4种新污染物对5种不同细胞的联合毒性研究
Joint Toxicity of Four Emerging Pollutants on Five Different Types of Cells
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摘要: 随着人类社会的发展,新污染物的种类逐渐增多。目前新污染物的毒性研究主要集中于单一毒性的评价,由于人类可能通过各种途径暴露于新污染物的混合物,因此评估新污染物混合物对人类健康的潜在风险越来越受到关注。本研究采用5种常见的体外毒性研究细胞模型——人正常肝细胞L02、小鼠正常肝细胞AML12、人肾小管上皮细胞HK2、大鼠胶质瘤细胞C6、小鼠海马神经元细胞HT22,测定不同浓度炔雌醇(ethinyl estradiol, EE2)、双酚A(bisphenol A, BPA)、邻苯二甲酸二丁酯(dibutyl phthalate, DBP)、全氟辛酸(perfluorooctanoic acid, PFOA)对5种细胞的相对生长抑制率,分别计算污染物在不同生长抑制率下的效应浓度(F%-maximum effective concentration, ECF,其中F=10、20、25、33、50)。按照EC50∶EC50 (半数效应浓度)、EC33∶EC33∶EC33 (生长抑制率为33%下的效应浓度)、EC25∶EC25∶EC25∶EC25 (生长抑制率为25%下的效应浓度)的比例分别进行二元、三元、四元等毒性比例混合,以1/2为稀释因子进行浓度梯度处理,计算抑制率并拟合实际作用曲线,采用浓度加和(concentration addition, CA)模型和独立作用(independent action, IA)模型预测不同污染物之间的联合效应。4种污染物对5种细胞的生长抑制均存在剂量-效应关系。暴露48 h后,在所有细胞中EE2的毒性最大,PFOA的毒性最小,HK2细胞对4种污染物的敏感性最弱。在二元组合中,EE2与BPA的混合物在2种神经细胞C6与HT22上都存在明显的协同作用。随着混合物的组分增加,三元和四元混合物更易产生相加与拮抗作用。4种污染物对所有的受试细胞都具有一定的毒性,其联合效应会随着组分及浓度等的变化而不同。Abstract: The development of society has led to an increase in the types of new pollutants. With the development of society, the types of new pollutants are gradually increasing. Currently, the toxicity studies on new pollutants mainly focuses on the evaluation of a single toxicity. However, as humans may be exposed to mixtures of new pollutants through various routes, the assessment of the potential risks of these mixtures to human health has received increasing attention. This study used L02, AML12, HK2, C6, and HT22 cells as models to measure the growth inhibition rates of five types of cells under different concentrations of ethinyl estradiol (EE2), bisphenol A (BPA), dibutyl phthalate (DBP), and perfluorooctanoic acid (PFOA). The effective concentrations (ECF, where F = 10, 20, 25, 33, 50) of emerging pollutants at different growth inhibition rates were calculated. Binary, ternary, and quaternary mixtures of emerging pollutants were designed according to the ratios of EC50∶EC50, EC33∶EC33∶EC33, and EC25∶EC25∶EC25∶EC25, and then diluted with a dilution ratio of 1/2. The inhibition rates were calculated, and the actual action curves were fitted. The concentration addition model (CA) and the independent action model (IA) were used to evaluate the combined effects of the different emerging pollutants. There was a dose-effect relationship between the four kinds types of emerging pollutants on the growth inhibition of the 5 types of cells. After 48 hours of exposure, EE2 showed the highest toxicity, while PFOA showed the least toxicity in all types of cells. HK2 showed the weakest sensitivity to the four types of emerging pollutants. In binary combinations, EE2+BPA showed significant synergistic inhibition on C6 and HT22. As the number of components increased, ternary and quaternary mixtures were more likely to exhibit additive and antagonistic effects. The four types of emerging pollutants were toxic to all tested cells, and the combined toxic effects varied with the changes in components and concentrations.
