网站首页期刊介绍通知公告编 委 会投稿须知电子期刊广告合作联系我们
最新消息:
2019—2023年唐山市大气PM2.5中多环芳烃特征及健康风险评价
作者:周君  周婉笛  郑一诺  郭慧敏  张志坤 
单位:唐山市疾病预防控制中心 环境卫生监测与评价所, 河北 唐山 063000
关键词:大气污染物 多环芳烃 源分析 健康风险评价 
分类号:R122
出版年·卷·期(页码):2026·54·第一期(16-25)
摘要:

目的:分析唐山市大气PM2.5中16种多环芳烃(PAHs)的污染水平、季节分布与来源特征,并评估其对人群的潜在健康风险。方法:于2019—2023年在唐山市两个代表性区域连续采集PM2.5样品866份,采用高效液相色谱法测定16种PAHs的质量浓度。综合运用特征比值法与主成分分析法解析污染来源,并评估其经吸入途径的致癌与慢性非致癌风险。结果:2019—2023年唐山市PAHs总浓度呈显著下降趋势(P<0.001),年均浓度依次为12.64、4.51、2.24、3.09、2.14 ng·m-3。同时,PAHs总浓度具有显著的季节性特征,呈现冬季高、夏季低的“U”型分布规律(P<0.05)。16种PAHs质量浓度在不同地区比较,差异无统计学意义(P>0.05),且其组分构成基本一致。PAHs组成以4~6环为主,其中冬季6环组分所占比例显著升高。主成分分析提取出1个主成分,能解释总方差的82.80%,该主成分主要是菲(Phe)、荧蒽(Flu)、芘(Pyr)、(Chr)、苯并[a]蒽(BaA)、苯并[b]荧蒽(BbF)、苯并[a]芘(BaP)、二苯并[a,h]蒽(DahA)、苯并[ghi]苝(BghiP)及茚并[1,2,3-cd]芘(IcdP)。在慢性非致癌风险评估中,BaP危害商(HQ)在2019、2020年均大于1,冬季风险尤为突出(HQ =2.049)。在致癌风险评估中,BaP和BghiP 5年年均浓度对2~16岁及>16岁的人群超额致癌风险和终生致癌风险均高于1×10-6,且风险同样呈现冬季高,夏季低的季节特征。从年龄分层来看,致癌风险表现为成年人最高,其次为青少年,儿童最低。结论:2019—2023年唐山市PM2.5中的PAHs浓度呈现逐年下降的趋势,但其冬季健康风险仍不可忽视,污染来源以化石燃料燃烧、燃煤及机动车排放为主。建议相关部门重点加强冬季工业与移动源管控,并针对成年人及户外作业人群实施健康防护干预。

Objective: To analyze the pollution levels, seasonal distribution and source characteristics of 16 polycyclic aromatic hydrocarbons(PAHs) in atmospheric PM2.5 of Tangshan City, and to assess their potential health risks to the population. Methods: A total of 866 PM2.5 samples were continuously collected from two representative areas in Tangshan City during 2019—2023. The mass concentrations of 16 PAHs were determined by high-performance liquid chromatography. Diagnostic ratio analysis and principal component analysis were comprehensively applied to identify the pollution sources, and the inhalation-based carcinogenic and non-carcinogenic risks were evaluated. Results: The total PAHs concentration in Tangshan City showed a significant downward trend from 2019 to 2023(P<0.001), with the annual average concentrations being 12.64, 4.51, 2.24, 3.09, and 2.14 ng·m-3 in sequence. Meanwhile, the total PAHs concentration exhibited obvious seasonal characteristics, presenting a “U-shaped” distribution pattern with higher levels in winter and lower levels in summer(P<0.05). No statistically significant difference was observed in the mass concentrations of 16 PAHs between different areas(P>0.05), and their component compositions were basically consistent. PAHs were dominated by 4-to 6-ring congeners, among which the proportion of 6-ring components increased significantly in winter. PCA extracted one principal component that explained 82.80% of the total variance; this component mainly consisted of phenanthrene(Phe), fluoranthene(Flu), pyrene(Pyr), chrysene(Chr), benzo[a]anthracene(BaA), benzo[b]fluoranthene(BbF), benzo[a]pyrene(BaP), dibenzo[a,h]anthracene(DahA), benzo[ghi]perylene(BghiP) and indeno[1,2,3-cd]pyrene(IcdP). In the non-carcinogenic risk assessment, the hazard quotient(HQ) of BaP was greater than 1 in both 2019 and 2020, with the risk being particularly prominent in winter(HQ=2.049). In the carcinogenic risk assessment, the 5-year average concentrations of BaP and BghiP resulted in excess carcinogenic risk and lifetime carcinogenic risk higher than 1×10-6 for populations aged 2-16 years and over 16 years, and the risks also showed seasonal characteristics of higher levels in winter and lower levels in summer. In terms of age stratification, the carcinogenic risk was the highest in adults, followed by adolescents and then children. Conclusion: The PAHs concentration in PM2.5 of Tangshan City decreased year by year from 2019 to 2023, but the health risks in winter cannot be ignored. The pollution sources are mainly fossil fuel combustion, coal burning and motor vehicle emissions. It is suggested that the relevant authorities should focus on strengthening the control of industrial and mobile sources in winter, and implement health protection interventions for adults and outdoor workers.

