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Inverse modeling of SO<sub>2</sub> and NO<sub><i>x</i></sub> emissions over China using multisensor satellite data – Part 1: Formulation and sensitivity analysis
oleh: Y. Wang, J. Wang, J. Wang, X. Xu, X. Xu, D. K. Henze, Z. Qu, K. Yang
| Format: | Article |
|---|---|
| Diterbitkan: | Copernicus Publications 2020-06-01 |
Deskripsi
<p><span class="inline-formula">SO<sub>2</sub></span> and <span class="inline-formula">NO<sub>2</sub></span> observations from the Ozone Mapping and Profiler Suite (OMPS) sensor are used for the first time in conjunction with the GEOS-Chem adjoint model to optimize both <span class="inline-formula">SO<sub>2</sub></span> and <span class="inline-formula">NO<sub><i>x</i></sub></span> emission estimates over China for October 2013. Separate and joint (simultaneous) optimizations of <span class="inline-formula">SO<sub>2</sub></span> and <span class="inline-formula">NO<sub>2</sub></span> emissions are both conducted and compared. Posterior emissions, compared to the prior, yield improvements in simulating columnar <span class="inline-formula">SO<sub>2</sub></span> and <span class="inline-formula">NO<sub>2</sub></span>, in comparison to measurements from the Ozone Monitoring Instrument (OMI) and OMPS. The posterior <span class="inline-formula">SO<sub>2</sub></span> and <span class="inline-formula">NO<sub><i>x</i></sub></span> emissions from separate inversions are 748 Gg S and 672 Gg N, which are 36 % and 6 % smaller than prior MIX emissions (valid for 2010), respectively. In spite of the large reduction of <span class="inline-formula">SO<sub>2</sub></span> emissions over the North China Plain, the simulated sulfate–nitrate–ammonium aerosol optical depth (AOD) only decrease slightly, which can be attributed to (a) nitrate rather than sulfate as the dominant contributor to AOD and (b) replacement of ammonium sulfate with ammonium nitrate as <span class="inline-formula">SO<sub>2</sub></span> emissions are reduced. For joint inversions, both data quality control and the weight given to <span class="inline-formula">SO<sub>2</sub></span> relative to <span class="inline-formula">NO<sub>2</sub></span> observations can affect the spatial distributions of the posterior emissions. When the latter is properly balanced, the posterior emissions from assimilating OMPS <span class="inline-formula">SO<sub>2</sub></span> and <span class="inline-formula">NO<sub>2</sub></span> jointly yield a difference of <span class="inline-formula">−3</span> % to 15 % with respect to the separate assimilations for total anthropogenic <span class="inline-formula">SO<sub>2</sub></span> emissions and <span class="inline-formula">±</span>2 % for total anthropogenic <span class="inline-formula">NO<sub><i>x</i></sub></span> emissions; but the differences can be up to 100 % for <span class="inline-formula">SO<sub>2</sub></span> and 40 % for <span class="inline-formula">NO<sub>2</sub></span> in some grid cells. Improvements on <span class="inline-formula">SO<sub>2</sub></span> and <span class="inline-formula">NO<sub>2</sub></span> simulations from the joint inversions are overall consistent with those from separate inversions. Moreover, the joint assimilations save <span class="inline-formula">∼</span> 50 % of the computational time compared to assimilating <span class="inline-formula">SO<sub>2</sub></span> and <span class="inline-formula">NO<sub>2</sub></span> separately in a sequential manner of computation. The sensitivity analysis shows that a perturbation of <span class="inline-formula">NH<sub>3</sub></span> to 50 % (20 %) of the prior emission inventory can (a) have a negligible impact on the separate <span class="inline-formula">SO<sub>2</sub></span> inversion but can lead to a decrease in posterior <span class="inline-formula">SO<sub>2</sub></span> emissions over China by <span class="inline-formula">−2.4</span> % (<span class="inline-formula">−7.0</span> %) in total and up to <span class="inline-formula">−9.0</span> % (<span class="inline-formula">−27.7</span> %) in some grid cells in the joint inversion with <span class="inline-formula">NO<sub>2</sub></span> and (b) yield posterior <span class="inline-formula">NO<sub><i>x</i></sub></span> emission decreases over China by <span class="inline-formula">−0.7</span> % (<span class="inline-formula">−2.8</span> %) for the separate <span class="inline-formula">NO<sub>2</sub></span> inversion and by <span class="inline-formula">−2.7</span> % (<span class="inline-formula">−5.3</span> %) in total and up to <span class="inline-formula">−15.2</span> % (<span class="inline-formula">−29.4</span> %) in some grid cells for the joint inversion. The large reduction of <span class="inline-formula">SO<sub>2</sub></span> between 2010 and 2013, however, only leads to <span class="inline-formula">∼</span> 10 % decrease in AOD regionally; reducing surface aerosol concentration requires the reduction of emissions of <span class="inline-formula">NH<sub>3</sub></span> as well.</p>