5A.1 Lifetimes and Timescales of Tropospheric Ozone (Invited Presentation)

Tuesday, 30 January 2024: 8:30 AM
310 (The Baltimore Convention Center)
Michael Prather, University of California Irvine, Irvine, CA; and X. Zhu

Ozone is a secondary pollutant, produced in the atmosphere from other pollutants (Haagen-Smit, 1952). Because of this lack of direct emissions, our understanding and modeling of O3 is quite different from that of other chemical pollutants and greenhouse gases. For example, we do not create atmospheric budgets tied to emissions, natural and anthropogenic, and thus do not derive lifetimes as we do for other gases like methane from the atmospheric burden divided by the emissions. In this work, we take a new approach to the study of tropospheric O3 by hypothesizing a direct emission source of O3 and then following its perturbation on the background atmosphere to derive that source's lifetime for O3 and the atmospheric time scale to remove the excess O3.

We study the perturbation to O3 from hypothesized primary emissions associated with surface industrial pollution, aviation, and stratosphere-troposphere exchange using the UC Irvine chemistry-transport model with stratospheric-plus-tropospheric chemistry. A constant 3D emission pattern of 100 Tg-O3/yr is run, identifying the pattern and burden of excess O3 over four years. As expected for most any trace gas, the O3 lifetime varies with season and location of emissions. When emissions are suddenly cut, we can observe and calculate the timescale of the O3 perturbation, which is expected to differ from the lifetime due to the coupled O3-HOx-NOx chemistry.

We find a number of not unexpected, but still surprising facts about tropospheric O3. For example, (1) summertime NH urban O3 pollution tends to have minimal hemispheric impact per mole produced; (2) the STE influx of O3 is responsible for <10% of the tropospheric O3 burden, and even less at the surface; (3) comparing aviation direct O3 emissions vs. NOx emissions, we calculate an ozone production efficiency of about 30 moles of O3 per mole of NOx; (4) O3 perturbations decay with a timescale of 10-20 days in summer and 30-40 days in winter.

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