nav emailalert searchbtn searchbox tablepage yinyongbenwen piczone journalimg journalInfo journalinfonormal searchdiv searchzone qikanlogo popupnotification paper paperNew
2025, 09, v.55 103-113
好氧反硝化菌Marinobacter sp. strain B108固定化及脱氮动力学研究
基金项目(Foundation): 国家自然科学基金项目(51978636)资助~~
邮箱(Email): tengfei_945@163.com;
DOI: 10.16441/j.cnki.hdxb.20240175
摘要:

为实现循环海水养殖系统中硝酸盐的经济、高效去除,采用固定化好氧反硝化菌(Marinobacter sp. strain B108)有效解决菌剂持留问题,进而提升好氧环境下硝酸盐去除效率。本研究以Marinobacter sp. strain B108为研究对象,采用聚乙烯醇(PVA)、海藻酸钠(SA)、茶渣粉为固定化载体材料,探究并优化菌球固定化材料配比,在此基础上进一步研究固定化好氧反硝化菌球的理化特征及脱氮动力学特性。结果表明,固定化材料最佳配比为PVA 10.103%、SA 1.548%、茶渣粉0.732%。最佳配比条件下固定化菌球机械强度高,耐受机械剪切力强;当初始NO■-N浓度为100 mg/L时,固定化菌球7 h内NO■-N去除率可达98.63%。固定化菌球对NO■-N去除动力学过程可用Monod模型拟合,拟合得出最大比去除速率Vmax为5.041 mg/(L·g·h),半饱和常数Km为24.810 mg/L;固定化菌球对NO■-N去除动力学过程可用Andrews模型拟合,拟合得出Vmax为0.790 mg/(L·g·h),Km为23.783 mg/L,抑制常数Ki为0.092 mg/L。研究可为好氧反硝化菌在循环海水养殖系统硝酸盐处理中的应用奠定基础。

Abstract:

Immobilized aerobic denitrifying bacteria(Marinobacter sp. strain B108) can solve the problem of bacterial retention and improve the nitrate removal efficiency under aerobic environment, thus removing nitrate from marine recirculating aquaculture systems(MRAS) economically and efficiently. Polyvinyl alcohol(PVA), sodium alginate(SA) and tea residue powder were used as support materials to immobilize Marinobacter sp. strain B108. The ratios of immobilized materials were explored and optimized, and the physicochemical characteristics and denitrification kinetics of immobilized aerobic denitrifying bacterial pellets were further investigated on the basis of the optimal immobilized materials ratio. The optimum ratios of support materials were 10.103% PVA, 1.548% SA, and 0.732% tea residue powder. Under the optimum conditions, the immobilized bacterial pellets had high mechanical strength and strong resistance to mechanical shear, and the removal efficiency of NO■-N within 7 h was 98.63% as initial influent NO■-N concentration was 100 mg/L. The kinetic process of NO■-N removal could be fitted by Monod model, and the Vmax and Km were 5.041 mg/(L·g·h) and 24.810 mg/L, respectively. The kinetic process of NO■-N removal could be fitted by Andrews model, and the Vmax, Km and Ki were 0.790 mg/(L·g·h), 23.783 mg/L, and 0.092 mg/L, respectively. The conclusions could lay a good foundation for aerobic denitrifying bacteria practical application in MRAS for nitrate removal treatment.

参考文献

[1] Alberto B,Miguel A Vela M,Silvie D,et al.Rearing performance of juvenile yellowtail snapper,Ocyurus chrysurus,in a sea water recirculation system at two different stocking densities[J].Journal of the World Aquaculture Society,2023,54(6):1430-1446.

[2] Zhang W,Liu B,Sun Z,et al.Comparision of nitrogen removal characteristic and microbial community in freshwater and marine recirculating aquaculture systems[J].The Science of the Total Environment,2023,878:162870.

[3] Li Q,Hasezawa R,Saito R,et al.Abundance anddiversity of nitrifying microorganisms in marine recirculating aquaculture systems[J].Water,2022,14(17):2744-2750.

[4] Isaza D F G,Cramp R L,Franklin C E.Living in polluted waters:A meta-analysis of the effects of nitrate and interactions with other environmental stressors on freshwater taxa[J].Environmental Pollution,2020,261(C):114091.

