北京工业大学学报
北京工業大學學報
북경공업대학학보
Journal of Beijing University of Technology
2015年
10期
1469-1478
,共10页
张捍民%李义菲%赵然%高范%杨凤林
張捍民%李義菲%趙然%高範%楊鳳林
장한민%리의비%조연%고범%양봉림
厌氧氨氧化%电气石%驯化%启动%氮去除
厭氧氨氧化%電氣石%馴化%啟動%氮去除
염양안양화%전기석%순화%계동%담거제
Anammox%tourmaline%enrichment%start-up%nitrogen removal
为了研究电气石对厌氧氨氧化菌驯化过程的影响,采用2个平行的连续搅拌式生物反应器,其中一个添加电气石(记为R1),另一个未添加电气石作为空白对照(记为R2).2个反应器均在第23天观察到显著的NH4+-N和NO2--N同时去除,即表现出厌氧氨氧化活性.添加电气石反应器R2的污泥适应期比对照反应器R1缩短42 d ( R2为12 d,R1为54 d),且最高氮负荷达到205.0 mg/( L·d),比对照表现出更好的耐负荷冲击能力.此外,电气石可以调控pH和氧化还原电位使其保持在厌氧氨氧化菌适合范围内,为驯化提供稳定环境.厌氧氨氧化活性批式实验显示,添加电气石驯化得到的菌体的SAA最高比对照增加48.8%,微生物胞外聚合物( extracellular polymeric substances, EPS)检测结果显示,添加电气石反应器R2的多糖、蛋白质和总EPS分别比对照反应器R1增加7.6%、86.7%和43.8%,说明电气石可以促进微生物生长代谢,提高厌氧氨氧化反应活性.粒径与扫描电子显微镜检测说明:电气石并不利于污泥颗粒化,而是大部分污泥与电气石分散生长.谱系分析说明:驯化过程中,微生物组成由接种活性污泥中大量杆菌与丝状菌逐渐演变,筛选出如反硝化菌、亚硝化菌等功能菌种.
為瞭研究電氣石對厭氧氨氧化菌馴化過程的影響,採用2箇平行的連續攪拌式生物反應器,其中一箇添加電氣石(記為R1),另一箇未添加電氣石作為空白對照(記為R2).2箇反應器均在第23天觀察到顯著的NH4+-N和NO2--N同時去除,即錶現齣厭氧氨氧化活性.添加電氣石反應器R2的汙泥適應期比對照反應器R1縮短42 d ( R2為12 d,R1為54 d),且最高氮負荷達到205.0 mg/( L·d),比對照錶現齣更好的耐負荷遲擊能力.此外,電氣石可以調控pH和氧化還原電位使其保持在厭氧氨氧化菌適閤範圍內,為馴化提供穩定環境.厭氧氨氧化活性批式實驗顯示,添加電氣石馴化得到的菌體的SAA最高比對照增加48.8%,微生物胞外聚閤物( extracellular polymeric substances, EPS)檢測結果顯示,添加電氣石反應器R2的多糖、蛋白質和總EPS分彆比對照反應器R1增加7.6%、86.7%和43.8%,說明電氣石可以促進微生物生長代謝,提高厭氧氨氧化反應活性.粒徑與掃描電子顯微鏡檢測說明:電氣石併不利于汙泥顆粒化,而是大部分汙泥與電氣石分散生長.譜繫分析說明:馴化過程中,微生物組成由接種活性汙泥中大量桿菌與絲狀菌逐漸縯變,篩選齣如反硝化菌、亞硝化菌等功能菌種.
위료연구전기석대염양안양화균순화과정적영향,채용2개평행적련속교반식생물반응기,기중일개첨가전기석(기위R1),령일개미첨가전기석작위공백대조(기위R2).2개반응기균재제23천관찰도현저적NH4+-N화NO2--N동시거제,즉표현출염양안양화활성.첨가전기석반응기R2적오니괄응기비대조반응기R1축단42 d ( R2위12 d,R1위54 d),차최고담부하체도205.0 mg/( L·d),비대조표현출경호적내부하충격능력.차외,전기석가이조공pH화양화환원전위사기보지재염양안양화균괄합범위내,위순화제공은정배경.염양안양화활성비식실험현시,첨가전기석순화득도적균체적SAA최고비대조증가48.8%,미생물포외취합물( extracellular polymeric substances, EPS)검측결과현시,첨가전기석반응기R2적다당、단백질화총EPS분별비대조반응기R1증가7.6%、86.7%화43.8%,설명전기석가이촉진미생물생장대사,제고염양안양화반응활성.립경여소묘전자현미경검측설명:전기석병불리우오니과립화,이시대부분오니여전기석분산생장.보계분석설명:순화과정중,미생물조성유접충활성오니중대량간균여사상균축점연변,사선출여반초화균、아초화균등공능균충.
In this study, the effect of tourmaline on the enrichment of Anammox bacteria for nitrogen removal was investigated by two parallel lab-scale continuously stirred tank bioreactors ( CSTR ) with tourmaline addition R2 and without tourmaline as control R1, respectively. After 23 days of operation, Anammox activity was achieved with a simultaneous consumption of NH4+-N and NO2--N in both reactors. Time of sludge adaptation period of R2 was shorter than that of R1 by 42 days ( R2:12 d, R1:54 d) . R2 showed a stronger capacity for nitrogen removal and resisting nitrogen shock load with the maximum nitrogen loading rate ( NLR) of 205. 0 mg/( L·d) . In addition, tourmaline can control pH and oxidation reduction potential ( ORP) values to provide a stable environment for enrichment of Anammox bacteria. Anammox activity batch tests demonstrate that addition of tourmaline can enhance the activity of Anammox bacteria with a maximum increase of 48. 8% higher than the control. Analysis of extracellular polymeric substances ( EPS ) show that the maximum increase of carbohydrate, protein and total EPS production is obtained in R2 by 7. 6%, 86. 7% and 43. 8%, respectively, which indicate that tourmaline can promote the growth and metabolism of bacteria and enhance the activity of Anammox reaction. According to the results of the particle size observation and scanning electron microscope ( SEM) images, there is no visible benefit for the granulation of Anammox sludge by adding tourmaline and great number of the Amammox sludge and tourmaline developed separately in the component. Phylogenetic tree of bacteria demonstrates that numbers of the functional bacteria such as denitrifying bacteria and nitrococcus are extracted from the seed sludge which contain a big quantity of brevibacterium and filamentous bacteria during the enrichment process.