中国环境科学
中國環境科學
중국배경과학
China Environmental Science
2015年
9期
2644-2649
,共6页
王国英%崔杰%岳秀萍%李亚男%贾子龙
王國英%崔傑%嶽秀萍%李亞男%賈子龍
왕국영%최걸%악수평%리아남%가자룡
异养硝化%好氧反硝化%苯酚%氨氮
異養硝化%好氧反硝化%苯酚%氨氮
이양초화%호양반초화%분분%안담
heterotrophic nitrification%aerobic denitrification%phenol%ammonium
研究了异养硝化-好氧反硝化菌Diaphorobacter sp. PDB3去除氨氮同时降解苯酚的特性.在最佳碳氮比7和摇床转速160r/min下,该菌在21h内对初始浓度365mg/L苯酚的降解率达94.9%,总有机碳去除率达90.8%,同时40mg N/L氨氮被完全去除,中间代谢物硝态氮和亚硝态氮逐渐积累并在后期降低.氮平衡分析表明,52.3%的氨氮转化为胞内氮,37.2%转化为氮气,菌株主要通过细胞同化作用和异养硝化-好氧反硝化作用去除氨氮.检测到羟胺氧化酶、硝酸还原酶及亚硝酸还原酶活性,表明菌株PDB3具有完整的异养硝化-好氧反硝化偶联途径.随着苯酚浓度升高,抑制作用增强,脱氮效率降低.
研究瞭異養硝化-好氧反硝化菌Diaphorobacter sp. PDB3去除氨氮同時降解苯酚的特性.在最佳碳氮比7和搖床轉速160r/min下,該菌在21h內對初始濃度365mg/L苯酚的降解率達94.9%,總有機碳去除率達90.8%,同時40mg N/L氨氮被完全去除,中間代謝物硝態氮和亞硝態氮逐漸積纍併在後期降低.氮平衡分析錶明,52.3%的氨氮轉化為胞內氮,37.2%轉化為氮氣,菌株主要通過細胞同化作用和異養硝化-好氧反硝化作用去除氨氮.檢測到羥胺氧化酶、硝痠還原酶及亞硝痠還原酶活性,錶明菌株PDB3具有完整的異養硝化-好氧反硝化偶聯途徑.隨著苯酚濃度升高,抑製作用增彊,脫氮效率降低.
연구료이양초화-호양반초화균Diaphorobacter sp. PDB3거제안담동시강해분분적특성.재최가탄담비7화요상전속160r/min하,해균재21h내대초시농도365mg/L분분적강해솔체94.9%,총유궤탄거제솔체90.8%,동시40mg N/L안담피완전거제,중간대사물초태담화아초태담축점적루병재후기강저.담평형분석표명,52.3%적안담전화위포내담,37.2%전화위담기,균주주요통과세포동화작용화이양초화-호양반초화작용거제안담.검측도간알양화매、초산환원매급아초산환원매활성,표명균주PDB3구유완정적이양초화-호양반초화우련도경.수착분분농도승고,억제작용증강,탈담효솔강저.
The simultaneous removal of phenol and ammonium by a heterotrophic nitrifying-aerobic denitrifying bacterium Diaphorobactersp.PDB3 was investigated. The optimal C/N ratio was 7and the optimal shaking speed was 160r/min. The strain degraded 94.9% of 365mg/L phenol in 21h, and 90.8% of total organic carbon was removed. Simultaneously, ammonium at an initial concentration of 40mg N/L was completely removed. The intermediates nitrate and nitrite accumulated in the early phase and declined in the later phase. The nitrogen balance analysis showed that 52.3% of removed nitrogen was finally transformed to intracellular nitrogen and 37.2% was converted to nitrogen gas. Ammonium was removed mainly through cellular assimilation and heterotrophic nitrification-aerobic denitrification. The detection of hydroxylamine oxidase, nitrate reductase and nitrite reductase activities demonstrated a coupled heterotrophic nitrifying-aerobic denitrifying pathway of strain PDB3. With the increase of phenol concentration, the inhibitory effect increased, leading to lower efficiency of ammonium removal.