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Attribution of Tropospheric Ozone to NO<sub><i>x</i></sub> and VOC Emissions: Considering Ozone Formation in the Transition Regime

143

Citations

26

References

2018

Year

Abstract

An improved three-regime (3R) O<sub>3</sub> attribution technique for O<sub>3</sub> source apportionment in regional chemical transport models is developed to divide the entire range of VOC-NO <sub>x</sub>-O<sub>3</sub> formation sensitivity to VOC-limited, transition, and NO <sub>x</sub>-limited regimes based on the value of a regime indicator R. The threshold R values to mark the start ( R<sub>ts</sub>) and end ( R<sub>te</sub>) of the transition regime are defined at the point where O<sub>3</sub>-NO <sub>x</sub> sensitivity turns from negative to positive and where O<sub>3</sub>-NO <sub>x</sub> sensitivity is ten times higher than O<sub>3</sub>-VOC sensitivity, respectively. R<sub>ts</sub> and R<sub>te</sub> are determined using NO <sub>x</sub> and VOC sensitivity simulations in a box model with a modified SAPRC-11 mechanism. For the widely used indicator ration R = ( P<sub>H2O2</sub> + P<sub>ROOH</sub>)/ P<sub>HNO3,</sub> which is based on the production rates of H<sub>2</sub>O<sub>2</sub>, HNO<sub>3</sub> and organic hydroperoxides (ROOH), the recommended R<sub>ts</sub> and R<sub>te</sub> values are 0.047 and 5.142, respectively. Parameterized attribution functions, depending only on the values of R, are developed to apportion modeled in situ O<sub>3</sub> formation in the transition regime to NO <sub>x</sub> and VOCs. The new 3R and the traditional two-regime (2R) schemes are incorporated into the Community Multiscale Air Quality (CMAQ) model to quantify NO <sub>x</sub> and VOC contributions to regional O<sub>3</sub> concentrations in China in August 2013. The 3R approach predicts approximately 5-10 ppb and up to 15 ppb higher NO <sub>x</sub> contributions to 8 h O<sub>3</sub> in in the North China Plain, the Yangtze River Delta and the Pearl River Delta than the 2R approach. The big differences in O<sub>3</sub> attribution between 2R and 3R can have significant policy implications for air pollution emission controls.

References

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