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Zhang M, Sun Y, Xun B, et al. Analysis of the spatial distribution characteristics of emerging pollutants in China[J]. Water, 2023, 15(21): 3782 La Merrill M A, Vandenberg L N, Smith M T, et al. Consensus on the key characteristics of endocrine-disrupting chemicals as a basis for hazard identification[J]. Nature Reviews Endocrinology, 2020, 16(1): 45-57 Liu J L, Wong M H. Pharmaceuticals and personal care products (PPCPs): A review on environmental contamination in China[J]. Environment International, 2013, 59: 208-224 Snyder S A, Westerhoff P, Yoon Y, et al. Pharmaceuticals, personal care products, and endocrine disruptors in water: Implications for the water industry[J]. Environmental Engineering Science, 2003, 20(5): 449-469 Liu Z H, Kanjo Y, Mizutani S. Removal mechanisms for endocrine disrupting compounds (EDCs) in wastewater treatment—Physical means, biodegradation, and chemical advanced oxidation: A review[J]. Science of the Total Environment, 2009, 407(2): 731-748 Campbell C G, Borglin S E, Green F B, et al. Biologically directed environmental monitoring, fate, and transport of estrogenic endocrine disrupting compounds in water: A review[J]. Chemosphere, 2006, 65(8): 1265-1280 Rudel R A, Camann D E, Spengler J D, et al. Phthalates, alkylphenols, pesticides, polybrominated diphenyl ethers, and other endocrine-disrupting compounds in indoor air and dust[J]. Environmental Science & Technology, 2003, 37(20): 4543-4553 Diamanti-Kandarakis E, Bourguignon J P, Giudice L C, et al. Endocrine-disrupting chemicals: An Endocrine Society scientific statement[J]. Endocrine Reviews, 2009, 30(4): 293-342 龚剑, 冉勇, 陈迪云, 等. 珠江三角洲两条主要河流沉积物中的典型内分泌干扰物污染状况[J]. 生态环境学报, 2011, 20(6): 1111-1116 Gong J, Ran Y, Chen D Y, et al. Contamination of typical endocrine-disrupting chemicals in the sediment of two main rivers from the Pearl River Delta[J]. Ecology and Environmental Sciences, 2011, 20(6): 1111-1116(in Chinese)
马晓雁, 高乃云, 李青松, 等. 黄浦江原水及水处理过程中内分泌干扰物状况调查[J]. 中国给水排水, 2006, 22(19): 1-4 Ma X Y, Gao N Y, Li Q S, et al. Investigation of several endocrine disrupting chemicals in Huangpu River and water treatment units of a waterworks[J]. China Water & Wastewater, 2006, 22(19): 1-4(in Chinese)
邵晓玲, 马军. 松花江水中13种内分泌干扰物的初步调查[J]. 环境科学学报, 2008, 28(9): 1910-1915 Shao X L, Ma J. Preliminary investigation on 13 endocrine disrupting chemicals in the Songhua River[J]. Acta Scientiae Circumstantiae, 2008, 28(9): 1910-1915(in Chinese)
Yoon Y, Ryu J, Oh J, et al. Occurrence of endocrine disrupting compounds, pharmaceuticals, and personal care products in the Han River (Seoul, South Korea)[J]. Science of the Total Environment, 2010, 408(3): 636-643 Cargouët M, Perdiz D, Mouatassim-Souali A, et al. Assessment of river contamination by estrogenic compounds in Paris area (France)[J]. Science of the Total Environment, 2004, 324(1/2/3): 55-66 Sharma B M, Bharat G K, Chakraborty P, et al. A comprehensive assessment of endocrine-disrupting chemicals in an Indian food basket: Levels, dietary intakes, and comparison with European data[J]. Environmental Pollution, 2021, 288: 117750 Ibor O R, Nnadozie P, Ogarekpe D M, et al. Public health implications of endocrine disrupting chemicals in drinking water and aquatic food resources inNigeria: A state-of-the-science review[J]. Science of the Total Environment, 2023, 858(Pt 2): 159835 Mohamad Haron D E, Yoneda M, Ahmad E D, et al. PFAS, bisphenol, and paraben in Malaysian food and estimated dietary intake[J]. Food Additives & Contaminants Part B, Surveillance, 2023, 16(2): 161-175 Ribeiro E, Ladeira C, Viegas S. EDCs mixtures: A stealthy hazard for human health?[J]. Toxics, 2017, 5(1): 5 Valbonesi P, Profita M, Vasumini I, et al. Contaminants of emerging concern in drinking water: Quality assessment by combining chemical and biological analysis[J]. Science of the Total Environment, 2021, 758: 143624 Hartmann C, Jamnik T, Weiss S, et al. Results of the Austrian children’s biomonitoring survey 2020 part A: Per- and polyfluorinated alkylated substances, bisphenols, parabens and other xenobiotics[J]. International Journal of Hygiene and Environmental Health, 2023, 249: 114123 Velázquez-Gómez M, Lacorte S. Organic pollutants in indoor dust from Ecuadorian Amazonia areas affected by oil extractivism[J]. Environmental Research, 2020, 186: 109499 Balabanič D, Filipič M, Krivograd Klemenčič A, et al. Genotoxic