“…For example, laboratory studies have shown that organic pollutants are released more rapidly from MPs in simulated gut media than in seawater . Whilst there is ongoing debate in the literature as to the relevance of so-called Trojan horse effects for aquatic organisms under environmentally relevant scenarios, , there is evidence for its importance for seabirds, , and indeed the kinetic features of drug release from polymer particles have long been actively exploited to optimize bioavailability in therapeutic context. , In environmental context, the toxicity of plastic leachates, extracted from the plastic material prior to exposure, has been demonstrated. , Disparate information has been reported from laboratory studies on the effects of contaminants in combination with MPs and nanoplastics (NPs): the body burden and/or toxicity of organic contaminants may be decreased, , increased, , or unaffected, , depending on the spatial and temporal conditions in the exposure medium and within the organism, , the extent to which the contaminants are released from the particles within the organism (which is generally not determined), and the measured toxicological endpoint. Clarification of the potential risks to aquatic organisms posed by polymer additives and other acquired co-contaminants requires a mechanistic approach that accounts for the dynamic nature of the involved processes including characterization of the uptake/release kinetics of contaminant–MP/NP interactions, concentration gradients in the polymer and aqueous phases, sorption affinity of the polymer backbone for each (class of) contaminant, particle size, local exposure conditions within organisms as well as the particle residence time and location within the organism (gut vs muscle tissue vs lipid-rich tissues, etc.…”