• 文献检索
  • 文档翻译
  • 深度研究
  • 学术资讯
  • Suppr Zotero 插件Zotero 插件
  • 邀请有礼
  • 套餐&价格
  • 历史记录
应用&插件
Suppr Zotero 插件Zotero 插件浏览器插件Mac 客户端Windows 客户端微信小程序
定价
高级版会员购买积分包购买API积分包
服务
文献检索文档翻译深度研究API 文档MCP 服务
关于我们
关于 Suppr公司介绍联系我们用户协议隐私条款
关注我们

Suppr 超能文献

核心技术专利:CN118964589B侵权必究
粤ICP备2023148730 号-1Suppr @ 2026

文献检索

告别复杂PubMed语法,用中文像聊天一样搜索,搜遍4000万医学文献。AI智能推荐,让科研检索更轻松。

立即免费搜索

文件翻译

保留排版,准确专业,支持PDF/Word/PPT等文件格式,支持 12+语言互译。

免费翻译文档

深度研究

AI帮你快速写综述,25分钟生成高质量综述,智能提取关键信息,辅助科研写作。

立即免费体验

某些内分泌干扰物的水相氯化动力学

Aqueous chlorination kinetics of some endocrine disruptors.

作者信息

Deborde Marie, Rabouan Sylvie, Gallard Hervé, Legube Bernard

机构信息

Laboratoire de Chimie de l'Eau et de l'Environnement, UMR CNRS 6008, Ecole Supérieure d'Ingénieurs de Poitiers-40, 86022 Poitiers Cedex, France.

出版信息

Environ Sci Technol. 2004 Nov 1;38(21):5577-83. doi: 10.1021/es040006e.

DOI:10.1021/es040006e
PMID:15575274
Abstract

The aqueous chlorination kinetics of six endocrine disruptors (EDs: 4-n-nonylphenol, beta-estradiol, estrone, estriol, 17alpha-ethinylestradiol, progesterone) were studied in the 3.50-12.00 pH range, at 20+/-2 degrees C, in the presence of an excess of total chlorine. Under these conditions, all molecules with a phenolic group in their structure were rapidly oxidized by chlorine, whereas progesterone remained unchanged. In the first step, apparent kinetic rate constants were determined at various pH levels. Then each elementary reaction kinetic rate constant, i.e., the reaction of hypochlorous acid (HOCl) with ionized EDs and neutral EDs and an acid-catalyzed reaction of HOCl with neutral EDs, was calculated in the second step. The results showed that chlorination exhibits a second-order reaction rate. The rate constants for the acid-catalyzed reaction ranged from 3.02 x 10(4) M(-1) s(-1) (for 4-n-nonylphenol) to 1.82-2.62 x 10(5) M(-1) s(-1) (for hormones). The rate constants of HOCI reactions with ionized EDs were found to be equal to 7.5 x 10(4) M(-1) s(-1) (for 4-n-nonylphenol) and between 3.52 and 4.15 x 10(5) M(-1) s(-1) (for hormones), while the rate contants of HOCI with neutral EDs were much lower, i.e., between 1.31 M(-1) s(-1) (for 4-n-nonylphenol) and 3.74-4.82 M(-1) s(-1) (for hormones). At pH 7, the apparent-second-order rate constants were calculated to range from 12.6 to 131.1 M(-1) s(-1). For a total chlorine concentration of 1 mg/L, the corresponding half-life times at pH 7 were about 65 min for 4-n-nonylphenol and 6-8 min for hormones.

摘要

在20±2℃、pH值为3.50 - 12.00的范围内,在总氯过量的条件下,研究了六种内分泌干扰物(EDs:4 - 正壬基酚、β - 雌二醇、雌酮、雌三醇、17α - 乙炔雌二醇、孕酮)的水相氯化动力学。在这些条件下,结构中含有酚羟基的所有分子都能被氯迅速氧化,而孕酮则保持不变。第一步,在不同pH值水平下测定表观动力学速率常数。第二步,计算每个基元反应动力学速率常数,即次氯酸(HOCl)与离子化EDs和中性EDs的反应以及HOCl与中性EDs的酸催化反应。结果表明,氯化反应表现出二级反应速率。酸催化反应的速率常数范围为3.02×10⁴ M⁻¹ s⁻¹(对于4 - 正壬基酚)至1.82 - 2.62×10⁵ M⁻¹ s⁻¹(对于激素)。发现HOCl与离子化EDs反应的速率常数等于7.5×10⁴ M⁻¹ s⁻¹(对于4 - 正壬基酚),在3.52至4.15×10⁵ M⁻¹ s⁻¹之间(对于激素),而HOCl与中性EDs的速率常数要低得多,即1.31 M⁻¹ s⁻¹(对于4 - 正壬基酚)至3.74 - 4.82 M⁻¹ s⁻¹(对于激素)。在pH值为7时,表观二级速率常数经计算范围为12.6至131.1 M⁻¹ s⁻¹。对于总氯浓度为1 mg/L的情况,在pH值为7时,4 - 正壬基酚的相应半衰期约为65分钟,激素的半衰期为6 - 8分钟。

