| 269 | 6 | 287 |
| 下载次数 | 被引频次 | 阅读次数 |
本文考察了二价钴离子(Co(II))浓度变化对序批式反应器(SBR)性能、脱氮速率、微生物酶活性和微生物群落的影响。结果表明,进水中Co(II)浓度在0~10 mg/L时,COD和NH+_4-N去除率分别为(92.21±1.31)%和(98.40±0.66)%。在进水Co(II)浓度为20 mg/L时,COD和NH+_4-N去除率分别降至(81.78±0.52)%和(80.30±1.08)%。与进水未添加Co(II)时相比,活性污泥比耗氧速率、脱氮速率、脱氢酶活性和与脱氮相关的微生物酶活性在进水Co(II)浓度小于5 mg/L时略微升高,而在进水Co(II)浓度为10和20 mg/L时则明显降低。活性污泥活性氧产生量和乳酸脱氢酶释放量随进水Co(II)浓度升高而逐渐增加,表明Co(II)的存在能造成细胞氧化应激和细胞膜损伤。随着进水Co(II)浓度从0 mg/L升至20 mg/L,活性污泥微生物群落丰富度和多样性逐渐降低,且活性污泥中硝化菌属(Nitrosomonas、Nitrospira)和反硝化菌属(Luteimonas、Flavobacterium、Comamonas、Thauera和Zoogloea)的相对丰度发生改变,从而影响SBR脱氮性能。
Abstract:The performance, nitrogen removal rate, microbial enzymatic activity and microbial community of a sequencing batch reactor(SBR) were evaluated at different Co(Ⅱ) concentrations. The present results indicated that the COD and NH+_4-N removal efficiency maintained at(92.21±1.31)% and(98.40±0.66)% at 0~10 mg/L Co(Ⅱ), respectively, whereas reduced to(81.78±0.52)% and(80.30±1.08)% at 20 mg/L Co(Ⅱ), respectively. Compared to the absence of Co(Ⅱ), the oxygen uptake rate, nitrogen removal rate, dehydrogenase activity and microbial enzymatic activity related to nitrogen removal had slight increase at below 5 mg/L Co(Ⅱ), whereas showed obvious decrease at 10 and 20 mg/L Co(Ⅱ). The reactive oxygen species production and lactate dehydrogenase release increased with the increase of Co(Ⅱ) concentration, suggesting that the presence Co(Ⅱ) caused oxidative stress and cytomembrane damage of activated sludge microorganisms. High throughput sequencing indicated that the microbial richness and diversity of activated sludge gradually decreased with Co(Ⅱ) concentration increasing from 0 to 20 mg/L. The relative abundance of nitrification genera(e.g. Nitrosomonas and Nitrospira) and denitrification genera(e.g. Luteimonas, Flavobacterium, Comamonas, Thauera and Zoogloea) changed under different Co(Ⅱ) concentrations, which could further affect the nitrogen removal of SBR.
[1] Al-Shahrani S S.Treatment of wastewater contaminated with cobalt using Saudi activated bentonite[J].Alexandria Engineering Journal,2014,53:205-211.
[2] Fristák V,Pipiska M,Horník M,et al.Sludge of wastewater treatment plants as Co2+ ions sorbent[J].Chemical Papers,2013,67(3):265-273.
[3] Zeeshan M,Murugadas A,Ghaskadbi S,et al.Ecotoxicological assessment of cobalt using Hydra model:ROS,oxidative stress,DNA damage,cell cycle arrest,and apoptosis as mechanisms of toxicity[J].Environmental Pollution,2017,224:54-69.
[4] Gikas P.Kinetic responses of activated sludge to individual and joint nickel (Ni(II)) and cobalt (Co(II)):An isobolographic approach[J].Journal of Hazardous Materials,2007,143:246-256.
[5] Bestawy E E,Helmy S,Hussein H,et al.Optimization and/or acclimatization of activated sludge process under heavy metals stress[J].World Journal of Microbiology and Biotechnology,2013,29:693-705.
[6] Barnett J,Richardson D,Stack K,et al.Addition of trace metals and vitamins for the optimisation of a pulp and paper mill activated sludge wastewater treatment plant[J].Appita Journal,2012,65(3):237-243.
[7] Hernandez-Martinez G R,Ortiz-Alvarez D,Perez-Roa M,et al.Multiparameter analysis of activated sludge inhibition by nickel,cadmium,and cobalt[J].Journal of Hazardous Materials,2018,351:63-70.
[8] Cecen F,Semerci N,Geyik A G.Inhibitory effects of Cu,Zn,Ni and Co on nitrification and relevance of speciation[J].Journal of Chemical Technology & Biotechnology,2010,85:520-528.
[9] Zou G,Papirio S,Ylinen A,et al.Fluidized-bed denitrification for mine waters.Part II:Effects of Ni and Co[J].Biodegradation,2014,25:417-423.
