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首页> 外文期刊>Chemosphere >Formation of N-nitrosamines by chloramination or ozonation of amines listed in Pollutant Release and Transfer Registers (PRTRs)
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Formation of N-nitrosamines by chloramination or ozonation of amines listed in Pollutant Release and Transfer Registers (PRTRs)

机译:通过对污染物排放和转移登记簿(PRTR)中列出的胺进行氯化或臭氧化来形成N-亚硝胺

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We determined whether or not the chloramination or ozonation of amines and hydrazines listed in Pollutant Release and Transfer Registers (PRTRs) results in the formation of N-nitrosamines when reacted in secondary wastewater effluent. We selected 12 primary, 2 secondary, 2 tertiary amines and 3 hydrazines from the PRTRs of Japan, the USA, and Korea. In this study, based on the assumption that there is a production of N-nitrosamines by not only the original selected amines and hydrazines but also the intermediate products in case of chloramination and ozonation, it was examined whether precursors were identified by selected amines and hydrazines based on the gap of the N-nitrosamines formation potential between day 0 and day 10 rather than analyzing the contribution depending on the concentration of selected amines and hydrazines. Many of the primary amines (notably 2,6-xylidine) and all of the secondary and tertiary amines produced N-nitrosodimethylamine (NDMA) by chloramination. Furthermore, the primary amines 2,6-xylidine, 3,3'-dimethylbenzidine, 4,4'-methylenebis(2-chloroaniline), 4-aminoazo-benzene, p-chloroaniline, and p-cresidine produced more NDMA than did the secondary amines. The secondary amines produced mainly NDMA. Ozonation produced NDMA only from the hydrazine 1,1-dimethylhydrazine, and at a higher concentration than by chloramination. We identified 2,6-xylidine, 3,3'-dimethylbenzidine, 4,4'-methylenebis(2-chloroaniline), 4-aminoazobenzene, p-chloroaniline, p-cresidine, 1,1-dimethylhydrazine, diethylamine, 4,4'-methylenebis(N,N-dimethyl)benzenamine, and chinomethionat as warranting further study.
机译:我们确定了污染物释放和转移登记表(PRTR)中列出的胺和肼的氯化或臭氧化反应是否会导致其在次要废水中的反应而形成N-亚硝胺。我们从日本,美国和韩国的PRTR中选择了12种伯胺,2种仲胺,2种叔胺和3种肼。在这项研究中,基于这样的假设:不仅最初选择的胺和肼还会产生N-亚硝胺,而且在氯化和臭氧化的情况下还会产生中间产物,因此检查了是否通过选择的胺和肼鉴定了前体基于第0天到第10天之间N-亚硝胺形成潜力的差距,而不是根据所选胺和肼的浓度分析影响。许多伯胺(尤其是2,6-二甲苯胺)以及所有仲胺和叔胺通过氯化作用生成N-亚硝基二甲胺(NDMA)。此外,伯胺2,6-二甲苯胺,3,3'-二甲基联苯胺,4,4'-亚甲基双(2-氯苯胺),4-氨基偶氮苯,对氯苯胺和对甲酚比苯胺产生更多的NDMA。仲胺。仲胺主要产生NDMA。臭氧化仅从肼1,1-二甲基肼产生NDMA,并且其浓度高于通过氯化的浓度。我们确定了2,6-二甲苯胺,3,3'-二甲基联苯胺,4,4'-亚甲基双(2-氯苯胺),4-氨基偶氮苯,对氯苯胺,对甲酚,1,1-二甲基肼,二乙胺,4,4 '-亚甲基双(N,N-二甲基)苯胺和甲壳蛋氨酸值得进一步研究。

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