Key Laboratory of Urban Environment and Health, Institute of Urban Environment, Chinese Academy of Sciences, 1799 Jimei Bouleward, Jimei District, Xiamen, 361021, China.
Centre for Ecotoxicology, Ecotoxicology and Environmental Contaminants Sections, Department of Environment and Climate Change, 480 Weeroona Road, P.O. Box 29, Lidcombe, New South Wales 2141, Australia.
Environ Toxicol Chem. 2010 Feb;29(2):365-372. doi: 10.1002/etc.31.
The chronic toxicity of dietary cadmium to the saltwater cladoceran Moina monogolica Daday and its relative toxicity compared with aquatic exposure were investigated in the present study. The microalgae Chlorella pyrenoidosa, exposed to cadmium in growth inhibition tests, had a 96-h median effective concentration (EC50) of 81.2 microg Cd/L (95% confidence intervals [CIs] = 71.9-95.1). C. pyrenoidosa exposed for 96 h to sublethal dissolved cadmium concentrations in the range 4.10 +/- 0.30 to 70.29 +/- 0.31 microg/L resulted in algal cadmium burdens up to 73.86 x 10(-16) g Cd/cell. Cellular cadmium burdens accumulated in a dose-dependent manner, whereas cell densities inversely declined from 670 x 10(4) to 38 x 10(4) cells/ml with exposure to the increasing aqueous cadmium concentrations. C. pyrenoidosa preexposed to cadmium and used as food in a chronic 21-d toxicity test with the cladoceran M. monogolica, containing no added dissolved cadmium, inhibited reproduction. Significant reductions of the net reproduction rate (R(0)) per brood were observed in all broods, and the decline in the number of neonates produced increased with each subsequent brood. The cadmium concentration (4.10 +/- 0.30 microg/L) in the algal culture water that produced the lowest algal cadmium burden (2.85 +/- 0.76 x 10(-16) g Cd/cell) was shown to inhibit M. monogolica reproduction and was compared with the water quality criteria (WQC) of China. This comparison indicated that dietary exposure to cadmium may cause sublethal responses at concentrations below the current cadmium WQC of China for aquaculture.
本研究调查了膳食镉对盐水溞状蚤(Moina monogolica Daday)的慢性毒性及其与水生暴露的相对毒性。在生长抑制试验中,暴露于镉的微藻蛋白核小球藻的 96 小时半数有效浓度(EC50)为 81.2 微克 Cd/L(95%置信区间[CI] = 71.9-95.1)。蛋白核小球藻在 4.10 +/- 0.30 至 70.29 +/- 0.31 微克/L 的亚致死溶解镉浓度下暴露 96 小时,导致藻类镉负担高达 73.86 x 10(-16) g Cd/细胞。细胞内镉负担呈剂量依赖性积累,而细胞密度则随暴露于增加的水溶液镉浓度而相反下降,从 670 x 10(4) 至 38 x 10(4) 细胞/ml。蛋白核小球藻预先暴露于镉,并用作为含有未添加溶解镉的溞状蚤(M. monogolica)慢性 21 天毒性试验的食物,抑制了繁殖。所有后代的净生殖率(R(0))均显著降低,产生的幼体数量随每一代后代的增加而下降。在产生最低藻类镉负担(2.85 +/- 0.76 x 10(-16) g Cd/细胞)的藻类培养液中,浓度为 4.10 +/- 0.30 微克/L 的镉被证明抑制了溞状蚤的繁殖,并与中国的水质标准(WQC)进行了比较。该比较表明,膳食暴露于镉可能导致在低于中国现行水产养殖镉 WQC 的浓度下产生亚致死反应。