参考文献:

[1] LI T,ZHANG Y,JIANG N,et al.Ambient fine particulate matter and cardiopulmonary health risks in China[J].Chin Med J,2023,136(3):287-294.
[2] 热孜亚木,丁丽,杨浩峰,等.乌鲁木齐部分区域大气PM2.5中多环芳烃污染特征及健康风险评估[J].环境与健康杂志,2024,41(10):852-857.
[3] 王敏,邢燕,高慧,等.2018年淄博市某城区大气PM2.5中多环芳烃的源解析及健康风险评估[J].预防医学论坛,2021,27(6):437-439,444.
[4] 程强,亢润润,张海蕾,等.2017—2022年台州市某城区空气PM2.5中重金属和多环芳烃分布特征及来源分析[J].环境与职业医学,2024,41(10):1144-1150.
[5] 时巧梅,解晔,李秋梅,等.2020—2022年扬州市二氧化氮对居民冠心病发病的急性效应研究[J].东南大学学报(医学版),2025,44(3):395-403.
[6] 沈登辉,唐剑,张汉杰,等.2020—2021年芜湖市主城区大气PM2.5中多环芳烃污染特征及健康风险评估[J].现代预防医学,2021,48(23):4252-4255,4316.
[7] 李文静,张美云,万博宇,等.北京市朝阳区大气PM2.5中多环芳烃的污染特征及健康风险评估[J].职业与健康,2021,37(16):2235-2238,2242.
[8] 李盛,王金玉,李普,等.兰州市某工业区大气PM2.5中多环芳烃污染特征及健康风险评估[J].环境与职业医学,2021,38(2):137-141.
[9] 杜美锦.新污染物暴露下环境与人体健康风险评估及其调控策略[D].北京:华北电力大学,2024.
[10] HO M S,LIN M Y,WANG J D,et al.An integrated approach to characterize temporal-spatial variations in PM2.5 concentrations at the ground level and its implication on health impact assessments[J].Front Environ Sci,2022,10:901754.
[11] 中华人民共和国环境保护部.环境空气和废气 气相和颗粒物中多环芳烃的测定 高效液相色谱法:HJ 647—2013[S].北京:中国环境科学出版社,2013.
[12] 吴和岩,任亮,张艳,等.珠海市2022年大气PM2.5中多环芳烃污染特征及人群健康风险评估[J].华南预防医学,2024,50(12):1094-1098,1103.
[13] 程永兵,刘思岑,刘志朝,等.2020—2022年西安市两城区大气PM2.5中16种多环芳烃污染特征及健康风险分析评估[J].公共卫生与预防医学,2025,36(5):23-27.
[14] 易仁玲,陈志永,王珂,等.常州市武进区大气PM2.5中多环芳烃的污染特征及健康风险评估[J].现代医学,2024,52(9):1412-1419.
[15] 中华人民共和国国家卫生健康委员会.大气污染人群健康风险评估技术规范(WS/T 666-2019)[S].北京:中国标准出版社,2019.
[16] 李欢,杨升美,高昇,等.2021年呼和浩特市大气PM2.5中多环芳烃污染特征及健康风险评价[J].实用预防医学,2024,31(6):650-656.
[17] 周慧霞,崔宝荣,潘颖,等.北京市丰台区大气PM2.5中多环芳烃污染特征及来源分析[J].环境卫生学杂志,2024,14(12):987-994.
[18] KO J H,WANG J,XU Q.Impact of pyrolysis conditions on polycyclic aromatic hydrocarbons(PAHs) formation in particulate matter(PM) during sewage sludge pyrolysis[J].Chemosphere,2018,208:108-116.
[19] 王英锋,张姗姗,李杏茹,等.北京大气颗粒物中多环芳烃浓度季节变化及来源分析[J].环境化学,2010,29(3):369-375.
[20] DEABJI N,FOMBA K W,DOS SANTOS SOUZA E J,et al.Influence of anthropogenic activities on metals,sugars and PAHs in PM10 in the city of Fez,Morocco:implications on air quality[J].Environ Sci Pollut Res,2024,31(17):25238-25257.
[21] VISHWAKARMA P,RAJEEV P,RABHA S,et al.Wintertime trends of particulate-bound polycyclic aromatic hydrocarbons(PAHs) at north-east site of India:chemical characterization and source identification[J].J Atmos Chem,2023,80(4):251-269.
[22] HONG W J,DONG W J,ZHAO T T,et al.Ambient PM2.5-bound polycyclic aromatic hydrocarbons in Ningbo Harbor,Eastern China:seasonal variation,source apportionment,and cancer risk assessment[J].Air Qual Atmos Health,2023,16(9):1809-1821.
[23] 张艳秋,于光,王伟,等.2019—2021年泰州市某区大气PM2.5中多环芳烃源解析及健康风险评估[J].环境与职业医学,2024,41(1):54-61.
[24] CHEN Y,GE C,LIU Z,et al.Characteristics,sources and health risk assessment of trace metals and polycyclic aromatic hydrocarbons in PM2.5 from Hefei,China[J].Environ Geochem Health,2023,45(11):7651-7663.
[25] 束文涛,张婷,李晔,等.2016—2021年江苏省扬州市PM2.5中多环芳烃的来源解析及健康风险评价[J].环境化学,2024,43(8):2781-2791.
[26] 赵敏娴,刘强,王瑛,等.2018—2021年苏州市大气PM2.5中多环芳烃污染特征及健康风险评估[J].中国预防医学杂志,2024,25(10):1289-1293.
[27] 牛计伟,李晓恒,季佳佳,等.2016—2022年珠三角地区PM2.5中多环芳烃污染特征及健康风险[J].环境卫生学杂志,2024,14(5):431-437,447.

服务与反馈:
文章下载】【发表评论】【查看评论】【加入收藏
提示:您还未登录,请登录!点此登录
您是第 1079351 位访问者


 ©《现代医学》编辑部
联系电话:025-83272481;83272479
电子邮件: xdyx@pub.seu.edu.cn

本系统由北京博渊星辰网络科技有限公司设计开发 技术支持电话:010-63361626

苏ICP备09058541