Use of fish otoliths as a temporal biomarker of field uranium exposure.

This study aimed to determine uranium (U) pollution over time using otoliths as a marker of fish U contamination. Experiments were performed in field contamination (~20 µg L-1: encaged fish: 15d, 50d and collected wild fish) and in laboratory exposure conditions (20 and 250 µg L-1, 20d). We reported the U seasonal concentrations in field waterborne exposed roach fish (Rutilus rutilus), in organs and otoliths. Otoliths were analyzed by ICPMS and LA-ICP SF MS of the entire growth zone. Concentrations were measured on transects from nucleus to the edge of otoliths to characterize environmental variations of metal accumulation. Results showed a spatial and temporal variation of U contamination in water (from 51 to 9.4 µg L-1 at the surface of the water column), a high and seasonal accumulation in fish organs, mainly the digestive tract (from 1000 to 30,000 ng g-1, fw), the gills (from 1600 to 3200 ng g-1, fw) and the muscle (from 144 to 1054 ng g-1, fw). U was detected throughout the otolith and accumulation varied over the season from 70 to 350 ng g-1, close to the values measured (310 ng g-1) after high exposure levels in laboratory conditions. U in otoliths of encaged fish showed rapid and high U accumulation from 20 to 150 ng g-1. The U accumulation signal was mainly detected on the edge of the otolith, showing two U accumulation peaks, probably correlated to fish age, i.e. 2 years old. Surprisingly, elemental U and Zn signatures followed the same pattern therefore using the same uptake pathways. Laboratory, caging and field experiments indicated that otoliths were able to quickly accumulate U on the surface even for low levels and to store high levels of U. This study is an encouraging first step in using otoliths as a marker of U exposure.

Subcellular fractionation and chemical speciation of uranium to elucidate its fate in gills and hepatopancreas of crayfish Procambarus clarkii.

Knowledge of the organ and subcellular distribution of metals in organisms is fundamental for the understanding of their uptake, storage, elimination and toxicity. Detoxification via MTLP and MRG formation and chelation by some proteins are necessary to better assess the metal toxic fraction in aquatic organisms. This work focused on uranium, natural element mainly used in nuclear industry, and its subcellular fractionation and chemical speciation to elucidate its accumulation pattern in gills and hepatopancreas of crayfish Procambarus clarkii, key organs of uptake and detoxification, respectively. Crayfish waterborne exposure was performed during 4 and 10d at 0, 30, 600 and 4000 µg UL(-1). After tissue dissection, uranium subcellular fractionation was performed by successive ultracentrifugations. SEC-ICP MS was used to study uranium speciation in cytosolic fraction. The uranium subcellular partitioning patterns varied according to the target organ studied and its biological function in the organism. The cytosolic fraction accounted for 13-30% of the total uranium amount in gills and 35-75% in hepatopancreas. The uranium fraction coeluting with MTLPs in gills and hepatopancreas cytosols showed that roughly 55% of uranium remained non-detoxified and thus potentially toxic in the cytosol. Furthermore, the sum of uranium amount in organelle fractions and in the non-detoxified part of cytosol, possibly equivalent to available fraction, accounted for 20% (gills) and 57% (hepatopancreas) of the total uranium. Finally, the SEC-ICP MS analysis provided information on potential competition of U for biomolecules similar than the ones involved in endogenous essential metal (Fe, Cu) chelation.

Uranium-induced sensory alterations in the zebrafish Danio rerio.

The effect of chronic exposure to uranium ions (UO(2)(2+)) on sensory tissues including the olfactory and lateral line systems was investigated in zebrafish (Danio rerio) using scanning electron microscopy. The aim of this study was to determine whether exposure to uranium damaged sensory tissues in fish. The fish were exposed to uranium at the concentration of 250 µg l(-1) for 10 days followed by a depuration period of 23 days. Measurements of uranium uptake in different fish organs: olfactory rosettes and bulbs, brain, skin, and muscles, were also determined by ICP-AES and ICP-MS during the entire experimental period. The results showed that uranium displayed a strong affinity for sensory structures in direct contact with the surrounding medium, such as the olfactory and lateral line systems distributed on the skin. A decreasing gradient of uranium concentration was found: olfactory rosettes>olfactory bulbs>skin>muscles>brain. At the end of the experiment, uranium was present in non-negligible quantities in sensory tissues. In parallel, fish exposed to uranium showed severe sensory tissue alterations at the level of the olfactory and lateral line systems. In both sensory systems, the gross morphology was altered and the sensory hair cells were significantly damaged very early after the initiation of exposure (from the 3rd day). At the end of the experiment, after 23 days of depuration, the lateral line system still displayed slight tissue alterations, but approximately 80% of the neuromasts in this system had regenerated. In contrast, the olfactory system took more time to recover, as more than half of the olfactory rosettes observed remained destroyed at the end of the experiment. This study showed, for the first time, that uranium is able to damage fish sensory tissues to such an extent that tissue regeneration is delayed.