Laboratório de Ecofisiologia Animal-Departamento de Ciências Fisiológicas, Universidade Estadual de Londrina, Rodovia Celso Garcia Cid, Km 380. C.P. 10011, CEP: 86051-970 Londrina, Paraná, Brazil; Instituto Federal do Paraná, Campus Londrina, Rua João XXIII, 600, Jardim Dom Bosco, CEP: 86060-370, Londrina, Paraná, Brasil.
Laboratório de Ecofisiologia Animal-Departamento de Ciências Fisiológicas, Universidade Estadual de Londrina, Rodovia Celso Garcia Cid, Km 380. C.P. 10011, CEP: 86051-970 Londrina, Paraná, Brazil; Instituto Federal do Paraná, Campus Londrina, Rua João XXIII, 600, Jardim Dom Bosco, CEP: 86060-370, Londrina, Paraná, Brasil.
Ecotoxicol Environ Saf. 2018 Oct;161:735-745. doi: 10.1016/j.ecoenv.2018.06.029. Epub 2018 Jun 25.
Important concentrations of Zn, Mn and Fe were detected in a stream near a coal mining area and promoted, in field, biomarkers alterations in the bivalve Anodontites trapesialis. In order to understand the isolated and mixed effects of these metals on these Neotropical bivalves, we run short-term experiments under laboratory controlled conditions. After 96 h-exposure, tissues (gills, mantle, digestive gland, muscle, hemolymph) were removed for metal bioaccumulation analysis, oxidative stress biomarkers (reactive oxygen species (ROS), total antioxidant capacity, lipoperoxidation (LPO), proteins carbonylation (PC), metallothionein (MT), activity of superoxide dismutase and glutathione S-transferase and hemocytes DNA damage) and cholinesterase (ChE versus ASCh activity) activity evaluation. We run three independent tests. In Zn test, clams were exposed to three concentrations of Zn (0.18 mg L, 1.0 mg L, 5.0 mg L); in Mn test, clams were exposed to three concentrations of Mn (0.1 mg L, 0.5 mg L, 5.0 mg L) and in Mix test, clams were exposed to the mixture Zn (1 mg L) + Mn (0.5 mg L), with and without Fe (5.0 mg L). After single exposure to 5.0 mg L, Zn bioaccumulated in all tissues, but only in mantle and hemolymph after exposure to 1.0 mg L. The increased MT in gills of A. trapesialis exposed to Zn appears to be sufficient to avoid damage, since LPO occurred only in digestive glands from animals exposed to 5.0 mg L. We suggested that A. trapesialis had a metabolic suppression in consequence of Mn presence, based on the following results: the decrease of ROS in gills, the decrease of the Zn and Mn concentrations in tissues and the decrease of ChE versus ASCh activity in muscle. Despite this, animals exposed to Mn suffer oxidative damages (LPO and PC) in the mantle and digestive gland and MT increased in the mantle. These results showed A. trapesialis responded differently to each metal and Mn caused more damage. When exposed to Fe, gills level of ROS was increased, despite no changes in metal accumulation occurred. On the other hand, after exposure to the mixtures, tissues bioaccumulated Zn and previously observed damages caused by Mn and Fe disappeared. Consequently, biomarkers were less affected under mixture treatments, demonstrating mixtures effects or responses were not simply a combination of single exposures to Zn, Mn and Fe, but depend on metals toxicokinetics.
在一个采煤区附近的溪流中检测到 Zn、Mn 和 Fe 的重要浓度,并在野外促进了双壳类 Anodontites trapesialis 生物标志物的改变。为了了解这些金属对这些新热带双壳类动物的单独和混合影响,我们在实验室控制条件下进行了短期实验。暴露 96 小时后,取出组织(鳃、套膜、消化腺、肌肉、血淋巴)进行金属生物积累分析、氧化应激生物标志物(活性氧(ROS)、总抗氧化能力、脂质过氧化(LPO)、蛋白质羰基化(PC)、金属硫蛋白(MT)、超氧化物歧化酶和谷胱甘肽 S-转移酶的活性和血细胞 DNA 损伤)和胆碱酯酶(ChE 与 ASCh 活性)活性评估。我们进行了三个独立的测试。在 Zn 测试中,蛤暴露于三种 Zn 浓度(0.18mg/L、1.0mg/L、5.0mg/L);在 Mn 测试中,蛤暴露于三种 Mn 浓度(0.1mg/L、0.5mg/L、5.0mg/L),在混合测试中,蛤暴露于混合物 Zn(1mg/L)+Mn(0.5mg/L),有和没有 Fe(5.0mg/L)。暴露于 5.0mg/L 后,Zn 会在所有组织中积累,但仅在暴露于 1.0mg/L 后在套膜和血淋巴中积累。暴露于 Zn 后,A. trapesialis 鳃中的 MT 增加,表明可能足以避免损伤,因为仅在暴露于 5.0mg/L 的动物的消化腺中发生 LPO。我们认为 A. trapesialis 由于 Mn 的存在而发生代谢抑制,这是基于以下结果:鳃中 ROS 的减少、组织中 Zn 和 Mn 浓度的减少以及肌肉中 ChE 与 ASCh 活性的减少。尽管如此,暴露于 Mn 的动物在套膜和消化腺中受到氧化损伤(LPO 和 PC),并且 MT 在套膜中增加。这些结果表明 A. trapesialis 对每种金属的反应不同,并且 Mn 造成的损害更大。当暴露于 Fe 时,鳃中的 ROS 水平增加,尽管金属积累没有变化。另一方面,暴露于混合物后,组织中积累了 Zn,以前由 Mn 和 Fe 引起的损伤消失了。因此,在混合物处理下,生物标志物受影响较小,表明混合物的作用或反应不是 Zn、Mn 和 Fe 的单一暴露的简单组合,而是取决于金属的毒代动力学。