Imad El Haddad’s research while affiliated with Paul Scherrer Institute and other places

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Publications (250)


Apolitical Science
  • Article

April 2025

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192 Reads

Environmental Science and Technology

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Gregory Lowry

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Fernando Rosario-Ortiz

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Fig. 1 Adopted model's domains. d1 to d4 indicates domains at 27, 9, 3, and 1 km resolution, respectively. The red and blue lines are the western and eastern valley ridges along the Khumbu valley, respectively. The black line follows the Khumbu valley floor profile all the way from the NCO-P observational site to the Tibetan Plateau.
Fig. 2 (a) Modelled 400 hPa geopotential height (m), (b) along-valley winds, (c) crossvalley winds (m s −1 ) with overlapped potential temperature (K). (d) Wind roses of model and observations data obtained from the Namche stations. All data as 9-15 local time averages. Results are shown for the inner domain at 1 km resolution.
Fig. 3 (a) Average a-pinene emissions over the inner resolution domain (1 km) and (b) along the latitudinal (B-B) and (c) longitudinal (A-A) sections of the Khumbu valley. Dots along the profiles indicate the location and intensity of the emissions (g m −2 s −1 ). The dependence of the a-pinene emission on the latitudinal section is additionally reported as scatter plots, and colour coded by the temperature (K) in the lower right panel, (d). Data have been averaged between the 17th and 21st of December 2014.
Fig. 4 Upper-panel: modelled particle number size distribution. 17th of December on the left (a), and 18th of December on the right (b). Lower-panel: a-pinene biogenic emissions at the A-A section (blue line) colour coded by short-wave radiation (W m −2 ), ULVOCs concentrations (molecules per cm 3 ), J 1.7 nucleation rate (particles per cm 3 per s) colour coded by condensational sink (molecules per s), and wind direction in black arrow. 17th of December on the left (c), and 18th of December on the right (b).
Fig. 5 Condensational sink (molecules per s) at (a) 9 and (b) 13 local time of the 18th of December 2014 along the latitudinal section of the Khumbu valley.

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The impact of the Himalayan aerosol factory: results from high resolution numerical modelling of pure biogenic nucleation over the Himalayan valleys
  • Article
  • Full-text available

March 2025

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20 Reads

Faraday Discussions

A schematic of the “Himalayan aerosol factory”. Courtesy of Sole Lätti (https://kuvittajat.fi/).

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Apparent HOM yields and fraction of nitrogen-containing HOMs
a, ξHOMs from different precursors as a function of OH concentration. b, Ratio of nitrogen-containing HOMs (N-HOMs) to total HOMs as a function of NO. Toluene, 1,2,4-trimethylbenzene and naphthalene are marked by circles, triangles and diamonds, respectively. The colours of the symbols present average NO and OH concentrations in a and b, respectively. Yield data are from different VOC and NOx injections as well as different light settings. which produced different OH levels (Supplementary Table 13).
An example experiment of OH-initiated toluene oxidation in the presence of NO
a, OH (black line, left axis) and NO (blue line, right axis) concentrations of the experiment on 8 November 2016. b, Measured time series of C7H8O8 (green dots) and C7H10O8 (purple dots). Lines represent modelled time evolutions of first-generation (green) and second-generation (purple) oxidation products, assuming a wall-loss lifetime of 0.0014 s–1 for both products. c, Secondary aerosol mass closure in the CLOUD chamber. The coloured areas are modelled particle volumes based on gas-phase measurements using PTR3 and NO3-CIMS data. The red, dark green and light green areas are the modelled volume concentrations of sulfate, ELVOCs and LVOCs, respectively. The solid circles represent the particle volume based on the scanning mobility particle sizer (SMPS) measurements, highlighting the great model–measurement agreement. d, Growth rate contributions of (NH4)2SO4, first- and second-generation oxidation products for 15 nm particles. Sky blue circles show measured growth rates for 10 to 20 nm particles ± 95% fitting confidence interval using the appearance time method. Lavender area is potential growth rate contribution of SOA if first-generation oxidation products are not lost to the chamber walls (Supplementary Figs. 4 and 5).
2D VBS of oxidation products of toluene, trimethylbenzene and naphthalene
The background colours indicate the C* ranges of ELVOCs (grey), LVOCs (pink), SVOCs (green) and IVOCs (blue). G1 (green) and G2 (purple) oxidation products are plotted as carbon oxidation states (OSc¯\documentclass[12pt]{minimal} \usepackage{amsmath} \usepackage{wasysym} \usepackage{amsfonts} \usepackage{amssymb} \usepackage{amsbsy} \usepackage{mathrsfs} \usepackage{upgreek} \setlength{\oddsidemargin}{-69pt} \begin{document}$${\mathrm{O}}{\overline{{\mathrm{S}}_{\mathrm{c}}}}$$\end{document}) versus log10C* with marker areas proportional to their mass yields with NO. Coloured lines show the mean cumulative mass yields (right) of G1 (green) and G2 (purple) products with NO (dashed) or without NO (solid). Shaded areas show standard deviations of different chamber fillings or light conditions. Yields with NO are determined from experiments with NO concentration higher than 0.2 ppbv. OH concentrations are in the range of 0.8–8.7 × 10⁶ cm⁻³. Supplementary Tables 1–12 present the yields of individual compounds, associated standard deviations based on experimental variability, volatility and assignment to G1 versus G2 products.
Annual AOA concentration and fraction of second-generation SOA
a, Spatial distribution of yearly averaged AOA. b, Fraction of second-generation SOA (ASOA_2nd) to AOA. c, The population-density-weighted probability density function (PDF) of ASOA_2nd to AOA.
Comparison of oxidation products from chamber and ambient measurements
Kendrick mass defect of the aromatic oxidation products in ref. ¹² compared with those detected in our chamber at high NOX from the three precursors. Compounds in common with ref. ¹² are coloured according to the precursor and first or second generation. Compounds detected in ref. ¹² but not in our chamber are shown in grey.
Anthropogenic organic aerosol in Europe produced mainly through second-generation oxidation

