Find in Library
Search millions of books, articles, and more
Indexed Open Access Databases
Reactive nitrogen around the Arabian Peninsula and in the Mediterranean Sea during the 2017 AQABA ship campaign
oleh: N. Friedrich, P. Eger, J. Shenolikar, N. Sobanski, J. Schuladen, D. Dienhart, B. Hottmann, I. Tadic, H. Fischer, M. Martinez, R. Rohloff, S. Tauer, H. Harder, E. Y. Pfannerstill, N. Wang, J. Williams, J. Brooks, F. Drewnick, H. Su, G. Li, Y. Cheng, J. Lelieveld, J. N. Crowley
| Format: | Article |
|---|---|
| Diterbitkan: | Copernicus Publications 2021-05-01 |
Deskripsi
<p>We present shipborne measurements of NO<span class="inline-formula"><sub><i>x</i></sub></span> (<span class="inline-formula">≡</span> NO <span class="inline-formula">+</span> NO<span class="inline-formula"><sub>2</sub></span>) and NO<span class="inline-formula"><sub><i>y</i></sub></span> (<span class="inline-formula">≡</span> NO<span class="inline-formula"><sub><i>x</i></sub>+</span> gas- and particle-phase organic and inorganic oxides of nitrogen) in summer 2017 as part of the expedition “Air Quality and climate change in the Arabian BAsin” (AQABA). The NO<span class="inline-formula"><sub><i>x</i></sub></span> and NO<span class="inline-formula"><sub><i>z</i></sub></span> (<span class="inline-formula">≡</span> NO<span class="inline-formula"><sub><i>y</i></sub></span>-NO<span class="inline-formula"><sub><i>x</i></sub></span>) measurements, made with a thermal dissociation cavity ring-down spectrometer (TD-CRDS), were used to examine the chemical mechanisms involved in the processing of primary NO<span class="inline-formula"><sub><i>x</i></sub></span> emissions and their influence on the NO<span class="inline-formula"><sub><i>y</i></sub></span> budget in chemically distinct marine environments, including the Mediterranean Sea, the Red Sea, and the Arabian Gulf, which were influenced to varying extents by emissions from shipping and oil and gas production. Complementing the TD-CRDS measurements, NO and NO<span class="inline-formula"><sub>2</sub></span> data sets from a chemiluminescence detector (CLD) were used in the analysis. In all regions, we find that NO<span class="inline-formula"><sub><i>x</i></sub></span> is strongly connected to ship emissions, both via direct emission of NO and via the formation of HONO and its subsequent photolytic conversion to NO. The role of HONO was assessed by calculating the NO<span class="inline-formula"><sub><i>x</i></sub></span> production rate from its photolysis. Mean NO<span class="inline-formula"><sub>2</sub></span> lifetimes were 3.9 h in the Mediterranean Sea, 4.0 h in the Arabian Gulf, and 5.0 h in the Red Sea area. The cumulative loss of NO<span class="inline-formula"><sub>2</sub></span> during the night (reaction with O<span class="inline-formula"><sub>3</sub></span>) was more important than daytime losses (reaction with OH) over the Arabian Gulf (by a factor 2.8) and over the Red Sea (factor 2.9), whereas over the Mediterranean Sea, where OH levels were high, daytime losses dominated (factor 2.5). Regional ozone production efficiencies (OPEs; calculated from the correlation between O<span class="inline-formula"><sub><i>x</i></sub></span> and NO<span class="inline-formula"><sub><i>z</i></sub></span>, where O<span class="inline-formula"><sub><i>x</i></sub>=</span> O<span class="inline-formula"><sub>3</sub>+</span> NO<span class="inline-formula"><sub>2</sub></span>) ranged from 10.5 <span class="inline-formula">±</span> 0.9 to 19.1 <span class="inline-formula">±</span> 1.1. This metric quantifies the relative strength of photochemical O<span class="inline-formula"><sub>3</sub></span> production from NO<span class="inline-formula"><sub><i>x</i></sub></span> compared to the competing sequestering into NO<span class="inline-formula"><sub><i>z</i></sub></span> species. The largest values were found over the Arabian Gulf, consistent with high levels of O<span class="inline-formula"><sub>3</sub></span> found in that region (10–90 percentiles range: 23–108 ppbv). The fractional contribution of individual NO<span class="inline-formula"><sub><i>z</i></sub></span> species to NO<span class="inline-formula"><sub><i>y</i></sub></span> exhibited a large regional variability, with HNO<span class="inline-formula"><sub>3</sub></span> generally the dominant component (on average 33 % of NO<span class="inline-formula"><sub><i>y</i></sub></span>) with significant contributions from organic nitrates (11 %) and particulate nitrates in the PM<span class="inline-formula"><sub>1</sub></span> size range (8 %).</p>