Graduate School of Engineering, Hiroshima University, Higashi-Hiroshima 739-8527, Japan.
Environmental Research Management Center, Hiroshima University, Higashi-Hiroshima 739-8513, Japan.
Chemosphere. 2015 Oct;136:153-9. doi: 10.1016/j.chemosphere.2015.04.069. Epub 2015 May 15.
Ozonation is believed to improve the biodegradability of organic compounds. In the present study, degradation of nonylphenol ethoxylates (NPEOs) was monitored in hybrid treatment systems consisting of ozonation and microbial degradation processes. We found that ozonation of NPEOs decreased, rather than increased, the biodegradability under certain conditions. The timing of ozonation was a definitive factor in determining whether ozonation increased or decreased the biodegradation rates of NPEOs. Initial ozonation of NPEOs prior to biodegradation reduced the rate of dissolved organic carbon (DOC) removal during the subsequent 14 d of biodegradation, whereas intermediate ozonation at the 9th day of biodegradation improved subsequent DOC removal during 14 d of NPEO biodegradation. Furthermore, reduction of DOC removal was also observed, when initial ozonation prior to biodegradation was subjected to cetyl alcohol ethoxylates. The production of less biodegradable intermediates, such as mono- and dicarboxylated polyethylene glycols (MCPEGs and DCPEGs), was responsible for the negative effect of ozonation on biodegradability of NPEOs. DCPEGs and MCPEGs were produced by biodegradation of polyethylene glycols (PEGs) that were ozonolysis products of the NPEOs, and the biodegradability of DCPEGs and MCPEGs was less than that of the precursor PEGs. The results indicate that, if the target chemicals contain ethoxy chains, production of PEGs may be one of the important factors when ozonation is considered.
臭氧氧化被认为可以提高有机化合物的可生物降解性。在本研究中,监测了由臭氧氧化和微生物降解过程组成的混合处理系统中非离子型壬基酚聚氧乙烯醚(NPEOs)的降解情况。我们发现,在某些条件下,臭氧氧化会降低 NPEOs 的可生物降解性,而不是提高其可生物降解性。臭氧氧化的时机是决定臭氧氧化是否会增加或降低 NPEOs 生物降解速率的决定性因素。在生物降解之前对 NPEOs 进行初始臭氧氧化会降低随后 14 天生物降解过程中溶解有机碳(DOC)的去除率,而在生物降解第 9 天进行中间臭氧氧化则会提高随后 14 天 NPEO 生物降解过程中 DOC 的去除率。此外,当在生物降解之前对初始臭氧氧化进行十六醇乙氧基化物处理时,也观察到 DOC 去除率的降低。更难生物降解的中间产物,如单羧酸和二羧酸聚乙二醇(MCPEGs 和 DCPEGs)的产生,是臭氧氧化对 NPEOs 可生物降解性产生负面影响的原因。DCPEGs 和 MCPEGs 是 NPEOs 的臭氧氧化产物聚乙二醇(PEGs)生物降解的产物,而 DCPEGs 和 MCPEGs 的生物降解性低于其前体 PEGs。结果表明,如果目标化学品含有乙氧基链,那么当考虑臭氧氧化时,PEGs 的产生可能是一个重要因素。