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颗粒物中苯并噻唑及其衍生物的污染特征及暴露评价
Pollution characteristics and exposure assessment of benzothiazole and its derivatives in ambient air particulates
在城市内选取包括城市背景空气、市区以小型客车为主的路边和大量大型货车通行的3个路边采样点进行了空气中PM2.5和PM10的采集,建立了利用超高效液相色谱串联三重四级杆质谱仪(UPLC-MS/MS)对颗粒物中苯并噻唑及其5种衍生物(BT、2-NH2-BT、2-OH-BT、MBT、MTBT)的检测方法,并对其污染特征及暴露风险进行了分析.结果显示,3点位PM2.5和PM10样品中均为BT的浓度最高,占总浓度的44.4%~55.2%;各化合物浓度呈路边环境高于城市背景环境,表明高制动频率导致路边空气中含有较多的轮胎磨损颗粒物;除2-NH2-BT外,其它4种BTs化合物与PM2.5和PM10的浓度之间具有较好的线性关系,表明二者具有相同的来源;各化合物在PM2.5和PM10中浓度的比值(PM2.5/PM10)范围为0.41~0.95,说明BTs更易于富集在较细颗粒物中或轮胎磨损排放的细颗粒较多.暴露评价结果显示,路边工作者对BTs的日呼吸暴露量大于其他人,可能具有更高的健康风险其中BT的贡献量最大.
A sampling program was conducted to determine the levels of benzothiazole and its five derivatives (BTs, including BT、2-NH2-BT、2-OH-BT、MBT、MTBT) in PM2.5 and PM10 using UPLC-triple quadrupole MS. Three sampling points located at urban background and roadsides were selected. Pollution characteristics and exposure risks of target compounds were evaluated. The concentration of BT in PM2.5 and PM10 samples was the highest at all three points, accounting for 44.4%~55.2% of the total concentration. Concentration of BTs tended to be the highest at the roadside with high braking frequency, indicating that high braking frequency resulted in more tire wear particles in roadside air. There were good linear relationships between the concentration of BTs (except 2-NH2-BT) in PM2.5 and PM10, which indicates that PM2.5 and PM10 of roadside air have the same source. The ratio of the concentration of BTs in PM2.5 and PM10(PM2.5/PM10) ranged from 0.41 to 0.95, indicating that BTs are more easily concentrated in fine particles or fine particles are the main fraction of tire wear emission. The results of exposure assessment showed that the daily inhalation exposure dose of roadside workers to BTs was greater than other people, which may cause a higher health risk. BT contributed the most to inhalation exposure dose among five compounds.
PM2.5和PM10 / 暴露风险 / 苯并噻唑及其衍生物 / 路边环境 / 轮胎磨损
benzothiazole and its derivatives / exposure assessment / PM2.5 and PM10 / roadside environment / tire wear
[1] Amato F, Cassee F R, Denier van der Gon, et al. Urban air quality:The challenge of traffic non-exhaust emissions[J]. Journal of Hazardous Materials, 2014,275:31-36.
[2] Pant P, Harrison R M. Estimation of the contribution of road traffic emissions to particulate matter concentrations from field measurements:A review[J]. Atmospheric Environment, 2013,77(7):78-97.
[3] Keuken M, Gon H D V D, Valk K V D. Non-exhaust emissions of PM and the efficiency of emission reduction by road sweeping and washing in the Netherlands[J]. Science of the Total Environment, 2010,408(20):4591-4599.
[4] Kwak J H, Kim H, Lee J, et al. Characterization of non-exhaust coarse and fine particles from on-road driving and laboratory measurements[J]. Science of The Total Environment, 2013,458-460:273-282.
[5] Thorpe A, Harrison R M. Sources and properties of non-exhaust particulate matter from road traffic:A review[J]. Science of the Total Environment, 2008,400(1-3):270-282.
[6] Avagyan R, Sadiktsis I, Bergvall C, et al. Tire tread wear particles in ambient air-a previously unknown source of human exposure to the biocide 2-mercaptobenzothiazole[J]. Environmental Science and Pollution Research, 2014,21(19):11580-11586.
[7] Herrero P, Borrull F, Pocurull E, et al. An overview of analytical methods and occurrence of benzotriazoles, benzothiazoles and benzenesulfonamides in the environment[J]. TrAC Trends in Analytical Chemistry, 2014,62:46-55.
