Instituto de Ciências Biológicas, Universidade Federal do Rio Grande (FURG), Rio Grande, RS, Brazil.
Aquat Toxicol. 2011 Jan 17;101(1):88-99. doi: 10.1016/j.aquatox.2010.09.005. Epub 2010 Sep 18.
In vivo and in vitro studies were performed to evaluate acute toxicity, organ-specific distribution, and tissue accumulation of copper in Callinectes sapidus acclimated to two different experimental salinities (2 and 30 ppt). Blue crabs were quite tolerant to copper. Acute dissolved copper toxicity (96-h LC(50) and its corresponding 95% confident interval) was higher at salinity 2 ppt (5.3 (3.50-8.05) μM Cu) than at 30 ppt (53.0 (27.39-102.52) μM Cu). The difference between salinities can be completely explained based on the water chemistry because it disappeared when 96-h LC(50) values were expressed as the free Cu(2+) ion (3.1 (1.93-4.95) μM free Cu at 2 ppt versus 5.6 (2.33-13.37) μM free Cu at 30 ppt) or the Cu(2+) activity (1.4 (0.88-2.26) μM Cu activity at 2 ppt versus 1.7 (0.71-4.07) μM Cu activity at 30 ppt). The relationships between gill Cu burden and % mortality were very similar at 2 and 30 ppt, in accord with the Biotic Ligand Model. In vivo experiments showed that copper concentration in the hemolymph is not dependent on metal concentration in the surrounding medium at either experimental salinity. They also showed that copper flux into the gills is higher than into other tissues analyzed, and that anterior and posterior gills are similarly important sites of copper accumulation at both experimental salinities. In vitro experiments with isolated-perfused gills showed that there is a positive relationship between copper accumulation in this tissue and the metal concentration in the incubation media for both anterior and posterior gills. A similar result was observed at both low and high salinities. Furthermore, in vitro experiments showed that copper accumulation in posterior gills is also positively and strongly dependent on the incubation time with copper. Gill copper accumulation occurred at a lower rate in the first 2h of metal exposure, increasing markedly after this "steady-state" period. This finding was corroborated by a significant increase in copper influx to the gill perfusate (corresponding to crab hemolymph) after this time, measured using (64)Cu. In vivo, after uptake from solution, (64)Cu was primarily accumulated in the gills and the rest of the body rather than in the hemolymph, hepatopancreas, or other internal tissues. Overall, the present findings indicate that gills are a key target organ for copper accumulation, as well as an important biological barrier against the excessive uptake of copper into the hemolymph and the subsequent distribution of this metal to internal organs of the blue crab.
进行了体内和体外研究,以评估在适应两种不同实验盐度(2 和 30 ppt)的美味蓝蟹中铜的急性毒性、器官特异性分布和组织积累。蓝蟹对铜具有很强的耐受性。在盐度为 2 ppt(5.3(3.50-8.05)μM Cu)时,急性溶解铜毒性(96-h LC50 及其相应的 95%置信区间)高于 30 ppt(53.0(27.39-102.52)μM Cu)。盐度之间的差异可以完全用水化学来解释,因为当 96-h LC50 值表示为游离 Cu(2+)离子(2 ppt 时为 3.1(1.93-4.95)μM 游离 Cu,30 ppt 时为 5.6(2.33-13.37)μM 游离 Cu)或 Cu(2+)活性(2 ppt 时为 1.4(0.88-2.26)μM Cu 活性,30 ppt 时为 1.7(0.71-4.07)μM Cu 活性)时,差异就消失了。2 和 30 ppt 时,鳃铜负担与死亡率之间的关系非常相似,符合生物配体模型。体内实验表明,在任一实验盐度下,血淋巴中的铜浓度都不依赖于周围介质中的金属浓度。实验还表明,铜流入鳃的速度高于流入其他组织的速度,而且在前、后鳃同样是铜积累的重要部位,在两种实验盐度下都是如此。用离体灌流鳃进行的体外实验表明,在前、后鳃中,该组织的铜积累与孵育介质中的金属浓度之间存在正相关关系。在低盐度和高盐度下都观察到了类似的结果。此外,体外实验还表明,在后鳃中,铜的积累也与暴露于铜的孵育时间呈正相关且很强。在暴露于金属的最初 2 小时内,鳃铜的积累速度较低,在这个“稳定状态”期之后,积累速度显著增加。这一发现得到了(64)Cu 测量到的鳃灌流液(对应于蟹血淋巴)中铜流入增加的证实。在体内,从溶液中摄取后,(64)Cu 主要积累在鳃和身体的其他部位,而不是在血淋巴、肝胰腺或其他内部组织中。总的来说,本研究结果表明,鳃是铜积累的关键靶器官,也是阻止铜过度摄取到血淋巴并随后将这种金属分配到蓝蟹内部器官的重要生物屏障。