Department of Biochemistry, Delta State University, Abraka, Nigeria.
Biometals. 2010 Dec;23(6):961-71. doi: 10.1007/s10534-010-9313-5. Epub 2010 Feb 27.
This study sets out to compare the absorption and toxicity of Cadmium (Cd) administered via the food-chain and inorganic Cd administered in drinking water after 1 and 3 months exposure using rats as animal model. The food-chain was mimicked by exposing rats to diet containing Cd pre-exposed fish. The uptake of Cd by the rats after both mode of exposure was calculated by summing up the Cd burden in the liver and kidneys and was expressed in terms of % intake. The toxicity of Cd was assessed by monitoring biochemical indices of liver function in the plasma and liver. Regardless of the mode of exposure of the rats, the Cd load in the liver and kidney was significantly (P < 0.05) higher than the respective controls with the kidney having a significantly higher load than the liver after both periods of exposure. However irrespective of the mode of exposure, more Cd was accumulated in the liver and kidney of the 3 months exposed rats relative to those exposed for 1 month. The uptake of Cd by rats exposed to Cd via the food-chain for 1 and 3 months was significantly (P < 0.05) lower when compared to the corresponding water mediated Cd exposed rats, except for the liver after 3 months of exposure. The liver L-ALT activity of rats administered inorganic Cd in drinking water for 1 and 3 months was significantly (P < 0.05) lower as compared to controls. Parallel analysis of the plasma showed no significant (P > 0.05) difference in L-ALT activity between both groups after the same periods of exposure. The L-AST activity in the plasma of rats similarly exposed to Cd for 1 and 3 months was significantly (P < 0.05) higher as compared to controls with a corresponding reduction in the liver. Conversely no significant (P > 0.05) change was observed in plasma and liver L-ALT and L-AST activities after food-chain mediated exposure to Cd for 1 and 3 months in relation to their respective controls. These findings indicate that Cd incorporated in fish is more easily bioavailable, but less toxic relative to inorganic Cd salts at the end of 3 months of exposure in rats.
本研究旨在比较通过食物链摄入和经饮水摄入的 Cd(镉)在 1 个月和 3 个月暴露后的吸收和毒性,以大鼠为动物模型。通过让大鼠摄入预先暴露于 Cd 的鱼的饮食来模拟食物链。两种暴露方式后,大鼠对 Cd 的吸收量通过将肝脏和肾脏中的 Cd 负担相加来计算,并以摄入量的百分比表示。通过监测血浆和肝脏中肝功能的生化指标来评估 Cd 的毒性。无论大鼠的暴露方式如何,暴露 1 个月和 3 个月后,肝脏和肾脏中的 Cd 负荷均显著(P < 0.05)高于相应的对照组,且暴露 3 个月后肾脏的负荷显著高于肝脏。然而,无论暴露方式如何,暴露 3 个月的大鼠肝脏和肾脏中积累的 Cd 均明显(P < 0.05)高于暴露 1 个月的大鼠。与相应的饮水 Cd 暴露大鼠相比,经食物链暴露 1 个月和 3 个月的大鼠对 Cd 的吸收量显著(P < 0.05)降低,只有暴露 3 个月后的肝脏除外。经饮水摄入无机 Cd 1 个月和 3 个月的大鼠肝脏 L-ALT 活性显著(P < 0.05)低于对照组。同样,经过相同时间的暴露后,两组之间的血浆 L-ALT 活性无显著差异(P > 0.05)。同样暴露 1 个月和 3 个月的大鼠血浆 L-AST 活性显著(P < 0.05)高于对照组,而肝脏则相应降低。相反,经食物链摄入 Cd 1 个月和 3 个月后,血浆和肝脏 L-ALT 和 L-AST 活性均无明显变化(P > 0.05)与各自的对照组。这些发现表明,在暴露结束时,与无机 Cd 盐相比,鱼类中所含的 Cd 更容易被生物利用,但毒性较低。