Urinary metabolites of organophosphate esters: Concentrations and age trends in Australian children

被引:109
作者
He, Chang [1 ]
Toms, Leisa-Maree L. [2 ]
Phong Thai [3 ]
Van den Eede, Nele [4 ]
Wang, Xianyu [1 ]
Li, Yan [1 ]
Baduel, Christine [1 ,5 ]
Harden, Fiona A. [6 ]
Heffernan, Amy L. [1 ,7 ]
Hobson, Peter [8 ]
Covaci, Adrian [4 ]
Mueller, Jochen F. [1 ]
机构
[1] Univ Queensland, QAEHS, 39 Kessels Rd, Brisbane, Qld 4108, Australia
[2] Queensland Univ Technol, Inst Hlth & Biomed Innovat, Sch Publ Hlth & Social Work, Brisbane, Qld 4000, Australia
[3] Queensland Univ Technol, Int Lab Air Qual & Hlth, Brisbane, Qld 4000, Australia
[4] Univ Antwerp, Toxicol Ctr, Univ Pl 1, B-2610 Antwerp, Belgium
[5] Univ Claude Bernard Lyon 1, ENS Lyon, Inst Sci Analyt, CNRS,UMR 5280, 5 Rue Doua, F-69100 Villeurbanne, France
[6] Hunter Ind Med, Newcastle, NSW, Australia
[7] Univ Melbourne, Florey Inst Neurosci & Mental Hlth, Melbourne, Vic 3000, Australia
[8] Sullivan Nicolaides Pathol, Brisbane, Qld, Australia
基金
澳大利亚研究理事会; 英国医学研究理事会;
关键词
Organophosphate flame retardants; Alternative flame retardants; Metabolites; Biomonitoring; Children; Exposure assessment; TANDEM MASS-SPECTROMETRY; PHOSPHORUS FLAME RETARDANTS; HUMAN LIVER-MICROSOMES; HUMAN EXPOSURE; INDOOR EXPOSURE; BREAST-MILK; PHOSPHATE; PLASTICIZERS; DUST; SERUM;
D O I
10.1016/j.envint.2017.11.019
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
There is growing concern around the use of organophosphate esters (OPEs) due to their suspected reproductive toxicity, carcinogenicity, and neurotoxicity. OPEs are used as flame retardants and plasticizers, and due to their extensive application in consumer products, are found globally in the indoor environment. Early life exposure to OPEs is an important risk factor for children's health, but poorly understood. To study age and sex trends of OPE exposures in infants and young children, we collected, pooled, and analysed urine samples from children aged 0-5 years from Queensland, Australia for 9 parent OPEs and 11 metabolites. Individual urine samples (n = 400) were stratified by age and sex, and combined into 20 pools. Three individual breast milk samples were also analysed to provide a preliminary estimate on the contribution of breast milk to the intake of OPEs. Bis(1-chloroisopropyl) phosphate (BCIPP), 1-hydroxy-2-propyl bis(1-chloro-2-propyl) phosphate (BCIPHIPP), bis(1,3-dichloroisopropyl) phosphate (BDCIPP), dibutyl phosphate (DBP), diphenyl phosphate (DPHP), bis(2-butoxyethyl) phosphate (BBOEP), bis(2-butoxyethyl) 3-hydroxyl-2-butoxyethyl phosphate (3OH-TBOEP), and bis(2-butoxyethyl) hydroxyethyl phosphate (BBOEHEP) were detected in all urine samples, followed by bis(methylphenyl) phosphate (80%), and bis(2-ethylhexyl) phosphate (BEHP, 20%), and bis(2-chloroethyl) phosphate (BCEP, 15%). Concentrations of tris(2-chloroethyl) phosphate (TCEP), BCEP, tris(2-ethylhexyl) phosphate (TEHP), and DBP decreased with age, while bis(methylphenyl) phosphate (BMPP) increased with age. Significantly higher concentrations of DPHP (p = 0.039), and significantly lower concentrations of TEHP (p = 0.006) were found in female samples compared to males. The estimated daily intakes (EDIs) via breast-feeding, were 4.6, 26 and 76 ng/kg/day for TCEP, TBP and TEHP, respectively, and were higher than that via air and dust, suggesting higher exposure through consumption of breast milk.
引用
收藏
页码:124 / 130
页数:7
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