以丝瓜络为碳源的固相反硝化系统性能  

Solid phase denitrification system performance using loofah sponge as carbon source

作　　者：高书伟 张凯[1] 李志斐[1] 谢骏[1] 王广军[1] 郁二蒙[1] 李红燕 夏耘[1] 田晶晶 龚望宝[1] GAO Shuwei;ZHANG Kai;LI Zhifei;XIE Jun;WANG Guangjun;YU Ermeng;LI Hongyan;XIA Yun;TIAN Jingjing;GONG Wangbao(Key Laboratory of Tropical&Subtropical Fishery Resource Application and Cultivation,Ministry of Agriculture and Rural Affairs,Pearl River Fisheries Research Institute,Chinese Academy of Fishery Sciences,Guangdong Key Laboratory of Aquatic Animal Immunity Technology,Guangzhou 510380,Guangdong,China;National Demonstration Center for Experimental Fisheries Science Education,Shanghai Ocean University,Shanghai 201306,China)

机构地区：[1]中国水产科学研究院珠江水产研究所,农业农村部热带亚热带水产资源利用与养殖重点实验室,广东省水产动物免疫技术重点实验室,广东广州510380 [2]上海海洋大学,水产科学国家级实验教学示范中心,上海201306

出　　处：《水产学报》2024年第2期164-177,共14页Journal of Fisheries of China

基　　金：国家重点研发计划(2019YFD0900302);广东省促进经济发展专项资金(粤农2019B13);国家现代农业产业技术体系(CARS-45-21);中国水产科学研究院基本科研业务费(2020TD58)。

摘　　要：构建以丝瓜络为碳源的固相反硝化系统,探究不同水力停留时间(HRT)和进水硝酸盐浓度(INC)下该系统的反硝化性能,为丝瓜络作为水产养殖尾水反硝化碳源的工艺优化提供理论依据。以丝瓜络(LS)为一维反硝化反应器(denitrification reactor,DR)外加碳源,在流场环境下,测定不同HRT(16、20、24和28 h)和INC(50、75、100和125 mg/L)下反硝化系统对硝酸盐氮(NO_(3)^(-)-N)、亚硝酸盐氮(NO_(2)^(-)-N)、氨氮(NH_(4)^(+)-N)、总氮(TN)、总磷(TP)和化学需氧量(CODcr)的去除效果。并采用高通量测序技术对丝瓜络反硝化反应器(LS-DR)在运行初期和末期时的细菌群落结构进行分析。当INC为50 mg/L,HRT为24h时,LS-DR对NO_(3)^(-)-N和TN均有较好的去除效果,去除率分别为98.97%±0.52%和97.84%±0.94%,此时出水NO_(2)^(-)-N浓度也达到较低水平(小于0.5 mg/L);在HRT为24 h的基础上,当INC增加至75、100和125 mg/L时,其NO_(3)^(-)-N去除率和NO_(3)^(-)-N去除速率(NRR)均随INC的增加而显著增加,出水COD则随INC的增加而降低,但均未实现完全反硝化,然而,LS-DR在整个实验期间均能完全去除NH_(4)^(+)-N;扫描电镜结果显示,丝瓜络表面结构有利于微生物附着生长;高通量测序结果显示,LS-DR的优势菌门包括变形菌门、拟杆菌门、弯曲杆菌门、厚壁菌门和疣微菌门;被鉴定的优势菌属中热单胞菌属(1.46%)、陶厄氏菌属(0.55%)、固氮螺菌属(3.32%)、Simplicispira(1.01%)、假黄色单胞菌属(0.39%)、草螺菌属(3.02%)和Uliginosibacterium(0.9%)主要参与反硝化的进行,Cytophaga xylanolytica(1.61%)和Cloacibacterium(2.69%)主要参与了丝瓜络的降解,黄杆菌属(1.17%)和Diaphorobacter(0.64%)既能进行反硝化,也能降解丝瓜络。LS-DR的最佳HRT为24 h,最适宜的INC为50 mg/L。本研究为丝瓜络固相反硝化工艺的优化提供了理论基础,为开发新型缓释碳源在养殖尾水处理中的应用提供参考。The second national pollution sources survey showed that the total nitrogen emission from aquaculture is 99100 tons in 2017.To protect the environment and human health,it is important to remove nitrogen from aquaculture wastewater before being discharged to surrounding waters.Biological denitrification is considered the most promising approach methods,since nitrate can be reduced to harmless nitrogen gas by bacteria.Sufficient carbon source is necessary during heterotrophic denitrification process.To solve the problems mentioned above,external carbon sources such as methanol,acetic acid and glucose were added to the wastewater,whereas they were generally high-cost,high-energy and high operating requirement.In contrast,agricultural wastes were used as carbon source,which has shown significant economic advantages and highefficiency.Many aquaculture wastewater treatment systems often face variations in hydraulic retention time(HRT)and Influent nitrate concentration(INC)which are caused by acute change of wastewater characteristics and production,and HRT and INC often exert a profound effect on the treatment performance of biological treatment systems.The purpose of this study is to construct a solid-phase denitrification system with loo-fah sponge as carbon source,and investigate the effects of HRT and INC on the denitrification performance of loofah sponge-denitrification reactor(LS-DR),so as to provide a theoretical basis for the further optimization of denitrification process of loofah sponge as denitrification carbon source in aquaculture tailwater.Loofah sponge,one typical agricultural waste,was studied as the carbon source for solid phase denitrification under dynamic flow conditions by using 1-D column experiment.We aim to preliminarily investigate the LS-DR’s NO_(3)^(−)-N,NO_(2)^(−)-N,NH_(4)^(+)-N,TN,TP and COD removal effect at different HRT(16,20,24 and 28 h)and INC(50,75,100 and 125 mg/L).The optimal HRT of denitrification reactor was optimized by one-way ANOVA analysis.And,the high-throughput seque

关 键 词：养殖尾水 固相反硝化 水力停留时间 进水硝酸盐浓度 丝瓜络 微生物群落 

分 类 号：S949[农业科学—水产养殖] Q89[农业科学—水产科学]