Figure 10 ,Table 2个

    • 图  1  FWFL的COD、多糖、蛋白质、NH4+-N和TP随发酵时间的质量浓度变化

      Figure 1.  Changes in COD, the mass concentrations of polysaccharides, proteins, NH4+-N and TP of the food waste fermentation with the fermentation time

    • 图  2  C/N和人工湿地高度对COD去除效果的影响

      Figure 2.  Effects of C/N ratio and constructed wetland height on COD removal

    • 图  3  C/N和人工湿地高度对NH4+-N去除效果的影响

      Figure 3.  Effects of C/N ratio and constructed wetland height on NH4+-N removal

    • 图  4  C/N和人工湿地高度对NO3−-N去除效果的影响

      Figure 4.  Effects of C/N ratio and constructed wetland height on NO3−-N removal

    • 图  5  C/N和人工湿地高度对NO2−-N去除效果的影响

      Figure 5.  Effects of C/N ratio and constructed wetland height on NO2−-N removal

    • 图  6  C/N和人工湿地高度对TN去除效果的影响

      Figure 6.  Effects of C/N ratio and constructed wetland height on TN removal

    • 图  7  C/N和人工湿地高度对TP去除效果的影响

      Figure 7.  Effects of C/N ratio and constructed wetland height on TP removal

    • 图  8  人工湿地填料生物膜的反硝化速率、厌氧氨氧化速率、NAR活性、NIR活性、AMO活性与ETSA

      Figure 8.  Denitrification rate, ANAMMOX rate, NAR, NIR and AMO activity, ETSA of medium biofilm in constructed wetlands

    • 图  9  不同C/N人工湿地生物膜门水平和属水平细菌的相对丰度

      Figure 9.  Relative abundance of bacteria at the phylum and genus level in constructed wetlands with different C/N

    • 图  10  环境因子与人工湿地菌群在门水平层面的典型对应分析排序

      Figure 10.  CCA sequencing of environmental factors and constructed wetlands bacteria at the phylum level