— The paper examines the temperature dependence of the specific growth rate and ratio of variable to maximum fluorescence ( FV/ FM) in a number of marine planktonic algae from collections of...

The high rate of production and use of copper oxide nanoparticles (CuO NPs) results in its accumulation in the environment. However, the effect of large quantities of CuO NPs on aquatic ecosystems is not fully known. In aquatic ecosystems, phytoplankton is the primary producer of organic matter and the basis of all the trophic interactions; accordingly, the potential effect of CuO NPs on the microalgae community is of great concern. This study established the main patterns of changes in morphological, structural, functional, fluorescent and cytometric parameters in the marine diatom Thalassiosira weissflogii after adding CuO NPs to the medium at concentrations of 250–2500 µg L-1. As shown, the investigated pollutant has cytotoxic, genotoxic and mechanical effect on the microalga covering almost all the aspects of cell functioning. A two-fold decrease in the culture abundance relative to the control is observed at the toxicant content of 550 µg L-1 in the medium. At CuO NPs content above 750 µg L-1, a pronounced inhibition of the alga growth is recorded, as well as a decrease in the efficiency of its photosynthetic apparatus, a disturbance of membrane integrity, an increase in cell volume, a rise in abundance of dead/inactive cells in the culture, enlargement and deformation of nuclei, an increase in reactive oxygen species production, and depolarisation of the mitochondrial membrane. Our results show that high CuO NPs concentrations in water can cause serious disruptions in phytoplankton functioning and in equilibrium of aquatic ecosystems in general.

Comparative assessment of stress responses of two microalgal species differing in their cell structure and habitats, Prorocentrum cordatum and Dunaliella salina, to the presence of copper oxide nanoparticles (NP) in the medium was carried out. The nanoparticles were found to have a similar effect on both species. Their toxic effect resulted in progressing production of reactive oxygen species in the algal cells, while their specific growth rates decreased, probably due to Cu²⁺ release from the oxide or to penetration of some nanoparticles into the cells. NP mechanical impact resulted in their aggregation at the cell surface and deformation of the cell envelopes. The presence in the toxicant in the medium caused a reliable increase in cell volume, plasmalemma perforation, and predominance of deformed cells of irregular shape in the cultures. Two species exhibited different resistance to CuO NP. The sublethal and lethal concentrations for P. cordatum were 400 and 520 µg/L, respectively, compared to 3000 and 3750 µg/L for D. salina. The possible causes for resistance of D. salina to CuO NP are discussed. D. salina is able to produce ligands (phytochelatins and metallothionenis) in high concentrations, which may be released into the medium and bind the Cu²⁺ ions. Moreover, the habitats of D. salina are extreme, which may promote its stress tolerance, probably a genetically determined feature and a part of their overall resistance to other contaminants. High resistance of D. salina to CuO NP may also be due to its ability to secrete extracellular polymers under stress conditions; they may form a protective layer preventing the interaction between the microalgae and NP. Application of P. cordatum for biomonitoring of NP-contaminated seawater environments is proposed. D. salina may be promising for water bioremediation.