降解DMF引起污泥毒性及其毒性空间分布特性研究

以处理有毒难降解有机污染物N,N-二甲基甲酰胺(DMF)的序批式好氧活性污泥系统(SBR)为对象,在进水化学需氧量(COD)为300 mg.L-1左右,各初始DMF浓度(40、80、120 mg.L-1)驯化阶段皆为30 d,运行周期为12 h,溶解氧(DO)为2.0～3.0 mg.L-1的条件下,研究了DMF在水、泥相的分布及污泥有机毒性变化趋势;探讨了单个运行周期内,出水COD、水相和泥相DMF浓度及毒性随时间的变化趋势.研究表明,各DMF浓度运行阶段的污泥毒性都体现为先升高后降低的趋势,污泥毒性随初始DMF浓度的升高而升高,污泥有机毒性主要由DMF降解过程引起,且主要集中在内层胞外聚合物(EPS)以及胞内区域.

Research on Sludge Toxicity Caused by DMF Biodegradation and Toxicity Spatial Distribution in Sludge Flocs

The aerobic sequencing batch activated sludge system (SBR) was used to remove the toxic and refractory organic pollutant, N,N-dimethylformamide (DMF). The formation property and spatial distribution of the organic toxicity in sludge were studied. The operation parameters were controlled as follows: influent COD was about 300 mg·L^-1, every DMF concentration phase lasted 30 d(40 mg·L^-1, 80 mg·L^-1, 120 mg·L^-1), the SBR cycle lasted 12 h, and DO was 2.0-3.0 mg·L^-1. The results showed that the sludge toxicity increased in the beginning and then decreased to a steady range at each DMF concentration phase; there was a positive correlation between the sludge toxicity and the initial DMF concentration; most of the sludge organic toxicity was caused by DMF biodegradation and existed in the inner extracellular polymeric substances (EPS) and intracellular section of sludge flocs.