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反硝化活性污泥对壬基酚聚乙氧基化物的生物降解作用

Biodegradation of nonylphenol polyethoxylates by denitrifying activated sludge.

作者信息

Lu Jian, Jin Qiang, He Yiliang, Wu Jun, Zhang Wenying, Zhao Juan

机构信息

School of Environmental Science and Engineering, Shanghai Jiao Tong University, Shanghai 200240, PR China.

出版信息

Water Res. 2008 Feb;42(4-5):1075-82. doi: 10.1016/j.watres.2007.09.031. Epub 2007 Oct 5.

Abstract

Biodegradation of nonylphenol polyethoxylates (NPEOs) by denitrifying activated sludge was investigated. The results showed that NPEOs were readily degraded in the denitrifying activated sludge process. Organic substance, initial concentration, and temperature had great influence on biodegradation of NPEOs in the denitrifying activated sludge process while the influence of biodegradation intermediates such as nonylphenol (NP) could be neglected. Biodegradation of NPEOs was severely inhibited in the presence of organic substances. Different organic substances had different inhibition ability on the biodegradation of NPEOs. The maximum biodegradation rate increased 2.51 microM d(-1) for each 10 microM increase in initial concentration of NPEOs. This linear relationship was maintained even at relatively high initial concentration. The decrease in temperature caused a sharp decrease in the removal efficiency of NPEOs. The temperature coefficient (Phi) for the biodegradation of NPEOs in the denitrifying activated sludge process was 0.011 degrees C(-1). NPEOs were biodegraded through a nonoxidative pathway, through which NPEOs were degraded via sequential removal of ethoxyl units (as acetaldehyde) to NP. Compared to anaerobic activated sludge treatment, denitrifying activated sludge treatment had much higher removal efficiency of NPEO contaminants. To our knowledge, it is the first report on the biodegradation of NPEOs in denitrifying activated sludge process.

摘要

研究了反硝化活性污泥对壬基酚聚乙氧基化物(NPEOs)的生物降解作用。结果表明,NPEOs在反硝化活性污泥工艺中易于降解。有机物、初始浓度和温度对反硝化活性污泥工艺中NPEOs的生物降解有很大影响,而壬基酚(NP)等生物降解中间体的影响可忽略不计。在存在有机物的情况下,NPEOs的生物降解受到严重抑制。不同的有机物对NPEOs生物降解的抑制能力不同。NPEOs初始浓度每增加10微摩尔,最大生物降解速率增加2.51微摩尔·天⁻¹。即使在相对较高的初始浓度下,这种线性关系也能保持。温度降低导致NPEOs去除效率急剧下降。反硝化活性污泥工艺中NPEOs生物降解的温度系数(Phi)为0.011℃⁻¹。NPEOs通过非氧化途径进行生物降解,通过该途径,NPEOs通过依次去除乙氧基单元(作为乙醛)降解为NP。与厌氧活性污泥处理相比,反硝化活性污泥处理对NPEO污染物的去除效率要高得多。据我们所知,这是关于反硝化活性污泥工艺中NPEOs生物降解的首次报道。

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