[5] Poulsen R,Cedergreen N,Hayes T,et al.Nitrate:An environmental endocrine disruptor?A review of evidence and research needs[J].Environmental Science and Technology,2018,52(7):3869-3887.

[6] Morris A L,Hamlin H J,Francis-Floyd R,et al.Nitrate-induced goiter in captive whitespotted bamboo sharks Chilosryllium plagiosum[J].Journal of Aquatic Animal Health,2011,23(2):92-99.

[7] Ashok V,Hait S.Remediation of nitrate-contaminated water by solid-phase denitrification process:A review[J].Environmental Science and Pollution Research International,2015,22(11):8075-8093.

[8] Luo Y,Xu W,Zuo X,et al.Performance,community dynamics and network of an aerobic denitrifying consortium from a coastal mariculture area[J].International Biodeterioration and Biodegradation,2023,184:105649.

[9] Yan L,Yin M,Miao J,et al.Removal of nitrate nitrogen by Pseudomonas JI-2 under strong alkaline conditions:Performance and mechanism[J].Bioresource Technology,2023,388:129755.

[10] Gao Y,Zhu J,Wang K,et al.Discovery of a heterotrophic aerobic denitrification Pseudomonas sp.G16 and its unconventional nitrogen metabolic pathway[J].Bioresource Technology,2023,387:129670.

[11] Gupta A B,Gupta S K.Simultaneous carbon and nitrogen removal from high strength domestic wastewater in an aerobic RBC biofilm[J].Water Research,2001,35(7):1714-1722.

[12] 陈海升,曹刚,张迪,等.复合菌株YH01+YH02强化SBR好氧反硝化脱氮及菌群结构分析[J].环境科学,2018,39(4):1773-1781.Chen H S,Cao G,Zhang D,et al.Aerobic denitrification and microbial community shift in SBR bioaugmented with strains YH01 and YH02[J].Environmental Science,2018,39(4):1773-1781.

[13] Zhang Q,Liu H,Liang S,et al.Comparison of moving bed biofilm reactor and bio-contact oxidation reactor start-up with heterotrophic nitrification-aerobic denitrification bacteria and activated sludge inoculation under high ammonia nitrogen conditions[J].Bioresource Technology,2024,395:130408.

[14] Sun H,Jin J,Sun Y,et al.Preparation of microbial agent immobilized composites for Cr(VI) removal from wastewater[J].Environmental Technology,2024,3(1):11-13.

[15] Bouabidi Z B,El-Naas M H,Zhang Z.Immobilization of microbial cells for the biotreatment of wastewater:A review[J].Environmental Chemistry Letters,2019,17(1):241-257.

[16] Abu-Saied M A,Taha T H,El-Deeb N M,et al.Polyvinyl alcohol/Sodium alginate integrated silver nanoparticles as probable solution for decontamination of microbes contaminated water[J].International Journal of Biological Macromolecules,2018,107:1773-1781.

[17] Xiang X,Yi X,Zheng W,et al.Enhanced biodegradation of thiamethoxam with a novel polyvinyl alcohol (PVA)/sodium alginate (SA)/biochar immobilized Chryseobacterium sp H5[J].Journal of Hazardous Materials,2022,443:130247.

[18] He Q,Shen Y,Li R,et al.Rice washing drainage (RWD) embedded in poly(vinyl alcohol)/sodium alginate as denitrification inoculum for high nitrate removal rate with low biodiversity[J].Bioresource Technology,2022,355:127288.

[19] Cheng H,Xu A,Awasthi M K,et al.Aerobic denitrification performance and nitrate removal pathway analysis of a novel fungus Fusarium Solani RADF-77[J].Bioresource Technology,2020,295:122250.

[20] Gong Y,Niu Q,Liu Y,et al.Development of multifarious carrier materials and impact conditions of immobilised microbial technology for environmental remediation:A review[J].Environmental Pollution.2022,314:120232.

[21] 苏鑫,王诗涵,刘佩武,等.微生物复合载体制备及包埋Halomonas sp.NH2B的硝化性能[J].环境科学与技术,2023,46(11):1-10.Su X,Wang S H,Liu P W,et al.Preparation of microbial composite carrier and nitration performance of Halomonas sp.NH2B encapsulation[J].Environmental Science and Technology,2023,46(11):1-10.

