<HashMap><database>biostudies-literature</database><scores/><additional><submitter>Sarwar G</submitter><funding>Natural Environment Research Council</funding><funding>Intramural EPA</funding><pagination>170406</pagination><full_dataset_link>https://www.ebi.ac.uk/biostudies/studies/S-EPMC10922608</full_dataset_link><repository>biostudies-literature</repository><omics_type>Unknown</omics_type><volume>917</volume><pubmed_abstract>We use the Community Multiscale Air Quality (CMAQv5.4) model to examine the potential impact of particulate nitrate (pNO&lt;sub>3&lt;/sub>&lt;sup>-&lt;/sup>) photolysis on air quality over the Northern Hemisphere. We estimate the photolysis frequency of pNO&lt;sub>3&lt;/sub>&lt;sup>-&lt;/sup> by scaling the photolysis frequency of nitric acid (HNO&lt;sub>3&lt;/sub>) with an enhancement factor that varies between 10 and 100 depending on pNO&lt;sub>3&lt;/sub>&lt;sup>-&lt;/sup> and sea-salt aerosol concentrations and then perform CMAQ simulations without and with pNO&lt;sub>3&lt;/sub>&lt;sup>-&lt;/sup> photolysis to quantify the range of impacts on tropospheric composition. The photolysis of pNO&lt;sub>3&lt;/sub>&lt;sup>-&lt;/sup> produces gaseous nitrous acid (HONO) and nitrogen dioxide (NO&lt;sub>2&lt;/sub>) over seawater thereby increasing atmospheric HONO and NO&lt;sub>2&lt;/sub> mixing ratios. HONO subsequently undergoes photolysis, producing hydroxyl radicals (OH). The increase in NO&lt;sub>2&lt;/sub> and OH alters atmospheric chemistry and enhances the atmospheric ozone (O&lt;sub>3&lt;/sub>) mixing ratio over seawater, which is subsequently transported to downwind continental regions. Seasonal mean model O&lt;sub>3&lt;/sub> vertical column densities without pNO&lt;sub>3&lt;/sub>&lt;sup>-&lt;/sup> photolysis are lower than the Ozone Monitoring Instrument (OMI) retrievals, while the column densities with the pNO&lt;sub>3&lt;/sub>&lt;sup>-&lt;/sup> photolysis agree better with the OMI retrievals of tropospheric O&lt;sub>3&lt;/sub> burden. We compare model O&lt;sub>3&lt;/sub> mixing ratios with available surface observed data from the U.S., Japan, the Tropospheric Ozone Assessment Report - Phase II, and OpenAQ; and find that the model without pNO&lt;sub>3&lt;/sub>&lt;sup>-&lt;/sup> photolysis underestimates the observed data in winter and spring seasons and the model with pNO&lt;sub>3&lt;/sub>&lt;sup>-&lt;/sup> photolysis improves the comparison in both seasons, largely rectifying the pronounced underestimation in spring. Compared to measurements from the western U.S., model O&lt;sub>3&lt;/sub> mixing ratios with pNO&lt;sub>3&lt;/sub>&lt;sup>-&lt;/sup> photolysis agree better with observed data in all months due to the persistent underestimation of O&lt;sub>3&lt;/sub> without pNO&lt;sub>3&lt;/sub>&lt;sup>-&lt;/sup> photolysis. Compared to the ozonesonde measurements, model O&lt;sub>3&lt;/sub> mixing ratios with pNO&lt;sub>3&lt;/sub>&lt;sup>-&lt;/sup> photolysis also agree better with observed data than the model O&lt;sub>3&lt;/sub> without pNO&lt;sub>3&lt;/sub>&lt;sup>-&lt;/sup> photolysis.</pubmed_abstract><journal>The Science of the total environment</journal><pubmed_title>Impact of particulate nitrate photolysis on air quality over the Northern Hemisphere.