Alexandros Milousis’s scientific contributions

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Publications (6)


Figure 4: (a) Average surface concentrations of PM2.5 NO3 -for the period of 2008 -2018 as 428 simulated by EMAC from the base case. White areas indicate average concentrations smaller than 429 0.25 µg/m 3 . Percentage changes of the EMAC-simulated average surface concentrations of PM2.5 430 NO3 -between the base case model run and the (b) 'THERM' case (c) 'RES_low' case, (d) 431 'RES_high' case, (e) 'CMIP' case, (f) 'HTAP' case, (g) 'HYDRO' case and (h) 'SCAV' case 432 model runs. Negative values in red indicate higher concentrations by the respective sensitivity case 433 and positive values in blue indicate the opposite. 434
Statistical evaluation of EMAC simulated PM1 NO3 -surface concentrations from the base 410 case against observations during 2010-2018. The used metrics include the Mean Absolute Gross 411 Error (MAGE), Mean Bias (MB), Normalized Mean Error (NME), Normalized Mean Bias (NMB) 412 and Root Mean Square Error (RMSE). 413
Global Perspectives on Nitrate Aerosol Dynamics: A Comprehensive Sensitivity Analysis
  • Preprint
  • File available

February 2025

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7 Reads

Alexandros Milousis

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Susanne M. C. Scholz

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Hendrik Fuchs

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[...]

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In recent years, nitrate aerosols have emerged as a dominant component of atmospheric composition, surpassing sulfate aerosols in both concentration and climatic impact. However, accurately simulating nitrate aerosols remains a significant challenge for global atmospheric models due to the complexity of their formation and regional variability. This study investigates key factors influencing nitrate aerosol formation to improve simulation accuracy in highly polluted regions. Using the advanced EMAC climate and chemistry model, we assess the effects of grid resolution, emission inventories, and thermodynamic, chemical, and aerosol scavenging processes. The ISORROPIA II thermodynamic model is employed to simulate the formation of inorganic aerosols. Model predictions are compared with surface observations of particulate nitrate in PM1 and PM2.5 size fractions, including PM2.5 data from filter-based observational networks and PM1 data from aerosol mass spectrometer field campaigns across Europe, North America, East Asia, and India. Results show that the model overestimates PM2.5 nitrate concentrations, especially in East Asia, with biases up to a factor of three. Increasing grid resolution, adjusting N2O5 hydrolysis uptake coefficient, and utilizing an appropriate emission database (e.g., CMIP6) improve performance. However, these adjustments do not necessarily enhance PM1 predictions, which remain underestimated, especially in urban downwind sites. Seasonal variations and diurnal trends reveal discrepancies in model performance, especially in Europe and urban downwind locations. In Europe, model bias is driven by an unrealistically sharp decrease in nitrate aerosol levels from morning maxima to evening minima. Sensitivity tests show relatively small impact on total tropospheric nitrate burden, with variations within 25 %.

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Impact of mineral dust on the global nitrate aerosol direct and indirect radiative effect

January 2025

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91 Reads

Nitrate (NO3-) aerosol is projected to increase dramatically in the coming decades and may become the dominant inorganic particle species. This is due to the continued strong decrease in SO2 emissions, which is not accompanied by a corresponding decrease in NOx and especially NH3 emissions. Thus, the radiative effect (RE) of NO3- aerosol may become more important than that of SO42- aerosol in the future. The physicochemical interactions of mineral dust particles with gas and aerosol tracers play an important role in influencing the overall RE of dust and non-dust aerosols but can be a major source of uncertainty due to their lack of representation in many global climate models. Therefore, this study investigates how and to what extent dust affects the current global NO3- aerosol radiative effect through both radiation (REari) and cloud interactions (REaci) at the top of the atmosphere (TOA). For this purpose, multiyear simulations nudged towards the observed atmospheric circulation were performed with the global atmospheric chemistry and climate model EMAC, while the thermodynamics of the interactions between inorganic aerosols and mineral dust were simulated with the thermodynamic equilibrium model ISORROPIA-lite. The emission flux of the mineral cations Na⁺, Ca²⁺, K⁺, and Mg²⁺ is calculated as a fraction of the total aeolian dust emission based on the unique chemical composition of the major deserts worldwide. Our results reveal positive and negative shortwave and longwave radiative effects in different regions of the world via aerosol–radiation interactions and cloud adjustments. Overall, the NO3- aerosol direct effect contributes a global cooling of -0.11 W m⁻², driven by fine-mode particle cooling at short wavelengths. Regarding the indirect effect, it is noteworthy that NO3- aerosol exerts a global mean warming of +0.17 W m⁻². While the presence of NO3- aerosol enhances the ability of mineral dust particles to act as cloud condensation nuclei (CCN), it simultaneously inhibits the formation of cloud droplets from the smaller anthropogenic particles. This is due to the coagulation of fine anthropogenic CCN particles with the larger nitrate-coated mineral dust particles, which leads to a reduction in total aerosol number concentration. This mechanism results in an overall reduced cloud albedo effect and is thus attributed as warming.


