The aquatic environment and the associated fish assemblages are being exposed to an increasing amount of microplastics. Despite the high number of publications on the presence of microplastics in fish, little is known about their uptake, translocation and accumulation within fish organs. Experimental studies on the detection and effects of pristine microplastics in fish have shown controversial and ambiguous results, respectively. Here, we conducted two experiments to detect and assess the impacts of dietary exposure of Danio rerio to different types of pristine microplastics. Our results show that D. rerio recognizes plastic particles as inedible materials but ingests them when mixed with food or fish oil. Accidental ingestion occurs in fish exposed to relatively small (1-5 µm) microplastic particles without associated food or fish oil. Additionally, D. rerio effectively eliminated pristine microplastics 24 h after ingestion; however, retention time was associated with increasing particle size and the intake of additional meals. Clinical signs, such as anorexia and lethargy, are present in fish fed relatively large microplastics (120-220 µm). The ingestion of microplastics does not induce any histopathological changes. To the best of our knowledge, we are able, for the first time, to fully demonstrate the uptake and translocation of plastic microbeads using confocal microscopy. Our results question the findings of previous studies on the detection and effects of pristine microplastics in fish and state that inaccurate interpretations of the histological findings regarding microplastics in fish organs is a prevalent flaw in the current scientific literature. The ever-growing production of plastics 1,2 and their relatively short lifespan 3 , combined with indiscriminate waste-disposal practices and accidental releases 1 , have led to the accumulation of plastics in aquatic environments worldwide 4-9. This situation is especially worrisome due to their long degradation time 2 and potential to be ingested by aquatic organisms 3. In water, plastics undergo weathering 10 through photolytic, mechanical and biological degradation 11,12. Under these circumstances, larger plastics degrade into smaller fragments 12 , i.e., microplastics (MPs) (< 5 mm) 13. Another source of MPs in aquatic environments is micro-sized particles intentionally manufactured for use in domestic products (e.g., cosmetics and clothing) and industrial products (media blasting and industrial feedstock) 11,12 , which are directly introduced into the environment by human activity 10. MPs can display a variety of shapes, sizes and colours 12. In aquatic systems, the predominant shapes of MPs are fibres 14-18 , fragments 6,7,19,20 and microbeads 21. The small size and ubiquity of MPs 22 makes them easily available to aquatic fauna, which are prone to ingest them by confusion with food, accidental ingestion or by transfer through the food chain 23,24. Several studies have documented the ingestion of plastic and MP particles in aquatic species (invertebrat...