[10] 国家环境保护总局,水和废水监测分析方法编委会.水和废水监测分析方法(第四版)[M].北京:中国环境科学出版社,2002.Chinese NEPA.Water and Wastewater Monitoring Methods[M].Fourth ed.Beijing:Chinese Environmental Science Publishing Press,2002.
[11] Ma B R,Wang S,Li Z W,et al.Magnetic Fe3O4 nanoparticles induced effects on performance and microbial community of activated sludge from a sequencing batch reactor under long-term exposure[J].Bioresource Technology,2017,225:377-385.
[12] Wang S,Gao,M C,She,Z L,et al.Long-term effects of ZnO nanoparticles on nitrogen and phosphorus removal,microbial activity and microbial community of a sequencing batch reactor[J].Bioresource Technology,2016,216:428-436.
[13] Chen Y J,He H J,Liu H Y,et al.Effect of salinity on removal performance and activated sludge characteristics in sequencing batch reactors[J].Bioresource Technology,2018,249:890-899.
[14] 谢冰.重金属对活性污泥微生物的影响[J].上海化工,2004,2:13-16.Xie B.A review of effects of heavy metals on activated sludge microorganism[J].Shanghai Chemical Industry,2004,2:13-16.
[15] Qian J,Li K,Wang P F,et al.Toxic effects of three crystalline phases of TiO2 nanoparticles on extracellular polymeric substances in freshwater biofilms[J].Bioresource Technology,2017,241:276-283.
[16] Wu D L,Zheng S S,Ding A Q,et al.Performance of a zero valent iron-based anaerobic system in swine wastewater treatment[J].Journal of Hazardous Materials,2015,286:1-6.
[17] Davies K J A.Oxidative stress,antioxidant defenses,and damage removal,repair,and replacement systems[J].Advances in Bioscience and Biotechnology,2000,3(7A):279-289.
[18] Liu Z D,Zhang C,Wang L J,et al.Effects of furan derivatives on biohydrogen fermentation from wet steam-exploded cornstalk and its microbial community[J].Bioresource Technology,2015,175:152-159.
[19] Hill M O.Diversity and evenness:A unifying notation and its consequences[J].Ecology,1973,54(2):427-432.
[20] Koops H P,Bottcher B,Moller U C,et al.Classification of eight new species of ammonia-oxidizing bacteria:Nitrosomonas communis sp.nov.,Nitrosomonas ureae sp.nov.,Nitrosomonas aestuarii sp.nov.,Nitrosomonas marina sp.nov.,Nitrosomonas nitrosa sp.nov.,Nitrosomonas eutropha sp.nov.,Nitrosomonas oligotropha sp.nov.and Nitrosomonas halophila sp.nov.[J].Journal of General Microbiology,1991,137:1689-1699.
[21] Watson S W,Bock E,Valois F W,et al.Nitrospira marina gen.nov.sp.nov.:a ehemolithotrophie nitrite-oxidizing bacterium[J].Archives of Microbiology,1986,144:1-7.
[22] Fin kmann W,Altendorf K,Stackebrandt E,et al.Characterization of N2O-producing Xanthomonas-like isolates from biofilters as Stenotrophomonas nitritireducens sp.nov.,Luteimonas mephitis gen.nov.,sp.nov.and Pseudoxanthomonas broegbernensis gen.nov.,sp.nov.[J].International Journal of Systematic and Evolutionary Microbiology,2000,50:273-282.
[23] Betlach M R,Tiedje J M.Kinetic explanation for accumulation of nitrite,nitric oxide,and nitrous oxide during bacterial denitrification[J].Applied and Environmental Microbiology,1981,42(6):1074-1084.
[24] Gumaelius L,Magnusson G,Pettersson B,et al.Comamonas denitrificans sp.nov.,an efficient denitrifying bacterium isolated from activated sludge[J].International Journal of Systematic and Evolutionary Microbiology,2001,51:999-1006.
[25] Fida T T,Gassara F,Voordouw G.Biodegradation of isopropanol and acetone under denitrifying conditions by Thauera sp.TK001 for nitrate-mediated microbiallyenhanced oil recovery[J].Journal of Hazardous Materials,2017,334:68-75.
[26] Huang T L,Zhou S L,Zhang H H,et al.Nitrogen removal characteristics of a newly isolated indigenous aerobic denitrifier from oligotrophic drinking water reservoir,Zoogloea sp.N299[J].International Journal of Molecular Sciences,2015,16:10038-10060.
基本信息:
DOI:10.16441/j.cnki.hdxb.20190233
中图分类号:X172;X703
引用信息:
[1]赵长坤,于娜玲,马丙瑞,等.二价钴离子对序批式反应器性能、微生物活性及其微生物群落的影响[J],2020,50(06):101-108.DOI:10.16441/j.cnki.hdxb.20190233.
基金信息:
国家自然科学基金项目(51178437)资助~~