Advanced Materials Research ISSN: 1662-8985, Vols. 418-420, pp 2286-2289 doi:10.4028/www.scientific.net/AMR.418-420.2286 © 2012 Trans Tech Publications, Switzerland Online: 2011-12-06 Contributions of Microorganisms to Nitrogen Cycle of Wuyiling Wetland in Yichun in Northeast China Li Ji-guang1, 2, a, Ren Yi-bin2, Ren Nan-qi2, Yang Chun-wen1, Zuo Chun-sheng1, Jin zhi-min1, Shao Yan-qiu1 1 2 College of Life Sciences and Technology, Mudanjiang Teachers College, Mudanjiang, Heilongjiang, 157012, China State Key Laboratory of Urban Water Resource and Environment, Harbin Institute of Technology, Harbin Heilongjiang, 150090, China a [email protected] Keywords: Microorganisms, Nitrogen Cycle, Wetland, Bacterial strain, Ammonium oxidation. Abstract. Wetland is the important part in urban ecosystem. Microorganisms is integral component of urban wetland ecosystem is the main factor of wetlands sewage treatment, and plays an irreplaceable role in the degradation. In this paper, the authors regard urban wetland of Yichun in north shore of Tangwang river as the research object, through experiments to identify the microorganisms types, finding five microorganisms types being nitrify fungi. The article analyzes the contributions of microorganisms in nitrogen cycle of urban wetland. It is present that microorganisms plays an irreplaceable role in controlling pollutions and nitrification and anti-nitrification reactions play the most significant role in the degradation of nitrogen compounds and ammonium oxidation is a possible process in deducing nitrogen pollutions. Introduction Wetland is a special amphibious transitional ecosystem[1]. The ramsar convention wetlands defined as ask its natural or artificial, long-term or intermittent swamp, wet original, peatland or water zone, providing static or flowing water, brackish or salt, low water depth is not more than 6m waters[2]. Urban wetland refers to distributed in the city wetland, including all kinds of natural and artificial wetland[3]. Urban wetland has unique hydrology, soil, vegetation and biological characteristics of the ecological system[4]. Urban wetland is not only a large reservoirs, still can eliminate toxic substances into the water, which mainly rely on wetland of animals and plants and a lot of microorganisms to solve[5]. The study area is located in Yichun Tangwang river north shore with urban water-barrier opposite between north and south in the Tangwang river embankment with total area of 88 square kilometers. Range is bound up with Yichun west coast state railway bridge, east to the north on changing forward dike, the south to the north, and Yichun Tangwang river mainstream city of pearl river. The area is river wetland mudflat the flora. All rights reserved. No part of contents of this paper may be reproduced or transmitted in any form or by any means without the written permission of Trans Tech Publications, www.ttp.net. (ID: 130.203.136.75, Pennsylvania State University, University Park, USA-05/03/16,17:42:22) Advanced Materials Research Vols. 418-420 2287 Microorganisms in Wuyiling Wetland Source of wetland microbial Wetland the microorganism mainly comes from earth, air, water or death of animal and plant body etc. Corruption Especially in the soil microorganisms, often with soil was the rains washed out into rivers and lakes in. Soil bacteria, actinomyces and fungi all the most, in the wetlands can be found in almost any. Most wetland in water is given priority to, the main photosynthetic organisms are microorganisms. In aerobic zone to cyanobacteria and algae, being While in anaerobic area are in photosynthetic bacteria in the majority. These microbes, pass photosynthesis, will change into organic, inorganic composition itself, known as primary producers. Regional wetland microorganism strains identified Taken from the Tangwang river north shore artificial wetland and natural wetland three groups of water, strains morphological characteristics such as shown in table 1, strains of physiological and biochemical characteristics, the article selected strains are the process of cultivation grew significantly in chemical reaction with the morphological characteristics are representative. Besides that, as higher biological adopts the traditional morphology, physiology and ecology characters, but also must find new features as the basis of classification and identification [6]. Experimental results on the basis of the above berger's handbook classify bacteria appraisal appraisal, identified the partial strains to genus, the rest will continue to appraise the strains, strains identified results such as shown in table 1 Through the identification of these strains belong to bacteria and actinomyces, 5 kinds of microbe has nitrate reducing activity, for nitrification fungi, the results is shown in Table 1. Table 1 Physiological biochemical identification of bacteria types Physiological and biochemical experiment reaction conditions Item mesh Starch hydrolysis Citrate utilization test Sugar or alcohol fermentation tests Nitrate reducing Gelatin V-P test test liquefaction test Indoles test J1 + + + + + + - J2 - + + - + + - J3 + - + + + + - J4 + - + - - - - J5 - + + + - - - J6 + - + - - + - J7 - + + + - + - J8 + - + + - + - J9 - - + - + + - Due to the development of ecological environment, urban wetland within the microorganisms may also produces change, through the appraisal, determine strains loose north of urban wetland in microbial species, is for the purpose of studying wetland microbes to the influence of the function of the city wetland. Urban wetlands have purify environment pollution, degradation of function, microbial species for wetland play that functions play an important role, the wetland of microorganism chemical and biological process can be made into wetland degradation and toxic substance transformation, different microbial plays a different role. 