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Methyl iodide (CH<sub>3</sub>I), bromoform (CHBr<sub>3</sub>) and dibromomethane (CH<sub>2</sub>Br<sub>2</sub>), which are produced naturally in the oceans, take part in ozone chemistry both in the troposphere and the stratosphere. The significance of oceanic upwelling regions for emissions of these trace gases in the global context is still uncertain although they have been identified as important source regions. To better quantify the role of upwelling areas in current and future climate, this paper analyzes major factors that influenced halocarbon emissions from the tropical North East Atlantic including the Mauritanian upwelling during the DRIVE expedition. Diel and regional variability of oceanic and atmospheric CH<sub>3</sub>I, CHBr<sub>3</sub> and CH<sub>2</sub>Br<sub>2</sub> was determined along with biological and physical parameters at six 24 h-stations. Low oceanic concentrations of CH<sub>3</sub>I from 0.1–5.4 pmol L<sup>−1</sup> were equally distributed throughout the investigation area. CHBr<sub>3</sub> and CH<sub>2</sub>Br<sub>2</sub> from 1.0 to 42.4 pmol L<sup>−1</sup> and to 9.4 pmol L<sup>−1</sup>, respectively were measured with maximum concentrations close to the Mauritanian coast. Atmospheric CH<sub>3</sub>I, CHBr<sub>3</sub>, and CH<sub>2</sub>Br<sub>2</sub> of up to 3.3, 8.9, and 3.1 ppt, respectively were detected above the upwelling, as well as up to 1.8, 12.8, and 2.2 ppt at the Cape Verdean coast. While diel variability in CH<sub>3</sub>I emissions could be mainly ascribed to oceanic non-biological production, no main driver was identified for its emissions over the entire study region. In contrast, biological parameters showed the greatest influence on the regional distribution of sea-to-air fluxes of bromocarbons. The diel impact of wind speed on bromocarbon emissions increased with decreasing distance to the coast. The height of the marine atmospheric boundary layer (MABL) influenced halocarbon emissions via its influence on atmospheric mixing ratios. Oceanic and atmospheric halocarbons correlated well in the study region, and in combination with high oceanic CH<sub>3</sub>I, CHBr<sub>3</sub> and CH<sub>2</sub>Br<sub>2</sub> concentrations, local hot spots of atmospheric halocarbons could solely be explained by marine sources. This conclusion is in contrast to previous studies that hypothesized elevated atmospheric halocarbons above the eastern tropical Atlantic to be mainly originated from the West-African continent.
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The hydroxyl radical oxidation of α-pinene under high NO<sub>x</sub> conditions was studied in a photochemical reaction chamber to investigate organic nitrate (RONO<sub>2</sub>) production and partitioning between the gas and particle phases. We report an organic nitrate yield of 26 ± 7% from the oxidation of this monoterpene in the presence of nitric oxide (NO). However, the organic nitrate yield was found to be highly dependent on both chamber relative humidity (RH) and seed aerosol acidity, likely as a result of particle phase hydrolysis. The particle phase loss of organic nitrates perturbs the gas-particle equilibrium within the system, leading to decreased RONO<sub>2</sub> yields in both the gas and particle phases at elevated RH and an apparent non-equilibrium partitioning mechanism. This resulted in smaller apparent partition coefficients of the total organic nitrate species under high chamber RH. The hydrolysis of particle phase organic nitrates at low chamber relative humidity in this study implies that aerosol partitioning of organic nitrates may be an important sink for atmospheric NO<sub>x</sub> and may have a significant impact on regional air quality.
