Toxicological Center, University of Antwerp, Universiteitsplein 1, 2610 Wilrijk, Antwerp, Belgium; Environmental Pollution Control Laboratory, Aristotle University, 54124 Thessaloniki, Greece.
Toxicological Center, University of Antwerp, Universiteitsplein 1, 2610 Wilrijk, Antwerp, Belgium.
Chemosphere. 2018 Apr;196:231-239. doi: 10.1016/j.chemosphere.2017.12.132. Epub 2017 Dec 23.
Organophosphorus flame retardants (PFRs) and emerging PFRs (ePFRs) are two groups of compounds used as replacements for brominated flame retardants (BFRs). They have already been detected in indoor dust (mainly in homes and offices). To date, few studies investigated the occurrence of FRs in car dust and the information of possible health risks is still limited. The present study reports on the investigation of the levels and profiles of eight target PFRs: tris(2-ethylhexyl) phosphate (TEHP), tris(2-chloroethyl) phosphate (TCEP), tris(2-butoxyethyl) phosphate (TBEP), triphenyl phosphate (TPHP), 2-ethylhexyl diphenyl phosphate (EHDPHP), tris(1-chloro-2-propyl) phosphate (TCIPP), tri cresyl phosphate (TCP), tris(1,3-dichloro-2-propyl) phosphate (TDCIPP) and four target ePFRs; 2,2-bis(chloromethyl)propane-1,3-diyltetrakis(2-chloroethyl)bisphosphate (V6), isodecyl diphenyl phosphate (iDDPHP), resorcinol bis(diphenylphosphate) (RDP) and bisphenol A-bis(diphenyl phosphate) (BDP) in car dust from Greece. The samples were collected from the interior of 25 private cars in Thessaloniki, Greece, with different years of manufacture (1997-2015) and continents of origin. After ultrasonic extraction and Florisil fractionation, the PFR analysis was carried out by GC-EI/MS, whereas the ePFRs were analyzed by LC-MS/MS. Levels of ΣPFRs varied from 2000 to 190,000 ng g, with mean and median concentrations of 20,000 and 11,500 ng g, respectively. The concentrations of ΣePFRs ranged from 44 to 8700 ng g, with mean and median values at 1100 and 190 ng g, respectively. Estimations of human exposure showed that toddlers are more exposed than adults to both PFRs and ePFRs. Yet, the intake via dust ingestion and dermal absorption was several orders of magnitude lower than the corresponding reference doses.
有机磷阻燃剂(PFRs)和新兴的 PFRs(ePFRs)是两组用作溴化阻燃剂(BFRs)替代品的化合物。它们已经在室内灰尘(主要是家庭和办公室)中被检测到。迄今为止,很少有研究调查 FRs 在车内灰尘中的存在情况,并且有关可能的健康风险的信息仍然有限。本研究报告了对八种目标 PFRs 的水平和分布情况的调查:磷酸三(2-乙基己基)酯(TEHP)、磷酸三(2-氯乙基)酯(TCEP)、磷酸三(2-丁氧基乙基)酯(TBEP)、磷酸三苯酯(TPHP)、2-乙基己基二苯基磷酸酯(EHDPHP)、磷酸三(1-氯-2-丙基)酯(TCIPP)、磷酸三甲苯酯(TCP)、磷酸三(1,3-二氯-2-丙基)酯(TDCIPP)和四种目标 ePFRs:2,2-双(氯甲基)-1,3-丙二醇四(2-氯乙基)双磷酸酯(V6)、异癸基二苯基磷酸酯(iDDPHP)、双酚 A 双(二苯基磷酸酯)(BDP)。这些样品是从希腊塞萨洛尼基的 25 辆私家车的内部收集的,这些汽车的制造年份(1997-2015 年)和起源地不同。经过超声提取和 Florisil 分馏后,通过 GC-EI/MS 对 PFR 进行分析,而通过 LC-MS/MS 对 ePFRs 进行分析。ΣPFRs 的水平从 2000 到 190000ng/g 不等,平均浓度和中位数浓度分别为 20000 和 11500ng/g。ΣePFRs 的浓度范围从 44 到 8700ng/g,平均浓度和中位数浓度分别为 1100 和 190ng/g。对人体暴露的估计表明,幼儿比成年人更容易受到 PFRs 和 ePFRs 的影响。然而,通过灰尘摄入和皮肤吸收摄入的量要低几个数量级,远低于相应的参考剂量。