| Tropospheric ozone(O3)pollution frequently occurs in China during summer.High O3 concentrations exert detrimental impacts on the health of human beings and ecosystems.O3 is formed by a series of complex photochemical reactions of nitrogen oxides(NOX)、volatile organic compounds(VOCs),and carbon monoxide(CO)in the presence of sunlight with no direct emissions.O3 concentrations are influenced by the intricacies of atmospheric chemistry and meteorology.An increasing trend was shown by long-term observations of near-surface O3 concentrations in China.Particulate matter(PM)concentrations have significantly decreased since the implementation of the“Air Pollution Prevention and Control Action Plan”during 2013–2017.Near-surface O3 concentrations have dramatically increased and O3 pollution becomes a primary environmental challenge in China recently.The North China Plain(NCP)is featured by the heaviest pollution of O3 among megacity clusters.Previous studies about O3 concentration attributions and drivers of O3 enhancement are traditionally focused on anthropogenic precursor sources(including NOX and VOCs emissions from industrial,power plant,traffic,and residential sources)and meteorological factors(including air temperature,relative humidity,wind direction,and wind speed).However,the mechanism of deteriorated O3 pollution remains controversial currently.Therefore,to explore summertime near-surface O3 pollution in the NCP,combining observations and model simulations,the effects of weather conditions,precursor emissions,and chemical processes on O3 pollution and its deterioration were investigated in this paper.Studies included no-traditional effects of(1)extreme weather conditions——heat waves,(2)cropland NOX emission,(3)vessel emission,and(4)HO2·heterogeneous uptake on wet aerosol surfaces on near-surface O3 concentrations in summer in the NCP.Detailed information and main outcomes are represented as follows:(1)Effects of heat waves on O3 pollution:Remarkably elevated surface air temperature and intensified UV radiation were observed in summer in the Beijing-Tianjin-Hebei region(BTH)during 2013–2017.The main part of the WPSH extended considerably westward and northward in the summer of 2017,inducing a warmer and drier climate in the BTH.Compared to those in the 2013–2016 mean,the frequencies,duration,and intensity of heat waves remarkably increased by 11%,31%,and 102%,respectively,in the BTH in JJA 2017,providing weather conditions that facilitate O3formation and accumulation.The frequency of O3 exceedances in JJA 2017 was 1.5-times the average frequency of O3 exceedances during JJA 2013–2016,and O3exceedances lasting more than six days significantly increased.However,the contribution of weather shifts to O3 concentration variability owing to climate change remains elusive.The WRF-Chem model was used to investigate the impacts of the anthropogenic emission mitigation and weather condition shifts on summertime O3concentration variability in the BTH region.Results showed that anthropogenic emission changes contributed approximately 23%of the increase in maximum daily average 8-hour(MDA8)O3 concentrations in the BTH in JJA 2017 compared with that in 2013.The consecutive occurrences of unfavorable weather conditions(heat wave events)substantially contributed 15.5μg m-3(approximately 50%)of the MDA8 O3concentration enhancements,constituting one of the most important factors worsening summertime O3 pollution over the BTH region in JJA 2017.(2)Effects of cropland NOX emissions on O3 pollution:Soil NOX emissions were measured and estimated to be the second most significant contributor to the NOX burden following the fossil fuel combustion source globally.NOX emissions from croplands were subject to being underestimated or overlooked in air pollution simulations of regional atmospheric chemistry models.With constraints of ground and space observations of NO2,the WRF-Chem model was used to explore the cropland NOXemission and its contribution to the near-surface O3 pollution in NCP during a growing season.Model simulations revealed that the cropland NOX emissions were underestimated by around 80%without constraints of satellite measured NO2 column densities.The biogenic NOX source was estimated to account for 49%of the anthropogenic NOX emissions in the NCP during the growing season.Additionally,the cropland NOX source contributed around 5.0%of MDA8 O3 concentration and 27.7%of NO2 concentration in the NCP.Our results suggest that agriculture NOX emission exerts non-negligible impacts on the summertime air quality and needs to be considered when designing emission abatement strategies.(3)Effects of vessel emissions on O3 pollution:The NCP region is adjacent to the Bohai and Yellow Sea.However,the role of vessel emissions in near-surface O3pollution in the NCP remains elusive.Using the WRF-Chem model,this study quantitatively evaluated the effects of vessel emissions and the differences in ultraviolet(UV)albedo between the ocean and land surfaces on near-surface MDA8 O3concentrations over the ocean,the whole region,and coastal cities of the NCP in June2018.Results showed that vessel emissions contributed 34.0%,7.7%,and 10.2%to the mean NO2,O3,and MDA8 O3 concentrations over the ocean,respectively,and ship-induced NOX emissions dominated the contributions.Daytime(6:00–18:00)photolysis rate coefficient for NO2 was averaged higher over the ocean than that over the land,resulting in approximately 12%of NO2 being photolyzed over the ocean and 4%of MDA8 O3 increases.Vessel emissions played an important role in MDA8 O3concentrations over the ocean,and the higher surface UV albedo for the ocean further amplified the ship-induced effects,with a combined contribution of 12.6%to MDA8O3 concentrations over the ocean.The ship-induced near-surface MDA8 O3concentrations over the whole region and coastal cities of the NCP are 0.6%and 3.0%,respectively.And the contributions increased to 0.9%and 5.2%,respectively,when combined with the effect of higher surface UV albedo for the ocean.Vessel emissions played an insignificant role in the mean near-surface O3 concentrations in the NCP but a non-negotiable role in O3 pollution in the coastal cities of the NCP.Given the growing NOX emissions from vessels,emission abetment policies for the shipping industry should be carried out.(4)Effects of HO2·heterogenous loss on the O3 pollution:Hydroperoxy radical(HO2)is a crucial oxidant participating in the oxidation of nitrogen oxide to nitrogen dioxide which constitutes one of the most important pathways for the O3 photochemical formation in the troposphere.Laboratory experiments and field observations have revealed efficient HO2 heterogeneous uptake on wet aerosols,but its impact on the O3formation remains controversial.The WRF-Chem model was employed to evaluate the impacts of the HO2 heterogeneous loss on the O3 formation in the NCP in the summer of 2018.Results showed that the HO2 heterogeneous loss decreased the daytime HO2and MDA8 O3 concentration by about 5%and 1%,respectively,in the NCP with an effective uptake coefficient(!"!)of 0.2.Emission mitigation from 2013 to 2018 led to a 2.1μg m-3(5%)increase in the MDA8 O3 concentration due to decreased aerosol sink for the HO2 heterogeneous loss in the NCP.Our results revealed that decreased HO2 heterogeneous uptake does not constitute an important factor driving the O3 trend since 2013 in the NCP. |