EFFECT OF DIFFERENT CARBON SOURCES ON N2O RELEASE IN DENITRIFICATION PROCESS OF A SBR REACTOR
-
摘要: 试验使用SBR反应器,采用乙酸钠、乙醇、葡萄糖和蔗糖4种常用的外加有机碳源,对反硝化反应中N2O释放过程进行研究。结果表明:4种碳源条件下,N2O积累量均呈先升高后降低最后保持稳定的趋势。N2O最大积累量分别为1.59,1.25,5.43,0.66 mg/L,最大转化率分别为1.61%、1.36%、5.44%和0.67%;最终积累量分别为1.02,0.67,3.12,0.49 mg/L,最终转化率分别为1.04%、0.73%、3.13%和0.50%。N2O释放量及转化率顺序均为葡萄糖>乙酸钠>乙醇>蔗糖。游离亚硝酸抑制、不同反硝化酶的电子竞争和微生物群落结构差异均是影响N2O释放的因素。Abstract: N2O is a potent greenhouse gas, and releases a lot in wastewater treatment. Understanding the influencing factors of N2O release in wastewater treatment can reduce N2O emissions. Four classical external organic carbon sources, such as sodium acetate, ethanol, glucose and sucrose, were used to study the N2O release process in denitrification process with SBR reactors. The results showed that under the 4 carbon source conditions, the accumulation of N2O showed a trend of first increasing, then decreasing, and finally remaining stable. The maximum accumulation of N2O were 1.59, 1.25, 5.43, 0.66 mg/L, and the maximum conversion rates were 1.61%, 1.36%, 5.44% and 0.67%, respectively. The final accumulation of N2O were 1.02, 0.67, 3.12, 0.49 mg/L, and the final conversion rates were 1.04%, 0.73%, 3.13% and 0.50%, respectively. The N2O release amount and conversion rate in descending order were glucose, sodium acetate, ethanol and sucrose. FNA inhibition, electronic competition of different denitrifying enzymes and differences in microbial community structure were factors affecting N2O release.
-
Key words:
- external carbon source /
- nitrous oxide /
- denitrification /
- FNA /
- SBR
-
[1] IPCC.Climate Change 2007:the IPCC Scientific Assessment[M].Cambridge:Cambridge University Press,2007. [2] PORTMANN R W,DANIEL J S,RAVISHANKARA A R.Stratospheric ozone depletion due to nitrous oxide:influences of other gases[J].Philosophical Transactions of the Royal Society of London,2012,1593(367):1256-1264. [3] GRUBER W,VILLEZ K,KIPF M,et al.N2O emission in full-scale wastewater treatment:proposing a refined monitoring strategy[J].Science of the Total Environment,2019,699:1-24. [4] 刘国华,庞毓旻,齐鲁,等.SBR工艺污水生物脱氮过程中N2O的释放特征[J].环境工程,2020,38(7):51-57. [5] 孙英杰,吴昊,王亚楠.硝化反硝化过程中N2O释放影响因素[J].生态环境学报,2011,20(2):384-388. [6] 毛跃建.废水处理系统中重要功能类群Thauera属种群结构与功能的研究[D].上海:上海交通大学,2009. [7] 郭泓利,李鑫玮,任钦毅,等.全国典型城市污水处理厂进水水质特征分析[J].给水排水,2018,54(6):12-15. [8] 付昆明,廖敏辉,王俊安,等.村镇低浓度生活污水现状及处理技术分析[J].环境工程,2019,37(4):48-51. [9] SONG M J,CHOI S,BAE W B,et al.Identification of primary effecters of N2O emissions from full-scale biological nitrogen removal systems using random forest approach[J].Water Research,2020,184:1-9. [10] ZHOU Y,LIM M,HARJONO S,et al.Nitrous oxide emission by denitrifying phosphorus removal culture using polyhydroxyalkanoates as carbon source[J].Journal of Environmental Sciences,2012,24(9):1616-1623. [11] CAO X S,QIAN D,MENG X Z.Effects of pH on nitrite accumulation during wastewater denitrification[J].Environmental Technology,2013,34(1/2/3/4):45-51. [12] 巩有奎,彭永臻.