测定处理湿地区相关生物膜的微生物活性和生物量以研究活性污染物处理场地

Adane Sirage Ali
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引用次数: 0

摘要

尽管浮动处理湿地(FTW)比其他自然处理设施具有巨大的优势,但目前还没有关于FTW生物膜功能和微生物过程的信息。因此,本研究旨在通过利用大型植物来评估FTW根部、底部和水柱区微生物基础过程的大小。本实验以生活初级污水出水为实验对象,分别饲喂两对富蹼蹼足鼠和一对对照富蹼蹼足鼠。总微生物活性通过FDA水解活性估计,特定微生物活性通过反硝化和硝化活性检测,而活菌数量和分布在FTW隔间使用ATP测定。FTWs的平均硝化速率分别为0.55、0.81和2.75 μg/ml / h;反硝化率分别为0.022、0.053和0.132 μg/ml。根系、砾石和自由水中荧光素的平均浓度分别为9.2、1.1和0.06 μg/ml,表明FTW中微生物活性最高的是与根系相关的生物膜。根表面、水表面和砂砾表面的平均活菌群分别为3.85 × 108、3.7 × 107和1.3 × 107个/ml。因此,所有结果表明,所有FTW桩的主动污染物去除都发生在根区。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Determination of Microbial Activities and Biomass in Biofilm Associated with Treatment Wetlands Compartments to Investigate Active Pollutant Processing Site
Although Floating treatment wetlands (FTWs) provide immense advantages over other natural treatment facilities, there is no information about biofilm functioning and microbial-based processes in FTW. Therefore, this study was aimed to evaluate the magnitude of microbial-based processes in the root, bottom and water column zones of the FTW by employing of macrophytes. For this experiment, primary domestic wastewater effluent was used in two pairs of FTWs (I. psuedacorus and P. stratiotes) and a pair of control. Total microbial activity was estimated using FDA hydrolytic activity and specific microbial activities were examined as denitrification and nitrification activities, whilst viable microbial number and distribution in the FTW compartments were determined using ATP assay. The average nitrification rates in the FTWs were 0.55, 0.81 and 2.75 μg/ml of water, gravel and root surface per hour respectively; and denitrification rates were 0.022, 0.053 and 0.132 μg/ml of water, gravel and roots surface respectively. The mean fluorescein concentration for the FTWs were 9.2, 1.1 and 0.06 μg/ml of root, gravel and freewater respectively, indicating that the highest total microbial activity in the FTW occurs in the biofilm associated with the root system. Mean viable microbial community 3.85 × 108, 3.7 × 107 and 1.3 × 107 cells/ml of root surface, water and gravel surface. Therefore, all the result suggested that active pollutant removal in all FTW stakes place in the root zone.
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