A novel approach to assess the health risk of aryl hydrocarbon receptor-bound contaminants via inhalation exposure using CYP1A1 expression as a biomarker

被引:0
|
作者
Zhong, Huixia [1 ,2 ]
Yu, Lili [3 ]
Lv, Xiaomei [4 ]
Yu, Yingxin [1 ,2 ]
Hu, Junjie [4 ]
机构
[1] Guangdong Univ Technol, Inst Environm Hlth & Pollut Control, Guangdong Hong Kong Macao Joint Lab Contaminants E, Guangdong Key Lab Environm Catalysis & Hlth Risk C, Guangzhou 510006, Guangdong, Peoples R China
[2] Guangdong Univ Technol, Sch Environm Sci & Engn, Guangzhou Key Lab Environm Catalysis & Pollut Cont, Key Lab City Cluster Environm Safety & Green Dev, Guangzhou 510006, Peoples R China
[3] Jinan Univ, Shenzhen Peoples Hosp, Clin Med Coll 2, Shenzhen 518020, Peoples R China
[4] Dongguan Univ Technol, Sch Environm & Civil Engn, Dongguan 523808, Peoples R China
基金
中国国家自然科学基金;
关键词
Dose-response curve; Gene expression; Toxic equivalence factor; Contributor; POLYCYCLIC AROMATIC-HYDROCARBONS; IN-VITRO; CYP1A INDUCTION; DIOXINS; POTENCIES; PAHS; TRANSACTIVATION; EXPRESSION; MECHANISM; BIOASSAY;
D O I
10.1016/j.ecoenv.2024.116466
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Polycyclic aromatic hydrocarbons (PAHs) and dioxins are potential causes of multiple diseases by activating the aryl hydrocarbon receptor (AhR) pathway. Health risk assessment of chemicals primarily relies on the relative potency factor (RPF), although its accuracy may be limited when solely using EC50 values. The induction of cytochrome P4501A1 (CYP1A1) serves as a biomarker for AhR activation and is an integrator of dioxin-like toxicity. Here, we present a method for evaluating the risks associated with AhR activation using mathematical models of dose-CYP1A1 induction. The dose-effect curves for certain PAHs and dioxins, including Ant, BghiP, 1,2,3,4,7,8-HxCDD, and others, exhibited a non-classical S-shaped form. The toxic equivalent factor (TEF) profiles revealed a broad range of toxic equivalent factor values. The TEFs for PAHs ranged from approximately 0.01 to 6, with higher values being observed when the concentration was less than 10-10 M, with the exceptions of Ace, Phe, and BghiP. Most congeners of dioxins got the lowest TEF value at around 10-10 M, ranging from 0.04 to 1.00. The binding affinity of AhR to ligands did not display a strong correlation with the EC50 of CYP1A1 expression, suggesting that the AhR-mediated effects of PAHs and dioxins are not fixed but instead fluctuate with the dose. Air samples acquired from a parking area were used to compare the proficiency of RPF and our current approach. In the current method, naphthalene and chrysene were the primary contributors of PAHs to AhRmediated risks in parking lots air samples, respectively. However, the contributions of naphthalene and chrysene could be disregarded in the RPF approach.
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页数:10
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