By-side impurities in chloronaphthalene mixtures of the Halowax series:: All 75 chlorodibenzo-p-dioxons

被引:20
作者
Noma, Y
Minetomatsu, K
Falandysz, J
Swietojanska, A
Flisak, M
Miyaji, K
Sakai, S
机构
[1] Natl Inst Environm Studies, Tsukuba, Ibaraki 3058506, Japan
[2] Univ Gdansk, Dept Environm Chem & Ecotoxicol, Gdansk, Poland
[3] Towa Kagaku Co Ltd, Hiroshima, Japan
来源
JOURNAL OF ENVIRONMENTAL SCIENCE AND HEALTH PART A-TOXIC/HAZARDOUS SUBSTANCES & ENVIRONMENTAL ENGINEERING | 2005年 / 40卷 / 01期
关键词
PCDFs; CDDs; PCDDs; polychlorinated dibenzo-p-dioxins; CNs; PCNs; polychlorinated naphthalenes; waste; hazardous chemicals; dioxinlike compounds; industrial chemicals; contamination; environmental pollution; POPs;
D O I
10.1081/ESE-200033581
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
A by-side chlorodibenzo-p-dioxins (CDDs) has been identified as impurity in concentration between 1.5 and 370 ng/g in the Halowax formulations of all type. Halowax 1014 was relatively richer in number of CDD congeners detected when compared to six other CN formulations examined. Amongst the mono- to tri-CDDs, the most prevalent in the Halowaxes were 1- and 2-MoCDD, and especially they were abundant in the formulations of a lower than a higher degree of chlorination. Amongst the tetra- to octaCDD only 1,2,3,4-/1,2,4,6-/1,2,4,9-/ 1,2,3,8-TeCDD, 1,2,3,4,6,7,8-HpCDD and OcCDD were found in all the Halowaxes, and 1,2,3,4,6,7,97H CDD remained undetected only in Halowax 1099 p and 1013, while most of TeCDDs, PeCDD, and HxCDDs were absent in a majority of the formulations examined. The compositional profile of 1,2,3,4-/1,2,4,6-/1,2,4,,-/1,2,3,8TeCDD and OcCDD congeners found in the Halowaxes seem to indicate, that after an initial in situ formation of mono- and di-CDDs during CNs synthesis, a further increase of reaction time, temperature, and pressure can lead to successive chlorination of the already established chlorodibenzo-p-dioxin molecule, and so to enrichment in 1,2,3,4-/ 1,2,4,6-/1,2,4,9,-/1,2,3,8-TeCDD but also OcCDD content for most of the final products obtained. Nevertheless, also due to the co-synthesis of chlorophenols in the Halowaxes, their condensation reactions could also contribute to the formation of CDDs. In term of dioxin-like toxicity the most potent due to CDDs content was Halowax 1014 with 0.95 ng TCDD TEQ/g, and between 0.00068,and 0.058 ng/g were for other formulations. A rough estimation made implies that a net CDDs production due to manufacture of the technical CNs in the XX century could reach an amount between 3.0 and 12.6 kg, while for most toxic dioxin-like constituents between 5.25 and 24 g TCDD TEQ, For the worst case scenario and involvement of Halowax 1014 only the net total CDDs production was estimated to be 1.5 kg, and for highly-toxic congeners 71 g TCDD TEQ. All these figures are much lower when compared to co-production of CDFs.
引用
收藏
页码:77 / 89
页数:13
相关论文
共 30 条
[1]   PROFILE AND PATTERN OF MONOCHLORODIBENZODIOXINS THROUGH OCTACHLORODIBENZODIOXINS AND OCTACHLORODIBENZOFURANS IN CHIMNEY DEPOSITS FROM WOOD BURNING [J].
BACHER, R ;
SWEREV, M ;
BALLSCHMITER, K .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 1992, 26 (08) :1649-1655
[2]   Brominated dioxin-like compounds: in vitro assessment in comparison to classical dioxin-like compounds and other polyaromatic compounds [J].
Behnisch, PA ;
Hosoe, K ;
Sakai, S .
ENVIRONMENT INTERNATIONAL, 2003, 29 (06) :861-877
[3]   Relative potencies of individual polychlorinated naphthalenes and halowax mixtures to induce Ah receptor-mediated responses [J].
Blankenship, AL ;
Kannan, K ;
Villalobos, SA ;
Villeneuve, DL ;
Falandysz, J ;
Imagawa, T ;
Jakobsson, E ;
Giesy, JP .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 2000, 34 (15) :3153-3158
[4]   DETERMINATION OF CHLORINATED DIBENZO-PARA-DIOXIN CONTAMINANTS IN 2,4-D PRODUCTS BY GAS CHROMATOGRAPHY-MASS SPECTROMETRIC TECHNIQUES [J].
COCHRANE, WP ;
SINGH, J ;
MILES, W ;
WAKEFORD, B .
JOURNAL OF CHROMATOGRAPHY, 1981, 217 (NOV) :289-299
[5]  
Crow K D, 1970, Trans St Johns Hosp Dermatol Soc, V56, P79
[6]   Computational prediction of 7-ethoxyresorufin-O-diethylase (EROD) and luciferase (luc) inducing potency for 75 congeners of chloronaphthalene [J].
Falandysz, J ;
Puzyn, T .
JOURNAL OF ENVIRONMENTAL SCIENCE AND HEALTH PART A-TOXIC/HAZARDOUS SUBSTANCES & ENVIRONMENTAL ENGINEERING, 2004, 39 (06) :1505-1523
[7]   Chloronaphthalenes as food-chain contaminants: a review [J].
Falandysz, J .
FOOD ADDITIVES AND CONTAMINANTS PART A-CHEMISTRY ANALYSIS CONTROL EXPOSURE & RISK ASSESSMENT, 2003, 20 (11) :995-1014
[8]   Composition of chloronaphthalene congeners in technical chloronaphthalene formulations of the Halowax series [J].
Falandysz, J ;
Kawano, M ;
Ueda, M ;
Matsuda, M ;
Kannan, K ;
Giesy, JP ;
Wakimoto, T .
JOURNAL OF ENVIRONMENTAL SCIENCE AND HEALTH PART A-TOXIC/HAZARDOUS SUBSTANCES & ENVIRONMENTAL ENGINEERING, 2000, 35 (03) :281-298
[9]   Polychlorinated naphthalenes: an environmental update [J].
Falandysz, J .
ENVIRONMENTAL POLLUTION, 1998, 101 (01) :77-90
[10]  
Falandysz J, 2001, POL J ENVIRON STUD, V10, P217