March 2025

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181 Reads

Exposure to anthropogenic atmospheric aerosol is a major health issue, causing several million deaths per year worldwide. The oxidation of aromatic hydrocarbons from traffic and wood combustion is an important anthropogenic source of low-volatility species in secondary organic aerosol, especially in heavily polluted environments. It is not yet established whether the formation of anthropogenic secondary organic aerosol involves mainly rapid autoxidation, slower sequential oxidation steps or a combination of the two. Here we reproduced a typical urban haze in the ‘Cosmics Leaving Outdoor Droplets’ chamber at the European Organization for Nuclear Research and observed the dynamics of aromatic oxidation products during secondary organic aerosol growth on a molecular level to determine mechanisms underlying their production and removal. We demonstrate that sequential oxidation is required for substantial secondary organic aerosol formation. Second-generation oxidation decreases the products’ saturation vapour pressure by several orders of magnitude and increases the aromatic secondary organic aerosol yields from a few percent to a few tens of percent at typical atmospheric concentrations. Through regional modelling, we show that more than 70% of the exposure to anthropogenic organic aerosol in Europe arises from second-generation oxidation.


(a) Temporal profiles of mixing ratios measured by Vocus and the evolution of CO, CO2, AAE, f60, MCE, and key aerosol compositions during burning cycles of beech log stove burning. (b) Geometric mean of the primary EFs for gas-phase species of different functional groups during the flaming and smoldering phase (the flaming and smoldering were separated by the experimental record and calculated MCE). Error bars correspond to the sample geometric standard deviation of the replicates. The square represents the mixing ratio between smoldering and flaming. In this study, the MCE is used to indicate the flaming stage and smoldering, and a significant decrease in MAC and CO2 was observed from the flaming phase to the smoldering phase.
The correlation matrix of organic vapors measured with Vocus (F represents flaming phase, S represents smoldering phase, and unmarked columns and rows represent mixtures of both flaming and smoldering phases). Pie charts showing the contribution of elemental families are on the diagonal.
The average carbon distribution is colored by the H/C (a) and O/C (b) for non-N-containing species. The pie charts are the corresponding contribution of a range of H/C or O/C ratios.
Volatility and average accumulated EFs (assume the average molecular weight of each bin is same), with the distribution of primary emissions as a function of binned saturation vapor concentration. Shaded areas indicate the volatility ranges in units of µgm-3: VOCs (yellow) as log⁡10(C∗)> 6.5, IVOCs (blue) as log⁡10(C∗) between 6.5 to 2.5, semi-VOCs (SVOCs; green) as log⁡10(C∗) between 2.5 to -0.5, and low-VOCs (LVOCs; orange) as log⁡10(C∗)<-0.5). The relative contributions of LVOCs and SVOCs are multiplied by a factor of 1000 and 10, respectively.
Mass defect plots identifying potential markers sized by the square root of fractional contribution (%) and colored by log⁡2 (the fold change). The dashed line represents the series of homologues.
Chemical characterization of organic vapors from wood, straw, cow dung, and coal burning

