CAJ | 학술논문

采用自制厌氧序批式反应器（ASBR），分别以好氧絮状污泥和厌氧颗粒污泥为接种污泥探究厌氧氨氧化反应器的启动情况。分别经过70、40 d的培养，厌氧氨氧化反应得以发生。随后通过加大进水基质浓度来提高污泥的脱氮活性，到第120天时，两个反应器对氨氮和亚硝氮的去除率分别达到了44.6%、57.5%和64.2%、71.7%；其中氨氮去除量与亚硝氮去除量和硝氮生成量的物质的量之比分别为：1∶1.28∶0.23和1∶1.23∶0.23，接近理论值（1∶1.32∶0.26）。
채용자제염양서비식반응기（ASBR），분별이호양서상오니화염양과립오니위접충오니탐구염양안양화반응기적계동정황。분별경과70、40 d적배양，염양안양화반응득이발생。수후통과가대진수기질농도래제고오니적탈담활성，도제120천시，량개반응기대안담화아초담적거제솔분별체도료44.6%、57.5%화64.2%、71.7%；기중안담거제량여아초담거제량화초담생성량적물질적량지비분별위：1∶1.28∶0.23화1∶1.23∶0.23，접근이론치（1∶1.32∶0.26）。
In the same anaerobic sequencing batch reactors,respectively used aerobic flocculent sludge and anaero-bic granular sludge as inoculation sludge to explore the start-up of ANAMMOX reactor. After 70 and 40 days ,the ANAMMOX reaction has appeared. Then through increasing the concentration of ammonia nitrogen and nitrite nitro-gen to improve the activity of denitrification of the sludge,in the 120 d,the removal rate of ammonia nitrogen and ni-trite nitrogen in the two reactors respectively reached to 44.6%,57.5% and 64.2%,71.7%,and the ratio of the amount of ammonia nitrogen reduced,nitrite nitrogen reduced and nitrate nitrogen increased was 1∶1.28∶0.23 and 1∶1.23∶0.23,which close to the theoretical value(1∶1.32∶0.26).