The effect of thermal hydrolysis pretreatment on the anaerobic degradation of nonylphenol and short-chain nonylphenol ethoxylates in digested biosolids

被引:39
作者
McNamara, P. J. [1 ]
Wilson, C. A. [2 ]
Wogen, M. T. [3 ]
Murthy, S. N. [4 ]
Novak, J. T. [5 ]
Novak, P. J. [1 ]
机构
[1] Univ Minnesota, Dept Civil Engn, Minneapolis, MN 55455 USA
[2] Greeley & Hansen Engineers, Richmond, VA USA
[3] Univ Minnesota, Sch Publ Hlth, Minneapolis, MN 55455 USA
[4] Dist Columbia Water & Sewer Author, Washington, DC USA
[5] Virginia Tech, Dept Civil & Environm Engn, Blacksburg, VA USA
基金
美国国家科学基金会;
关键词
Anaerobic digestion; Thermal hydrolysis; Nonylphenol; Nonylphenol ethoxylates; Biosolids; Estrogenicity; ENDOCRINE-DISRUPTING ACTIVITY; SEWAGE-SLUDGE; WASTE-WATER; ESTROGENIC ACTIVITY; IN-VITRO; CHEMICAL-ANALYSIS; FATE; SOIL; PHARMACEUTICALS; 4-NONYLPHENOL;
D O I
10.1016/j.watres.2012.03.015
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
The presence of micropollutants can be a concern for land application of biosolids. Of particular interest are nonylphenol diethoxylate (NP2EO), nonylphenol monoethoxylate (NP1EO), and nonylphenol (NP), collectively referred to as NPE, which accumulate in anaerobically digested biosolids and are subject to regulation based on the environmental risks associated with them. Because biosolids are a valuable nutrient resource, it is essential that we understand how various treatment processes impact the fate of NPE in biosolids. Thermal hydrolysis (TH) coupled with mesophilic anaerobic digestion (MAD) is an advanced digestion process that destroys pathogens in biosolids and increases methane yields and volatile solids destruction. We investigated the impact of thermal hydrolysis pretreatment on the subsequent biodegradation of NPE in digested biosolids. Biosolids were treated with TH, anaerobic digestion, and aerobic digestion in laboratory-scale reactors, and NPE were analyzed in the influent and effluent of the digesters. NP2EO and NP1EO have been observed to degrade to the more estrogenic NP under anaerobic conditions; therefore, changes in the ratio of NP:NPE were of interest. The increase in NP:NPE following MAD was 56%; the average increase of this ratio in four sets of TH-MAD samples, however, was only 24.6 +/- 3.1%. In addition, TH experiments performed in pure water verified that, during TH, the high temperature and pressure alone did not directly destroy NPE; TH experiments with NP added to sludge also showed that NP was not destroyed by the high temperature and pressure of TH when in a more complex sludge matrix. The post-aerobic digestion phases removed NPE, regardless of whether TH pretreatment occurred. This research indicates that changes in biosolids processing can have impacts beyond just gas production and solids destruction. (C) 2012 Elsevier Ltd. All rights reserved.
引用
收藏
页码:2937 / 2946
页数:10
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