The global production of plastics has grown drastically due to their low cost and versatility. In 2022, over 400 million metric tons were produced, with polyethylene (PE) accounting for 26.3%. Microplastics (MPs), which are plastic particles ranging from 1 µm to 5 mm, represent a significant environmental threat, mainly entering the ocean through freshwater sources and inadequate disposal and recycling practices. It is estimated that between 0.13 and 3.8 million metric tons of plastic end up in the world’s seas and oceans each year. MPs accumulate in all parts of the ocean, affecting marine life through physical and chemical interactions and transporting pollutants such as heavy metals and pesticides. The thesis hypothesis suggests that high-density polyethylene (HDPE) MPs can produce toxic effects and adsorb metallic and organic contaminants, modulating their bioavailability and toxicity for aquatic species in the marine trophic chain formed by microalgae, zooplankton, and fish. The general objective is to evaluate the ecotoxicological effects of HDPE MPs alone and in combination with contaminants like mercury (Hg) and the pesticide chlorpyrifos (CPF) in a model marine trophic chain. The toxic impact of oxidized and non-oxidized HDPE MPs on the microalga Rhodomonas lens was examined. The effects of contaminants such as chlorpyrifos (CPF) and mercury (Hg), alone and combined with MPs, on the growth, cell viability, and pigment content of the microalgae were investigated. The results indicated that non-oxidized MPs initially increased cell concentration due to the release of exopolymeric substances by the microalgae, facilitating the aggregation of MPs and microalgae. However, at 96 hours, there were no significant differences in growth rates compared to the controls. Cell viability was significantly reduced due to surface damage caused by physical interaction with MPs. The combination of MPs with contaminants generally showed reduced toxicity compared to contaminants alone, suggesting lower bioavailability of the contaminants when adsorbed on MPs. This highlights the complexity of interactions between MPs and contaminants and their impact on marine microalgae. The thesis also focused on studying the impact of HDPE MPs on the copepods Acartia tonsa, investigating physiological, reproductive, and biochemical responses, as well as the bioaccumulation of Hg and CPF. Oxidized and non-oxidized MPs did not show significant lethal or sublethal effects after 48 hours, but exposure increased the antioxidant system response in the copepods. Bioaccumulation of Hg and CPF was similar between MPs and contaminants dissolved in water, although exposure to MPs loaded with contaminants slightly increased physiological and reproductive toxicity. Furthermore, copepods exposed to MA+Hg/CPF showed lower bioaccumulation and lesser biological effects compared to those exposed to MPs+Hg/CPF, highlighting the importance of particle nature in contaminant toxicity. The effects of trophic transfer of MPs, alone and combined with Hg and CPF, on fish larvae (Scophthalmus maximus) through the ingestion of contaminated copepods were also evaluated. The responses analyzed included bioaccumulation of Hg/CPF, biochemical biomarkers, and physiological responses. Bioaccumulation of Hg was significantly higher through MPs compared to MA, while CPF bioaccumulation showed similar patterns in MPs and MA. The larvae showed alterations in antioxidant enzymes and evident neurotoxicity with non-oxidized MPs; however, no significant effects were observed on growth, condition index, or survival. Exposure to Hg and MPs+Hg produced histological changes in the gills, suggesting that MPs can increase the bioavailability of Hg, causing adverse effects on tissues. The toxic effects were generally lower with MA+Hg/CPF, highlighting the lower risk of natural particles in the transfer of contaminants in the trophic chain.



