Posgrado en Biotecnología, Universidad Politécnica de Pachuca, Ex-Hacienda de Santa Bárbara, Municipio. Zempoala, Hgo., C.P, 43830, Carretera Pachuca Cd. Sahagún Km. 20, Mexico.
Departamento de Biotecnología, Universidad Autónoma Metropolitana, Av. San Rafael Atlixco 186, Leyes de Reforma 1ra Secc, Iztapalapa, 09340, Ciudad de México, Mexico.
J Environ Manage. 2021 Aug 1;291:112688. doi: 10.1016/j.jenvman.2021.112688. Epub 2021 May 6.
We evaluated and characterized the biodegradation of the herbicide diuron in its commercial form above its saturation concentration by Lysinibacillus fusiformis acclimatized by sequential batch culturing. Acclimatization was carried out in eight cycles in liquid culture, improving the capacity of L. fusiformis to remove diuron from 55.13 ± 1.3% in the first batch to 87.2 ± 0.11% in the eighth batch. Diuron biosorption was characterized with Langmuir and Freundlich isotherms, obtaining a maximum biosorption (q) of 0.00885 mg mg. In diuron biodegradation assays, a consumption substrate biomass yield (Y) of 6.266 mg mg was obtained, showing that biodegradation was the main mechanism in diuron removal. Diuron biodegradation by L. fusiformis was characterized by the Monod model, with a maximum specific growth rate (μ) of 0.0245 h and an affinity constant (K) of 344.09 mg L. A low accumulation of 3,4-dichloroaniline with the production of chloride ions indicated dechlorination when diuron was present at high concentrations. A phytotoxic assay conducted with Lactuca sativa showed that the toxicity of an effluent with diuron at 250 mg L decreased when it was pretreated with acclimatized L. fusiformis. Acclimatization by sequential batch culturing improved the ability of L. fusiformis to biodegrade diuron at high concentrations, showing potential in the bioremediation of diuron-contaminated sites.
我们通过连续批次培养使适应后的解草唑(一种除草剂)在其商业形式和过饱和浓度下进行生物降解,并对其进行了评估和特性分析。在液体培养中进行了 8 个周期的适应化处理,提高了 L. fusiformis 从第 1 批的 55.13±1.3%去除解草唑的能力到第 8 批的 87.2±0.11%。采用 Langmuir 和 Freundlich 等温线对解草唑的生物吸附进行了特征分析,得到最大生物吸附(q)为 0.00885mgmg。在解草唑生物降解试验中,获得了 6.266mgmg 的消耗底物生物量产率(Y),表明生物降解是去除解草唑的主要机制。L. fusiformis 对解草唑的生物降解通过 Monod 模型进行了描述,最大比生长速率(μ)为 0.0245h,亲和常数(K)为 344.09mgL。当解草唑浓度较高时,会产生氯离子并积累少量的 3,4-二氯苯胺,表明发生了脱氯作用。用莴苣进行的植物毒性试验表明,当用适应后的 L. fusiformis 预处理含有 250mgL 解草唑的废水时,其毒性会降低。通过连续批次培养进行的适应化处理提高了 L. fusiformis 对高浓度解草唑的生物降解能力,在受解草唑污染的场地的生物修复方面具有潜在应用价值。