[22] Takei T,Ikeda K,Ijima H,et al.Fabrication of poly(vinyl alcohol) hydrogel beads crosslinked using sodium sulfate for microorganism immobilization[J].Process Biochemistry,2011,46(2):566-571.

[23] Hassan C M,Peppas N A.Structure andapplications of poly(vinyl alcohol) hydrogels produced by conventional crosslinking or by freezing/thawing methods[J].Advances in Polymer Science,2000(153):37-65.

[24] 刘祥,王婧瑶,吴娟娟,等.微藻固定化条件优化及其污水氨氮去除潜力分析[J].环境科学,2019,40(7):3126-3134.Liu X,Wang J Y,Wu J J,et al.Optimization of the parameters for microalgae immobilization and analysis of its recovery potential for ammonia nitrogen in wastewater[J].Environmental Science,2019,40(7):3126-3134.

[25] Liao H,Liu Y,Wang Q,et al.Structure and properties of porouspoly(vinyl alcohol) hydrogel beads prepared through a physical-chemical crosslinking method[J].Journal of Applied Polymer Science,2018,135(26):46402.

[26] Zhang S,Han D,Ding Z,et al.Fabrication and characterization of one interpenetrating network hydrogel based on sodium alginate and polyvinyl alcohol[J].Journal of Wuhan University of Technology,2019,34(3):744-751.

[27] Dong Y,Zhang Y,Tu B,et al.Immobilization of ammonia-oxidizing bacteria by calcium alginate[J].Ecological Engineering,2014,73:809-814.

[28] 马洪婧,刘鹰,慕欣廷,等.耐盐高效好氧反硝化菌Halomonas sp.HRL-11的分离鉴定及反硝化性能[J].大连海洋大学学报,2022,37(2):227-234.Ma H J,Liu Y,Mu X T,et al.Isolation,identification and denitrification performance of a salt-tolerant and efficient aerobic denitrifier Halomonas sp.HRL-11[J].Journal of Dalian Ocean University,2022,37(2):227-234.

[29] 陈均利,刘锋,张树楠,等.固定化Alcaligenes faecalis WT14对累积亚硝酸盐的还原[J].水处理技术,2021,47(11):65-70.Chen J L,Liu F,Zhang S N,et al.Reduction of accumulated nitrite by immobilized Alcaligenes faecalis WT14 during aerobic denitrification process[J].Technology of Water Treatment,2021,47(11):65-70.

[30] Miyo N,Tadashi I,Suguru O,et al.Effect of salinity on denitrification under limited single carbon source by Marinobacter sp.isolated from marine sediment[J].Journal of Basic Microbiology,2010,50(3):285-289.

[31] Yin J,Hunt K A,Xie T,et al.Pairing denitrifying phosphorus accumulating organisms with anaerobic ammonium oxidizing bacteria for simultaneous N and P removal[J].Science of the Total Environment,2021,787:147521.

[32] 李艳丽,杨垒,张志昊,等.好氧反硝化细菌Burkholderia sp.ZH8的脱氮特性与生物强化作用研究[J].中国环境科学,2024,3(15):1-11.Li Y L,Yang L,Zhang Z H,et al.Nitrogen removal characteristics and bioenhancement effects of aerobic denitrifying bacteria Burkholderia sp.ZH8[J].China Environmental Science,2024,15(3):1-11.

基本信息:

DOI:10.16441/j.cnki.hdxb.20240175

中图分类号:X172;X714

引用信息:

[1]王文鑫,林久淑,聂新华,等.好氧反硝化菌Marinobacter sp. strain B108固定化及脱氮动力学研究[J].中国海洋大学学报(自然科学版),2025,55(09):103-113.DOI:10.16441/j.cnki.hdxb.20240175.

基金信息:

国家自然科学基金项目(51978636)资助~~

投稿时间:

2024-04-23

投稿日期(年):

2024

终审时间:

2024-05-16

终审日期(年):

2024

修回时间:

2024-05-11

审稿周期(年):

1

发布时间:

2025-08-26

出版时间:

2025-08-26

检 索 高级检索

引用

GB/T 7714-2015 格式引文
MLA格式引文
APA格式引文