21 research outputs found

    NO3 radical measurements in a polluted marine environment: links to ozone formation

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    Nighttime chemistry in polluted regions is dominated by the nitrate radical (NO3) including its direct reaction with natural and anthropogenic hydrocarbons, its reaction with NO2 to form N2O5, and subsequent reactions of N2O5 to form HNO3 and chlorine containing photolabile species. We report nighttime measurements of NO3, NO2, and O3, in the polluted marine boundary layer southwest of Vancouver, BC during a three week study in the summer of 2005. The concentration of N2O5 was calculated using the well known equilibrium, NO3+NO2↔N2O5. Median overnight mixing ratios of NO3, N2O5 and NO2 were 10.3 ppt, 122 ppt and 8.3 ppb with median N2O5/NO3 molar ratios of 13.1 and median nocturnal partitioning of 4.9%. Due to the high levels of NO2 that can inhibit approach to steady-state, we use a method for calculating NO3 lifetimes that does not assume the steady-state approximation. Median and average lifetimes of NO3 in the NO3-N2O5 nighttime reservoir were 1.1–2.3 min. We have determined nocturnal profiles of the pseudo first order loss coefficient of NO3 and the first order loss coefficients of N2O5 by regression of the NO3 inverse lifetimes with the [N2O5]/[NO3] ratio. Direct losses of NO3 are highest early in the night, tapering off as the night proceeds. The magnitude of the first order loss coefficient of N2O5 is consistent with, but not verification of, recommended homogeneous rate coefficients for reaction of N2O5 with water vapor early in the night, but increases significantly in the latter part of the night when relative humidity increases beyond 75%, consistent with heterogeneous reactions of N2O5 with aerosols with a rate constant khet=(1.2±0.4)×10−3 s−1−(1.6±0.4)×10−3 s−1. Analysis indicates that a correlation exists between overnight integrated N2O5 concentrations in the marine boundary layer, a surrogate for the accumulation of chlorine containing photolabile species, and maximum 1-h average O3 at stations in the Lower Fraser Valley the next day when there is clear evidence of a sea breeze transporting marine air into the valley. The range of maximum 1-h average O3 increase attributable to the correlation is ΔO3=+1.1 to +8.3 ppb throughout the study for the average of 20 stations, although higher increases are seen for stations far downwind of the coastal urban area. The correlation is still statistically significant on the second day after a nighttime accumulation, but with a different spatial pattern favouring increased O3 at the coastal urban stations, consistent with transport of polluted air back to the coast

    NO<sub>3</sub> radical measurements in a polluted marine environment: links to ozone formation