March 2025

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55 Reads

Solid fuel (SF) combustions, including coal and biomass, are important sources of pollutants in the particle and gas phase and therefore have significant implications for air quality, climate, and human health. In this study, we systematically examined gas-phase emissions, using the Vocus proton-transfer-reaction time-of-flight (PTR-TOF) mass spectrometer, from a variety of solid fuels, including beech logs, spruce/pine logs, spruce/pine branches and needles, straw, cow dung, and coal. The average emission factors (EFs) for organic vapors ranged from 4.8 to 74.2 gkg-1, depending on the combustion phases and solid fuel types. Despite slight differences in modified combustion efficiency (MCE) for some experiments, increasing EFs for organic vapors were observed with lower MCE. The relative contribution of different classes showed large similarities between the combustion phases in beech logs stove burning, relative to the large change in EFs observed. The CxHyOz family is the most abundant group of the organic vapor emitted from all SF combustion. However, among these SF combustions, a greater contribution of nitrogen-containing species and CxHy families (related to polycyclic aromatic hydrocarbons) is observed in the organic vapors from cow dung burning and coal burning, respectively. Intermediate-volatility organic compounds (IVOCs) constituted a significant fraction of emissions in solid fuel combustion, ranging from 12.6 % to 39.3 %. This was particularly notable in the combustion of spruce/pine branches and needles (39.3 %) and coal (31.1 %). Using the Mann–Whitney U test on the studied fuels, we identified specific potential new markers for these fuels based on the Vocus measurements. The product from pyrolysis of coniferyl-type lignin and the extract of cedar pine needle were identified as markers in the open burning of spruce/pine branches and needles (e.g., C10H14O2, C11H14O2, C10H10O2). The product (C9H12O) from the pyrolysis of beech lignin was identified as the potential new marker for beech log stove burning. Many series of nitrogen-containing homologues (e.g., C10H11–21NO, C12H11–21N, C11H11–23NO, and C15H15–31N) and nitrogen-containing species (e.g., acetonitrile, acrylonitrile, propanenitrile, methylpentanenitrile) were specifically identified in cow dung burning emissions. Polycyclic aromatic hydrocarbons (PAHs) with 9–12 carbons were identified with significantly higher abundance from coal burning compared to emissions from other studied fuels. The composition of these organic vapors reflects the burned solid fuel types and can help constrain emissions of solid fuel burning in regional models.


Observations of high-time-resolution and size-resolved aerosol chemical composition and microphysics in the central Arctic: implications for climate-relevant particle properties

February 2025

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98 Reads

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1 Citation

Aerosols play a critical role in the Arctic's radiative balance, influencing solar radiation and cloud formation. Limited observations in the central Arctic leave gaps in understanding aerosol dynamics year-round, affecting model predictions of climate-relevant aerosol properties. Here, we present the first annual high-time-resolution observations of submicron aerosol chemical composition in the central Arctic during the Arctic Ocean 2018 (AO2018) and the 2019–2020 Multidisciplinary drifting Observatory for the Study of Arctic Climate (MOSAiC) expeditions. Seasonal variations in the aerosol mass concentrations and chemical composition in the central Arctic were found to be driven by typical Arctic seasonal regimes and resemble those of pan-Arctic land-based stations. Organic aerosols dominated the pristine summer, while anthropogenic sulfate prevailed in autumn and spring under haze conditions. Ammonium, which impacts aerosol acidity, was consistently less abundant, relative to sulfate, in the central Arctic compared to lower latitudes of the Arctic. Cyclonic (storm) activity was found to have a significant influence on aerosol variability by enhancing emissions from local sources and the transport of remote aerosol. Local wind-generated particles contributed up to 80 % (20 %) of the cloud condensation nuclei population in autumn (spring). While the analysis presented herein provides the current central Arctic aerosol baseline, which will serve to improve climate model predictions in the region, it also underscores the importance of integrating short-timescale processes, such as seasonal wind-driven aerosol sources from blowing snow and open leads/ocean in model simulations. This is particularly important, given the decline in mid-latitude anthropogenic emissions and the increase in local ones.


