EFFECT OF FREE AMMONIA ON PHOSPHORUS REMOVAL EFFICIENCY AND MICROBIAL COMMUNITY STRUCTURE IN AN EBPR SYSTEM
-
摘要: 为探究游离氨(FA)影响强化生物除磷(EBPR)系统除磷效能的生物学机制,采用SBR反应器,以EBPR系统的活性污泥为研究对象,探究了FA浓度分别为0,0.2,1,4,10,15,25,50 mg/L对EBPR系统除磷效能及菌群结构的影响。结果显示,FA浓度为0.2 mg/L时,对EBPR系统除磷产生促进作用,当FA浓度为1~50 mg/L时,对EBPR系统除磷产生抑制作用;门水平下,变形杆菌门Proteobacteria的丰度随着FA浓度的升高而升高;纲水平下,γ-变形菌纲Gammaproteobacteria的丰度与FA浓度呈正相关;属水平下,聚磷菌Ca. Accumulibacter与 Tetrasphaera相比,Tetrasphaera的丰度变化趋势更符合FA对除磷性能的影响;LEfSe分析显示低、中、高浓度样品的微生物标记物分别为绿弯菌门Chloroflexi、拟杆菌门Bacteroidetes及β-变形菌纲Betaproteobacteriales。研究结果明确了FA对 EBPR 系统影响的过程,加深了对EBPR系统除磷过程菌群结构的认识,可为深入研究生物除磷的抑制机理提供借鉴。Abstract: Based on 16S rRNA genes-Illumina MiSeq high-throughput sequencing, this study aimed to investigate the effects of FA concentrations of 0, 0.2, 1, 4, 10, 15, 25, 50 mg/L on phosphorus removal efficiency and bacterial community structure of an EBPR system. Results indicated that when the concentration of FA was 0.2 mg/L, it promoted the phosphorus removal of the EBPR system; and when the concentration of FA was 1~50 mg/L, it inhibited the phosphorus removal of the EBPR system. The relative abundance of Proteobacteria increased with the increase of FA concentration. The relative abundance of Gammaproteobacteria was positively correlated with the FA concentration at the class level. At the genus level, the relative abundance of Tetrasphaera was more consistent with the effect of FA on phosphorus removal performance than Ca. Accumulibacter. LEfSe analysis showed that the biomarkers of Low, Mid and High were Chloroflexi, Bacteroidetes and Betaproteobacteriales, respectively. This study clarified the process of the effect of FA on the EBPR system, deepened the understanding of the bacterial community structure during the phosphorus removal process of the EBPR system, and provided a reference for the in-depth study of the inhibition mechanism of biological phosphorus removal.
-
[1] 常烁, 曾薇. EBPR系统中聚糖菌及其反硝化代谢机理的研究进展[J]. 工业水处理, 2019, 39(9):8-13. [2] NAIR A M, GONZALEZ-SILVA B M, HAUGEN F A, et al. Real-time monitoring of enhanced biological phosphorus removal in a multistage EBPR-MBBR using a soft-sensor for phosphates[J]. Journal of Water Process Engineering, 2020, 37(10):101494. [3] MOHAMED A Y A, WELLES L, SIGGINS A, et al. Effects of substrate stress and light intensity on enhanced biological phosphorus removal in a photo-activated sludge system[J]. Water Research, 2021, 189(2):116606. [4] RWA B, CY A, HU H A, et al. The impact of the varying nutrient concentrations on the enhanced biological phosphorus removal performance and functional phosphorus-accumulating and denitrifying genes in an anaerobic-aerobic-anoxic sequencing batch reactor-Science Direct[J]. Environmental Technology & Innovation, 2020, 21(2):101256. [5] 冉治霖, 姚强, 姜丙玉. 碳源浓度对强化生物除磷工艺中微生物菌群的影响[J]. 化学工程师, 2019, 33(9):1-8. [6] FUX C, BOEHLER M, HUBER P, et al. Biological treatment of ammonium-rich wastewater by partial nitritation and subsequent anaerobic ammonium oxidation (anammox) in a pilot plant[J]. Journal of Biotechnology, 2002, 99(3):295-306. [7] KIM D J, LEE D I, KELLER J. Effect of temperature and free ammonia on nitrification and nitrite accumulation in landfill leachate and analysis of its nitrifying bacterial community by FISH[J]. Bioresource Technology, 2006, 97(3):459-468. [8] JIANG Y, POH L S, LIM C P, et al. Effect of free ammonia inhibition on process recovery of partial nitritation in a membrane bioreactor[J]. Bioresource Technology Reports, 2019,6(7):152-158. [9] 孙洪伟,尤永军,赵华南,等. 游离氨对硝化菌活性的抑制及可逆性影响[J]. 中国环境科学, 2015,35(1):95-100. [10] 孙洪伟,吕心涛,魏雪芬,等. 游离氨(FA)耦合曝气时间对硝化菌活性的抑制影响[J]. 环境科学, 2016, 37(3):1075-1081. [11] 张亮,张树军,彭永臻. 污水处理中游离氨对硝化作用抑制影响研究[J]. 哈尔滨工业大学学报, 2012, 44(2):75-79. [12] YAO Q, PENG D C, WANG B, et al. Effect of free ammonium and free nitrous acid on the activity, aggregate morphology and EPS distribution of ammonium oxidizing bacteria in partial nitrification[J]. Journal of Bioence & Bioengineering, 2017,124(3):319-326. [13] POOT V, HOEKSTRA M, GELEIJNSE M A A, et al. Effects of the residual ammonium concentration on NOB repression during partial nitritation with granular sludge[J]. Water Research, 2016, 106(12):518-530. [14] KENT T R, SUN Y W, AN Z H, et al. Mechanistic understanding of the NOB suppression by free ammonia inhibition in continuous flow aerobic granulation bioreactors[J]. Environment International, 2019,131(10):105005. [15] DUAN H R, YE L, WANG Q L, et al. Nitrite oxidizing bacteria (NOB) contained in influent deteriorate mainstream NOB suppression by sidestream inactivation[J]. Water Research, 2019, 