Université de Bordeaux, UMR EPOC 5805, GEMA Team Av. des Facultés, 33405 Talence, France.
Ecotoxicol Environ Saf. 2011 May;74(4):600-6. doi: 10.1016/j.ecoenv.2010.10.020. Epub 2010 Oct 28.
Laboratory experiments using stable Cd isotopes ((110)Cd and (112)Cd) were conducted to separately and simultaneously characterize Cd accumulation in different tissues of Pacific oysters (Crassostrea gigas) via the (i) trophic and (ii) direct pathways. For this, we exposed juvenile oysters to (110)Cd-spiked seawater ((110)Cd: 2 μg l(-1); constant level) and (112)Cd-spiked food (Thalassiossera weissflogii, (112)Cd: 2 μg l(-1) in 35×10(3) cells/oyster/L) in four experimental treatment groups, each containing 6 oysters, for 21 days with constant trophic feeding. These Cd contamination levels were ∼10 times lower than those typically used in experimental accumulation studies. Three oysters per treatment group were dissected every 7 days with separate sampling of the gills, digestive gland and the rest of the body. Metallothioneins were analysed in the digestive gland and gills. Cadmium concentrations and isotope ratios were measured in water (daily) and tissues (weekly) by GF-AAS and ICP-MS. The observed time-dependant evolution in Cd concentrations and (110)Cd/(114)Cd and (112)Cd/(114)Cd isotope ratios clearly revealed the bio-accumulation short-term kinetics and pathways of Cd contamination in the different tissues. Under the experimental conditions, significantly changed isotope ratios in gills and the digestive gland of oysters suggested rapid and efficient contamination by (110)Cd derived from direct exposure followed by internal Cd transfer between organs. Trophic contamination became measurable after 14 days of exposure corresponding to a trophic transfer rate of 1%. Constant metallothionein levels during the experiment suggested that the initially present metallothionein levels were sufficient to deal with the experimental Cd exposure.
采用稳定的 Cd 同位素((110)Cd 和 (112)Cd)进行实验室实验,分别和同时通过(i)摄食和(ii)直接途径来描述太平洋牡蛎(Crassostrea gigas)不同组织中 Cd 的积累。为此,我们将幼年牡蛎暴露于 (110)Cd 污染海水((110)Cd:2μg l(-1);恒定水平)和 (112)Cd 污染食物(Thalassiossera weissflogii,(112)Cd:35×10(3)个细胞/牡蛎/L 中的 2μg l(-1))中,在 4 个实验处理组中,每组包含 6 只牡蛎,进行为期 21 天的持续摄食。这些 Cd 污染水平比实验积累研究中通常使用的水平低约 10 倍。每 7 天从每个处理组中解剖 3 只牡蛎,分别采集鳃、消化腺和其余身体部分。在消化腺和鳃中分析金属硫蛋白。用 GF-AAS 和 ICP-MS 每周测量水(每天)和组织(每周)中的 Cd 浓度和同位素比值。观察到的 Cd 浓度和 (110)Cd/(114)Cd 和 (112)Cd/(114)Cd 同位素比值的时间依赖性演变清楚地揭示了不同组织中 Cd 污染的生物积累短期动力学和途径。在实验条件下,牡蛎鳃和消化腺中同位素比值的显著变化表明,直接暴露后 Cd 的快速和有效污染,以及器官之间的内部 Cd 转移。暴露 14 天后,摄食污染变得可测量,对应的摄食转移率为 1%。实验过程中金属硫蛋白水平保持恒定,表明最初存在的金属硫蛋白水平足以应对实验中的 Cd 暴露。