Figure 1: Exemplary (a) AMS and (b) EESI mass spectrum at POA conditions of BBOA particles from experiment spruce2 highlighting important ions. The y-scale intensity is in (a) relative to the average POA mass concentration summed over each nominal mass up to m/z 170 and in (b) relative to the total average intensity at POA conditions (b). Note that in (b), the most intense fraction of C6H10O5 would expand the y-scale by factor 3 (relative intensity of 0.17), so this ion was not considered for setting the scale.
Ozonolysis of primary biomass burning organic aerosol particles: Insights into reactivity and phase state

February 2025

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47 Reads

Biomass burning organic aerosol (BBOA) particles are a major contributor to atmospheric particulate matter with various effects on climate and public health. Quantifying these effects is limited by our understanding of the BBOA particles’ evolving chemical composition during atmospheric aging, driven by their exposure to atmospheric oxidants. This study explores the role of ozone (O3) as atmospheric oxidant in processing primary BBOA particles. We exposed particulate emissions from beech, spruce and pine wood fires to O3 in an oxidative flow reactor, monitoring their chemical evolution using high-resolution time-of-flight aerosol mass spectrometry (HR-AMS) and extractive electrospray ionization time-of-flight mass spectrometry (EESI-ToF). We found that the oxidative state of the particles increased with O3 exposure, as shown by the consistent, albeit minor, rise in O/C ratios. Analysis of the EESI-ToF data revealed specific molecular groups containing 18 and 20 carbon atoms, likely mainly abietic, linoleic, and oleic acid, as highly reactive toward O3 and driving the increase in oxidative state. At higher relative humidity, increased oxidation and loss of reactive species indicate that enhanced O3 diffusion into particles allows the ozonolysis to progress further, highlighting humidity's role in overcoming diffusion barriers that limit the ozonolysis in dry conditions. This study provides qualitative insights into the oxidative processing of primary BBOA particles in different phase states, presenting O3 as selective oxidant. Further research could focus on quantifying the progression of the ozonolysis, in particular the change in diffusion rates depending on relative humidity conditions or particle sizes.




Photodegradation of naphthalene-derived particle oxidation products

January 2025

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41 Reads

While photochemical aging is known to alter secondary organic aerosol (SOA) properties, this process remains poorly constrained for anthropogenic SOA. This study investigates the photodegradation of SOA produced from the hydroxyl radical-initiated oxidation of naphthalene under low- and high-NOx conditions. We used state-of-the-art mass spectrometry (MS) techniques, including extractive electrospray ionization and chemical ionization MS, for the in-depth molecular characterization of gas and particulate phases. SOA were exposed to simulated irradiation at different stages, i.e., during formation and growth. We found a rapid (i.e. >30 min) photodegradation of high-molecular-weight compounds in the particle-phase. Notably, species with 20 carbon atoms (C20) decreased by 2/3 in the low-NOx experiment which was associated with particle mass loss (∼12%). Concurrently, the formation of oligomers with shorter carbon skeletons in the particle-phase was identified along with the release of volatile products such as formic acid and formaldehyde in the gas-phase. These reactions are linked to photolabile functional groups within the naphthalene-derived SOA products, which increases their likelihood of being degraded under UV light. Overall, photodegradation caused a notable change in the molecular composition altering the physical properties (e.g., volatility) of naphthalene-derived SOA.



Citations (67)


... NaCl mass concentrations were estimated using the AMS 23 Na 35 Cl þ signal multiplied by 51, following an approach of Ovadnevaite et al. (2012). Since the calibration factor of the AMS used in Ovadnevaite et al. (2012) is unlikely to be identical to the AMS used during MOSAiC, our NaCl signals are provided in arbitrary units (a.u.), as in Heutte et al. (2025). We only assess submicron NaCl in fall and spring as the AMS was not operational in winter (December-February). ...

Reference:

Characteristics and effects of aerosols during blowing snow events in the central Arctic
Observations of high-time-resolution and size-resolved aerosol chemical composition and microphysics in the central Arctic: implications for climate-relevant particle properties

... Biogenic volatile organic compounds (BVOCs) are highly reactive organic gases predominantly emitted from terrestrial vegetation, contributing to about 90% of global atmospheric non-methane VOC emissions (Guenther et al., 1995(Guenther et al., , 2012. These compounds significantly influence the atmospheric budget of hydroxyl radicals (Di Carlo et al., 2004), affect the formation of tropospheric ozone and secondary organic aerosols (SOA) (Chameides et al., 1988;Claeys et al., 2004;Palmer et al., 2022;Pfannerstill et al., 2024), and drive new particle formation (Curtius et al., 2024;Shen et al., 2024;Zhao et al., 2024), thereby affecting atmospheric chemistry and the fate of climate (Peñuelas & Staudt, 2010;Weber et al., 2024). Zhang et al., 2024). ...

