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Seasonal ozone behavior along an elevation gradient in the Colorado Front Range Mountains
Authors:Molly Brodin  Detlev Helmig  Samuel Oltmans
Institution:1. School of Water Resources and Environment, China University of Geosciences, Beijing 100083, China;2. China National Environmental Monitoring Center, State Environmental Protection Key Laboratory of Quality Control in Environmental Monitoring, Beijing 100012, China;3. Lancaster Environment Centre, Lancaster University, Lancaster LA1 4YQ, UK;1. Department of Earth and Atmospheric Sciences, University of Houston, Houston, TX 77204, USA;2. Institute of Environmental Studies, Pusan National University, Busan 46241, Republic of Korea;3. Division of Earth Environmental System, Pusan National University, Busan 46241, Republic of Korea;4. Department of Earth Science Education, Pusan National University, Busan 46241, Republic of Korea
Abstract:Ambient surface ozone was monitored for one year at a series of seven sites along an elevation gradient from 1600 m to 3500 m above sea level (ASL) in Boulder County, Colorado. Spatial variability of ozone, quantified as the root mean squared deviation of hourly ozone per kilometer horizontal separation, decreased with elevation and distance from local sources, validating the assumption that (except at the City of Boulder (BO) site) the results of the study are representative of the Colorado Front Range. The northern hemisphere (NH) tropospheric spring ozone peak was clearly apparent in late April and early May and affected ozone at all elevations. Ozone consistently increased with elevation during winter, with a mean monthly rate of 1.5 ppbv per 100 m elevation. In summer, this monotonic increase in ozone with elevation was not observed; instead mean monthly ozone increased in two steps, by ~15 ppbv between 1610 m and 1940 m ASL and by ~10 ppbv between 3350 m and 3530 m ASL to a maximum of 60 ppbv. The amplitude of the diurnal ozone cycle decreased with increasing elevation. Average summertime diurnal swings in ozone concentration had a magnitude of 29 ppbv at 1610 m ASL, and 7–16 ppbv at the mid-elevation sites. In winter a diurnal cycle was observed only at the BO site, ozone concentrations at the remaining six locations changed on a multi-day timescale, indicating regional background behavior as the primary factor for wintertime ozone. Even the highest elevation site was influenced by transported urban air pollution in summer, indicated by the average 5 ppbv diurnal increase in ozone. Ozone exposure at the mid- to high-elevation sites in many instances approached and exceeded the 8-h National Ambient Air Quality Standard of 75 ppbv. The elevated ozone levels along this transect were interpreted to be caused by the confounding effects of the high elevation of these sites, increased ozone in long-range transported air, and anthropogenic ozone production in air transported from the nearby urban and suburban areas east of the Colorado Front Range Mountains.
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