Barata Carlos, Markich Scott J, Baird Donald J, Taylor Graeme, Soares Amadeu M V M
Departamento de Biologia, Universidade de Aveiro, Campus de Santiago, 3810-193, Aveiro, Portugal.
Aquat Toxicol. 2002 Oct 2;60(1-2):85-99. doi: 10.1016/s0166-445x(01)00275-2.
To date, studies on genetic variability in the tolerance of aquatic biota to chemicals have focused on exposure to single chemicals. In the field, metals occur as elemental mixtures, and thus it is essential to study whether the genetic consequences of exposure to such mixtures differs from response to single chemicals. This study determined the feeding responses of three Daphnia magna Straus clones exposed to Cd and Zn, both individually and as mixtures. Tolerance to mixtures of Cd and Zn was expressed as the proportional feeding depression of D. magna to Cd at increasing zinc concentrations. A quantitative genetic analysis revealed that genotype and genotype x environmental factors governed population responses to mixtures of both metals. More specifically, genetic variation in tolerance to sublethal levels of Cd decreased at those Zn concentrations where there were no effects on feeding, and increased again at Zn concentrations that affected feeding. The existence of genotype x environmental interactions indicated that the genetic consequences of exposing D. magna to mixtures of Cd and Zn cannot be predicted from the animals' response to single metals alone. Therefore, current ecological risk assessment methodologies for predicting the effects of chemical mixtures may wish to incorporate the concept of genetic variability. Furthermore, exposure to low and moderate concentrations of Zn increased the sublethal tolerance to Cd. This induction of tolerance to Cd by Zn was also observed for D. magna fed algae pre-loaded with both metals. Furthermore, in only one clone, physiological acclimatization to zinc also induced tolerance to cadmium. These results suggest that the feeding responses of D. magna may be related to gut poisoning induced by the release of metals from algae under low pH conditions. In particular, both induction of metallothionein synthesis by Zn and competition between Zn and Cd ions for uptake at target sites on the gut wall may be involved in determining sublethal responses to mixtures of both metals.
迄今为止,关于水生生物对化学物质耐受性的遗传变异性研究主要集中在单一化学物质的暴露上。在野外,金属以元素混合物的形式存在,因此研究暴露于此类混合物的遗传后果是否不同于对单一化学物质的反应至关重要。本研究确定了三个大型溞(Daphnia magna Straus)克隆在单独暴露于镉(Cd)和锌(Zn)以及同时暴露于二者混合物时的摄食反应。对Cd和Zn混合物的耐受性表现为在锌浓度增加时大型溞对Cd的摄食抑制比例。定量遗传分析表明,基因型和基因型×环境因素决定了种群对两种金属混合物的反应。更具体地说,在对摄食无影响的锌浓度下,对亚致死水平镉的耐受性遗传变异降低,而在影响摄食的锌浓度下又再次增加。基因型×环境相互作用的存在表明,仅根据动物对单一金属的反应无法预测大型溞暴露于Cd和Zn混合物的遗传后果。因此,当前用于预测化学混合物影响的生态风险评估方法可能需要纳入遗传变异性的概念。此外,暴露于低浓度和中等浓度的锌会增加对镉的亚致死耐受性。对于预先加载了两种金属的藻类喂养的大型溞,也观察到锌对镉耐受性的这种诱导作用。此外,仅在一个克隆中,对锌的生理适应也诱导了对镉的耐受性。这些结果表明,大型溞的摄食反应可能与低pH条件下藻类释放金属引起肠道中毒有关。特别是,锌诱导金属硫蛋白合成以及锌和镉离子在肠道壁靶位点上的吸收竞争可能都参与了决定对两种金属混合物的亚致死反应。