Aerosol Composition Trends during 2000–2020: In depth insights from model predictions and multiple worldwide observation datasets

December 2024

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56 Reads

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1 Citation

Atmospheric aerosols significantly impact Earth’s climate and air quality. In addition to their number and mass concentrations, their chemical composition influences their environmental and health effects. This study examines global trends in aerosol composition from 2000 to 2020, using the EMAC atmospheric chemistry-climate model and a variety of observational datasets. These include PM2.5 data from regional networks and 744 PM1 datasets from AMS field campaigns conducted at 169 sites worldwide. Results show that organic aerosol (OA) is the dominant fine aerosol component in all continental regions, particularly in areas with significant biomass burning and biogenic VOC emissions. EMAC effectively reproduces the prevalence of secondary OA but underestimates the aging of OA in some cases, revealing uncertainties in distinguishing fresh and aged SOA. While sulfate is a major aerosol component in filter-based observations, AMS and model results indicate nitrate predominates in Europe and Eastern Asia. Mineral dust also plays a critical role in specific regions, as highlighted by EMAC. The study identifies substantial declines in sulfate, nitrate, and ammonium concentrations in Europe and North America, attributed to emission controls, with varying accuracy in model predictions. In Eastern Asia, sulfate reductions due to SO2 controls are partially captured by the model. OA trends differ between methodologies, with filter data showing slight decreases, while AMS data and model simulations suggest slight increases in PM1 OA across Europe, North America, and Eastern Asia. This research underscores the need for integrating advanced models and diverse datasets to better understand aerosol trends and guide environmental policy.


Figure 1: Conceptual illustration of how dust-nitrate interactions affect the total NO3 -(left) REari and 240 (right) REaci. a) In dust-rich environments, nitric acid transported from anthropogenic pollution and biomass 241 burning regions interacts with mineral cations to form a soluble coating on the surface of dust particles. The 242 dominant effect of these interactions is an enhanced LW absorption (warming REari) by the coarse dust 243 particles. b.) In nitrate-rich environments, the intrusion of dust particles and their subsequent interaction 244 with freshly emitted nitric acid leads to an overall increase in aerosol hygroscopicity and thus a stronger 245 SW reflection (cooling REari). c.) In dust-rich environments, the number of ice crystals in cirrus clouds is 246 reduced while their size is increased due to the interaction of dust particles with the transported HNO3. This 247 results in an optical thinning of the ice clouds, which leads to less trapping of outgoing LW radiation 248 (cooling REaci). d.) In nitrate-rich environments, the increased wet radius of aged dust particles leads to 249 enhanced coagulation with smaller particles, resulting in a decrease in the number of smaller aerosols and, 250 in turn, a decrease in the number of activated particles in cloud droplets by smaller aerosols, which 251 ultimately leads to a reduction in the backscattering of SW radiation by warm clouds (warming REari). 252
Impact of mineral dust on the global nitrate aerosol direct and indirect radiative effect

