Heitkamp M A, Adams W J, Hallas L E
Environmental Sciences Center, Monsanto Company, St. Louis, MO 63167.
Can J Microbiol. 1992 Sep;38(9):921-8. doi: 10.1139/m92-149.
To evaluate immobilized bacteria technology for the removal of low levels of glyphosate (N-phosphonomethylglycine) from aqueous industrial effluents, microorganisms with glyphosate-degrading activity obtained from a fill and draw enrichment reactor inoculated with activated sludge were first exposed to glyphosate production wastes containing 500-2000 mg glyphosate/L. The microorganisms were then immobilized by adsorption onto a diatomaceous earth biocarrier contained in upflow Plexiglas columns. The columns were aerated, maintained at pH 7.0-8.0, incubated at 25 degrees C, supplemented with NH4NO3 (50 mg/L), and exposed to glyphosate process wastes pumped upflow through the biocarrier. Glyphosate degradation to aminomethylphosphonic acid was initially > 96% for 21 days of operation at flows yielding hydraulic residence times (HRTs) as short as 42 min. Higher flow rate studies showed > 98% removal of 50 mg glyphosate/L from the waste stream could be achieved at a HRT of 23 min. Glyphosate removal of > 99% at a 37-min HRT was achieved under similar conditions with a column inoculated with a pure culture of Pseudomonas sp. strain LBr, a bacterium known to have high glyphosate-degrading activity. After acid shocking (pH 2.8 for 18 h) of a column of immobilized bacteria, glyphosate-degrading activity was regained within 4 days without reinoculation. Although microbial growth and glyphosate degradation were not maintained under low organic nutrient conditions in the laboratory, the low levels of degradable carbon (45-94 mg/L) in the industrial effluent were sufficient to support prolonged glyphosate-degrading activity. The results demonstrated that immobilized bacteria technology is effective in removing low levels of glyphosate in high-volume liquid waste streams.
为评估固定化细菌技术去除工业废水中低浓度草甘膦(N-膦酰基甲基甘氨酸)的效果,首先将从接种活性污泥的填充-间歇式富集反应器中获得的具有草甘膦降解活性的微生物,暴露于含有500-2000mg/L草甘膦的生产废水之中。然后通过吸附到上流有机玻璃柱中包含的硅藻土生物载体上,将这些微生物固定化。这些柱子进行曝气,维持pH值在7.0-8.0,在25℃下培养,补充硝酸铵(50mg/L),并使草甘膦生产废水以向上流的方式泵入通过生物载体。在水力停留时间(HRT)短至42分钟的流量下运行21天,草甘膦降解为氨基甲基膦酸的初始降解率>96%。更高流速的研究表明,在HRT为23分钟时,可从废水中去除>98%的50mg/L草甘膦。在类似条件下,用已知具有高草甘膦降解活性的假单胞菌属菌株LBr的纯培养物接种的柱子,在37分钟HRT时可实现>99%的草甘膦去除率。在对一列固定化细菌进行酸冲击(pH2.8,持续18小时)后,无需重新接种,草甘膦降解活性在4天内恢复。尽管在实验室的低有机养分条件下微生物生长和草甘膦降解无法维持,但工业废水中低水平的可降解碳(45-94mg/L)足以支持长时间的草甘膦降解活性。结果表明,固定化细菌技术对于去除大量液体废水中的低浓度草甘膦是有效的。