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This present study suggests a method to calculate the SO2 flow rate from a source area to receptor areas on a regional scale using Ozone Monitoring Instrument (OMI) SO2 products, surface in situ SO2 data, and the hybrid single particle Lagrangian integrated trajectory (HYSPLIT) model. The method was implemented to calculate the SO2 flow rate from continental Asia to northeast Asia and the Northwest Pacific Ocean. For the high SO2 events when SO2 was transported from continental Asia to Japan via the Korean Peninsula on 22-24 December 2006, the long-range transported SO2 flow rates were 14.0 (21.0) Mg·h-1 OMI·gird-1 at Gangneung (Seoul) in Korea and 4.2 (5.3) Mg·h-1 OMI·gird-1 at Hiroshima (Kumamoto) in Japan. For the long-range transport of SO2 from continental Asia to the Northwest Pacific Ocean on 6-7 October 2008 (9-11 October 2006), the flow rates were 16.1 (16.2) Mg·h-1 OMI·gird-1 at Hokkaido, Japan (Vladivostok, Russia) and 5.6 (16.7) Mg·h-1 OMI·gird-1 at the Aleutian Islands, Northwest Pacific Ocean (Bering Sea). The mean rates of decrease in the SO2 flow rate per 1000 km were also calculated between continental Asia and the receptor areas. Uncertainties in the flow rate estimates were also assessed and discussed. [ABSTRACT FROM AUTHOR]

An investigation into the diurnal characteristics of vertical formaldehyde (HCHO) profiles was conducted based on multi-axis differential optical absorption spectroscopy (MAX-DOAS) measurements in Beijing during the CAREBEIJING campaign, covering a month-long period through August and September 2006. Vertical HCHO profiles were retrieved based on a combined differential optical absorption spectroscopy (DOAS) technique and an optimal estimation method (OEM). The HCHO volume-mixing ratio (VMR) was found to be highest in the layer from the surface up to an altitude of 1 km and to decrease with altitude above this layer. In all retrieved profiles, HCHO was not detected in the layer from 3-4 km. Over the diurnal cycle, the HCHO VMR values were generally highest at 15:00 local time (LT) and were lower in the morning and late afternoon. The mean HCHO VMRs were 6.17, 1.82, and 0.80 ppbv for the 0-1, 1-2, and 2-3-km layers, respectively, at 15:00 LT, whereas they were 3.54 (4.79), 1.06 (1.43), and 0.46 (0.63) ppbv for the 0-1, 1-2, and 2-3-km layers, respectively, at 09:00 (17:00) LT. The HCHO VMRs reached their highest values at 15:00 LT on August 19, which were 17.71, 5.20, and 2.31 ppbv for the 0-1, 1-2, and 2-3-km layers, respectively. This diurnal pattern implies that the photo-oxidation of volatile organic compounds (VOCs) was most active at 15:00 LT for several days during the campaign period. In a comparison of the derived HCHO VCDs with those obtained from the Ozone Monitoring Instrument (OMI) measurements, the HCHO vertical column density (VCD) values obtained from the OMI measurements tend to be smaller than those from the MAX-DOAS. [ABSTRACT FROM AUTHOR]

This study introduces a new method of combining Imaging Differential Optical Absorption Spectroscopy (Imaging-DOAS) data and plume dispersion formulas for power plant emissions to determine the threedimensional structure of a dispersing pollution plume and the spatial distributions of trace gas volume mixing ratios (VMRs) under conditions of negligible water droplet and aerosol effects on radiative transfer within the plume. This novel remote-sensing method, applied to a power plant stack plume, was used to calculate the twodimensional distributions of sulfur dioxide (SO2) and nitrogen dioxide (NO2) VMRs in stack emissions for the first time. High SO2 VMRs were observed only near the emission source, whereas high NO2 VMRs were observed at locations several hundreds of meters away from the initial emission. The results of this study demonstrate the capability of this new method as a tool for estimating plume dimensions and trace gas VMRs in power plant emissions. [ABSTRACT FROM AUTHOR]

Abstract We investigate the simultaneous effects of aerosol peak height (APH), aerosol properties, measurement geometry, and other factors on the air mass factor for NO2 retrieval at sites with high NO2 concentration. A comparison of the effects of high and low surface reflectance reveals that NO2 air mass factor (AMF) values over a snowy surface (surface reflectance 0.8) are generally higher than those over a deciduous forest surface (surface reflectance 0.05). Under high aerosol optical depth (AOD) conditions, the aerosol shielding effect over a high-albedo surface is revealed to reduce the path-length of light at the surface, whereas high single scattering albedo (SSA) conditions (e.g., SSA = 0.95) lead to an increase in the aerosol albedo effect, which results in an increased AMF over areas with low surface reflectance. We also conducted an in-depth study of the APH effect on AMF. For an AOD of 0.1 and half width (HW) of 5 km, NO2 AMF decreases by 29% from 1.36 to 0.96 as APH changes from 0 to 2 km. In the case of high-AOD conditions (0.9) and HW of 5 km, the NO2 AMF decreases by 240% from 1.85 to 0.54 as APH changes from 0 to 2 km. The AMF variation due to error in the model input parameters (e.g., AOD, SSA, aerosol shape, and APH) is also examined. When APH is 0 km with an AOD of 0.4, SSA of 0.88, and surface reflectance of 0.05, a 30% error in AOD induces an AMF error of between 4.85% and −3.67%, an SSA error of 0.04 leads to NO2 VCD errors of between 4.46% and −4.77%, and a 30% error in AOD induces an AMF error of between −9.53% and 8.35% with an APH of 3 km. In addition to AOD and SSA, APH is an important factor in calculating AMF, due to the 2 km error in APH under high-SZA conditions, which leads to an NO2 VCD error of over 60%. Aerosol shape is also found to have a measureable effect on AMF under high-AOD and small relative azimuth angle (RAA) conditions. The diurnal effect of the NO2 profile is also examined and discussed. [ABSTRACT FROM AUTHOR]

A novel system for removing toluene, p-xylene, and ethylene was developed that combines a biotrickling filtration system with a nonthermal plasma reactor. The limitations of an individual biotrickling filter for treating slowly biodegradable volatile organic compound (VOC) gases with high concentrations were thereby avoided. Performance for removing toluene, p-xylene, and ethylene of a biotrickling filter and a plasma reactor was investigated at a variety of flow rates and inlet concentrations of the test gases. The biotrickling filter was exposed to toluene gas only for over 1 month, to cultivate specific micro-organisms. Biofiltration treatment removed toluene more efficiently than p-xylene and ethylene. However, the nonthermal plasma removed ethylene more effectively than p-xylene and toluene, due to the fact that ethylene has a weak π bond. For the case of the plasma-pretreated biotrickling system, the efficiency with which toluene, p-xylene, and ethylene were removed was 95.2 ± 0.1%, 95.8 ± 0.2%, and 81.3 ± 0.8%, respectively, at an inlet concentration of 116.5, 132.4, and 127.5 ppm and gas flow rate of 20 L/min. Results obtained showed that the performance of the combination system of nonthermal plasma and biotrickling filter was much better than the stand-alone biotrickling filter for removing p-xylene and ethylene (improvements of 28.0 ± 2.0%, and 29.7 ± 1.95%, respectively), while it was a little better for removing toluene (improvement of 5.3 ± 4.0%). Results suggest that a combined nonthermal plasma/biofiltration system can be used effectively to remove slowly biodegradable pollutants with high concentrations that are different from the gases that were used to cultivate the micro-organisms. [ABSTRACT FROM AUTHOR]