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      An Integrated Approach to Assess Exposure and Health-Risk from Polycyclic Aromatic Hydrocarbons (PAHs) in a Fastener Manufacturing Industry

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          Abstract

          An integrated approach was developed to assess exposure and health-risk from polycyclic aromatic hydrocarbons (PAHs) contained in oil mists in a fastener manufacturing industry. One previously developed model and one new model were adopted for predicting oil mist exposure concentrations emitted from metal work fluid (MWF) and PAHs contained in MWF by using the fastener production rate ( Pr) and cumulative fastener production rate ( CPr) as predictors, respectively. By applying the annual Pr and CPr records to the above two models, long-term workplace PAH exposure concentrations were predicted. In addition, true exposure data was also collected from the field. The predicted and measured concentrations respectively served as the prior and likelihood distributions in the Bayesian decision analysis (BDA), and the resultant posterior distributions were used to determine the long-term exposure and health-risks posed on workers. Results show that long term exposures to PAHs would result in a 3.1%, 96.7%, and 73.4% chance of exceeding the PEL-TWA (0.2 mg/m 3), action level (0.1 mg/m 3), and acceptable health risk (10 −3), respectively. In conclusion, preventive measures should be taken immediately to reduce workers’ PAH exposures.

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          Most cited references38

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          Toxic equivalency factors (TEFs) for polycyclic aromatic hydrocarbons (PAHs).

          The polycyclic aromatic hydrocarbons (PAHs; also referred to as the polynuclear aromatic hydrocarbons or PNAs) are commonly encountered at hazardous waste sites and are often the focus of site remediation activities. However, toxicity criteria are not available for all the PAHs. In the past, EPA has assessed risks posed by mixtures of PAHs by assuming that all carcinogenic PAHs are as potent as benzo[a]pyrene (B[a]P), one of the most potent PAHs. The available information on the toxicity of the PAHs suggests that most are considerably less potent than B[a]P and therefore, the EPA approach is likely to overestimate risks. Several approaches have been developed to allow the relative potency of the different PAHs to be considered in a site-specific risk assessment. This paper evaluates these approaches and presents a modified version that we feel more accurately reflects the state of knowledge on the relative potency of these compounds.
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            Assessing and predicting the exposures of polycyclic aromatic hydrocarbons (PAHs) and their carcinogenic potencies from vehicle engine exhausts to highway toll station workers

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              Emission of polycyclic aromatic hydrocarbons and their carcinogenic potencies from cooking sources to the urban atmosphere.

              Traffic has long been recognized as the major contributor to polycyclic aromatic hydrocarbon (PAH) concentrations. However, this does not consider the contribution of cooking sources of PAHs. This study set out, first, to assess the characteristics of PAHs and their corresponding benzo[a]pyrene equivalent (B[a]Peq) emissions from cooking sources to the urban atmosphere. To illustrate the importance of cooking sources, PAH emissions from traffic sources were then calculated and compared. The entire study was conducted on a city located in southern Taiwan. PAH samples were collected from the exhaust stacks of four types of restaurant: Chinese, Western, fast food, and Japanese. For total PAHs, results show that the fractions of gaseous PAHs (range, 75.9-89.9%) were consistently higher than the fractions of particulate PAHs (range, 10.1-24.1%) in emissions from the four types of restaurant. But for total B[a]Peq, we found that the contributions of gaseous PAHs (range, 15.7-21.9%) were consistently lower than the contributions of particulate PAHs (range, 78.1-84.3%). For emission rates of both total PAHs and total B[a]Peq, a consistent trend was found for the four types of restaurant: Chinese (2,038 and 154 kg/year, respectively) > Western (258 and 20.4 kg/year, respectively) > fast food (31.4 and 0.104 kg/year, respectively) > Japanese (5.11 and 0.014 kg/year, respectively). By directly adapting the emission data obtained from Chinese restaurants, we found that emission rates on total PAHs and total B[a]Peq for home kitchen sources were 6,639 and 501 kg/year, respectively. By combining both restaurant sources and home kitchen sources, this study yielded emission rates of total PAHs and total B[a]Peq from cooking sources of the studied city of 8,973 and 675 kg/year, respectively. Compared with PAH emissions from traffic sources in the same city, we found that although the emission rates of total PAHs for cooking sources were significantly less than those for traffic sources (13,500 kg/year), the emission rates of total B[a]Peq for cooking sources were much higher than those for traffic sources (61.4 kg/year). The above results clearly indicate that although cooking sources are less important than traffic sources in contributing to total PAH emissions, PAH emissions from cooking sources might cause much more serious problems than traffic sources, from the perspective of carcinogenic potency.
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                Author and article information

                Journal
                Int J Environ Res Public Health
                Int J Environ Res Public Health
                ijerph
                International Journal of Environmental Research and Public Health
                MDPI
                1661-7827
                1660-4601
                15 September 2014
                September 2014
                : 11
                : 9
                : 9578-9594
                Affiliations
                [1 ]Department of Environmental and Occupational Health, Medical College, National Cheng Kung University, 138, Sheng-Li Rd., Tainan 70428, Taiwan; E-Mails: scenicii@ 123456gmail.com (H.-I.H.); m_lin@ 123456mail.ncku.edu.tw (M.-Y.L.); chenwy@ 123456mail.iosh.gov.tw (W.-I.C.)
                [2 ]Division of Environmental Health and Occupational Medicine, National Health Research Institutes, 35 Keyan Road, Zhunan Town, Miaoli County 350, Taiwan; E-Mail: yucheng@ 123456nhri.org.tw
                [3 ]Department of Environmental Health, Seoul National University, 1 Gwanak-ro, Gwanak-gu, Seoul 151-742, Korea; E-Mail: csyoon@ 123456snu.ac.kr
                [4 ]Department of Occupational Safety and Health, Chung Hwa University of Medical Technology, Wenhwa 1st St., Rende Dist., Tainan City 71703, Taiwan
                Author notes
                [* ]Authors to whom correspondence should be addressed; E-Mails: chenmj@ 123456mail.hwai.edu.tw (M.-R.C.); pjtsai@ 123456mail.ncku.edu.tw (P.-J.T.); Tel.: +886-6-267-1214 (M.-R.C.); +886-6-208-8391 (P.-J.T.); Fax: +886-6-384-2973 (M.-R.C.); +886-6-275-2484 (P.-J.T.).
                Article
                ijerph-11-09578
                10.3390/ijerph110909578
                4199036
                25226413
                0a7db5ec-9912-4e43-a659-7f91af93215a
                © 2014 by the authors; licensee MDPI, Basel, Switzerland.

                This article is an open access article distributed under the terms and conditions of the Creative Commons Attribution license ( http://creativecommons.org/licenses/by/3.0/).

                History
                : 04 June 2014
                : 11 August 2014
                : 15 September 2014
                Categories
                Article

                Public health
                polycyclic aromatic hydrocarbons,oil mist,exposure assessment,health-risk assessment,metal work fluid

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