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微囊藻毒素-RR在巴氏兵鲶、多齿珍妮丽鱼和博氏南美油鲶中的摄取、组织分布及积累。一项野外和实验室研究。

Uptake, tissue distribution and accumulation of microcystin-RR in Corydoras paleatus, Jenynsia multidentata and Odontesthes bonariensis. A field and laboratory study.

作者信息

Cazenave Jimena, Wunderlin Daniel Alberto, de Los Angeles Bistoni María, Amé María Valeria, Krause Eberhard, Pflugmacher Stephan, Wiegand Claudia

机构信息

Universidad Nacional de Córdoba, Facultad de Ciencias Exactas, Físicas y Naturales, Cátedra Diversidad Animal II, Velez Sarsfield 299, 5000 Córdoba, Argentina.

出版信息

Aquat Toxicol. 2005 Oct 15;75(2):178-90. doi: 10.1016/j.aquatox.2005.08.002.

Abstract

The uptake and accumulation of microcystin-RR (MC-RR) in fish was investigated under laboratory conditions and in wild fish. Jenynsia multidentata and Corydoras paleatus were exposed for 24h to 50mug/L MC-RR dissolved in water. After exposure, liver, gill, brain, intestine, gall bladder, blood and muscle were analyzed for MC-RR by HPLC and analysis confirmed by LC-ESI-TOF-MS spectrometry. Furthermore, wild individuals of Odontesthes bonariensis were sampled from the eutrophic, cyanobacteria-containing San Roque reservoir, and analyzed for the presence of MC-RR in liver, gill, intestine, and muscle. MC-RR was found in liver, gills, and muscle of all exposed and wild fish, while in C. paleatus MC-RR was also present in the intestine. Moreover, we found presence of MC-RR in brain of J. multidentata. Results indicate that MC-RR uptake might occur at two different organs: intestine and gills, through either feeding (including drinking) or respiratory activities. This suggests that MC-RR is taken into the blood stream after absorption, and distributed to different tissues. The liver showed the major bioaccumulation of MC-RR in both experimentally exposed and wild individuals, with muscle of wild fish showing relative high amounts of this toxin in comparison with those exposed in the laboratory; though MC-RR was present in muscle of fish exposed for 24h. The amount of MC-RR in muscle of O. bonariensis exceeded the value suggested by WHO to be safe, thus causing a health risk to persons consuming fish as a result of chronic exposure to microcystin. Gills also showed bioaccumulation of MC-RR, raising questions on the mechanism involved in the possible uptake of MC-RR through gills as well as on its accumulation in this organ. Although MC-LR has been reported in brain of fish, this is the first report confirming the presence of MC-RR in this organ, which means that both toxins are able to cross the blood-brain barrier. These findings also raise questions on the probable neurotoxicity of microcystins.

摘要

在实验室条件下以及对野生鱼类进行了微囊藻毒素-RR(MC-RR)在鱼类体内摄取和积累的研究。将多齿珍妮丽鱼和巴氏兵鲶暴露于溶解在水中的50μg/L MC-RR中24小时。暴露后,通过高效液相色谱法(HPLC)对肝脏、鳃、脑、肠道、胆囊、血液和肌肉中的MC-RR进行分析,并通过液相色谱-电喷雾离子化-飞行时间质谱法(LC-ESI-TOF-MS)进行确认。此外,从富营养化的、含有蓝藻的圣罗克水库采集了野生长臂银汉鱼个体,分析其肝脏、鳃、肠道和肌肉中MC-RR的存在情况。在所有暴露的和野生的鱼类的肝脏、鳃和肌肉中均发现了MC-RR,而在巴氏兵鲶的肠道中也存在MC-RR。此外,我们在多齿珍妮丽鱼的脑中发现了MC-RR的存在。结果表明,MC-RR的摄取可能发生在两个不同的器官:肠道和鳃,通过摄食(包括饮水)或呼吸活动。这表明MC-RR在吸收后进入血流,并分布到不同组织。在实验暴露的个体和野生个体中,肝脏均显示出MC-RR的主要生物积累,与实验室暴露的鱼类相比,野生鱼类的肌肉中该毒素含量相对较高;尽管在暴露24小时的鱼类肌肉中也存在MC-RR。长臂银汉鱼肌肉中的MC-RR含量超过了世界卫生组织建议的安全值,因此由于长期接触微囊藻毒素,食用鱼类会给人类健康带来风险。鳃也显示出MC-RR的生物积累,这引发了关于通过鳃摄取MC-RR的可能机制以及其在该器官中积累的问题。虽然已报道鱼类脑中存在微囊藻毒素-LR(MC-LR),但这是首次证实该器官中存在MC-RR的报告,这意味着两种毒素都能够穿过血脑屏障。这些发现也引发了关于微囊藻毒素可能的神经毒性的问题。

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