Copyright: © 2013 Xu-jie LU. This is an open-access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited. Nitrogen was a main contaminant of surface water in China presently. For instance, discharges of oil refining, chemical fertilizer, food and cultivation industry production have high concentration ammonia nitrogen in China, and the concentration of ammonia nitrogen is 200-6000 mg/L [1]. Uncontrolled discharge of nitrogen into natural water channels stimulates eutrophication of surface waters, such as lakes and rivers [1,2]. Thus, contamination of water bodies by nitrogen has led to increasing attention focused on wastewater treatment. As well, Nitrogen removal urgently needed to be solved as one of the difficult problem in the current wastewater treatment. At present, more and more researchers focused on simple and low-cost natural technologies (e.g constructed wetlands). As typical natural and environmental friendly systems [3,4] constructed wetlands primarily depend on naturally occurring energies such as solar radiation, and biomass storage, and using rooted water tolerant plants and media to provide treatment of wastewater [5,6]. As a green treatment technology and engineering measure, they have the unique advantage of producing higher effluent quality without the input of fossil energy thereby reducing operation costs and high costs of the maintenance [7-10]. Constructed wetlands are engineered wetlands with saturated or unsaturated substrates, a large biomass of plants, such as emergent, floating and submergent, and a large variety of microbial communities, like the as nitrifying bacteria denitrifying bacteria [6]. Compare with conventional technologies (such as membrane bioreactors), constructed wetlands have higher nitrogen removal efficiency and lower organic removal by increasing the contact time between wastewater and biofilms [11,12]. Besides, the characteristics of constructed wetlands are impacting resistance, stabilizing the effluent quality, simplifying operation and maintenance, and low operating cost. However, their floor spaces are larger, and the wetlands exhibit higher pollutant removal rates under greater loadings conditions [1]. In extremely cold areas, the phenomenon is more significant. The wastewater treatment technology of constructed wetlands is increasable widely used in urban and rural areas of South China [13-16]. However, constructed wetlands were not widespread uses of technology in China which spans 49 latitudes, resulting in the large differences in climate, terrain and plant communities between South and North China, especially low temperature under winter cold climate condition, such as in Northeast China. Hence, there are a lot of difficulties in adopting constructed wetlands in Northeast China.