Jo Kwan-Hyung, Silverstein JoAnn
Department of Civil and Environmental Engineering, Chungwoon University, Hongseong, Chungnam, Korea.
Water Sci Technol. 2004;50(5):45-50.
Biodegradation of 75 and 100 mg/l of 2,4-dinitrophenol (DNP) by activated sludge acclimated in a Sequencing Batch Reactor (SBR) consistently required less than 6 hours although a lag at the beginning of every 48-hour SBR cycle was observed. Other investigators have reported that DNP levels of 100 mg/l and higher are significantly toxic even to acclimated bacteria. The activated sludge acclimated to 75 mg/l initial DNP had over 100 times the DNP-degrading bacteria than an SBR acclimated to 10 mg/l DNP, although the MLSS concentration in both reactors was similar. Results suggest that two mechanisms are responsible for activated sludge acclimation to toxic levels of DNP: maintenance of DNP-degrading biomass sufficiently large to reduce initial DNP to non-toxic levels, allowing for subsequent rapid degradation; and extension of the aeration period well beyond the time required for degradation to prevent gradual accumulation of any by-product which might also be toxic.
尽管在每48小时的序批式反应器(SBR)周期开始时观察到有滞后现象,但在SBR中驯化的活性污泥对75毫克/升和100毫克/升的2,4-二硝基苯酚(DNP)进行生物降解始终需要不到6小时。其他研究人员报告称,100毫克/升及更高的DNP水平即使对驯化细菌也具有显著毒性。适应初始DNP浓度为75毫克/升的活性污泥中,DNP降解细菌的数量是适应10毫克/升DNP的SBR中的100多倍,尽管两个反应器中的混合液悬浮固体(MLSS)浓度相似。结果表明,活性污泥适应DNP毒性水平有两种机制:维持足够大的DNP降解生物量,将初始DNP降低到无毒水平,以便随后快速降解;将曝气时间延长到远远超过降解所需的时间,以防止可能同样有毒的任何副产物逐渐积累。