东南大学学报(自然科学版)
東南大學學報(自然科學版)
동남대학학보(자연과학판)
JOURNAL OF SOUTHEAST UNIVERSITY
2014年
6期
1278-1284
,共7页
王晓霞%王淑莹%彭永臻%翁冬晨%戴娴
王曉霞%王淑瑩%彭永臻%翁鼕晨%戴嫻
왕효하%왕숙형%팽영진%옹동신%대한
SBR%强化生物除磷%聚磷菌%同步硝化反硝化%脱氮除磷
SBR%彊化生物除燐%聚燐菌%同步硝化反硝化%脫氮除燐
SBR%강화생물제린%취린균%동보초화반초화%탈담제린
sequencing batch reactor%enhanced biological phosphorous removal%phosphorous accumula-ting organisms%simultaneous nitrification denitrification%nitrogen and phosphorous removal
为了解处理生活污水的强化生物除磷(EBPR)系统的除磷和脱氮特性,采用SBR接种普通活性污泥,通过逐步提高进水COD浓度的方式,结合短污泥龄控制,实现了EBPR系统的快速启动,并对启动后系统的脱氮除磷特性进行了研究.试验结果表明:当进水COD浓度由200 mg/L左右逐步提高至500 mg/L左右时,29 d可实现EBPR系统的启动,此后30 d内出水磷浓度稳定维持在0.5 mg/L以下,磷去除率平均达99.4%.该系统还可长期高效稳定地用于高磷污水(含磷40 mg/L)的处理.成功启动后的EBPR系统内聚磷菌(PAOs)为优势菌,占全菌总数的34%±3%,但也存在硝化反硝化菌和聚糖菌.在EBPR系统稳定运行时的好氧段,PAOs吸磷的同时伴随着脱氮菌群的同步硝化反硝化(SND)作用,使得平均总无机氮(TIN)损失达7.6 mg/L,系统总氮(TN)去除率在70%左右.EBPR系统内除磷耦合同步硝化反硝化,可实现污水的脱氮除磷.
為瞭解處理生活汙水的彊化生物除燐(EBPR)繫統的除燐和脫氮特性,採用SBR接種普通活性汙泥,通過逐步提高進水COD濃度的方式,結閤短汙泥齡控製,實現瞭EBPR繫統的快速啟動,併對啟動後繫統的脫氮除燐特性進行瞭研究.試驗結果錶明:噹進水COD濃度由200 mg/L左右逐步提高至500 mg/L左右時,29 d可實現EBPR繫統的啟動,此後30 d內齣水燐濃度穩定維持在0.5 mg/L以下,燐去除率平均達99.4%.該繫統還可長期高效穩定地用于高燐汙水(含燐40 mg/L)的處理.成功啟動後的EBPR繫統內聚燐菌(PAOs)為優勢菌,佔全菌總數的34%±3%,但也存在硝化反硝化菌和聚糖菌.在EBPR繫統穩定運行時的好氧段,PAOs吸燐的同時伴隨著脫氮菌群的同步硝化反硝化(SND)作用,使得平均總無機氮(TIN)損失達7.6 mg/L,繫統總氮(TN)去除率在70%左右.EBPR繫統內除燐耦閤同步硝化反硝化,可實現汙水的脫氮除燐.
위료해처리생활오수적강화생물제린(EBPR)계통적제린화탈담특성,채용SBR접충보통활성오니,통과축보제고진수COD농도적방식,결합단오니령공제,실현료EBPR계통적쾌속계동,병대계동후계통적탈담제린특성진행료연구.시험결과표명:당진수COD농도유200 mg/L좌우축보제고지500 mg/L좌우시,29 d가실현EBPR계통적계동,차후30 d내출수린농도은정유지재0.5 mg/L이하,린거제솔평균체99.4%.해계통환가장기고효은정지용우고린오수(함린40 mg/L)적처리.성공계동후적EBPR계통내취린균(PAOs)위우세균,점전균총수적34%±3%,단야존재초화반초화균화취당균.재EBPR계통은정운행시적호양단,PAOs흡린적동시반수착탈담균군적동보초화반초화(SND)작용,사득평균총무궤담(TIN)손실체7.6 mg/L,계통총담(TN)거제솔재70%좌우.EBPR계통내제린우합동보초화반초화,가실현오수적탈담제린.
In order to know the phosphorus and nitrogen removal characteristics of an enhanced bio-logical phosphorus removal (EBPR)system when dealing with domestic sewage,the EBPR system, which was inoculated with activated sludge in a SBR,was fast started up by gradually increasing the influent COD(chemical oxygen demand)concentration,combined with short sludge retention time control.The nitrogen and phosphorus removal characteristics of the EBPR after being started up were also studied.Experimental results showed that when the influent COD concentration is gradually in-creased from about 200 mg/L to about 500 mg/L,the EBPR system could be started up in 29 d. The effluent PO3-4 -P concentration remaines below 0. 5 mg/L in the following 30 d,and the average phosphorus removal efficiency reaches 99. 4%.Additionally,this system can be efficiently and stab-ly used for long to deal with high phosphorus wastewater (containing PO3-4 -P of 40 mg/L).After the successful start-up of the EBPR system,phosphorous accumulating organisms (PAOs)become the dominant bacteria which accountes for 34%± 3% of total biomass.However,these also exist nitrifying and denitrifying bacteria,and glycogen accumulating organisms (GAOs)as well.Moreo-ver,during the stable operation phase of the EBPR system,simultaneous nitrification and denitrifica-tion (SND)are detected at the aerobic stage,coupling with the phosphorous uptake process of PAOs.The SND process leads to an average total inorganic nitrogen loss (TIN)of 7. 6 mg/L and a total nitrogen (TN)removal efficiency of about 70%.Phosphorus removal coupling with SND with-in the EBPR system can achieve the nitrogen and phosphorous removal in wastewater treatment.