Abstract:Particulate matter (PM) adsorbed by air purifiers, normally used in residential buildings, was collected and analysed by this study. The concentrations of eight heavy metals and 16 poly-aromatic hydrocarbons (PAHs) in PM were determined by inductively coupled plasma-optical emission spectroscopy (ICP-OES) and gas chromatography-mass spectroscopy (GC-MS). The health risk of heavy metals and PAHs was assessed using the health assessment model recommended by the US Environment Protection Agency (EPA). The results… Show more
Workers in semiconductor factories have occupational health risks from exposure to chemical substances. This work analyzed hazardous chemical substances in the key process of a semiconductor factory in China, and studied cancer and non-cancer health risks and occupational health risks of workers. Research results show that more than half of the processes contain compounds such as hydrogen fluoride, chlorine, hydrogen chloride, ammonia and 2-propanol, and their concentrations vary greatly depending on the process. The occupational exposure index (Ei) of some processes is greater than 1, which means that there are adverse occupational health risks, including wet etching (WETCH), physical vapour deposition (PVD), furnace process (FUR), chemicals storehouse (CS) and diffusion (from inspection area). The pollutants with a high contribution rate to Ei vary with the process, and WETCH (operating area) has the highest contribution rate of sulphuric acid (93.33%). The Hazard Quotient (HQi) of PVD and CS is far greater than 1, indicating that there is a non-cancer risk. The lifetime cancer risk (LCRi) of wastewater treatment and CS is greater than 10−4, which indicates a risk of cancer. The General Engineer has higher health risks than the Duty Engineer due to the higher exposure frequency.
Workers in semiconductor factories have occupational health risks from exposure to chemical substances. This work analyzed hazardous chemical substances in the key process of a semiconductor factory in China, and studied cancer and non-cancer health risks and occupational health risks of workers. Research results show that more than half of the processes contain compounds such as hydrogen fluoride, chlorine, hydrogen chloride, ammonia and 2-propanol, and their concentrations vary greatly depending on the process. The occupational exposure index (Ei) of some processes is greater than 1, which means that there are adverse occupational health risks, including wet etching (WETCH), physical vapour deposition (PVD), furnace process (FUR), chemicals storehouse (CS) and diffusion (from inspection area). The pollutants with a high contribution rate to Ei vary with the process, and WETCH (operating area) has the highest contribution rate of sulphuric acid (93.33%). The Hazard Quotient (HQi) of PVD and CS is far greater than 1, indicating that there is a non-cancer risk. The lifetime cancer risk (LCRi) of wastewater treatment and CS is greater than 10−4, which indicates a risk of cancer. The General Engineer has higher health risks than the Duty Engineer due to the higher exposure frequency.
“…[89][90][91] Our present findings were almost consistent to those reported in earlier similar studies. 28,51,82,92,93…”
Section: Composition Of Pahs In Shdmentioning
confidence: 99%
“…5,21-27 Petroleum refining, petrochemical activities, power generation, vehicle emissions, waste water treatment plants and oil spills are the major sources of PAHs found outdoors. 28-33…”
Section: Introductionmentioning
confidence: 99%
“…5,[21][22][23][24][25][26][27] Petroleum refining, petrochemical activities, power generation, vehicle emissions, waste water treatment plants and oil spills are the major sources of PAHs found outdoors. [28][29][30][31][32][33] Indoor dust particles are important hazardous pollutants, as they act as a reservoir for hundreds of hazardous chemicals. 34 Dust particles can pose a substantial risk to human health through inhalation, since 93% of dust particles in indoor environments can be resuspended in the air, with approximately 20% inhaled.…”
Data dealing with polycyclic aromatic hydrocarbons (PAHs) levels in settled dust of Greater Cairo houses (GCH), Egypt, and their implication on human health risk are scarce. The goal of this study was to gain insights into the characterisations of PAHs in settled dust in GCH and their associated carcinogenic and mutagenic risks. ƩPAH concentrations were 3125 and 268 ng/g in settled dust in GCH and rural houses (RH), respectively. Heavier congeners (4–6 aromatic ring PAHs) represented 86.5% (GCH) and 92% (RH) of ƩPAHs. Houses on main streets are exposed to higher levels of PAHs than those on the side streets. The main sources of PAHs in GCH and RH were vehicular emissions (pyrogenic sources) and PAHs in GCH come from local emissions and in RH from the surrounding urban cities. Results showed that the carcinogenicity of PAHs associated with dust exceeds their mutagenicity. Based on Incremental Lifetime Cancer Risk (ILCR) estimations, the order of cancer risk (CR) was as follows: urban houses (UH) > suburban houses (SUH) > RH. CR and ILCRs calculations suggest that children and adults exposed to settled dust-bound PAHs in GCH and RH have an increase in CR, as CR and ILCRs values exceeded accepted levels.
“…At present, experts and scholars focused their attention on indoor air quality in urban buildings. According to statistics, 3,4 less than 10% of them have studied indoor air quality in rural regions. Due to the complexity of indoor air pollution sources and the limitations of living standards in rural regions, IAP has serious and potential health risks.…”
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