Uchiyama Shigehisa, Noguchi Mayumi, Hishiki Mayu, Shimizu Moka, Kunugita Naoki, Isobe Tomohiko, Nakayama Shoji F
Department of Environmental Health, National Institute of Public Health, 2-3-6, Minami, Wako-shi, Saitama 351-0197, Japan.
Faculty and Graduate School of Engineering, Chiba University, 1-33 Yayoicho, Inage-ku, Chiba-shi, Chiba 263-8522, Japan.
Sci Total Environ. 2024 Jan 1;906:167830. doi: 10.1016/j.scitotenv.2023.167830. Epub 2023 Oct 13.
Seasonal variations of chemical compounds in indoor air and outdoor air and personal exposure to these chemicals were continuously monitored for 6 years using four types of passive sampling devices: PSD-BPE/DNPH packed with 2,4-dinitrophenylhydrazine and trans-1,2-bis(2-pyridyl)ethylene coated silica for ozone and carbonyls; PSD-VOC packed with Carboxen 572 or Active Carbon Beads particles for volatile organic compounds; PSD-TEA packed with triethanolamine impregnated silica for acid gases; and PSD-TEA packed with phosphoric acid impregnated silica for basic gases. Many chemical compounds except for nitrogen dioxide, formic acid, and benzene showed seasonal variations with high concentrations in summer and low concentrations in winter. In particular, formaldehyde, nonanal, 2-ethyl-1-hexanol, 2,2,4-trimethyl-1,3-pentanediol monoisobutyrate, and ammonia concentrations showed remarkable seasonal variation. For example, the concentration of formaldehyde in February and August was 5.9 and 40 μg/m, respectively, a difference of about 7 times. Although there were large differences in the concentrations in each house, the fluctuation pattern was almost the same every year in each house. By contrast, nitrogen dioxide, formic acid, and benzene concentrations were low in summer and high in winter. These compounds were generated by kerosine and gas stoves in winter. Long-term continuous monitoring revealed that annual mean concentrations could be estimated using data from February and August. Personal exposure concentrations could be classified into four patterns: chemicals affected by the indoor environment such as formaldehyde, chemicals affected by the outdoor environment such as ozone, chemicals affected by the occupational environment such as hexane, and background level chemicals such as benzene (without kerosine and gas stoves). Indoor and outdoor measurements are means to investigate the "health" of each environment. Personal exposure measurement using PSD-samplers is suitable for assessing the health risk of chemical compounds to humans.
使用四种类型的被动采样装置,对室内空气、室外空气中化学化合物的季节性变化以及个人对这些化学物质的暴露情况进行了连续6年的监测:用于臭氧和羰基化合物的PSD - BPE/DNPH,填充有2,4 - 二硝基苯肼和涂有反式 - 1,2 - 双(2 - 吡啶基)乙烯的硅胶;用于挥发性有机化合物的PSD - VOC,填充有Carboxen 572或活性炭珠颗粒;用于酸性气体的PSD - TEA,填充有三乙醇胺浸渍的硅胶;用于碱性气体的PSD - TEA,填充有磷酸浸渍的硅胶。除二氧化氮、甲酸和苯外,许多化学化合物呈现出季节性变化,夏季浓度高,冬季浓度低。特别是甲醛、壬醛、2 - 乙基 - 1 - 己醇、2,2,4 - 三甲基 - 1,3 - 戊二醇单异丁酸酯和氨的浓度呈现出显著的季节性变化。例如,2月和8月甲醛浓度分别为5.9和40μg/m³,相差约7倍。尽管各房屋内浓度存在较大差异,但每年各房屋内的波动模式几乎相同。相比之下,二氧化氮、甲酸和苯的浓度夏季低冬季高。这些化合物是冬季由煤油炉和燃气炉产生的。长期连续监测表明,可使用2月和8月的数据估算年平均浓度。个人暴露浓度可分为四种模式:受室内环境影响的化学物质如甲醛、受室外环境影响的化学物质如臭氧、受职业环境影响的化学物质如己烷以及背景水平的化学物质如苯(无煤油炉和燃气炉)。室内和室外测量是调查每个环境“健康状况”的手段。使用PSD采样器进行个人暴露测量适用于评估化学化合物对人类的健康风险。