We use global airborne observations of propane (C<sub>3</sub>H<sub>8</sub>) and ethane (C<sub>2</sub>H<sub>6</sub>) from the Atmospheric Tomography (ATom) and HIAPER Pole-to-Pole Observations (HIPPO), as well as U.S.-based aircraft and tower observations by NOAA and from the NCAR FRAPPE campaign as tracers for emissions from oil and gas operations. To simulate global mole fraction fields for these gases, we update the default emissions' configuration of C<sub>3</sub>H<sub>8</sub> used by the global chemical transport model, GEOS-Chem v13.0.0, using a scaled C<sub>2</sub>H<sub>6</sub> spatial proxy. With the updated emissions, simulations of both C<sub>3</sub>H<sub>8</sub> and C<sub>2</sub>H<sub>6</sub> using GEOS-Chem are in reasonable agreement with ATom and HIPPO observations, though the updated emission fields underestimate C<sub>3</sub>H<sub>8</sub> accumulation in the arctic wintertime, pointing to additional sources of this gas in the high latitudes (e.g., Europe). Using a Bayesian hierarchical model, we estimate global emissions of C<sub>2</sub>H<sub>6</sub> and C<sub>3</sub>H<sub>8</sub> from fossil fuel production in 2016-2018 to be 13.3 ± 0.7 (95% CI) and 14.7 ± 0.8 (95% CI) Tg/year, respectively. We calculate bottom-up hydrocarbon emission ratios using basin composition measurements weighted by gas production and find their magnitude is higher than expected and is similar to ratios informed by our revised alkane emissions. This suggests that emissions are dominated by pre-processing activities in oil-producing basins.
The People's Republic of China, the world's most populous nation, is considering extensive development of its automotive transportation infrastructure. Upper limits to the associated pollution increases can be defined through scenarios with Western style vehicles and vehicle‐to‐person ratios. Here we construct estimates of fundamental changes to chemistry of the Pacific ocean/atmosphere system through simple budgeting procedures. Regional increases in tropospheric ozone could reach tens of parts per billion. Observations/experiments suggest that enhanced nitrogen oxides will react with sea salt aerosols to yield chlorine atoms in the marine boundary layer. Nitrate deposition onto the open sea surface would support several percent of exported North Pacific carbon production. Transport of biologically active iron to surface waters may follow from increases in mineral dust and acid sulfate aerosols. Altered plankton ecodynamics will feed back into climate processes through sea to air flux of reduced sulfur gases and through carbon dioxide drawdown.
Non-methane hydrocarbon (NMHC) at Cheju Island, South Korea has been continuously measured since March 1994. The measurements are conducted two times per week. The general trend of the NMHC concentrations shows a seasonal cycle with a maximum in the winter and a minimum in the summer. The winter to summer ratios for reactive hydrocarbons varies as the rate constant for the reaction with hydroxyl radicals. This suggests that the rate of photochemical degraded by reaction with hydroxyl radical contributes in a significant way to remove hydrocarbons from the atmosphere. The relative concentrations of hydrocarbons in ambient air are valuable atmosphere tracers which can provide useful information such as the roles of photochemical reaction, source contributions and atmospheric transport process. The natural logarithms of the ratio of n-butane to ethane is plotted against the ratio of propane to ethane concentrations along with the data from the urban measurements, such as Tokyo and Sydney. Compared to these urban data sets, Cheju shows a range of ratios smaller than those of the urban site and this indicates a strong role for chemical destruction during the long range transport process. The data is combined with supporting data on aerosol and meteorology to provide insightsmore » into the behavior of the abundance, composition, source distribution and long range transport processes of trace species in this region.« less
This paper summarizes the atmospheric cycles of carbon dioxide, methane, halocarbons and nitrous oxide. The emission sources and rates of change in the concentration of thee radiatively active trace gases are discussed.