</pubmed_title><pmcid>PMC10922608</pmcid><funding_grant_id>EPA999999</funding_grant_id><funding_grant_id>NE/S000518/1</funding_grant_id><funding_grant_id>NE/N009983/1</funding_grant_id><pubmed_authors>Henderson BH</pubmed_authors><pubmed_authors>Gilliam R</pubmed_authors><pubmed_authors>Callaghan AB</pubmed_authors><pubmed_authors>Carpenter LJ</pubmed_authors><pubmed_authors>Lee J</pubmed_authors><pubmed_authors>Sarwar G</pubmed_authors><pubmed_authors>Hogrefe C</pubmed_authors><pubmed_authors>Mathur R</pubmed_authors></additional><is_claimable>false</is_claimable><name>Impact of particulate nitrate photolysis on air quality over the Northern Hemisphere.</name><description>We use the Community Multiscale Air Quality (CMAQv5.4) model to examine the potential impact of particulate nitrate (pNO&lt;sub>3&lt;/sub>&lt;sup>-&lt;/sup>) photolysis on air quality over the Northern Hemisphere. We estimate the photolysis frequency of pNO&lt;sub>3&lt;/sub>&lt;sup>-&lt;/sup> by scaling the photolysis frequency of nitric acid (HNO&lt;sub>3&lt;/sub>) with an enhancement factor that varies between 10 and 100 depending on pNO&lt;sub>3&lt;/sub>&lt;sup>-&lt;/sup> and sea-salt aerosol concentrations and then perform CMAQ simulations without and with pNO&lt;sub>3&lt;/sub>&lt;sup>-&lt;/sup> photolysis to quantify the range of impacts on tropospheric composition. The photolysis of pNO&lt;sub>3&lt;/sub>&lt;sup>-&lt;/sup> produces gaseous nitrous acid (HONO) and nitrogen dioxide (NO&lt;sub>2&lt;/sub>) over seawater thereby increasing atmospheric HONO and NO&lt;sub>2&lt;/sub> mixing ratios. HONO subsequently undergoes photolysis, producing hydroxyl radicals (OH). The increase in NO&lt;sub>2&lt;/sub> and OH alters atmospheric chemistry and enhances the atmospheric ozone (O&lt;sub>3&lt;/sub>) mixing ratio over seawater, which is subsequently transported to downwind continental regions. Seasonal mean model O&lt;sub>3&lt;/sub> vertical column densities without pNO&lt;sub>3&lt;/sub>&lt;sup>-&lt;/sup> photolysis are lower than the Ozone Monitoring Instrument (OMI) retrievals, while the column densities with the pNO&lt;sub>3&lt;/sub>&lt;sup>-&lt;/sup> photolysis agree better with the OMI retrievals of tropospheric O&lt;sub>3&lt;/sub> burden. We compare model O&lt;sub>3&lt;/sub> mixing ratios with available surface observed data from the U.S., Japan, the Tropospheric Ozone Assessment Report - Phase II, and OpenAQ; and find that the model without pNO&lt;sub>3&lt;/sub>&lt;sup>-&lt;/sup> photolysis underestimates the observed data in winter and spring seasons and the model with pNO&lt;sub>3&lt;/sub>&lt;sup>-&lt;/sup> photolysis improves the comparison in both seasons, largely rectifying the pronounced underestimation in spring. Compared to measurements from the western U.S., model O&lt;sub>3&lt;/sub> mixing ratios with pNO&lt;sub>3&lt;/sub>&lt;sup>-&lt;/sup> photolysis agree better with observed data in all months due to the persistent underestimation of O&lt;sub>3&lt;/sub> without pNO&lt;sub>3&lt;/sub>&lt;sup>-&lt;/sup> photolysis. Compared to the ozonesonde measurements, model O&lt;sub>3&lt;/sub> mixing ratios with pNO&lt;sub>3&lt;/sub>&lt;sup>-&lt;/sup> photolysis also agree better with observed data than the model O&lt;sub>3&lt;/sub> without pNO&lt;sub>3&lt;/sub>&lt;sup>-&lt;/sup> photolysis.</description><dates><release>2024-01-01T00:00:00Z</release><publication>2024 Mar</publication><modification>2025-04-05T12:39:11.952Z</modification><creation>2025-04-05T12:39:11.952Z</creation></dates><accession>S-EPMC10922608</accession><cross_references><pubmed>38281631</pubmed><doi>10.1016/j.scitotenv.2024.170406</doi></cross_references></HashMap>