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Mercury is a contaminant of global concern. It is transported in the atmosphere primarily as gaseous elemental mercury, but its reactivity and deposition to the surface environment, through which it enters the aquatic food chain, is greatly enhanced following oxidation. Measurements and modelling studies of oxidised mercury in the polar to sub-tropical marine boundary layer (MBL) have suggested that photolytically produced bromine atoms are the primary oxidant of mercury. We report year-round measurements of elemental and oxidised mercury, along with ozone, halogen oxides (IO and BrO) and nitrogen oxides (NO<sub>2</sub>), in the MBL over the Galápagos Islands in the equatorial Pacific. Elemental mercury concentration remained low throughout the year, while higher than expected levels of oxidised mercury occurred around midday. Our results show that the production of oxidised mercury in the tropical MBL cannot be accounted for by bromine oxidation only, or by the inclusion of ozone and hydroxyl. As a two-step oxidation mechanism, where the HgBr intermediate is further oxidised to Hg(II), depends critically on the stability of HgBr, an additional oxidant is needed to react with HgBr to explain more than 50% of the observed oxidised mercury. Based on best available thermodynamic data, we show that atomic iodine, NO<sub>2</sub>, or HO<sub>2</sub> could all play the potential role of the missing oxidant, though their relative importance cannot be determined explicitly at this time due to the uncertainties associated with mercury oxidation kinetics. We conclude that the key pathway that significantly enhances atmospheric mercury oxidation and deposition to the tropical oceans is missing from the current understanding of atmospheric mercury oxidation.
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The RONOCO (ROle of Nighttime chemistry in controlling the Oxidising Capacity of the AtmOsphere) aircraft campaign during July 2010 and January 2011 made observations of OH, HO<sub>2</sub>, NO<sub>3</sub>, N<sub>2</sub>O<sub>5</sub> and a number of supporting measurements at night over the UK, and reflects the first simultaneous airborne measurements of these species. We compare the observed concentrations of these short-lived species with those calculated by a box model constrained by the concentrations of the longer lived species using a detailed chemical scheme. OH concentrations were below the limit of detection, consistent with model predictions. The model systematically underpredicts HO<sub>2</sub> by ~200% and overpredicts NO<sub>3</sub> and N<sub>2</sub>O<sub>5</sub> by around 80 and 50%, respectively. Cycling between NO<sub>3</sub> and N<sub>2</sub>O<sub>5</sub> is fast and thus we define the NO<sub>3x</sub> (NO<sub>3x</sub>=NO<sub>3</sub>+N<sub>2</sub>O<sub>5</sub>) family. Production of NO<sub>3x</sub> is overwhelmingly dominated by the reaction of NO<sub>2</sub> with O<sub>3</sub>, whereas its loss is dominated by aerosol uptake of N<sub>2</sub>O<sub>5</sub>, with NO<sub>3</sub>+VOCs (volatile organic compounds) and NO<sub>3</sub>+RO<sub>2</sub> playing smaller roles. The production of HO<sub>x</sub> and RO<sub>x</sub> radicals is mainly due to the reaction of NO<sub>3</sub> with VOCs. The loss of these radicals occurs through a combination of HO<sub>2</sub>+RO<sub>2</sub> reactions, heterogeneous processes and production of HNO<sub>3</sub> from OH+NO<sub>2</sub>, with radical propagation primarily achieved through reactions of NO<sub>3</sub> with peroxy radicals. Thus NO<sub>3</sub> at night plays a similar role to both OH and NO during the day in that it both initiates RO<sub>x</sub> radical production and acts to propagate the tropospheric oxidation chain. Model sensitivity to the N<sub>2</sub>O<sub>5</sub> aerosol uptake coefficient (γ<sub>N<sub>2</sub>O<sub>5</sub></sub>) is discussed and we find that a value of γ<sub>N<sub>2</sub>O<sub>5</sub></sub>=0.05 improves model simulations for NO<sub>3</sub> and N<sub>2</sub>O<sub>5</sub>, but that these improvements are at the expense of model success for HO<sub>2</sub>. Improvements to model simulations for HO<sub>2</sub>, NO<sub>3</sub> and N<sub>2</sub>O<sub>5</sub> can be realised simultaneously on inclusion of additional unsaturated volatile organic compounds, however the nature of these compounds is extremely uncertain.
