Evaluation of arsenical emission from semiconductor and opto-electronics facilities in Hsinchu, Taiwan

Abstract Semiconductor and opto-electronics industries use many chemicals including arsenics in manufacturing processes. Thus, the process vent stream contains toxic air pollutants including arsine and other arsenic compounds, and poses a potential source for the atmospheric arsenic. Limited data are published on arsenic risk assessment and work place condition for electronics industries. Moreover, as per our best knowledge there is no report available on arsenic pollution from the exhaust of semiconductor and opto-electronic industries. In this study, the total arsenic (arsenic compounds as arsenic in gaseous and particulate phase) concentration was measured in the flue gas of 20 stacks of different semiconductor and opto-electronics facilities situated in Science Based Industrial Park (SBIP), Hsinchu, Taiwan during August–September 2002. Ambient concentration of particulate arsenic (arsenic compounds as arsenic) was measured at 15 sites of SBIP twice, i.e. in September and October 2002. The concentration of the total arsenic in the flue gas was from 0 to 55.92 μg m −3 with the emission rate from 0 to 0.1427 g h −1 for the facilities. The ambient arsenic concentration was from 0 to 120 ng m −3 . The ambient air level goal (AALG) of arsenic compound is 4.6×10 −5  μg m −3 , if the lifetime cancer probability (LCP) level is 1.0×10 −6 . Based on simple risk assessment model, we used Industrial Source Complex Short Term 3 (ISCST3) model to calculate the maximum ground level concentration and employed the value of AALG; the emission limit of arsenic compounds from a factory was determined to be less than 1.0×10 −5  kg h −1 . On comparison, it was concluded that the arsenical emission of 11 out of 20 facilities was higher than the limited value.

[1]  Nikolaos S Thomaidis,et al.  Characterization of lead, cadmium, arsenic and nickel in PM(2.5) particles in the Athens atmosphere, Greece. , 2003, Chemosphere.

[2]  G. Nordberg,et al.  Lung cancer risks among lead smelter workers also exposed to arsenic. , 2001, The Science of the total environment.

[3]  Chuen-Jinn Tsai,et al.  Inorganic Acid Emission Factors of Semiconductor Manufacturing Processes , 2004, Journal of the Air & Waste Management Association.

[4]  R. L. Baskett,et al.  AIR: Toxic risk assessment and management: Public Health Risks from Normal Operations, by Gratt, Lawrence B. Van, Nostrand Reinhold, New York, NY, 1996, 388 pp. , 1997 .

[5]  Y. Tsai,et al.  Temporal characteristics of inhalable mercury and arsenic aerosols in the urban atmosphere in southern Taiwan , 2003 .

[6]  J. Sheehy,et al.  Assessment of arsenic exposures and controls in gallium arsenide production. , 1993, American Industrial Hygiene Association journal.

[7]  M. Chiaradia,et al.  Gas-to-particle conversion of mercury, arsenic and selenium through reactions with traffic-related compounds? Indications from lead isotopes , 2000 .

[8]  A. Silvers,et al.  Nonlinearity in the lung cancer dose-response for airborne arsenic: apparent confounding by year of hire in evaluating lung cancer risks from arsenic exposure in Tacoma smelter workers. , 1999, Regulatory toxicology and pharmacology : RTP.

[9]  G. Brenniman,et al.  Cancer risk assessment for the inhalation of metals from municipal solid waste incinerators impacting Chicago , 1993, Bulletin of environmental contamination and toxicology.

[10]  C. Johansson,et al.  Anthropogenic and natural levels of arsenic in PM10 in Central and Northern Chile , 2002 .

[11]  P. Hopke,et al.  Atmospheric aerosol over Vermont: chemical composition and sources. , 2001, Environmental science & technology.

[12]  L. Fan,et al.  Capture of gas-phase arsenic oxide by lime: kinetic and mechanistic studies. , 2001, Environmental science & technology.