Exposure assessment of elemental carbon, polycyclic aromatic hydrocarbons and crystalline silica at the underground excavation sites for top-down construction buildings

• Published in: PloS one 2020-09, Vol.15 (9), p.e0239010
• Main Authors: Park, Hyunhee, Hwang, Eunsong, Jang, Miyeon, Yoon, Chungsik, Khitab, Anwar
• Format: Article
• Language: English
• Subjects: Air quality; Air sampling; Blasting; Buildings; Carbon; Chromatography; Conferences; Construction; Construction materials; Construction sites; Crystal structure; Crystallinity; Diesel; Diesel engines; Dust; Engineering and Technology; Excavation; Excavators; Exhaust emissions; Exposure; Exposure limits; Fluorescence; Fourier transforms; Hazardous materials; Health aspects; Highway construction; Infrared analysis; Infrared spectroscopy; Light penetration; Liquid chromatography; Lung cancer; Medical research; Medicine and Health Sciences; Nitrogen dioxide; Occupational exposure; Occupational health; Occupational safety; Organic carbon; Particulates; Physical Sciences; Polycyclic aromatic hydrocarbons; Polyvinyl chloride; Public health; Silica; Silicon dioxide; Underground construction; Urban areas; Ventilation; Vinyl chloride; Work environment; Workers; Workshops
• ISSN: 1932-6203; 1932-6203
• DOI: 10.1371/journal.pone.0239010

Enclosed underground excavation worksite has an environment with poor ventilation and exposure to hazardous substances from diesel engine exhaust and construction materials. The objective of this study was to evaluate the exposure level of elemental carbon (EC), organic carbon (OC), total carbon (TC), polycyclic aromatic hydrocarbons (PAHs), dust and crystalline silica (CS) during underground excavation work for top down construction buildings. Active local air sampling for EC, OC, and TC (n = 105), PAHs (n = 50), dust (n = 34) and CS (n = 34) was conducted from inside and outside the excavator at underground excavation workshop in four different construction sites. EC, OC, TC and CS were sampled with each respirable and total particulates. EC, OC, and TC were collected on quartz-filter and analyzed using the thermal optical transmittance method. PAHs was collected on polytetrafluorethylene filter with XAD-2 and analyzed using liquid chromatography with fluorescence detector. CS and particulates were collected on poly vinyl chloride filter and analyzed using fourier-transform infrared spectroscopy. The geometric mean of respirable EC, OC, TC, total PAHs, respirable dust and respirable CS were 8.69 [mu]g/m.sup.3, 34.32 [mu]g/m.sup.3, 44.96 [mu]g/m.sup.3, 6.818 [mu]g/m.sup.3 0.13 mg/m.sup.3 and 0.02 mg/m.sup.3 from inside the excavator and 33.20 [mu]g/m.sup.3, 46.53 [mu]g/m.sup.3, 78.21 [mu]g/m.sup.3, 3.934 [mu]g/m.sup.3, 0.9 mg/m.sup.3 and 0.08 mg/m.sup.3 from outside the excavator (underground excavation workshop), respectively. The EC and RCS concentration from outside the excavator is significantly higher than that of inside the excavator (p