温度变化对短程生物脱氮及N2O释放影响[J].水处理技术,2020,46(8):110-115. [13] 付昆明,杨宗玥,刘凡奇,等.碳源种类对农村污水反硝化过程脱氮效果的影响[J].环境工程学报,2020,14(9):2331-2338. [14] 国家环保总局《水和废水监测分析方法》编委会.水和废水监测分析方法[M].4版.北京:中国环境科学出版社,2002. [15] KIMOCHI Y,INAMORI Y,MIZUOCHI M,et al.Nitrogen removal and N2O emission in a full-scale domestic wastewater treatment plant with intermittent aeration[J].Journal of Bioscience & Bioengineering,1998,86(2):202-206. [16] SHISKOWSKI D M.Nitrous oxide:a powerful greenhouse gas with a wastewater treatment connection[J].Proceedings of the Water Environment Federation,2007,2007(18):1279-1290. [17] PAN Y,NI B J,BOND P L,et al.Electron competition among nitrogen oxides reduction during methanol-utilizing denitrification in wastewater treatment[J].Water Research,2013,10(47):3273-3281. [18] ADOUANI N,LIMOUSY L,LENDORMI T,et al.N2O and NO emissions during wastewater denitrification step:influence of temperature on the biological process[J].Comptes Rendus Chimie,2015,18(1):15-22. [19] 付昆明,付巢,王会芳,等.CANON工艺中N2O的释放途径及影响因素[J].中国给水排水,2018,34(2):37-41. [20] ZHAO Y,MIAO J,REN X,et al.Effect of organic carbon on the production of biofuel nitrous oxide during the denitrification process[J].Environmental Science and Technology,2018,15(2):461-470. [21] 朱莹.Thauera linaloolentis 47Lol菌株nosZ基因不同拷贝的反硝化生理[D].上海:上海交通大学,2017. [22] LU H,CHANDRAN K,STENSEL D.Microbial ecology of denitrification in biological wastewater treatment[J].Water Research,2014,64(7):237-254. [23] SHEU S Y,SHIAU Y W,WEI Y T,et al.Gemmobacter lanyuensis sp.nov.,isolated from a freshwater spring[J].Systematic and Evolutionary Microbiology,2013,63(Pt 11):4039-4045. [24] KHAN S T,HIRAISHI A.Diaphorobacter nitroreducens gen.nov.,sp.nov.,a poly(3-hydroxybutyrate)-degrading denitrifying bacterium isolated from activated sludge[J].Journal of General & Applied Microbiology,2002,6(48):299-308. [25] BUCHANAN R E,GIBBONS N E.伯杰细菌鉴定手册[M].8版.北京:科学出版社,1984. [26] 张阳,王秀杰,王维奇,等.一株Acinetobacter johnsonii的部分反硝化特性及动力学研究[J].中国环境科学,2019,39(10):4369-4376. [27] 李相昆.反硝化除磷工艺与微生物学研究[D].哈尔滨:哈尔滨工程大学,2006. [28] 汪霞.好氧反硝化菌Enterobacter sp.FL的脱氮及自聚集特性研究[D].重庆:重庆大学,2017. [29] YANG Y W,WU R T,HU J X,et al.Dominant denitrifying bacteria are important hosts of antibiotic resistance genes in pig farm anoxic-oxic wastewater treatment processes[J].Environment International,2020(143):105897. [30] 鄢雨萌.河床沉积物淤积影响下河水入渗带中氧化还原分带研究[D].吉林:吉林大学,2020.
点击查看大图
计量
- 文章访问数: 211
- HTML全文浏览量: 38
- PDF下载量: 10
- 被引次数: 0