162(10):331-338. [16] LIU Y W, NGO H H, GUO W S, et al. The roles of free ammonia (FA) in biological wastewater treatment processes:a review[J]. Environment International, 2019,123(2):10-19. [17] WANG B, WANG Z H, WANG S Y, et al. Recovering partial nitritation in a PN/A system during mainstream wastewater treatment by reviving AOB activity after thoroughly inhibiting AOB and NOB with free nitrous acid[J]. Environment International,2020,139(3):105684. [18] ZHANG C, QIN Y G, XU Q X, et al. Free ammonia-based pretreatment promotes short-chain fatty acid production from waste activated sludge[J]. ACS Sustainable Chemistry and Engineering, 2018,6(7):9120-9129. [19] VADIVELU V M, KELLER J, YUAN Z G. Effect of free ammonia on the respiration and growth processes of an enriched Nitrobacter culture[J]. Water Research,2007, 41(4):826-834. [20] HULL S, VOLCKE E I, TERUEL J L, et al. Influence of temperature and pH on the kinetics of the Sharon nitritation process[J]. Journal of Chemical Technology & Biotechnology, 2007,82(5):471-480. [21] WANG D B, FU Q Z, XU Q X, et al. Free nitrous acid-based nitrifying sludge treatment in a two-sludge system enhances nutrient removal from low-carbon wastewater[J]. Bioresource Technology, 2017,244:920-928. [22] ZHANG Q H, YANG W N, NGO H H, et al. Current status of urban wastewater treatment plants in China[J]. Environment International, 2016, 92/93(7/8):11-22. [23] YARBROUGH J M, RAKE J B, EAGON R G. Bacterial inhibitory effects of nitrite:inhibition of active transport, but not of group translocation, and of intracellular enzymes[J]. Applied Environmental Microbiology, 1980, 39(4):831-834. [24] CHU Y J, COREY D R. RNA sequencing:platform selection, experimental design, and data interpretation[J]. Nucleic Acid Therapeutics, 2012, 22(4):271-274. [25] FRIAS L J, SHIY, TYSON G W, et al. Microbial community gene expression in ocean surface waters[J]. Proceedings of the National Academy of Sciences of the United States of America, 2008, 105(10):3805-3810. [26] HEWSON I, PORETSKY R S, TRIPP H J, et al. Spatial patterns and light-driven variation of microbial population gene expression in surface waters of the oligotrophic open ocean[J]. Environmental Microbiology, 2010, 12(7):1940-1956. [27] RADAX R, RATTEI T, LANZEN A, et al. Metatranscriptomics of the marine sponge Geodia barretti:tackling phylogeny and function of its microbial community[J]. Environmental Microbiology, 2012, 14(5):1308-1324. [28] VADIVELU V M, KELLER J, YUAN Z. Effect of free ammonia and free nitrous acid concentration on the anabolic and catabolic processes of an enriched nitrosomonas culture[J]. Biotechnology & Bioengineering, 2010, 95(5):830-839. [29] CHEN W J, DAI X H, CAO D W, et al. Performance and microbial ecology of a nitritation sequencing batch reactor treating high-strength ammonia wastewater[J]. Scientific Reports,2016, 6(10):1-8. [30] SUI Q, CHONG L, ZHANG J, et al. Response of nitrite accumulation and microbial community to free ammonia and dissolved oxygen treatment of high ammonium wastewater[J]. Applied Microbiology and Biotechnology, 2016,100(9):4177-4187. [31] 张昕, 吴长峰, 于雪, 等. pH值对亚硝酸盐氧化菌动力学及功能基因的影响[J]. 中国环境科学, 2020, 40(4):1537-1544. [32] 于雪. 温度、pH值和游离亚硝酸对亚硝酸盐氧化菌活性动力学及微生物种群结构影响研究[D]. 兰州:兰州交通大学, 2019. [33] GILBERT E M, AGRAWAL S, BRUNNER F, et al. Response of different nitrospira species to anoxic periods depends on operational do[J]. Environmental Science & Technology, 2014,48(5):2934-2941. [34] CAO J S, YU Y X, XIE K, et al. Characterizing the free ammonia exposure to the nutrients removal in activated sludge systems[J]. RSC Advances, 2017,7(87):55088-55097. [35] SUN H W, SHI W Y, CAI C J, et al. Responses of microbial structures, functions, metabolic pathways and community interactions to different C/N ratios in aerobic nitrification[J]. Bioresource Technology, 2020,311:123422. [36] HAN C, ANG L, DI C, et al. Evolution of microbial community and key genera in the formation and stability of aerobic granular sludge under a high organic loading rate[J]. Bioresource Technology ReportsVolum,2019, 7:100280. [37] 杨华,黄钧,赵永贵,等. 陶厄氏菌Thauera sp. strain TN9的鉴定及特性[J]. 应用与环境生物学报, 2013, 19(2):318-323. [38] SRINANDAN C S, SHAH M, PATEL B, et al. Assessment of denitrifying bacterial composition in activated sludge[J]. Bioresource Technology, 2011,102(20):9481-9489. [39] DU S, YA T, ZHANG M L, et al. Distinct microbial communities and their networks in an anammox coupled with sulfur autotrophic/mixotrophic denitrification system[J]. Environmental Pollution, 2020,262(7):114190.
点击查看大图
计量
- 文章访问数: 146
- HTML全文浏览量: 38
- PDF下载量: 3
- 被引次数: 0