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白鲢罗非鱼对微囊藻毒素急性、亚急性毒性响应
引用本文:沈强,刘永定,李敦海,李嗣新.白鲢罗非鱼对微囊藻毒素急性、亚急性毒性响应[J].中国环境科学,2019,39(6):2633-2643.
作者姓名:沈强  刘永定  李敦海  李嗣新
作者单位:1. 水利部中国科学院水工程生态研究所, 水利部水工程生态效应与生态修复重点实验室, 湖北 武汉 430079; 2. 中国科学院水生生物研究所, 湖北 武汉 430072
基金项目:湖北省自然科学基金资助项目(2017CFB678);948计划项目(201509)
摘    要:为了探究不同控藻鱼类对产毒微囊藻的适应机制,为生物操纵的鱼种选择提供依据,研究了白鲢和罗非鱼对微囊藻毒素(MC)的生物富集、降解,及两种鱼对毒素的抗性、解毒机制的差异性.结果发现:在喂食微囊藻实验中,白鲢、罗非鱼对MC日摄入量达到10mg/kg,2种鱼均对MC有较强抗性.微囊藻经鱼摄入后,MC总含量在白鲢、罗非鱼粪便中分别下降到71.5%、6.0%,罗非鱼对MC降解能力远高于白鲢.白鲢和罗非鱼的肝系数分别从(1.19±0.21)%、(2.24±0.19)%下降到(0.79±0.06)%、(1.72±0.07)%,均表现出显著差异性下降(P<0.05).微囊藻毒素在白鲢、罗非鱼肌肉中积累量分别为(1.57±0.31)μg/kg、(10.81±6.52)μg/kg (鲜重)、肝脏中积累量分别为(4.28±1.64)mg/kg、(2.48±0.15)mg/kg (鲜重).MC在白鲢、罗非鱼肌肉、肝脏中的积累量均存在显著差异性(P<0.05).罗非鱼肌肉中毒素含量是白鲢的6.9倍.在微囊藻毒素LR (MC-LR)对白鲢和罗非鱼的急性毒性效应实验中,MC-LR对白鲢、罗非鱼的LD50为270和790μg/kg,罗非鱼对毒素有更强耐受性.喂食毒藻和i.p.注射MC均导致白鲢和罗非鱼肝细胞内脂滴大量出现.2种鱼在MC-LR注射后,谷胱甘肽(GSH)含量均表现出6h内明显下降.6h后两种鱼GSH含量均逐步回升,二者差异显著(p<0.05).实验结果表明,罗非鱼对MC降解能力远高于白鲢.白鲢主要摄食群体微囊藻的群体胶鞘和附着细菌,胞内微囊藻毒素释放量小,白鲢这种摄食机制导致它能以产毒微囊藻为食而受到较轻危害.罗非鱼体内消化酶对微囊藻和MC具较强的消化降解能力;GSH含量及相关酶活性水平高,对体内毒素清除效率高.从食用安全性角度出发,与罗非鱼相比,白鲢是更适合用于控制蓝藻水华的鱼种,可广泛应用于蓝藻水华控制中.

关 键 词:有害藻类水华  微囊藻毒素  白鲢  罗非鱼  抗性机制  
收稿时间:2018-11-12

The acute and subacute response of sliver carp and tilapia to microcystin
SHEN Qiang,LIU Yong-ding,LI Dun-hai,LI Si-xin.The acute and subacute response of sliver carp and tilapia to microcystin[J].China Environmental Science,2019,39(6):2633-2643.
Authors:SHEN Qiang  LIU Yong-ding  LI Dun-hai  LI Si-xin
Institution:1. Key Laboratory of Ecological Impacts of Hydraulic-Projects and Restoration of Aquatic Ecosystem of Ministry of Water Resources, Institute of Hydroecology, Ministry of Water Resources and Chinese Academy of Sciences, Wuhan 430079, China; 2. Institute of Hydrobiology, the Chinese Academy of Sciences, Wuhan 430072, China
Abstract:In order to study adaptative mechanisms of sliver carp and tilapia on harmful algal blooms and provide scientific methods of fish species selection in biological manipulation, systematic research was conducted on bioaccumulation, degradation of microcystin and the differences in resistance and detoxification mechanisms on sliver carp (Hypophthalmichthys molitrix) and tilapia (Oreochromis niloticus). In toxic Microcystis feeding experiment, the daily intake of microcystin by sliver carp and tilapia was up to 10mg/kg body weight. Both fishes show strong resistance to MC. Microcystin concentrations in feces of sliver carp and tilapia after Microcystis intake were significantly decreased to 71.5% and 6.0% respectively (P<0.05). The degradation ability of tilapia to toxic Microcystis and microcystin is much higher than silver carp. The hepatosomatic index of sliver carp and tilapia was significantly decreased from (1.19±0.21)% and (2.24±0.19)% to (0.79±0.06)% and (1.72±0.07)% respectively (P<0.05). Bioaccumulations of MC of the two species were (1.57±0.31) and (10.81±6.52)μg/kg (fresh weight) in the muscle, (4.28±1.64) and (2.48±0.15)mg/kg (fresh weight) in the liver. There were significant differences between MC accumulation in the muscle and liver of each species (P<0.05). Microcystin concentration in the muscle of tilapia was 6.9 times higher than that of silver carp. During the toxic experiment, LD50 of microcystin-LR was 270µg/kg on sliver carp and 790µg/kg on tilapia, which suggested microcystin tolerance of tilapia is stronger than that of sliver carp. Enormous lipid droplets were observed in the liver cell of the two species whether fed with Microcystis or intraperitoneally injected with microcystin. After intraperitoneal injection with microcystin-LR, the content of GSH in the two species showed a significant decrease in 6h and then increased gradually. Significant difference of GSH content was found between the two species (P<0.05). The results showed that the degradation ability of tilapia to microcystin is much higher than silver carp. Silver carp mainly feeds on the mucilage sheath and adhesion bacteria of colonial Microcystis with small amount of intracellular microcystin released. This mechanism can effectively protect silver carp fed with Microcystis to less damage. The digestive enzymes in tilapia have strong digestion and degradation ability to Microcystis and microcystin, and the high level of GSH content and related enzyme activity ensure efficient detoxification of toxins in vivo. From the view of food safety, compared with tilapia, silver carp is the species which is more suitable and to be widely used for cyanobacteria bloom control.
Keywords:harmful algal blooms (HABs)  microcystin  sliver carp  tilapia  resistance mechanism  
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