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A Comparison of Microbial Bioaugmentation and Biostimulation for Hexavalent Chromium Removal from Wastewater

机译:微生物生物强化与生物刺激去除废水中六价铬的比较

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Hexavalent chromium (VI) in wastewater is a great risk to human health and to the quality of water sources. However, adapted microorganisms can rapidly reduce this chemical species to the trivalent form (III) and make it less active. Our objective was to evaluate the capacity of bacterial isolates for Cr (VI) reduction in nutrient medium and in effluent and to compare indigenous microorganisms with those isolated from wastewater contaminated with Cr (VI). Cr (VI) reduction was also tested with different sources of carbon, nitrogen, and phosphorus at two temperatures (10 and 30 degrees C). Initially, the resistant microorganisms were isolated from the solution with 100 mg L-1 of Cr (VI). Subsequently, we evaluated the effectiveness of the isolates in reducing Cr (VI) I in culture medium under temperature-controlled conditions, with concentrations of 10 and 100 mg L-1 of Cr (VI). In the subsequent step, we studied the isolates and autochthonous microorganism efficiency to reduce Cr (VI) present in contaminated effluent, with the addition of nutrients and at different temperatures (10 and 30 CC). In the culture medium containing 10 mg L-(1) of Cr (VI), isolates were reduced by 100 % in 48 h. When tested against 100 mg L-1 of Cr (VI), the decrease was 70 and 40 % at 120 h of incubation of the isolates 6 and 11, respectively. In the effluent, there was no significant reduction without nutritional biostimulation. When carbon and phosphorus were applied, isolates 6, 11, and indigenous microorganisms reduced 100 % of the Cr (VI) in 72 h. Nitrogen was not limited in terms of effluent characteristics. At 10 degrees C incubation temperature, Cr (VI) was completely reduced but slower compared to incubation at 30 degrees C. The results demonstrate that nutritional biostimulation aided by bioremediation is an excellent tool for reducing hexavalent chromium in wastewater.
机译:废水中的六价铬(六价铬)对人类健康和水源质量构成极大威胁。但是,适应的微生物可以将该化学物种快速还原为三价形式(III),并使其活性降低。我们的目标是评估细菌分离物在营养培养基和废水中还原Cr(VI)的能力,并将本机微生物与从受Cr(VI)污染的废水中分离的微生物进行比较。还在两个温度(10和30摄氏度)下使用不同的碳,氮和磷源测试了六价铬的还原。最初,从含有100 mg L-1的Cr(VI)的溶液中分离出抗性微生物。随后,我们在温度控制的条件下,以10和100 mg L-1的Cr(VI)浓度评估了分离株在还原培养基中Cr(VI)I方面的有效性。在随后的步骤中,我们研究了分离物和自生微生物的效率,以减少污染物,添加营养素并在不同温度(10和30 CC)下存在的六价铬(VI)。在含有10 mg L-(1)Cr(VI)的培养基中,分离株在48小时内减少了100%。当针对100 mg L-1的Cr(VI)进行测试时,在分离株6和11孵育120小时后,其减少分别为70%和40%。在没有营养生物刺激的情况下,废水没有明显的减少。当施用碳和磷时,分离株6、11和原生微生物在72小时内还原了100%的Cr(VI)。氮在流出特性方面不受限制。在30摄氏度的孵育温度下,铬(VI)完全降低,但比30摄氏度的孵育速度要慢。结果表明,生物修复辅助的营养生物刺激是减少废水中六价铬的极佳工具。

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