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China is the world’s leading producer and exporter of coke, and its annual production are at leading level in the world. Coke oven emissions (COE) are the predominant pollutants generated in coking production, which mainly contain particulate matter and volatile organic compounds, especially polycyclic aromatic hydrocarbons (PAHs). Coke oven workers are liable to be at risk for occupational COE exposure and for developing respiratory disorders and diseases, even lung cancer. In the context, this study deals with the assessment of the carcinogenic risk attributable to PAHs exposure based on data collected from the national reporting system of occupational disease in China and interpreted with field investigations. Consequently, coke oven emissions-induced lung cancer was mainly found in manufacturing industries, especially in petroleum processing, coking and nuclear fuel processing, followed by chemical raw materials and chemical products. Coke oven workers exposed to higher levels of PAHs in different workplaces have a higher risk of occupational lung cancer. These findings reinforce the notion that it is necessary to continuously strengthen the monitoring of the COE, regulate emissions, and maintain health surveillance for occupational protection and health promotion among coke oven workers.
In this study, the data from the Chinese reporting system of occupational disease from 2008 to 2019 were systematically gathered based on the retrieval of character strings such as “coke oven emission” and “occupational cancer or tumor”, etc., and the industrial distribution characteristics of lung cancer caused by coke oven emissions were then analyzed.
Based on this context, we selected some coking plants in the East and Southwest of China for further research. The selection of coking plants as key industries is based on these representative industries being closely related to coke oven emissions exposure. A total of 8 different working regions in different coking plants were selected for PAHs concentration detection by high-performance liquid chromatography. Meanwhile, the incremental lifetime cancer risks (ILCR) due to PAHs exposure in different working positions were calculated by using the following formula.
$$ ILCR=\frac{CSF\times C\times IR\times EF\times ED}{AT\times BW} $$ CSF represented the cancer slope factor, which was adopted in this study as 1.38 kg·day/mg proposed by Judith Petts in 1997 (1), C represented the exposure concentration (mg/m3), IR represented the respiration rate as 1.5 m3/h, EF represented days of exposure per year, ED represented the years of exposure, AT represented the average time — which is typically set to 70 years — and BW represented body weight (kg) and was assumed to be 70 kg for adults (2). ILCR was acceptable if it was no more than 1×10−6.
The industrial distribution of cases was shown in Figure 1. There were differences in the incidence of COE-induced lung cancer among occupational population in different industries, and the two industries with the highest incidence were petroleum processing and coking and nuclear fuel processing (60.93%), followed by chemical raw materials and chemical products (14.88%).
Figure 1.Industrial distribution of lung cancer cases caused by coke oven emissions in China from 2008 to 2019.
Coke oven emissions-caused lung cancer is one of the most prominent occupational cancers in the national occupational disease reporting system. The change pattern of proportion of COE-induced lung cancer in occupational tumors over time were shown in Figure 2. According to the Chinese reporting system of occupational disease, the proportion of total lung cancer of coke oven workers accounted for more than 25% of total reported occupational tumors in four years (2008, 2011, 2017, and 2019), with the highest in 2011 (27.17%). The coke output in China from 2008 to 2019 was illustrated in Figure 3A, and Figure 3B showed the top ten provincial-level administrative divisions (PLADs) with the highest coke output in China from 2008 to 2019. The average annual coke output from 2008 to 2019 was 4.29 million tons. Shanxi, Hebei, Shandong, Shaanxi, and Inner Mongolia were all PLADs contributing to the production of coke in China.
Figure 2.The proportion of lung cancer cases caused by coke oven emissions in occupational tumors from 2008 to 2019.
Abbreviation: COE=coke oven emissions.Figure 3.Coke production in China from 2008 to 2019 and the top ten PLADs in production from 2008 to 2019. (A) The coke output in China from 2008 to 2019, with with an average annual output of 4.29. (B) The top ten PLADs with the highest coke output in China from 2008 to 2019.
Abbreviations: GT=gigaton; MT=megaton; PLADs=provincial-level administrative divisions.Monitoring data of PAHs and risk analysis of lung cancer induced by coke oven emissions at different positions in coking plants in East and Southwest China were listed in Table 1. The riser platform had the highest carcinogenic risk in two coking plants.
Workplaces A plant in East of China A plant in Southwest of China PAHs concentration (ng/m3) Carcinogenic risk* PAHs concentration (ng/m3) Carcinogenic risk* Furnace cover 8,218.77 5.71×10−4 4,227.82 2.94×10−4 Riser platform 12,560.43 0.87×10−3 48,100.25 3.34×10−3 Coal filling car driver 3,678.99 0.26×10−3 24,145.17 1.68×10−3 Coke blocking car driver 1,852.47 1.29×10−4 1,620.04 1.13×10−4 Coke side door of coke oven 1,758.37 1.22×10−4 889.45 6.18×10−5 Pusher side door of coke oven 4,135.63 2.87×10−4 403.93 2.81×10−5 Coke pushing car driver 1,757.64 1.22×10−4 2,144.22 1.49×10−4 Switch control 291.40 2.02×10−5 681.45 4.73×10−5 * The ILCR due to PAHs exposures in different working positions were calculated by using the following formula:
$ ILCR=\dfrac{CSF\times C\times IR\times EF\times ED}{AT\times BW} $
where CSF represented the cancer slope factor which was adopted in this study as 1.38 kg·day/mg proposed by Judith Petts in 1997 (1), C represented the exposure concentration (mg/m3), IR represented the respiration rate as 1.5 m3/h, EF represented days of exposure per year, ED represented the years of exposure, AT represented the averaging time which is typically set to 70 years, BW represented body weight (kg) and is typically assumed to be 70 kg for adults (2).
Abbreviations: ILCR=lifetime cancer risks; PAHs=polycyclic aromatic hydrocarbons.Table 1. PAHs monitoring and carcinogenic risk evaluation at working positions in coking plants.
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