2288 Materials Processing Technology, ICAMMP2011 Nitrogen circulating system of Wuyiling Wetland Nitrogen cycling is a complex system, the biosphere by a large majority of nitrogen in the form of nitrogen gas in the atmosphere, nitrogen through living and non-living role of ammonia nitrogen, fixed generation after became assimilated into organic nitrogen or into nitric acid, nitric acid nitrogen and nitrogen through reverse nitrification into nitrogen or nitrous-oxide [7]. Improve nitrogen removal rate is the main purpose of the urban wetland research, so the city wetland nitrogen circulatory system is the key point. Urban wetland system nitrogen in the form of existence many, including urban wetland by agricultural pollution, nitrogen mainly exists in the form of nitrate nitrogen, From industrial wastewater pollution or animal husbandry, breeding polluted, nitrogen is mainly by ammonia nitrogen forms exist. Urban wetland systems, most of the microbial participate in a different form of inorganic nitrogen transformation, including plant, microorganism and soil participation of internal circulation is the main nitrogen cycle. Because in the whole nitrogen cycling, organic nitrogen through ammoniation role into inorganic nitrogen, after a series of reactions with inorganic nitrogen related, and the transformation of microbes in nitrogen cycle of use are mainly inorganic state of nitrogen, so here only discuss the inorganic nitrogen. Inorganic nitrogen mainly, the results is shown in Table 2. Table 2 Strains identified Project J1 J2 J3 J4 J5 J6 J7 J8 J9 Fungi genera Corynebacterium Micrococcus Staphylococus Bacillus Streptomyces Streptocucus Salmonella Lignieres Neisseria Trevisan Enterobacter Nitrogen nitrification and denitrification process is wetland ecosystem degradation of nitrogen in the main process, but anaerobic ammonium oxidation process offered to traditional nitrogen cycle theory added new content. Conclusion From the wetland nitrogen removal contaminants of Angle, microorganisms responsible nitrification and nitrogen is will pollutants from wetland system to remove the main way, the wetland nitrogen cycles of nitration and process will enter the wetland of most nitrogen transformation, general but will nitrogen removal 70% ~ 90%. Microbial role is decisive role, from combined nitrogen to gaseous nitrogen removal nitrogen pollution substance transformation mainly through nitrification[8]. Ammonia nitrogen to proposed by the transformation of nitrogen proposed form afterbirth fungus genera and proposed coccus of genera and proposed such action. Proposed nitrogen to nitric acid nitrogen ransformation mainly through the denitrifying bacteria, denitrifying aureus genera belong to play a role. Because these bacteria growth strictly aerobic and anaerobic cannot live so called the aerobic nitrogen-fixing microorganisms, and because they are in the Advanced Materials Research Vols. 418-420 2289 growth process does not require only organic, inorganic and CO2, via oxidative inorganic gain energy and material to assimilation CO2 component cells, so they all belong to which can since oxygen bacteria. Anaerobic ammonium oxidation process is the premise condition is ammonia nitrogen, proposed nitrogen also exists, and anaerobic environment, exist widely in the wetland aerobic/anaerobic interface is the establishment of anaerobic ammonium oxidation process in wetland existed in a premise, the role the this process is mainly anaerobic ammonium oxidation bacteria play a role. In wetland microbial gathered the root zone aerobic/anaerobic microenvironment, is possible that role, anaerobic ammonium oxidation reaction might also be removing nitrogen pollution ways, including the role the microorganisms need further research. Acknowledgments This work was supported by the Education Department of Heilongjiang Province, surface science and technology research projects(No.11551517),Young academic backbones of Mudanjiang Teachers College (No.200901),Mudanjiang Municipal Science and Technology Bureau of scientific and technological projects (No.200920065), National water pollution control technology major projects (No. 2009ZX07424-001),The funding from Project 50821002(National Creative Research Groups) supported by National Nature Science Foundation of China,the Major Program of National Natural Science Foundation of China (No. 50638020),State Key Laboratory of Urban Water Resource and Environment (No. 2010DX11). References [1] Shen Wanbin, Zhao Tao, Liu Peng, Zhong Yuhong, Zhang Haitao. Assessment of environmental and economic values for constructed wetland and a case study[J].Research of Environmental Sciences, 2005,2(18):70-73. [2] Guo Yuedong, He Yan, Deng Wei, Zhang Guangxin, Pan Jihua. Study on the spatial variability of water nitrogen and phosphorus in the zhalong wetland[J].Research of Environmental Sciences, 2005,2(18):51-56. [3] Cao Luomeng, Li Xiaoling, Yu Kongjian. Ecological function of urban wetland[J].City Science, ,2003,3(1):9-12. [4] Cao Luomeng , Yu Kongjian. The reasonable countermeasure of urban wetland utlization[J]. Information of China Construction, 2005,3(9):9-12. [5] Duan Changqun. Environment biology[M].Science Press,2004:102. [6] Shen Ping. Microbiology[M].Higher Education Press,2000,11(5):311-312. [7] Ruan Xiaohong, Zhang Ying, Huang Linnan, Ao Jing. Study on the contributions of microorganisms in nitrogen cycle of wetlands[J].Water Resource Protection,2004,9:61-69. [8] Porporato A,Odorico P D, Laio F, et al. Hydrologic controls on soil carbon and nitrogen cycles; I modeling scheme[J]. Advances in Water Resources,2003,26:45-58. Materials Processing Technology, ICAMMP2011 10.4028/www.scientific.net/AMR.418-420 Contributions of Microorganisms to Nitrogen Cycle of Wuyiling Wetland in Yichun in Northeast China 10.4028/www.scientific.net/AMR.418-420.2286
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