July 2024

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156 Reads

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1 Citation

Nitrate (NO3-) aerosol is projected to increase dramatically in the coming decades and may become the dominant inorganic particle species. This is due to the continued strong decrease in SO2 emissions, which is not accompanied by a corresponding decrease in NOx and especially NH3 emissions. Thus, the radiative effect (RE) of NO3- aerosol may become more important than that of SO42- aerosol in the future. The physicochemical interactions of mineral dust particles with gas and aerosol tracers play an important role in influencing the overall RE of dust and non-dust aerosols but can be a major source of uncertainty due to their lack of representation in many global climate models. Therefore, this study investigates how and to what extent dust affects the current global NO3- aerosol radiative effect through both radiation (REari) and cloud interactions (REaci) at the top of the atmosphere (TOA). For this purpose, multi-year simulations nudged towards the observed atmospheric circulation were performed with the global atmospheric chemistry and climate model EMAC, while the thermodynamics of the interactions between inorganic aerosols and mineral dust were simulated with the thermodynamic equilibrium model ISORROPIA-lite. The emission flux of the mineral cations Na+, Ca2+, K+ and Mg2+ is calculated as a fraction of the total aeolian dust emission based on the unique chemical composition of the major deserts worldwide. Our results reveal positive and negative shortwave and longwave radiative effects in different regions of the world via aerosol-radiation interactions and cloud adjustments. Overall, the NO3- aerosol direct effect contributes a global cooling of -0.11 W/m2, driven by coarse-mode particle cooling at short wavelengths. Regarding the indirect effect, it is noteworthy that NO3- aerosol exerts a global mean warming of +0.17 W/m2. While the presence of NO3- aerosol enhances the ability of mineral dust particles to act as cloud condensation nuclei (CCN), it simultaneously inhibits the formation of cloud droplets from the smaller anthropogenic particles. This is due to the coagulation of fine anthropogenic CCN particles with the larger nitrate-coated mineral dust particles, which leads to a reduction in total aerosol number concentration. This mechanism results in an overall reduced cloud albedo effect and is thus attributed as warming.


Implementation of the ISORROPIA-lite aerosol thermodynamics model into the EMAC chemistry climate model (based on MESSy v2.55): implications for aerosol composition and acidity

February 2024

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78 Reads

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5 Citations

This study explores the differences in performance and results by various versions of the ISORROPIA thermodynamic module implemented within the ECHAM/MESSy Atmospheric Chemistry (EMAC) model. Three different versions of the module were used, ISORROPIA II v1, ISORROPIA II v2.3, and ISORROPIA-lite. First, ISORROPIA II v2.3 replaced ISORROPIA II v1 in EMAC to improve pH predictions close to neutral conditions. The newly developed ISORROPIA-lite has been added to EMAC alongside ISORROPIA II v2.3. ISORROPIA-lite is more computationally efficient and assumes that atmospheric aerosols exist always as supersaturated aqueous (metastable) solutions, while ISORROPIA II includes the option to allow for the formation of solid salts at low RH conditions (stable state). The predictions of EMAC by employing all three aerosol thermodynamic models were compared to each other and evaluated against surface measurements from three regional observational networks in the polluted Northern Hemisphere (Interagency Monitoring of Protected Visual Environments (IMPROVE), European Monitoring and Evaluation Programme (EMEP), and Acid Deposition Monitoring Network of East Asia (EANET)). The differences between ISORROPIA II v2.3 and ISORROPIA-lite were minimal in all comparisons with the normalized mean absolute difference for the concentrations of all major aerosol components being less than 11 % even when different phase state assumptions were used. The most notable differences were lower aerosol concentrations predicted by ISORROPIA-lite in regions with relative humidity in the range of 20 % to 60 % compared to the predictions of ISORROPIA II v2.3 in stable mode. The comparison against observations yielded satisfactory agreement especially over the USA and Europe but higher deviations over East Asia, where the overprediction of EMAC for nitrate was as high as 4 µg m-3 (∼20%). The mean annual aerosol pH predicted by ISORROPIA-lite was on average less than a unit lower than ISORROPIA II v2.3 in stable mode, mainly for coarse-mode aerosols over the Middle East. The use of ISORROPIA-lite accelerated EMAC by nearly 5 % compared to the use of ISORROPIA II v2.3 even if the aerosol thermodynamic calculations consume a relatively small fraction of the EMAC computational time. ISORROPIA-lite can therefore be a reliable and computationally efficient alternative to the previous thermodynamic module in EMAC.