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Emissions factors (EFs) for gas and sub-micron particle-phase species were measured in intercepted plumes as a function of vessel speed from an underway research vessel, the NOAA ship <i>Miller Freeman</i>, operating a medium-speed diesel engine on low-sulfur marine gas oil (fuel sulfur content ~0.1% by weight). The low-sulfur fuel in use conforms to the MARPOL fuel sulfur limit within emission control areas set to take effect in 2015 and to California-specific limits set to take effect in 2014. For many of the particle-phase species, EFs were determined using multiple measurement methodologies, allowing for an assessment of how well EFs from different techniques agree. The total sub-micron PM (PM<sub>1</sub>) was dominated by particulate black carbon (BC) and particulate organic matter (POM), with an average POM / BC ratio of 1.3. Consideration of the POM / BC ratios observed here with literature studies suggests that laboratory and in-stack measurement methods may overestimate primary POM EFs relative to those observed in emitted plumes. Comparison of four different methods for black carbon measurement indicates that careful attention must be paid to instrument limitations and biases when assessing EF</sub>BC</sub>. Particulate sulfate (SO<sub>4</sub><sup>2−</sup>) EFs were extremely small and the particles emitted by <i>Miller Freeman</i> were inefficient as cloud condensation nuclei (CCN), even at high super saturations, consistent with the use of very low-sulfur fuel and the overall small emitted particle sizes. All measurement methodologies consistently demonstrate that the measured EFs (fuel mass basis) for PM<sub>1</sub> mass, BC and POM decreased as the ship slowed. Particle number EFs were approximately constant across the speed change, with a shift towards smaller particles being emitted at slower speeds. Emissions factors for gas-phase CO and formaldehyde (HCHO) both increased as the vessel slowed, while EFs for NO<sub>x</sub> decreased and SO<sub>2</sub> EFs were approximately constant.
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As precursors to tropospheric ozone and nitrate, nitrogen oxide (NO<sub>x</sub>) in the present atmosphere and its transformation in response to emission and climate perturbations are studied by using the CAM-Chem model and air quality measurements from the National Emissions Inventory (NEI), Clean Air Status and Trends Network (CASTNET), and Environmental Protection Agency Air Quality System (EPA AQS). It is found that NO<sub>x</sub> transformations in present atmospheric conditions show different sensitivities over industrial and non-industrial regions. As a result, the surface ozone and nitrate formations can be divided into several regimes associated with the dominant emission types and relative levels of NO<sub>x</sub> and volatile organic compounds (VOC). Ozone production in industrial regions (the main NO<sub>x</sub> emission source areas) increases in warmer conditions and slightly decreases following an increase in NO<sub>x</sub> emissions due to NO<sub>x</sub> titration, which is opposite to the response in non-industrial regions. The ozone decrease following a temperature increase in non-industrial regions indicates that ozone production in regions that lack NO<sub>x</sub> emission sources may be sensitive to NO<sub>x</sub> transformation in remote source regions. The increase in NO<sub>2</sub> from NO<sub>x</sub> titration over industrial regions results in an increase rate of total nitrate that remains higher than the increase rate of NO<sub>x</sub> emissions. The presented findings indicate that a change in the ozone concentration is more directly affected by changes in climate and precursor emissions, while a change in the nitrate concentration is affected by local ozone production types and their seasonal transfer. The sensitivity to temperature perturbations shows that a warmer climate accelerates the decomposition of odd nitrogen (NO<sub>y</sub>) during the night. As a result, the transformation rate of NO<sub>x</sub> to nitrate decreases. Examinations of the historical emissions and air quality records of a typical NO<sub>x</sub>-limited area, such as Atlanta and a VOC-limited area, such as Los Angeles further confirm the conclusions drawn from the modeling experiments.
