Control of denitrification in a septage-treating artificial wetland: the dual role of particulate organic carbon

被引:58
作者
Hamersley, MR
Howes, BL
机构
[1] Univ Massachusetts, Sch Marine Sci & Technol, New Bedford, MA 02744 USA
[2] Woods Hole Oceanog Inst, Dept Biol, Woods Hole, MA 02543 USA
关键词
anaerobic microsites; artificial wetlands; denitrification; nitrogen; particulate organic carbon; septage;
D O I
10.1016/S0043-1354(02)00134-3
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
We examined the factors controlling organic carbon (C) cycling and its control of nitrogen (N) removal via denitrification in an aerated artificial wetland treating highly concentrated wastewater to nutrient-removal standards. Processing of organic material by the septage-treating wetland affected the biological reactivity (half-life, or t(1/2)) Of organic C pools through microbial degradation and gravity fractionation of the influent septage. Primary sedimentation fractionated the initial septage material (t(1/2) = 8.4d) into recalcitrant waste solids (t1/2 = 16.7d) and highly labile supernatant (t(1/2) = 5.0d), allowing this reactive fraction to be further degraded during treatment in aerobic wetland tanks until a less labile material (t(1/2) = 7.3d) remained. Organic C contributions from in situ fixation by nitrifying bacteria or algae in these tanks were small, about 1% of the C degradation rate. In the aerated tanks, denitrification was correlated with particulate organic C loading rates, although the average C required (0.35 mg C L-1 h(-1)) to support denitrification was only 12% of the total C respiration rate (2.9 mg C L-1 h(-1)). Additions of plant litter (2.5 g C L-1) to the aerated tanks under normal operating conditions doubled denitrification rates to 0.58 mg N L-1 h(-1), and reduced effluent nitrate levels by half, from 12.7 to 6.4 mg N L-1. However, C degradation within the plant litter (0.15 mg C L-1 h(-1)) was sufficient to have accounted for only 35% of the additional denitrification. Evidence from laboratory and full-scale plant litter additions as well as process monitoring indicates that the stimulation of denitrification is due to the respiration-driven formation of anaerobic microsites within particulate organic C. In this aerated highly C-loaded septage-treating wetland, anaerobic microsite, rather than C substrate availability limits denitrification. (C) 2002 Elsevier Science Ltd. All rights reserved.
引用
收藏
页码:4415 / 4427
页数:13
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