activity of endocrine disrupting compounds commonly present in paper mill effluents[J]. Science of the Total Environment, 2021, 794: 148489 López-Velázquez K, Guzmán-Mar J L, Saldarriaga-Noreña H A, et al. Ecological risk assessment associated with five endocrine-disrupting compounds in wastewater treatment plants of NortheastMexico[J]. Environmental Science and Pollution Research International, 2023, 30(11): 30714-30726 Bérubé R, LeFauve M K, Heldman S, et al. Adipogenic and endocrine disrupting mixture effects of organic and inorganic pollutant mixtures[J]. Science of the Total Environment, 2023, 876: 162587 Wan H T, Leung P Y, Zhao Y G, et al. Blood plasma concentrations of endocrine disrupting chemicals in Hong Kong populations[J]. Journal of Hazardous Materials, 2013, 261(20): 763-769 Di Credico A, Gaggi G, Bucci I, et al. The effects of combined exposure to bisphenols and perfluoroalkyls on human perinatal stem cells and the potential implications for health outcomes[J]. International Journal of Molecular Sciences, 2023, 24(19): 15018 Manikkam M, Tracey R, Guerrero-Bosagna C, et al. Plastics derived endocrine disruptors (BPA, DEHP and DBP) induce epigenetic transgenerational inheritance of obesity, reproductive disease and sperm epimutations[J]. PLoS One, 2013, 8(1): e55387 Altenburger R, Nendza M, Schüürmann G. Mixture toxicity and its modeling by quantitative structure-activity relationships[J]. Environmental Toxicology and Chemistry, 2003, 22(8): 1900-1915 Gore A C, Chappell V A, Fenton S E, et al. EDC-2: The endocrine society’s second scientific statement on endocrine-disrupting chemicals[J]. Endocrine Reviews, 2015, 36(6): E1-E150 Padhye L P, Yao H, Kung’u F T, et al. Year-long evaluation on the occurrence and fate of pharmaceuticals, personal care products, and endocrine disrupting chemicals in an urban drinking water treatment plant[J]. Water Research, 2014, 51: 266-276 Guo Y, Kannan K. A survey of phthalates and parabens in personal care products from the United States and its implications for human exposure[J]. Environmental Science & Technology, 2013, 47(24): 14442-14449 Kannan K, Corsolini S, Falandysz J, et al. Perfluorooctanesulfonate and related fluorochemicals in human blood from several countries[J]. Environmental Science & Technology, 2004, 38(17): 4489-4495 Ryan B C, Hotchkiss A K, Crofton K M, et al. In utero and lactational exposure to bisphenol A, in contrast to ethinyl estradiol, does not alter sexually dimorphic behavior, puberty, fertility, and anatomy of female LE rats[J]. Toxicological Sciences, 2010, 114(1): 133-148 Yamamoto Y, Moore R, Hess H A, et al. Estrogen receptor alpha mediates 17alpha-ethynylestradiol causing hepatotoxicity[J]. Journal of Biological Chemistry, 2006, 281(24): 16625-16631 Arambula S E, Jima D, Patisaul H B. Prenatal bisphenol A (BPA) exposure alters the transcriptome of the neonate rat amygdala in a sex-specific manner: A CLARITY-BPA consortium study[J]. NeuroToxicology, 2018, 65: 207-220 Hu X Z, Hu D C. Effects of perfluorooctanoate and perfluorooctane sulfonate exposure on hepatoma Hep G2 cells[J]. Archives of Toxicology, 2009, 83(9): 851-861 Li K, Gao P, Xiang P, et al. Molecular mechanisms of PFOA-induced toxicity in animals and humans: Implications for health risks[J]. Environment International, 2017, 99: 43-54 刘树深, 刘玲, 陈浮. 浓度加和模型在化学混合物毒性评估中的应用[J]. 化学学报, 2013, 71(10): 1335-1340 Liu S S, Liu L, Chen F. Application of the concentration addition model in the assessment of chemical mixture toxicity[J]. Acta Chimica Sinica, 2013, 71(10): 1335-1340(in Chinese)
Caporale N, Leemans M, Birgersson L, et al. From cohorts to molecules: Adverse impacts of endocrine disrupting mixtures[J]. Science, 2022, 375(6582): eabe8244 Acconcia F, Pallottini V, Marino M. Molecular mechanisms of action of BPA[J]. Dose-response, 2015, 13(4): 332-341 Sonavane M, Gassman N R. Bisphenol A co-exposure effects: A key factor in understanding BPA’s complex mechanism and health outcomes[J]. Critical Reviews in Toxicology, 2019, 49(5): 371-386 Rahman M S, Pang W K, Amjad S, et al. Hepatic consequences of a mixture of endocrine-disrupting chemicals in male mice[J]. Journal of Hazardous Materials, 2022, 436: 129236 Lin Z W, Will Y. Evaluation of drugs with specific organ toxicities in organ-specific cell lines[J]. Toxicological Sciences, 2012, 126(1): 114-127 -

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