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Motivated by the potential for reactive heterogeneous chemistry occurring at the ocean surface, gas-phase products were observed when a reactive sea surface microlayer (SML) component, i.e. the polyunsaturated fatty acids (PUFA) linoleic acid (LA), was exposed to gas-phase ozone at the air–seawater interface. Similar oxidation experiments were conducted with SML samples collected from two different oceanic locations, in the eastern equatorial Pacific Ocean and from the west coast of Canada. Online proton-transfer-reaction mass spectrometry (PTR-MS) University of Colorado light-emitting diode cavity-enhanced differential optical absorption spectroscopy (LED-CE-DOAS) were used to detect oxygenated gas-phase products from the ozonolysis reactions. The LA studies indicate that oxidation of a PUFA monolayer on seawater gives rise to prompt and efficient formation of gas-phase aldehydes. The products are formed via the decomposition of primary ozonides which form upon the initial reaction of ozone with the carbon–carbon double bonds in the PUFA molecules. In addition, two highly reactive dicarbonyls, malondialdehyde (MDA) and glyoxal, were also generated, likely as secondary products. Specific yields relative to reactant loss were 78%, 29%, 4% and < 1% for n-hexanal, 3-nonenal, MDA and glyoxal, respectively, where the yields for MDA and glyoxal are likely lower limits. Heterogeneous oxidation of SML samples confirm for the first time that similar carbonyl products are formed via ozonolysis of environmental samples.
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We present a top-down ship NO<sub>x</sub> emission inventory for the Baltic Sea, the North Sea, the Bay of Biscay and the Mediterranean Sea based on satellite-observed tropospheric NO<sub>2</sub> columns of the Ozone Monitoring Instrument (OMI) for 2005–2006. We improved the representation of ship emissions in the GEOS-Chem chemistry transport model, and compared simulated NO<sub>2</sub> columns to consistent satellite observations. Relative differences between simulated and observed NO<sub>2</sub> columns have been used to constrain ship emissions in four European seas (the Baltic Sea, the North Sea, the Bay of Biscay and the Mediterranean Sea) using a mass-balance approach, and accounting for non-linear sensitivities to changing emissions in both model and satellite retrieval. These constraints are applied to 39 % of total top-down European ship NO<sub>x</sub> emissions, which amount to 0.96 Tg N for 2005, and 1.0 Tg N for 2006 (11–15% lower than the bottom-up EMEP ship emission inventory). Our results indicate that EMEP emissions in the Mediterranean Sea are too high (by 60%) and misplaced by up to 150 km, which can have important consequences for local air quality simulations. In the North Sea ship track, our top-down emissions amount to 0.05 Tg N for 2005 (35% lower than EMEP). Increased top-down emissions were found for the Baltic Sea and the Bay of Biscay ship tracks, with totals in these tracks of 0.05 Tg N (131% higher than EMEP) and 0.08 Tg N for 2005 (128% higher than EMEP), respectively. Our study explicitly accounts for the (non-linear) sensitivity of satellite retrievals to changes in the a priori NO<sub>2</sub> profiles, as satellite observations are never fully independent of model information (i.e. assumptions on vertical NO<sub>2</sub> profiles). Our study provides for the first time a space-based, top-down ship NO<sub>x</sub> emission inventory, and can serve as a framework for future studies to constrain ship emissions using satellite NO<sub>2</sub> observations in other seas.