New particle formation from isoprene under upper-tropospheric conditions

Nature

... In the UCR-ISOP mechanism, the formation of dimers from NISOPO2 + NISOPO2, as described above, also greatly contributes to SOA under this experimental condition. In a recent study, Graham et al. (2023) showed that SOA from isoprene + NO 3 exhibits lower volatility than that from αpinene + NO 3 , supporting the fact that dimers are largely present in isoprene + NO 3 SOA. ...

Volatility of aerosol particles from NO3 oxidation of various biogenic organic precursors

... Furthermore, the presence of iron will lead to the production of OH radicals through the Fenton reaction, 20 even in the absence of light. 21 The rate at which chemical reactions occur in organic aerosol particles is strongly dependent on their phase state, 22,23 which varies from liquid to solid depending on composition and ambient conditions such as temperature and relative humidity (RH). 24−29 Photochemical aging can also trigger changes in the viscosity of secondary organic aerosol (SOA) particles. ...

Iron-Containing Seed Particles Enhance α-Pinene Secondary Organic Aerosol Mass Concentration and Dimer Formation
  • Citing Article
  • September 2024

Environmental Science and Technology

... For instance, terpenes with cyclic or branched structures may have greater flexibility or accessibility to interact with ROS, facilitating their neutralization. They may also contain functional groups, such as hydroxyls, which are important for the neutralization of free radicals [126][127][128][129]. ...

Interactions of peroxy radicals from monoterpene and isoprene oxidation simulated in the radical volatility basis set

... Though a novel application of reactive DESI, the technique did not have any significant advantages over the traditionally used x-ray fluorescence analysis. Surdu et al. applied EESI-MS to the study of aerosols [135]. Organic aerosols are chemically complex and highly transient, making it challenging to understand their chemistry. ...

Real-Time Identification of Aerosol-Phase Carboxylic Acid Production Using Extractive Electrospray Ionization Mass Spectrometry

Environmental Science and Technology

... Nowadays, the inhalation of aerosol components significantly affects vulnerable groups, particularly young and elderly populations (Singh et al. 2021). Variations in oxidative potential, cytotoxicity, and potentials of human health contribute to accurate concentration-response (CR) functions and predict the PM 2.5 -attributed health burdens (Ayua et al. 2024;Bhattu et al. 2024;Salana et al. 2024;Verma et al. 2024). Therefore, it is essential to evaluate long-term variability and trends of aerosols component both at global and regional scales to understand the climate and health impacts. ...

Local incomplete combustion emissions define the PM2.5 oxidative potential in Northern India

... Over the last several decades, numerous studies have extensively documented the microphysical processes that govern nucleation, growth, and subsequent new particle formation (Kerminen et al., 2018;Kulmala et al., 2000Kulmala et al., , 2001Kulmala et al., , 2004Lee et al., 2019;Lehtipalo et al., 2018;Liu et al., 2018;Marten et al., 2024). The importance of photochemistry processes induced by ultraviolet (UV) radiation for NPF are well-documented (Hakala et al., 2019;Hallar et al., 2011;Jokinen et al., 2017;Kerminen et al., 2018). ...

Assessing the importance of nitric acid and ammonia for particle growth in the polluted boundary layer

... In fact, PM has been classified as a Group 1 carcinogen, and gaseous pollutants are also toxic and cause harm through inhalation exposure (Teng and Altaf, 2022;Ramamoorthy et al., 2024). Nitrogen dioxide (NO 2 ), sulfur dioxide (SO 2 ), ammonia (NH 3 ), and volatile organic compounds (VOCs), also contribute to the formation of secondary PM through gas-to-particle conversion processes (Behera et al., 2016;Li et al., 2024). ...

Uncovering the dominant contribution of intermediate volatility compounds in secondary organic aerosol formation from biomass-burning emissions

National Science Review

... In light of their interactions studied in recent literatures (de Souza Gonçalves & Chaudhuri, 2020;He et al., 2021;Liu et al., 2023;Ning et al., 2022;Rong et al., 2020;Wen et al., 2019;Wu et al., 2023;, multicomponent nucleation involving three or four vapors should more closely resemble the actual NPF mechanism and previous theoretical studies have explored several multicomponent nucleation systems in the marine atmosphere Zu, Chu, et al., 2024). More recently, CLOUD experiments combined with quantum chemical calculations found that SA synergistically nucleates with HIO 3 and HIO 2 , with the rate being 10-to 10,000-fold higher than that of SA-NH 3 (He et al., 2023). MSA was also proposed to nucleate with HIO 3 and HIO 2 (Li, Wu, et al., 2024;. ...

Iodine oxoacids enhance nucleation of sulfuric acid particles in the atmosphere

Science