相似文献

1
Aqueous chlorination kinetics of some endocrine disruptors.某些内分泌干扰物的水相氯化动力学
Environ Sci Technol. 2004 Nov 1;38(21):5577-83. doi: 10.1021/es040006e.
2
Kinetics of aqueous ozone-induced oxidation of some endocrine disruptors.水相中臭氧诱导的某些内分泌干扰物氧化动力学
Environ Sci Technol. 2005 Aug 15;39(16):6086-92. doi: 10.1021/es0501619.
3
Chlorination of bisphenol A: kinetics and by-products formation.双酚A的氯化:动力学及副产物生成
Chemosphere. 2004 Aug;56(5):465-73. doi: 10.1016/j.chemosphere.2004.03.001.
4
[Kinetics of endocrine disrupting chemical 4-tert-butylphenol during chlorination in aqua].水中氯化过程中内分泌干扰化学物质4-叔丁基苯酚的动力学
Huan Jing Ke Xue. 2007 Jul;28(7):1483-9.
5
Aqueous chlorination of diclofenac: kinetic study and transformation products identification.水相中双氯芬酸的氯化反应:动力学研究及转化产物鉴定。
Water Res. 2012 Jun 15;46(10):3377-86. doi: 10.1016/j.watres.2012.03.056. Epub 2012 Apr 2.
6
Aqueous chlorination of carbamazepine: kinetic study and transformation product identification.卡马西平的水氯化反应:动力学研究和转化产物鉴定。
Water Res. 2013 Sep 15;47(14):5076-87. doi: 10.1016/j.watres.2013.05.047. Epub 2013 Jun 15.
7
Ametryn degradation by aqueous chlorine: kinetics and reaction influences.莠灭净在含氯水溶液中的降解:动力学及反应影响因素
J Hazard Mater. 2009 Sep 30;169(1-3):586-92. doi: 10.1016/j.jhazmat.2009.03.147. Epub 2009 Apr 7.
8
Chlorination of phenols: kinetics and formation of chloroform.
Environ Sci Technol. 2002 Mar 1;36(5):884-90. doi: 10.1021/es010076a.
9
Transformation of aminopyrine in the presence of free available chlorine: Kinetics, products, and reaction pathways.在游离有效氯存在下氨基比林的转化:动力学、产物及反应途径
Chemosphere. 2017 Mar;171:625-634. doi: 10.1016/j.chemosphere.2016.12.033. Epub 2016 Dec 26.
10
Chlorination of tramadol: Reaction kinetics, mechanism and genotoxicity evaluation.曲马多的氯化:反应动力学、机理及遗传毒性评估。
Chemosphere. 2015 Dec;141:282-9. doi: 10.1016/j.chemosphere.2015.06.034. Epub 2015 Aug 26.

引用本文的文献

1
Computational Approaches for the Prediction of Environmental Transformation Products: Chlorination of Steroidal Enones.计算方法在环境转化产物预测中的应用:甾体烯酮的氯化反应。
Environ Sci Technol. 2021 Nov 2;55(21):14658-14666. doi: 10.1021/acs.est.1c04659. Epub 2021 Oct 12.
2
Reactions of α,β-Unsaturated Carbonyls with Free Chlorine, Free Bromine, and Combined Chlorine.α,β-不饱和羰基化合物与游离氯、游离溴及结合氯的反应
Environ Sci Technol. 2021 Mar 2;55(5):3305-3312. doi: 10.1021/acs.est.0c07660. Epub 2021 Feb 10.
3
Removal of Emerging Contaminants and Estrogenic Activity from Wastewater Treatment Plant Effluent with UV/Chlorine and UV/H₂O₂ Advanced Oxidation Treatment at Pilot Scale.
采用 UV/氯和 UV/H₂O₂ 高级氧化处理工艺在中试规模下从污水处理厂废水中去除新兴污染物和雌激素活性。
Int J Environ Res Public Health. 2018 May 7;15(5):935. doi: 10.3390/ijerph15050935.
4
Transformation of acetaminophen during water chlorination treatment: kinetics and transformation products identification.对乙酰氨基酚在水氯化处理过程中的转化:动力学及转化产物鉴定
Environ Sci Pollut Res Int. 2016 Jun;23(12):12303-11. doi: 10.1007/s11356-016-6341-x. Epub 2016 Mar 17.
5
Determination of selected pharmaceuticals in tap water and drinking water treatment plant by high-performance liquid chromatography-triple quadrupole mass spectrometer in Beijing, China.中国北京采用高效液相色谱 - 三重四极杆质谱仪测定自来水及饮用水处理厂中的选定药物。
Environ Sci Pollut Res Int. 2015 Feb;22(3):1854-67. doi: 10.1007/s11356-014-3473-8. Epub 2014 Sep 9.
6
Degradation of progestagens by oxidation with potassium permanganate in wastewater effluents.废水中高锰酸钾氧化降解孕激素
Chem Cent J. 2013 May 15;7:84. doi: 10.1186/1752-153X-7-84. eCollection 2013.
7
Quantification of bisphenol A, 353-nonylphenol and their chlorinated derivatives in drinking water treatment plants.饮用水处理厂中双酚 A、353-壬基酚及其氯化衍生物的定量分析。
Environ Sci Pollut Res Int. 2012 Nov;19(9):4193-205. doi: 10.1007/s11356-012-0972-3. Epub 2012 May 31.
8
Peroxisome proliferator-activated receptor γ is a target for halogenated analogs of bisphenol A.过氧化物酶体增殖物激活受体 γ 是双酚 A 的卤代类似物的作用靶点。
Environ Health Perspect. 2011 Sep;119(9):1227-32. doi: 10.1289/ehp.1003328. Epub 2011 May 11.