不同温度秸秆炭对好氧反硝化菌去除水中硝酸盐和N2O排放的影响

    Effects of Corn Straw Biochar Pyrolyzed at Different Temperatures on Nitrate Removal and N2O Emission Mediated by Aerobic Denitrifying Bacteria in Aquatic System

    • 摘要: 为探究不同温度(300、400和500 ℃)制得的玉米秸秆生物炭(BC300、BC400和BC500)在不同C/N比(4、6和8)条件下对好氧反硝化细菌去除水中硝酸盐和N2O排放的影响, 在生物炭制备表征与好氧反硝化细菌Paraclostridium benzoelyticum strain KD1筛选基础上, 将生物炭加入含有筛选菌株的培养体系, 同时设置不添加生物炭的对照处理, 开展特定C/N比条件下微生物去除模拟废水中硝酸盐(15 mg·L-1, 以N计)的好氧培养实验, 分析培养体系N2O排放和氮浓度的动态变化。结果表明, 该菌株0~24 h的NO3--N平均去除速率为0.322 mg·L-1·h-1。当C/N为4和6时, 生物炭对NO3--N反硝化去除有促进作用, 且BC400的促进作用最强; 生物炭显著抑制N2O排放, 且BC400的抑制作用最强, 主要原因为BC400中较高的溶解性有机碳含量以及丰富的表面氧化还原活性官能团促进了反硝化作用和N2O还原; 同时, BC400对培养体系硝酸盐异化还原为铵过程的促进作用可能是其抑制N2O排放的另一原因。当C/N为8时, 生物炭对NO3--N反硝化去除则呈抑制效应; 与对照处理相比, 添加生物炭处理的N2O累积排放量略有增加, 主要是由于充足的外加碳源在N2O生成和还原中扮演的角色优于生物炭。

       

      Abstract: The study investigated the effects of corn straw biochars (BC300, BC400, and BC500), pyrolyzed at 300, 400, and 500 ℃ respectively, on nitrate removal and N2O emission in aqueous system mediated by the aerobic denitrifying bacterium Paraclostridium benzoelyticum strain KD1 across varying C/N ratios (4, 6, and 8). Following comprehensive biochar characterization and bacterial strain screening, a series of aerobic incubation experiments were conducted using simulated wastewater containing nitrate (15 mg·L-1 in N). The experimental design included biochar-amended treatments and a non-amended control, with continuous monitoring of N2O emission and nitrogen species transformation dynamics. Results demonstrate that the selected strain exhibited an average NO3--N removal rate of 0.322 mg·L-1·h-1 during the initial 24-hour period. At C/N ratios of 4 and 6, biochar amendments significantly enhanced NO3--N removal by denitrification while concurrently suppressing N2O emission, with BC400 showing the most pronounced effects. The superior performance of BC400 was attributed to its relatively higher dissolved organic carbon content and abundant surface redox-active functional groups, which facilitated both denitrification process and N2O reduction. Additionally, BC400's promotion of dissimilatory nitrate reduction to ammonium within the incubation system may also have contributed to the observed N2O emission suppression. Contrastingly, at a higher C/N ratio of 8, biochar amendments exhibited an inhibitory effect on NO3--N removal through denitrification. In this scenario, the cumulative N2O emissions from biochar-amended treatments slightly exceeded that of the control, suggesting that sufficient exogenous carbon may exert a more substantial influence on N2O production and reduction than biochar amendment under these conditions.

       

    /

    返回文章
    返回