Deviller G, Palluel O, Aliaume C, Asanthi H, Sanchez W, Franco Nava M A, Blancheton J-P, Casellas C
Département sciences de l'environnement et santé publique, Faculté de pharmacie, UMR 5556, 15, av. Charles Flahault, 34060 Montpellier, France.
Ecotoxicol Environ Saf. 2005 May;61(1):89-97. doi: 10.1016/j.ecoenv.2004.07.011.
European sea bass were reared in three different systems: one flow-through (FTS), one recirculating (RAS), and one recirculating with a high-rate algae pond (RAS + HRAP). After 1 year of rearing, the final fish weight was 15% lower in the RAS compared to the FTS. The accumulation of a growth-inhibiting substance in the RAS is the main hypothesis explaining this difference. As in environmental risk assessment, fish bioaccumulation markers and biomarkers were used to demonstrate exposure to and effects of the rearing water in the three rearing systems. Thirty fish per system were sacrificed before their condition factor (CF) and liver somatic index (LSI) were calculated. Nine biomarkers, including ethoxyresorufin-O-deethylase (EROD) and superoxide dismutase (SOD), were measured in liver and twelve metals including As, Cd, Cu, Pb, Cr, and Zn, for which there are regulations regarding human consumption, were measured in liver and muscle. In all systems, CF and LSI were not significantly different and no correlation was found with biomarker activity or metal concentration. EROD and SOD activities were significantly increased in RAS. Accumulation of seven and four metals in muscle and liver, respectively, was significantly higher in the RAS relative to FTS. The HRAP prevented metal accumulation except for chromium and arsenic. Eight metal concentrations were significantly higher in liver than in muscle. Concentrations of toxic metals were similar to reported values and below FAO/WHO recommended values for human consumption.
一种是流水式(FTS),一种是循环水式(RAS),还有一种是带有高速藻类池塘的循环水式(RAS + HRAP)。养殖1年后,RAS系统中的最终鱼体重比FTS系统低15%。RAS系统中生长抑制物质的积累是解释这种差异的主要假设。与环境风险评估一样,鱼类生物累积标志物和生物标志物被用于证明三种养殖系统中养殖用水的暴露情况和影响。在计算每个系统中30条鱼的肥满度(CF)和肝脏体指数(LSI)之前,将它们宰杀。在肝脏中测量了9种生物标志物,包括乙氧基异吩唑酮 - O - 脱乙基酶(EROD)和超氧化物歧化酶(SOD),并在肝脏和肌肉中测量了12种金属,包括砷、镉、铜、铅、铬和锌,对于这些金属,有关于人类消费的规定。在所有系统中,CF和LSI没有显著差异,并且未发现与生物标志物活性或金属浓度存在相关性。RAS系统中EROD和SOD活性显著增加。相对于FTS系统,RAS系统中肌肉和肝脏中分别有7种和4种金属的积累显著更高。除铬和砷外,HRAP可防止金属积累。肝脏中的8种金属浓度显著高于肌肉中的浓度。有毒金属的浓度与报告值相似,且低于粮农组织/世界卫生组织推荐的人类消费值。