Zeman Florence Anna, Gilbin Rodolphe, Alonzo Frédéric, Lecomte-Pradines Catherine, Garnier-Laplace Jacqueline, Aliaume Catherine
Laboratoire de Radioécologie et Ecotoxicologie, Institut de Radioprotection et Sûreté Nucléaire, Cadarache, Bat 186, BP 3, 13115 Saint-Paul-lez-Durance Cedex, France.
Aquat Toxicol. 2008 Feb 18;86(3):370-8. doi: 10.1016/j.aquatox.2007.11.018. Epub 2007 Dec 4.
Acute uranium toxicity (48 h immobilisation test) for Daphnia magna was determined in two different exposure media, differing in pH and alkalinity. LC(50) varied strongly between media, from 390+/-40 microgL(-1)U at pH 7 to 7.8+/-3.2 mgL(-1)U at pH 8. According to the free ion activity model uranium toxicity varies as a function of free uranyl concentration. This assumption was examined by calculating uranium speciation in our water conditions and in those reported in the literature. Predicted changes in free uranyl concentration could not solely explain observed differences in toxicity, which might be due to a competition or a non-competitive inhibition of H(+) for uranium transport and/or the involvement of other bioavailable chemical species of uranium. Chronic effects of uranium at pH 7 on mortality, ingestion and respiration, fecundity and dry mass of females, eggs and neonates were investigated during 21-day exposure experiments. A mortality of 10% was observed at 100 microgL(-1)U and EC(10) for reproduction was 14+/-7 microgL(-1)U. Scope for growth was affected through a reduction in feeding activity and an increase in oxygen consumption at 25 microgL(-1)U after 7 days of exposure. This had strong consequences for somatic growth and reproduction, which decreased, respectively, by 50% and 65% at 50 microgL(-1)U after 7 days and at 25 microgL(-1)U after 21 days. Uranium bioaccumulation was quantified and associated internal alpha dose rates from 2.1 to 13 microGyh(-1) were estimated. Compared to the toxicity of other alpha-emitting radionuclides and stable trace metals, our results confirmed the general assumption that uranium chemical toxicity predominates over its radiotoxicity.
在两种pH值和碱度不同的暴露介质中测定了大型溞的急性铀毒性(48小时固定试验)。两种介质中的半数致死浓度(LC50)差异很大,从pH值为7时的390±40微克/升铀到pH值为8时的7.8±3.2毫克/升铀。根据自由离子活性模型,铀毒性随自由铀酰浓度的变化而变化。通过计算我们实验用水条件以及文献报道条件下的铀形态来检验这一假设。预测的自由铀酰浓度变化不能完全解释所观察到的毒性差异,这可能是由于H(+)对铀运输的竞争或非竞争性抑制作用,和/或其他生物可利用铀化学物种的参与。在为期21天的暴露实验中,研究了pH值为7时铀对雌性、卵和幼体的死亡率、摄食和呼吸、繁殖力及干重的慢性影响。在100微克/升铀时观察到10%的死亡率,繁殖的效应浓度(EC1)为14±7微克/升铀。暴露7天后,在25微克/升铀时,生长范围受到影响,摄食活动减少,耗氧量增加。这对体细胞生长和繁殖产生了强烈影响,在暴露7天后50微克/升铀时以及暴露21天后25微克/升铀时,体细胞生长和繁殖分别下降了50%和65%。对铀的生物累积进行了量化,并估计了2.1至13微戈瑞/小时的相关内部α剂量率。与其他发射α粒子的放射性核素和稳定痕量金属的毒性相比,我们的结果证实了一般假设,即铀的化学毒性高于其放射性毒性。