Aqueous chlorination kinetics of some endocrine disruptors

被引:134
作者
Deborde, M
Rabouan, S
Gallard, H
Legube, B
机构
[1] CNRS, UMR 6008, Ecole Super Ingn Poitiers, Lab Chim Eau & Environm, F-86022 Poitiers, France
[2] Fac Med & Pharm, Chim Analyt Lab, F-86005 Poitiers, France
关键词
D O I
10.1021/es040006e
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
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 degreesC, 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 HOCl 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 HOCl 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.
引用
收藏
页码:5577 / 5583
页数:7
相关论文
共 33 条
  • [1] AFNOR, 1994, REC NORM FRANC ENV Q, P403
  • [2] BEHAVIOR OF ALKYLPHENOL POLYETHOXYLATE SURFACTANTS IN THE AQUATIC ENVIRONMENT .2. OCCURRENCE AND TRANSFORMATION IN RIVERS
    AHEL, M
    GIGER, W
    SCHAFFNER, C
    [J]. WATER RESEARCH, 1994, 28 (05) : 1143 - 1152
  • [3] Albert A., 1984, DETERMINATION IONIZA
  • [4] *ALPHA AWWA WEF, 1995, STAND METH EX WAT WA, P38
  • [5] Monitoring natural and synthetic estrogens at activated sludge sewage treatment plants and in a receiving river water
    Baronti, C
    Curini, R
    D'Ascenzo, G
    Di Corcia, A
    Gentili, A
    Samperi, R
    [J]. ENVIRONMENTAL SCIENCE & TECHNOLOGY, 2000, 34 (24) : 5059 - 5066
  • [6] Analysis and occurrence of estrogenic hormones and their glucuronides in surface water and waste water in The Netherlands
    Belfroid, AC
    Van der Horst, A
    Vethaak, AD
    Schäfer, AJ
    Rijs, GBJ
    Wegener, J
    Cofino, WP
    [J]. SCIENCE OF THE TOTAL ENVIRONMENT, 1999, 225 (1-2) : 101 - 108
  • [7] CONCENTRATIONS OF ALKYLPHENOLS IN RIVERS AND ESTUARIES IN ENGLAND AND WALES
    BLACKBURN, MA
    WALDOCK, MJ
    [J]. WATER RESEARCH, 1995, 29 (07) : 1623 - 1629
  • [8] Burttschell R. H., 1959, J AM WATER WORKS ASS, V51, P205, DOI 10.1002/j.1551-8833.1959.tb15722.x
  • [9] CLARKE EGC, 1986, CLARKS ISOLOATION ID
  • [10] *EUR COMM, 1996, EUR WORKSH IMP END D