Departamento de Ciências Fisiológicas, Universidade Estadual de Londrina, CP 10011, 86057-970 Londrina, Paraná, Brazil.
Departamento de Ciências Fisiológicas, Universidade Estadual de Londrina, CP 10011, 86057-970 Londrina, Paraná, Brazil.
Ecotoxicol Environ Saf. 2014 Feb;100:7-14. doi: 10.1016/j.ecoenv.2013.11.014. Epub 2013 Dec 20.
The present study aimed to evaluate biochemical and genotoxic effects of the herbicides atrazine (ATZ) and Roundup(®) (RD) separately, as well as their mixture, on the freshwater clam Corbicula fluminea after 96 h exposure. Animals were exposed to 2 and 10 ppb of ATZ (ATZ2 and ATZ10), 2 and 10 ppm of RD (RD2 and RD10) and the following mixtures: 2 ppb ATZ+2ppm RD (AR2) and 10 ppb ATZ+10 ppm RD (AR10). Activities of ethoxyresorufin-O-deethylase (EROD), glutathione-S-transferase (GST), superoxide dismutase (SOD), catalase (CAT), glutathione peroxidase (GPx) and glutathione reductase (GR), as well as the multixenobiotic resistance mechanism (MXR), reduced glutathione concentrations (GSH) and lipid peroxidation (LPO) were measured in gills and digestive gland. DNA damage was determined in clams hemocytes through the comet assay. The gills were more susceptible to the action of the herbicides and the results showed that ATZ2 and ATZ10 caused a significant reduction in EROD and the mixture leads to a significant decrease in EROD and MXR. No significant change in the biotransformation parameters was observed in the digestive gland. Regarding the primary antioxidant defenses, SOD activity increased in the gills of clams exposed to ATZ10 and RD10 and in the digestive gland of animals exposed to RD2 and RD10, CAT activity was significantly reduced only in digestive gland of clams exposed RD10 while GPX increased in the gills after exposure to ATZ2 and RD10. The exposure to RD10 caused a significant increase in LPO in both gills and digestive gland. While the exposure to ATZ and RD separately did not increase DNA damage, the exposure to AR2 and AR10 caused a significant increase in the occurrence of DNA damage. In conclusion, this study showed that both herbicides applied alone caused effects on C. fluminea; ATZ interfered mostly in biotransformation while RD interfered mainly in antioxidant defenses leading to lipid peroxidation. The herbicides mixture showed antagonistic effects on the gills EROD and on lipid peroxidation in gills and digestive gland and synergistic effects on the gills MXR and on DNA damage in the hemocytes.
本研究旨在评估除草剂莠去津(ATZ)和草甘膦(RD)分别以及混合暴露 96 小时后对淡水蛤蜊 C. fluminea 的生化和遗传毒性影响。动物暴露于 2 和 10 ppb 的 ATZ(ATZ2 和 ATZ10)、2 和 10 ppm 的 RD(RD2 和 RD10)以及以下混合物:2 ppb ATZ+2ppm RD(AR2)和 10 ppb ATZ+10 ppm RD(AR10)。在鳃和消化腺中测量了乙氧基Resorufin-O-脱乙基酶(EROD)、谷胱甘肽 S-转移酶(GST)、超氧化物歧化酶(SOD)、过氧化氢酶(CAT)、谷胱甘肽过氧化物酶(GPx)和谷胱甘肽还原酶(GR)的活性,以及多药耐药机制(MXR)、还原型谷胱甘肽浓度(GSH)和脂质过氧化(LPO)。通过彗星试验测定了蛤蜊血细胞中的 DNA 损伤。结果表明,除草剂对鳃的作用更敏感,ATZ2 和 ATZ10 导致 EROD 显著降低,混合物导致 EROD 和 MXR 显著降低。在消化腺中未观察到生物转化参数的显著变化。关于初级抗氧化防御,暴露于 ATZ10 和 RD10 的蛤蜊鳃中 SOD 活性增加,暴露于 RD2 和 RD10 的动物消化腺中 CAT 活性显著降低,仅在暴露于 RD10 的蛤蜊消化腺中 GPX 增加。RD10 的暴露导致鳃和消化腺中 LPO 的显著增加。虽然单独接触 ATZ 和 RD 不会增加 DNA 损伤,但接触 AR2 和 AR10 会导致 DNA 损伤的发生率显著增加。综上所述,本研究表明,单独使用两种除草剂都会对 C. fluminea 产生影响;ATZ 主要干扰生物转化,而 RD 主要干扰抗氧化防御导致脂质过氧化。除草剂混合物对鳃 EROD 以及鳃和消化腺中的脂质过氧化具有拮抗作用,对鳃 MXR 和血细胞中的 DNA 损伤具有协同作用。