and microplastics on the availability of pharmaceuticals and personal care products in aqueous environment.

Nanoplastics (NPs) and microplastics (MPs) could act as potential carriers for pharmaceuticals and personal care products (PPCPs) and alter the bioavailability in the aquatic environment. The effects of NPs and MPs of polystyrene (PS) and polyethylene (PE) on the availability of five PPCPs including carbamazepine, bisphenol A, estrone, triclocarban and 4-tert-octylphenol were investigated by negligible depletion solid- phase microextraction (nd-SPME). The freely dissolved concentrations of PPCPs decreased with the increasing concentrations of NPs/MPs. The overall order of the sorption coefficients (log K NP / log K MP) of PPCPs was as follows: 100 nm PS > 50 nm PS > 1 µm PS > 100 µm PS > 100 µm PE. Sorption of PPCPs by NPs was generally 1–2 orders of magnitude stronger than to MPs. The log K NP / log K MP values (3.16–5.21) increased with the log K OW (2.45–5.28) of PPCPs, however, linear correlation was only observed between log K MP and log K OW. The particle size, specific surface area, aggregation state as well as hydrophobicity played an important role in the sorption. Coexistence of fulic acid (FA) with NPs inhibited the sorption due to the fouling of FA on NPs. This study suggests that sorption of PPCPs to MPs/NPs could reduce bioavailability of PPCPs in the aquatic environment. [Display omitted] • Nd-SPME was developed for PPCP availability study at environmental concentrations. • Sorption of PPCPs to NPs was 1–2 orders of magnitude stronger than to MPs. • The order of the sorption: 100 nm PS > 50 nm PS > 1 µm PS > 100 µm PS > 100 µm PE. • Sorption of PPCPs to NPs are differed from MPs due to specified aggregation of NPs. • Coexistence with fulic acid inhibited the sorption of PPCPs to NPs. [ABSTRACT FROM AUTHOR]