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    Nighttime chemistry in polluted regions is dominated by the nitrate radical (NO<sub>3</sub>) including its direct reaction with natural and anthropogenic hydrocarbons, its reaction with NO<sub>2</sub> to form N<sub>2</sub>O<sub>5</sub>, and subsequent reactions of N<sub>2</sub>O<sub>5</sub> to form HNO<sub>3</sub> and chlorine containing photolabile species. We report nighttime measurements of NO<sub>3</sub>, NO<sub>2</sub>, and O<sub>3</sub>, in the polluted marine boundary layer southwest of Vancouver, BC during a three week study in the summer of 2005. The concentration of N<sub>2</sub>O<sub>5</sub> was calculated using the well known equilibrium, NO<sub>3</sub>+NO<sub>2</sub>&harr;N<sub>2</sub>O<sub>5</sub>. Median overnight mixing ratios of NO<sub>3</sub>, N<sub>2</sub>O<sub>5</sub> and NO<sub>2</sub> were 10.3 ppt, 122 ppt and 8.3 ppb with median N<sub>2</sub>O<sub>5</sub>/NO<sub>3</sub> molar ratios of 13.1 and median nocturnal partitioning of 4.9%. Due to the high levels of NO<sub>2</sub> that can inhibit approach to steady-state, we use a method for calculating NO<sub>3</sub> lifetimes that does not assume the steady-state approximation. Median and average lifetimes of NO<sub>3</sub> in the NO<sub>3</sub>-N<sub>2</sub>O<sub>5</sub> nighttime reservoir were 1.1–2.3 min. We have determined nocturnal profiles of the pseudo first order loss coefficient of NO<sub>3</sub> and the first order loss coefficients of N<sub>2</sub>O<sub>5</sub> by regression of the NO<sub>3</sub> inverse lifetimes with the [N<sub>2</sub>O<sub>5</sub>]/[NO<sub>3</sub>] ratio. Direct losses of NO<sub>3</sub> are highest early in the night, tapering off as the night proceeds. The magnitude of the first order loss coefficient of N<sub>2</sub>O<sub>5</sub> is consistent with, but not verification of, recommended homogeneous rate coefficients for reaction of N<sub>2</sub>O<sub>5</sub> with water vapor early in the night, but increases significantly in the latter part of the night when relative humidity increases beyond 75%, consistent with heterogeneous reactions of N<sub>2</sub>O<sub>5</sub> with aerosols with a rate constant <i>k</i><sub>het</sub>=(1.2&plusmn;0.4)&times;10<sup>&minus;3</sup> s<sup>&minus;1</sup>&minus;(1.6&plusmn;0.4)&times;10<sup>&minus;3</sup> s<sup>&minus;1</sup>. Analysis indicates that a correlation exists between overnight integrated N<sub>2</sub>O<sub>5</sub> concentrations in the marine boundary layer, a surrogate for the accumulation of chlorine containing photolabile species, and maximum 1-h average O<sub>3</sub> at stations in the Lower Fraser Valley the next day when there is clear evidence of a sea breeze transporting marine air into the valley. The range of maximum 1-h average O<sub>3</sub> increase attributable to the correlation is &Delta;O<sub>3</sub>=+1.1 to +8.3 ppb throughout the study for the average of 20 stations, although higher increases are seen for stations far downwind of the coastal urban area. The correlation is still statistically significant on the second day after a nighttime accumulation, but with a different spatial pattern favouring increased O<sub>3</sub> at the coastal urban stations, consistent with transport of polluted air back to the coast

    Determination of tropospheric vertical columns of NO<sub>2</sub> and aerosol optical properties in a rural setting using MAX-DOAS

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    Multi-AXis Differential Optical Absorption Spectroscopy (MAX-DOAS) measurements were performed in a rural location of southwestern Ontario during the Border Air Quality and Meteorology Study. Slant column densities (SCDs) of NO<sub>2</sub> and O<sub>4</sub> were determined using the standard DOAS technique. Using a radiative transfer model and the O<sub>4</sub> SCDs, aerosol optical depths were determined for clear sky conditions and compared to OMI, MODIS, AERONET, and local PM<sub>2.5</sub> measurements. This aerosol information was input to a radiative transfer model to calculate NO<sub>2</sub> air mass factors, which were fit to the measured NO<sub>2</sub> SCDs to determine tropospheric vertical column densities (VCDs) of NO<sub>2</sub>. The method of determining NO<sub>2</sub> VCDs in this way was validated for the first time by comparison to composite VCDs derived from aircraft and ground-based measurements of NO<sub>2</sub>. The new VCDs were compared to VCDs of NO<sub>2</sub> determined via retrievals from the satellite instruments SCIAMACHY and OMI, for overlapping time periods. The satellite-derived VCDs were higher, with a mean bias of +0.5–0.9×10<sup>15</sup> molec cm<sup>−2</sup>. This last finding is different from previous studies whereby MAX-DOAS geometric VCDs were higher than satellite determinations, albeit for urban areas with higher VCDs. An effective boundary layer height, BLH<sub>eff</sub>, is defined as the ratio of the tropospheric VCD and the ground level concentration of NO<sub>2</sub>. Variations of BLH<sub>eff</sub> can be linked to time of day, source region, stability of the atmosphere, and the presence or absence of elevated NO<sub>x</sub> sources. In particular, a case study is shown where a high VCD and BLH<sub>eff</sub> were observed when an elevated industrial plume of NO<sub>x</sub> and SO<sub>2</sub> was fumigated to the surface as a lake breeze impacted the measurement site. High BLH<sub>eff</sub> values (~1.9 km) were observed during a regional smog event when high winds from the SW and high convection promoted mixing throughout the boundary layer. During this event, the regional line flux of NO<sub>2</sub> through the region was estimated to be greater than 112 kg NO<sub>2</sub> km<sup>−1</sup> h<sup>−1</sup>
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