4.8 Article

Large Contribution of Nitrous Acid to Soil-Emitted Reactive Oxidized Nitrogen and Its Effect on Air Quality

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ENVIRONMENTAL SCIENCE & TECHNOLOGY
卷 57, 期 9, 页码 3516-3526

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AMER CHEMICAL SOC
DOI: 10.1021/acs.est.2c07793

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soil background HONO emissions; soil background NO emissions; meta-analysis; model simulations; air pollution

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Soil emissions of nitric oxide (NO) and nitrous acid (HONO) were investigated in this study. HONO emissions were found to be higher than NO emissions, especially in northern China. Long-term fertilization increased the abundance of nitrite-producing genes more significantly than NO-producing genes, especially in northern China. Simulation using a chemistry transport model showed that HONO emissions had a greater effect on air quality than NO emissions. These findings highlight the importance of considering HONO in assessing the impact of soil emissions on air quality.
Soil emissions have long been recognized as an important source of nitric oxide (NO), which regulates atmospheric oxidative capacity and the production of air pollutants. Recent research has also indicated that nitrous acid (HONO) can be emitted in significant quantities from soil microbial activities. However, only a few studies have quantified emissions of HONO along with NO from a wide range of soil types. In this study, we measured emissions of HONO and NO from soil samples collected from 48 sites across China and found much higher emissions of HONO than of NO, especially for samples from northern China. We performed a meta-analysis of 52 field studies in China, which revealed that long-term fertilization increased the abundance of nitrite-producing genes much more than the abundance of NO-producing genes. This promotion effect was greater in northern China than in southern China. In simulations using a chemistry transport model with laboratory-derived parametrization, we found that HONO emissions had a greater effect than NO emissions on air quality. Moreover, we determined that with projected continuous reductions in anthropogenic emissions, the contribution from soils to maximum 1 h concentrations of hydroxyl radicals and ozone and daily average concentrations of particulate nitrate in the Northeast Plain will increase to 17%, 4.6%, and 14%, respectively. Our findings highlight the need to consider HONO in the assessment of the loss of reactive oxidized nitrogen from soils to the atmosphere and its effect on air quality.

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