Figure 2 : Bar chart plots depicting the 25 th , 50 th and 75 th percentiles (box) of the i) difference and ii) fractional difference in global daily mean surface concentrations of aerosol water (left y-axis), mineral ions, 300 NH4 + and SO4 2-in TSP as well as coarse and fine aerosol NO3 -(right y-axis) , as predicted by EMAC using ISORROPIA-lite and ISORROPIA II. The 10th and 90th percentiles (whiskers) for each aerosol component are also shown. Both models assume that the aerosol is at its metastable state at low RH and a positive change corresponds to higher concentrations by ISORROPIA-lite.
Figure 6 : Bar chart plots depicting the 25 th , 50 th and 75 th percentiles (box) of the i) difference and ii) fractional difference in global daily mean surface concentrations of aerosol water (left y-axis), mineral ions, NH4 + and SO4 2-in TSP as well as coarse and fine aerosol NO3 -(right y-axis) , as predicted by EMAC using ISORROPIA-lite and ISORROPIA II. The models assume different aerosol states at low RH and a positive 600 change corresponds to higher concentrations by ISORROPIA-lite.
Statistical evaluation of EMAC predicted surface concentrations of PM2.5 NO3 -using ISORROPIA-lite against observations during 2010.
Implementation of the ISORROPIA-lite Aerosol Thermodynamics Model into the EMAC Chemistry Climate Model 2.56: Implications for Aerosol Composition and Acidity

September 2023

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144 Reads

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1 Citation

This study explores the differences in performance and results by various versions of the ISORROPIA thermodynamic module implemented within the global atmospheric chemistry model EMAC. Three different versions of the module were used, ISORROPIA II v1, ISORROPIA II v2.3, and ISORROPIA-lite. First, ISORROPIA II v2.3 replaced ISORROPIA II v1 in EMAC to improve pH predictions close to neutral conditions. The newly developed ISORROPIA-lite has been added to EMAC alongside ISORROPIA II v2.3. ISORROPIA-lite is more computationally efficient and assumes that atmospheric aerosols exist always as supersaturated aqueous (metastable) solutions while ISORROPIA II includes the option to allow the formation of solid salts at low RH conditions (stable state). The predictions of EMAC by employing all three aerosol thermodynamic models were compared to each other and evaluated against surface measurements from three regional observational networks (IMPROVE, EMEP, EANET) in the polluted Northern Hemisphere. The differences between ISORROPIA II v2.3 and ISORROPIA-lite were minimal in all comparisons with the normalized mean absolute difference for the concentrations of all major aerosol components being less than 10 % even when different phase state assumptions were used. The most notable differences were lower aerosol concentrations predicted by ISORROPIA-lite in regions with relative humidity in the range of 20 % to 60 % compared to the predictions of ISORROPIA II v2.3 in stable mode. The comparison against observations yielded satisfactory agreement especially over the US and Europe, but higher deviations over East Asia, where the overprediction of EMAC for nitrate was as high as 4 μg m-3 (~ 20 %). The mean annual aerosol pH predicted by ISORROPIA-lite was on average less than a unit lower than ISORROPIA II v2.3 in stable mode, mainly for coarse mode aerosols over Middle East. The use of ISORROPIA-lite accelerated EMAC by 5 % compared to the use of ISORROPIA II v2.3 even if the aerosol thermodynamic calculations consume a relatively small fraction of the EMAC computational time. ISORROPIA-lite can therefore be a reliable and computationally effective replacement of the previous thermodynamic module in EMAC.

Citations (1)


... Overall, the OOA contribution range from 19% 339 (urban minimum) to 99% (rural maximum). The extreme shares were both found during computational speed of the model by 4% (Milousis et al., 2024). The assumption of 474 thermodynamic equilibrium is a good approximation for fine mode aerosols which can 475 reach equilibrium within the time frame of one model timestep. ...

Reference:

Aerosol Composition Trends during 2000–2020: In depth insights from model predictions and multiple worldwide observation datasets
Implementation of the ISORROPIA-lite aerosol thermodynamics model into the EMAC chemistry climate model (based on MESSy v2.55): implications for aerosol composition and acidity