Supernatant organics from anaerobic digestion after thermal hydrolysis cause direct and/or diffusional activity loss for nitritation and anammox

被引:65
作者
Zhang, Qi [1 ,2 ,3 ]
Vlaeminck, Siegfried E. [2 ,4 ]
DeBarbadillo, Christine [1 ]
Su, Chunyang [1 ]
Al-Omari, Ahmed [1 ]
Wett, Bernhard [5 ]
Pumpel, Thomas [6 ]
Shaw, Andrew [7 ]
Chandran, Kartik [3 ]
Murthy, Sudhir [1 ]
De Clippeleir, Haydee [1 ]
机构
[1] DC Water, 5000 Overlook Ave SW, Washington, DC 20032 USA
[2] Univ Ghent, Fac Biosci Engn, CMET, Coupure Links 653, B-9000 Ghent, Belgium
[3] Columbia Univ, Dept Earth & Environm Engn, 500 West 120th St, New York, NY USA
[4] Univ Antwerp, Dept Biosci Engn, Res Grp Sustainable Energy Air & Water Technol, Groenenborgerlaan 171, B-2020 Antwerp, Belgium
[5] ARAconsult, Unterbergerstr 1, A-6020 Innsbruck, Austria
[6] Inst Microbiol, Technikerstr 25, A-6020 Innsbruck, Austria
[7] Black & Veatch Consulting Engineers, 8400 Ward Pkwy, Kansas City, MO 64114 USA
关键词
Biological nutrient removal; Partial nitrification/anammox; Water resources recovery facility; WASTE ACTIVATED-SLUDGE; MAINSTREAM DEAMMONIFICATION; MUNICIPAL SLUDGE; NITROGEN REMOVAL; NITRIFICATION; INHIBITION; SUBSTRATE; CARBON; WATER; SOIL;
D O I
10.1016/j.watres.2018.06.037
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Treatment of sewage sludge with a thermal hydrolysis process (THP) followed by anaerobic digestion (AD) enables to boost biogas production and minimize residual sludge volumes. However, the reject water can cause inhibition to aerobic and anoxic ammonium-oxidizing bacteria (AerAOB & AnAOB), the two key microbial groups involved in the deammonification process. Firstly, a detailed investigation elucidated the impact of different organic fractions present in THP-AD return liquor on AerAOB and AnAOB activity. For AnAOB, soluble compounds linked to THP conditions and AD performance caused the main inhibition. Direct inhibition by dissolved organics was also observed for AerAOB, but could be overcome by treating the filtrate with extended aerobic or anaerobic incubation or with activated carbon. AerAOB additionally suffered from particulate and colloidal organics limiting the diffusion of substrates. This was resolved by improving the dewatering process through an optimized flocculant polymer dose and/or addition of coagulant polymer to better capture the large colloidal fraction, especially in case of unstable AD performance. Secondly, a new inhibition model for AerAOB included diffusion-limiting compounds based on the porter-equation, and achieved the best fit with the experimental data, highlighting that AerAOB were highly sensitive to large colloids. Overall, this paper for the first time provides separate identification of organic fractions within THP-AD filtrate causing differential types of inhibition. Moreover, it highlights the combined effect of the performance of THP, AD and dewatering on the downstream autotrophic nitrogen removal kinetics. (C) 2018 Elsevier Ltd. All rights reserved.
引用
收藏
页码:270 / 281
页数:12
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