好氧迁移外源有机物转变成内源聚合物驱动内源反硝化

    Aerobic Migration of Exogenous Organic Matter Into Endogenous Polymers to Drive Endogenous Denitrification

    • 摘要: 为解决生活污水碳氮比低、碳源不足导致的生物反硝化脱氮能力差的问题,研究根据活性污泥盛宴/饥饿非稳态理论探索好氧/缺氧(aerobic/anoxic,O/A)工艺模式实现在好氧条件下强化内源有机物积累,用于缺氧条件下内源反硝化脱氮.通过保持O/A时长比为0.11,温度为(28±2)℃,污泥龄(sludge retention time,SRT)为20 d的驯化条件,成功实现了进水负荷在0.31~0.41 g/(g·d)下好氧迁移56.00%±0.09%的COD,合成(8.05±1.32)mmol/L内源聚合物(聚羟基脂肪酸酯(polyhydroxyalkanoates,PHA)+糖原).缺氧段利用内源积累多聚物反硝化40 mg/L NO3--N,内源比反硝化速率为1.53 mg/(g·h).以单位NO3--N或NO2--N作为电子受体需要的反硝化内源聚合物的量不同,分别是2.24 mol内源物和1.59 mol内源物.内源反硝化优先消耗PHA,但是糖原贡献了77%的反硝化碳源.16S rRNA高通量测序表明,这种驯化模式显著改变了微生物的种群结构,提高了PHA和糖原积累菌群的丰度.研究结果表明,O/A工艺模式能够强化微生物积累内碳源并提高反硝化脱氮能力.

       

      Abstract: To solve poor biological nitrogen removal ability because of low ρ(C)/ρ(N) and insufficient carbon source of sewage wastewater, aerobic/anoxic (O/A) process mode enhancing the accumulation of endogenous organic matter under aerobic condition was explored based on the feast/famine non-steady state theory of activated sludge in this paper. Then, endogenous organic matter was used for denitrification in anoxic condition. When the influent load was 0.31-0.41 g/(g·d) and kept the conditions of 0.11 rate of O/A time, temperature (28±2)℃, sludge retention time(SRT) 20 d, 56.00%±0.09% COD was translated into endogenous polymers and (8.05±1.32)mmol/L endogenous polymers (polyhydroxyalkanoates + glycogen) was successfully accumulated. In the anoxic stage, 40 mg/L NO3--N was removed by endogenous polymers and the endogenous denitrification rate was 1.53 mg/1.53 mg/(g·h). Using NO3--N or NO2--N as electron acceptors, the amount of endogenous polymers for denitrifying nitrogen removal was different and were 2.24 mol endogenous source and 1.59 mol endogenous source, respectively. Endogenous denitrification preferentially consumed PHA, but Glycogen contributed 77% of the denitrifying carbon source. 16S rRNA high throughput sequencing showed that this domestication mode significantly changed the microbial population structure, promoted the abundance of PHA and Glycogen accumulation microbes. Results show that the O/A process can enhance the accumulation of internal carbon sources and enhance the ability of denitrification nitrogen removal.

       

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