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Not so dangerous? PET microplastics toxicity on freshwater microalgae and cyanobacteria

Environmental Pollution 2023 48 citations ? Citation count from OpenAlex, updated daily. May differ slightly from the publisher's own count. Score: 60 ? 0–100 AI score estimating relevance to the microplastics field. Papers below 30 are filtered from public browse.
Martin Brtnický, Martin Brtnický, Ondřej Pěnčík, Ondřej Pěnčík, Katarína Molnárová, Michaela Durdakova, Michaela Durdakova, Daniel Klofáč, Katarína Molnárová, Michaela Durdakova, Martin Brtnický, Martin Brtnický, Martin Brtnický, Martina Koláčková, Ondřej Pěnčík, Ondřej Pěnčík, Michaela Durdakova, Katarína Molnárová, Attilla Kucsera, Martina Koláčková, Dalibor Húska Martin Brtnický, Daniel Klofáč, Martin Brtnický, Daniel Klofáč, Martina Koláčková, Attilla Kucsera, Lukáš Richtera, Petr Cápal, Vojtěch Adam, P Svec, Dalibor Húska Martin Brtnický, Zuzana Bytešníková, Lukáš Richtera, Martin Brtnický, Vojtěch Adam, Martin Brtnický, Dalibor Húska

Summary

Researchers tested whether PET microplastics are toxic to freshwater algae and cyanobacteria and found that the effects were relatively mild compared to other plastic types. While PET particles did cause some changes in growth and photosynthesis at high concentrations, the organisms largely tolerated the exposure. The study suggests that not all microplastics are equally harmful, and PET may pose lower risks to aquatic primary producers.

Polymers
Study Type Environmental

Microalgae and cyanobacteria are among the most important primary producers and are responsible for the production of 50-80% of the oxygen on Earth. They can be significantly affected by plastic pollution, as the vast majority of plastic waste ends up in rivers and then the oceans. This research focuses on green microalgae Chlorella vulgaris (C. vulgaris), Chlamydomonas reinhardtii (C. reinhardtii), filamentous cyanobacterium Limnospira (Arthrospira) maxima (L.(A.) maxima) and how they are affected by environmentally relevant PET-MPs (polyethylene-terephtalate microplastics). Manufactured PET-MPs have asymmetric shape, size between 3 and 7 μm and were used in concentrations ranging from 5 mg/L to 80 mg/L. The highest inhibitory rate of growth was found in C. reinhardtii (-24%). Concentration-dependent changes in chlorophyll a composition were found in C. vulgaris and C. reinhardtii, not in L. (A.) maxima. Furthermore, cell damage was detected in all three organisms by CRYO-SEM (shriveling, cell wall disruption), but the cyanobacterium was the least damaged. A PET-fingerprint was detected on the surface of all tested organisms using FTIR, indicating the adherence of PET-MPs. The highest rate of PET-MPs adsorption was detected in L. (A.) maxima. Specifically, characteristic spectra were observed at ∼721, 850, 1100, 1275, 1342, and 1715 cm which are specific for functional groups of PET-MPs. Nitrogen and carbon content significantly increased in L. (A.) maxima under exposure to 80 mg/L due to the PET-MPs adherence and mechanical stress. In all three tested organisms, weak exposure-related ROS generation was detected. In general, cyanobacteria seem to be more resistant to the effects of MPs. However, organisms in the aquatic environment are exposed to MPs over a longer time scale, so it is important to use the present findings for further longer-term experiments on environmentally relevant organisms.

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