Bagchi D, Bagchi M, Hassoun E A, Stohs S J
Department of Pharmaceutical and Administrative Sciences, Creighton University, Omaha, NE 68178, USA.
Toxicology. 1995 Dec 15;104(1-3):129-40. doi: 10.1016/0300-483x(95)03156-a.
Reactive oxygen species may be involved in the toxicity of various pesticides and we have, therefore, examined the in vivo effects of structurally dissimilar polyhalogenated cyclic hydrocarbons (PCH), such as endrin and chlordane, chlorinated acetamide herbicides (CAH), such as alachlor, and organophosphate pesticides (OPS), such as chlorpyrifos and fenthion, on the production of hepatic and brain lipid peroxidation and DNA-single strand breaks (SSB), two indices of oxidative stress and oxidative tissue damage. The selected pesticides were administered p.o. to female Sprague-Dawley rats in two 0.25 LD50 doses at 0 h and 21 h and killed at 24 h. In a parallel set of experiments, we have determined the in vitro effects of these pesticides on the DNA-SSB and enhanced lactate dehydrogenase leakage (LDH) from neuroactive PC-12 cells in culture. In vitro production of reactive oxygen species by these pesticides was also assessed by determining the enhanced chemiluminescence responses of hepatic and brain homogenates. Following treatment of rats with endrin, chlordane, alachlor, chlorpyrifos and fenthion, increases of 2.8-, 3.0-, 4.2-, 4.3- and 4.8-fold were observed in hepatic lipid peroxidation, respectively, while at these same doses, increases in lipid peroxidation of 2.4-, 2.1-, 3.6-, 4.6- and 5.3-fold, respectively, were observed in brain homogenates. Increases of 4.4-, 3.9-, 1.6-, 3.0- and 3.5-fold were observed in hepatic DNA-SSB following treatment of the rats with endrin, chlordane, alachlor, chlorpyrifos and fenthion, respectively, while at these same doses, increases of 1.9-, 1.7-, 2.2-, 1.4-, 1.4-fold, respectively, were observed in brain nuclear DNA-SSB. Following in vitro incubation of hepatic and brain tissues with 1 nmol/ml of each of the five pesticides, maximum increases in chemiluminescence occurred within 4-7 min of incubation and persisted for over 10 min. Increases of 3.0-, 2.7-, 3.6-, 4.9- and 4.4-fold were observed in chemiluminescence following in vitro incubation of the liver homogenates with endrin, chlordane, alachlor, chlorpyrifos and fenthion, respectively, while increases of 1.7-, 1.8-, 2.0-, 3.4- and 3.7-fold, respectively, were observed in the brain homogenates. Increases of 2.2-, 2.3-, 2.9-, 2.9- and 3.4-fold were observed in the chemiluminescence responses in the liver homogenates of the animals treated with endrin, chlordane, alachlor, chlorpyrifos and fenthion, respectively, while increases of 1.8-, 2.0-, 3.2-, 2.9- and 2.4-fold, respectively, were observed in the brain homogenates. Cultured neuroactive PC-12 cells were incubated with the pesticides and the release of the enzyme lactate dehydrogenase (LDH) into the media as an indicator of cellular damage and cytotoxicity was examined. Maximal release of LDH from cultured PC-12 cells was observed at 100 nM concentrations of the pesticides. Increases of 2.3-, 2.5-, 2.8-, 3.1 and 3.4-fold were observed in LDH leakage following incubation of the PC-12 cells with endrin, chlordane, alachlor, chlorpyrifos and fenthion, respectively. Following incubation of the cultured PC-12 cells with 100 nM concentrations of these same pesticides, increases in DNA-SSB of 2.5-, 2.2-, 2.1-, 2.4- and 2.5-fold, respectively, were observed. The results clearly demonstrate that these different classes of pesticides induce production of reactive oxygen species and oxidative tissue damage which may contribute to the toxic manifestations of these xenobiotics. Reactive oxygen species may serve as common mediators of programmed cell death (apoptosis) in response to many toxicants and pathological conditions.
活性氧可能参与了各种农药的毒性作用,因此,我们研究了结构不同的多卤代环烃(PCH),如异狄氏剂和氯丹,氯代乙酰胺类除草剂(CAH),如甲草胺,以及有机磷农药(OPS),如毒死蜱和倍硫磷,对肝脏和脑组织脂质过氧化及DNA单链断裂(SSB)产生的影响,这两个指标反映了氧化应激和氧化组织损伤。将选定的农药以两个0.25 LD50剂量经口给予雌性Sprague-Dawley大鼠,给药时间分别为0小时和21小时,并于24小时处死。在一组平行实验中,我们测定了这些农药对培养的神经活性PC-12细胞DNA-SSB及乳酸脱氢酶(LDH)泄漏增加的体外影响。通过测定肝脏和脑组织匀浆增强的化学发光反应,也评估了这些农药在体外产生活性氧的情况。用异狄氏剂、氯丹、甲草胺、毒死蜱和倍硫磷处理大鼠后,肝脏脂质过氧化分别增加了2.8倍、3.0倍、4.2倍、4.3倍和4.8倍,而在相同剂量下,脑匀浆脂质过氧化分别增加了2.4倍、2.1倍、3.6倍、4.6倍和5.3倍。用异狄氏剂、氯丹、甲草胺、毒死蜱和倍硫磷处理大鼠后,肝脏DNA-SSB分别增加了4.4倍、3.9倍、1.6倍、3.0倍和3.5倍,而在相同剂量下,脑细胞核DNA-SSB分别增加了1.9倍、1.7倍、2.2倍、1.4倍和1.4倍。将肝脏和脑组织与五种农药中的每一种以1 nmol/ml进行体外孵育后,化学发光在孵育4 - 7分钟内达到最大增加,并持续超过10分钟。肝脏匀浆与异狄氏剂、氯丹、甲草胺、毒死蜱和倍硫磷体外孵育后,化学发光分别增加了3.0倍、2.7倍、3.6倍、4.9倍和4.4倍,而脑匀浆分别增加了1.7倍、1.8倍、2.0倍、3.4倍和3.7倍。用异狄氏剂、氯丹、甲草胺、毒死蜱和倍硫磷处理动物后,肝脏匀浆化学发光反应分别增加了2.2倍、2.3倍、2.9倍、2.9倍和3.4倍,而脑匀浆分别增加了1.8倍、2.0倍、3.2倍、2.9倍和2.4倍。将培养的神经活性PC-12细胞与这些农药孵育,并检测作为细胞损伤和细胞毒性指标的乳酸脱氢酶(LDH)释放到培养基中的情况。在农药浓度为100 nM时,观察到培养PC-12细胞中LDH的最大释放。PC-12细胞与异狄氏剂、氯丹、甲草胺、毒死蜱和倍硫磷孵育后,LDH泄漏分别增加了2.3倍、2.5倍、2.8倍、3.1倍和3.4倍。将培养的PC-12细胞与100 nM浓度的这些相同农药孵育后,DNA-SSB分别增加了2.5倍、2.2倍、2.1倍、2.4倍和2.5倍。结果清楚地表明,这些不同类别的农药诱导活性氧的产生和氧化组织损伤,这可能导致这些外源性物质的毒性表现。活性氧可能作为许多毒物和病理状况下程序性细胞死亡(凋亡)的共同介质。