Gadolinium at Low Concentration Suppresses both Osteoclastic and Osteoblastic Activities in the Scales of Goldfish

N. Suzuki, Kazuki Watanabe, Aika Sekimoto, M. Urata, M. Zanaty, T. Sekiguchi, Yoichiro Kitani, H. Matsubara, A. Srivastav, A. Hattori
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引用次数: 3

Abstract

For determining the effect of environmental pollutants on fish bone metabolism, we have developed an in vitro bioassay system using teleost scales that has osteoclasts, osteoblasts and bone matrix as markers: alkaline phosphatase (ALP) for osteoblasts and tartrate-resistant acid phosphatase (TRAP) for osteoclasts. Using this bioassay, the influence of gadolinium (Gd) on osteoclasts and osteoblasts of goldfish scales was examined in the present study. Gd sensitively inhibited TRAP activity. Even Gd at 10-13 M suppressed TRAP activity at 6 hours of incubation. At 18 hours of incubation, this inhibition occurred only at 10-7 and 10-6 M. After 36 hours of incubation, Gd did not influence TRAP activity. In osteoblasts, ALP activity was also suppressed by Gd in the range of 10-10 to 10-6 M for 6 to 18 hours of incubation. At 36 and 64 hours of incubation, ALP activity was significantly suppressed by Gd (36 hours: 10-9 to 10-6 M; 64 hours: 10-7 and 10-6 M). At 96 hours of incubation, however, Gd did not influence ALP activity. This is the first report to indicate the toxicity of Gd on fish bone metabolism using TRAP and ALP enzyme activities. The toxicity of Gd to osteoblasts is comparable to that of tributyltin, an aquatic environmental pollutant used as a biocide in anti-fouling paint. Gd is used in Magnetic Resonance Imaging (MRI) for clinical diagnoses. To avoid the toxicity of Gd ions, chelated forms, known as Gd-based contrast agents, are used for MRI diagnosis. Without a specific recycling process, these compounds are quickly released by urinary excretion and released into environmental waters. Therefore, it is possible that anthropogenic Gd influences aquatic animals. Considering our present data together with that of anthropogenic Gd pollution, we should conduct a Gd risk assessment to protect the ecosystem in the aquatic environment.
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低浓度钆抑制金鱼鳞片破骨细胞和成骨细胞活性
为了确定环境污染物对鱼骨代谢的影响,我们开发了一种体外生物测定系统,使用硬骨鱼鳞片,以破骨细胞、成骨细胞和骨基质为标记:碱性磷酸酶(ALP)用于成骨细胞,抗酒石酸酸性磷酸酶(TRAP)用于破骨细胞。采用生物测定法,研究了钆(Gd)对金鱼鳞片破骨细胞和成骨细胞的影响。Gd敏感地抑制TRAP活性。即使是10-13 M的Gd也能抑制6小时的TRAP活性。在孵育18小时时,这种抑制作用仅发生在10-7和10-6 m。孵育36小时后,Gd不影响TRAP活性。在成骨细胞中,Gd在10-10 ~ 10-6 M范围内抑制ALP活性,持续6 ~ 18小时。在孵育36和64 h时,Gd显著抑制ALP活性(36 h: 10-9 ~ 10-6 M;64小时:10-7 M和10-6 M)。然而,在96小时孵育时,Gd不影响ALP活性。这是第一次用TRAP和ALP酶活性研究Gd对鱼骨代谢的毒性。Gd对成骨细胞的毒性与三丁基锡相当,三丁基锡是一种水生环境污染物,用作防污涂料中的杀菌剂。Gd在磁共振成像(MRI)中用于临床诊断。为了避免Gd离子的毒性,被称为Gd基造影剂的螯合形式被用于MRI诊断。没有特定的回收过程,这些化合物很快通过尿液排泄释放到环境水体中。因此,可能是人为的Gd影响了水生动物。考虑到我们现有的数据和人为污染的数据,我们应该进行Gd风险评估,以保护水生环境的生态系统。
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