[8] Sadiktsis I, Bergvall C, Johansson C, et al. Automobile tires-A potential source of highly carcinogenic dibenzopyrenes to the environment[J]. Environmental Science & Technology, 2012,46(6):3326-3334.
[9] Fishbein L. Municipal and industrial hazardous waste management:an overview[J]. Toxicology and Industrial Health, 1991,7(5/6):209-220.
[10] Ginsberg G, Toal B, Kurland T. Benzothiazole toxicity assessment in support of synthetic turf field human health risk assessment[J]. Journal of Toxicology and Environmental Health, Part A, 2011,74(17):1175-1183.
[11] Sorahan, T. Cancer risks in chemical production workers exposed to 2-mercaptobenzothiazole[J]. Occupational and Environmental Medicine, 2008,66(4):269-273.
[12] Wang L, Zhang J, Sun H, et al. Widespread occurrence of benzotriazoles and benzothiazoles in tap water:Influencing factors and contribution to human exposure[J]. Environmental Science & Technology, 2016,50(5):2709-2717.
[13] Stasinakis A S, Thomaidis N S, Arvaniti O S, et al. Contribution of primary and secondary treatment on the removal of benzothiazoles, benzotriazoles, endocrine disruptors, pharmaceuticals and perfluorinated compounds in a sewage treatment plant[J]. Science of The Total Environment, 2013,463-464:1067-1075.
[14] Reddy C M, Quinn J G. Environmental chemistry of benzothiazoles derived from rubber[J]. Environmental Science & Technology, 1997, 31(10):2847-2853.
[15] Zhang J, Zhang X, Wu L, et al. Occurrence of benzothiazole and its derivates in tire wear, road dust, and roadside soil, Chemosphere, 2018,201:310-317.
[16] Wan Y, Xue J, Kannan K. Benzothiazoles in indoor air from Albany, New York, USA, and its implications for inhalation exposure[J]. Journal of Hazardous Materials, 2016,311:37-42.
[17] Wang L, Asimakopoulos A G, Moon H B, et al. Benzotriazole, benzothiazole, and benzophenone compounds in indoor dust from the United States and East Asian countries[J]. Environmental Science & Technology, 2013,47(9):4752-4759.
[18] García Gómez Diego, Bregy L, Nussbaumer Ochsner Y, et al. Detection and quantification of benzothiazoles in exhaled breath and exhaled breath condensate by real-time secondary electrospray ionization-high-resolution mass spectrometry and ultra-high performance liquid chromatography[J]. Environmental Science & Technology, 2015,49:12519-12524.
[19] Asimakopoulos A G, Wang L, Thomaidis N S, et al. Benzotriazoles and benzothiazoles in human urine from several countries:A perspective on occurrence, biotransformation, and human exposure[J] Environ. Int., 2013,59:274-281.
[20] Asimakopoulos A G, Wang L, Thomaidis N S, et al. Benzotriazoles and benzothiazoles in human urine from several countries:A perspective on occurrence, biotransformation, and human exposure[J]. Environment International, 2013,59:274-281.
[21] Liao C, Liu F, Guo Y, et al. Occurrence of eight bisphenol analogues in indoor dust from the United States and several Asian countries:Implications for human exposure[J]. Environmental Science & Technology, 2012,46(16):9138-9145.
[22] Ji Y, Wang F, Zhang L, et al. A comprehensive assessment of human exposure to phthalates from environmental media and food in Tianjin, China[J]. Journal of Hazardous Materials, 2014,279:133-140.
[23] Den B R V. Human exposure to soil contamination:a qualitative and quantitative analysis towards proposals for human toxicological intervention values (partly revised edition)[Z]. Rijksinstituut Voor Volksgezondheid En Milieu Rivm, 2007.
[24] Zheng N, Liu J, Wang Q, et al. Health risk assessment of heavy metal exposure to street dust in the zinc smelting district, Northeast of China[J]. Science of the Total Environment, 2010,408(4):726-733.
[25] United States Environmental Protection Agency. Human health evaluation manual (Part D, standardized planning, reporting, and review of superfund reporting and review of superfund risk assessments)[Z]. 2001.
[26] Man Y B, Sun X L, Zhao Y G, et al. Health risk assessment of abandoned agricultural soils based on heavy metal contents in Hong Kong, the world's most populated city[J]. Environment International, 2010,36(6):0-576.
国家重点研发计划(2016YFC0208200)
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