Department of Botany, Banaras Hindu University, Varanasi 221005, India.
Department of Botany, Banaras Hindu University, Varanasi 221005, India.
Ecotoxicol Environ Saf. 2021 Feb;209:111799. doi: 10.1016/j.ecoenv.2020.111799. Epub 2020 Dec 24.
Himalayan mountains are subjected to the intensive and unjudicial application of chlorpyrifos (CP) in agricultural practices; hence it has spurred concerns over food safety and environmental consequences. These low-temperature mountainous regions are foremost ecosystems, representing the large-scale distribution of cold trapped CP residues. A bacterial consortium ECO-M was formed by isolating the CP degrading bacterial strains viz Agrobacterium tumefaciens strain ECO1, Cellulosimicrobium funkei strain ECO2, Shinella zoogloeoides strain ECO3 and Bacillus aryabhattai strain ECO4. At an initial concentration of 50 mg L, consortium ECO-M degraded 100% of CP within 6 days. Emergence and subsequent degradation of the two metabolites, 3, 5, 6-trichloro-2-pyridinol (TCP) and 2-hydroxypyridine were confirmed by GC-MS analysis. A degradation pathway of CP by isolated strains has been proposed. A general factorial experimental design was effectuated to prognosticate the optimum biodegradation by manifesting the optimal biological and physicochemical factors. Fitness of the experimental design was affirmed experimentally by employing optimized factors i.e., temperature 30 °C, CP concentration 50 mg L and an inoculum size of 10% (v/v). The model appropriacy and the rationality of the optimization procedure were appraised by installing an in-situ microcosms experiment using the real contaminated soil collected from the Himalayan mountain ecosystem. The augmentation culture seems to be effectively conspicuous in stimulating maximum degradation up to 94.3% in the CP contaminated soil.
喜马拉雅山脉在农业实践中受到了氯吡硫磷(CP)的密集和不公正的应用;因此,人们对食品安全和环境后果表示担忧。这些低温山区是首要的生态系统,代表了大量低温被困 CP 残留的分布。通过分离 CP 降解细菌菌株,形成了一个细菌联合体 ECO-M,这些菌株分别是根癌农杆菌菌株 ECO1、纤维分解真菌菌株 ECO2、鞘氨醇单胞菌菌株 ECO3 和芽孢杆菌菌株 ECO4。在初始浓度为 50mg/L 的情况下,联合体 ECO-M 在 6 天内降解了 100%的 CP。通过 GC-MS 分析证实了两种代谢物 3,5,6-三氯-2-吡啶醇(TCP)和 2-羟基吡啶的出现和随后的降解。提出了一种由分离菌株降解 CP 的途径。通过实施一般的析因实验设计,通过表现出最佳的生物和物理化学因素来预测最佳的生物降解。通过使用优化的因素,即温度 30°C、CP 浓度 50mg/L 和 10%(v/v)的接种量,实验证实了实验设计的适用性。通过使用从喜马拉雅山生态系统中收集的实际污染土壤进行原位微宇宙实验来评估模型的适当性和优化程序的合理性。增菌培养似乎可以有效地刺激 CP 污染土壤中最大降解率达到 94.3%。