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The MEGAPOLI (Megacities: Emissions, urban, regional and Global Atmospheric POLlution and climate effects, and Integrated tools for assessment and mitigation) experiment took place in July 2009. The aim of this campaign was to study the aging and reactions of aerosol and gas-phase emissions in the city of Paris. Three ground-based measurement sites and several mobile platforms including instrument equipped vehicles and the ATR-42 aircraft were involved. We present here the variations in particle- and gas-phase species over the city of Paris, using a combination of high-time resolution measurements aboard the ATR-42 aircraft. Particle chemical composition was measured using a compact time-of-flight aerosol mass spectrometer (C-ToF-AMS), giving detailed information on the non-refractory submicron aerosol species. The mass concentration of black carbon (BC), measured by a particle absorption soot photometer (PSAP), was used as a marker to identify the urban pollution plume boundaries. Aerosol mass concentrations and composition were affected by air-mass history, with air masses that spent longest time over land having highest fractions of organic aerosol and higher total mass concentrations. The Paris plume is mainly composed of organic aerosol (OA), BC, and nitrate aerosol, as well as high concentrations of anthropogenic gas-phase species such as toluene, benzene, and NO<sub>x</sub>. Using BC and CO as tracers for air-mass dilution, we observe the ratio of ΔOA / ΔBC and ΔOA / ΔCO increase with increasing photochemical age (−log(NO<sub>x</sub> / NO<sub>y</sub>)). Plotting the equivalent ratios of different organic aerosol species (LV-OOA, SV-OOA, and HOA) illustrate that the increase in OA is a result of secondary organic aerosol (SOA) formation. Within Paris the changes in the ΔOA / ΔCO are similar to those observed during other studies in London, Mexico City, and in New England, USA. Using the measured SOA volatile organic compounds (VOCs) species together with organic aerosol formation yields, we were able to predict ~50% of the measured organics. These airborne measurements during the MEGAPOLI experiment show that urban emissions contribute to the formation of OA and have an impact on aerosol composition on a regional scale.
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Retrievals of tropospheric nitrogen dioxide (NO<sub>2</sub>) from the Ozone Monitoring Instrument (OMI) are subject to errors in the treatments of aerosols, surface reflectance anisotropy, and vertical profile of NO<sub>2</sub>. Here we quantify the influences over China via an improved retrieval process. We explicitly account for aerosol optical effects (simulated by nested GEOS-Chem at 0.667° long. × 0.5° lat. and constrained by aerosol measurements), surface reflectance anisotropy, and high-resolution vertical profiles of NO<sub>2</sub> (simulated by GEOS-Chem). Prior to the NO<sub>2</sub> retrieval, we derive the cloud information using consistent ancillary assumptions. <br><br> We compare our retrieval to the widely used DOMINO v2 product, using MAX-DOAS measurements at three urban/suburban sites in East China as reference and focusing the analysis on the 127 OMI pixels (in 30 days) closest to the MAX-DOAS sites. We find that our retrieval reduces the interference of aerosols on the retrieved cloud properties, thus enhancing the number of valid OMI pixels by about 25%. Compared to DOMINO v2, our retrieval better captures the day-to-day variability in MAX-DOAS NO<sub>2</sub> data (<i>R</i><sup>2</sup> = 0.96 versus 0.72), due to pixel-specific radiative transfer calculations rather than the use of a look-up table, explicit inclusion of aerosols, and consideration of surface reflectance anisotropy. Our retrieved NO<sub>2</sub> columns are 54% of the MAX-DOAS data on average, reflecting the inevitable spatial inconsistency between the two types of measurement, errors in MAX-DOAS data, and uncertainties in our OMI retrieval related to aerosols and vertical profile of NO<sub>2</sub>. <br><br> Sensitivity tests show that excluding aerosol optical effects can either increase or decrease the retrieved NO<sub>2</sub> for individual OMI pixels with an average increase by 14%. Excluding aerosols also complexly affects the retrievals of cloud fraction and particularly cloud pressure. Employing various surface albedo data sets slightly affects the retrieved NO<sub>2</sub> on average (within 10%). The retrieved NO<sub>2</sub> columns increase when the NO<sub>2</sub> profiles are taken from MAX-DOAS retrievals (by 19% on average) or TM4 simulations (by 13%) instead of GEOS-Chem simulations. Our findings are also relevant to retrievals of other pollutants (e.g., sulfur dioxide, ormaldehyde, glyoxal) from UV–visible backscatter satellite instruments.