Functional group analysis of high-molecular weight compounds in the water-soluble fraction of organic aerosols
Introduction
Atmospheric aerosol particles play a crucial role in many aspects of the earth's climate system due to the light scattering and light absorption properties of the particles and their role in cloud formation (Seinfeld and Pandis, 1988). In addition, epidemiological studies showed that ambient concentrations of aerosols are associated with morbidity and mortality (Delfino et al., 2005; Dockery et al., 1993). For many of these processes, the chemical composition of the particles is an important parameter. Although up to 50% or more of the total mass of ambient aerosols is organic material, only little is known about the chemical composition of this aerosol fraction, and only 10–20% of the organic mass can be resolved on a molecular level (Likens et al., 1983; Puxbaum et al., 2000; Seinfeld and Pandis, 1988).
In recent years, high-molecular weight compounds have been identified in ambient and laboratory-generated particles, which may explain up to 60% of the total organic aerosol mass (Facchini et al., 1999; Havers et al., 1998; Kalberer et al., 2004). Several studies investigating this class of compound in ambient samples showed that these complex compound mixtures have physico-chemical characteristics similar to those of humic and fulvic acids (Graber and Rudich, 2006) and therefore this compound class is often called humic-like substances (HULIS). The chemical characterization of HULIS is only at its very beginning.
One important aspect of the characterization of HULIS to estimate their role in atmospheric chemistry and to get insight into their formation mechanisms is the qualitative and quantitative determination of functional groups in HULIS. The average concentrations of functional groups in the complex HULIS compound mixture may, for example, influence the water solubility or toxicity of an aerosol particle.
Several studies have investigated functional groups of HULIS such as sulfates (Liggio et al., 2005; Reemtsma et al., 2006; Romero and Oehme, 2005) and sulfonates, nitrate groups (Reemtsma et al., 2006) with mass spectrometric methods. UV–vis spectroscopy and titration methods have been applied for the quantitative analysis of arylic, phenolic and acidic functional groups of HULIS (Dinar et al., 2006). H-NMR was used by several authors to estimate the quantity of a variety of functional groups such as aliphatic, arylic, carboxylic, acetalic, vinylic, alcoholic, ether or ester groups, as well as hydrogens in α-position to unsaturated carbons (Decesari et al., 2006; Havers et al., 1998). Time consuming derivatization reactions were used to specifically quantify carboxylic acids with H-NMR, which are otherwise not detectable with H-NMR when D2O is used as solvent (Tagliavini et al., 2006).
In the present study, H-NMR and acid titration was used in parallel to quantify several functional groups (acids, phenols, arylic H's, aliphatic H's) in the water-soluble fraction of HULIS isolated from urban atmospheric aerosols samples. The quantitative results for carboxylic acids obtained from H-NMR and potentiometric titrations were found to be in good agreement. In addition, pK distributions of carboxylic groups of HULIS were calculated from the titration measurements.
Section snippets
Aerosol sampling and HULIS isolation
Aerosol sampling was carried out at a suburban site of the Swiss National Air Pollution Monitoring Network near Zurich, Switzerland (NABEL, Station Dübendorf), in July/August 2005 and December 2005/January 2006. Temperature during sampling of aerosol was between 17 and 23 °C in summer and −3 and 5 °C in winter. A high-volume sampling system was used to collect weekly aerosol samples (PM1) on pre-baked quartz fiber filters (150 mm diameter) at a flow rate of 500 l/min (Model DA 80, Digitel AG,
H-NMR spectroscopy
H-NMR spectroscopy has been applied by several authors (Cavalli et al., 2006; Decesari et al., 2006; Matta et al., 2003; Tagliavini et al., 2006) to investigate the structure of HULIS in aerosol samples and to quantify the distribution of different functional groups. D2O was used in most of these studies as solvent for the H-NMR measurements, which makes it impossible to determine carboxyl and hydroxyl groups, because the hydrogen atoms of these groups rapidly exchange with a deuterium of D2O.
Conclusions
Atmospheric aerosol samples (particle size<1 μm) were collected in an urban area (Dübendorf, Switzerland) during summer 2005 and winter 2005/2006. Water-soluble HULIS were extracted and isolated and the concentrations of different functional groups in HULIS were determined.
In this study, we present a new and simple H-NMR method for the quantitative determination of a variety of functional groups without time consuming sample preparation. H-NMR was used to determine the concentration of
References (31)
- et al.
A statistical-model of proton binding by humus
Geochimica et Cosmochimica Acta
(1984) - et al.
Isolation of water-soluble organic matter from atmospheric aerosol
Talanta
(2001) - et al.
Size-segregated aerosol chemical composition at a boreal site in southern Finland, during the QUEST project
Atmospheric Chemistry and Physics
(2006) - et al.
Characterization of the organic composition of aerosols from Rondonia, Brazil, during the LBA-SMOCC 2002 experiment and its representation through model compounds
Atmospheric Chemistry and Physics
(2006) - et al.
Potential role of ultrafine particles in associations between airborne particle mass and cardiovascular health
Environmental Health Perspectives
(2005) - et al.
Cloud condensation nuclei properties of model and atmospheric HULIS
Atmospheric Chemistry and Physics
(2006) - et al.
An association between air-pollution and mortality in 6 United-States cities
New England Journal of Medicine.
(1993) - et al.
Evaporative light scattering: a novel detection method for the quantitative analysis of humic-like substances in aerosols
Environmental Science and Technology
(2007) - et al.
Partitioning of the organic aerosol component between fog droplets and interstitial air
Journal of Geophysical Research Atmosphere
(1999) - et al.
Chemical characterization of fine particle emissions from fireplace combustion of woods grown in the northeastern United States
Environmental Science and Technology
(2001)
Potentiometric analysis of complex protolytic systems by pK spectroscopy using linear regression
Journal of Analytical Chemistry
Potentiometric analysis of polyelectrolytes by pK spectroscopy using linear regression analysis
Journal of Analytical Chemistry
Atmospheric HULIS: how humic-like are they? A comprehensive and critical review
Atmospheric Chemistry and Physics
Determination of the equivalence point in potentiometric titrations. 2
Analyst
Spectroscopic characterization of humic-like substances in airborne particulate matter
Journal of Atmospheric Chemistry
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2018, Atmospheric EnvironmentCitation Excerpt :Another aliquot representing 14.8 mL of overall water extract was further adjusted to pH 2 with HCl and used for HULIS separation. Due to its simplicity and selective isolation, solid-phase extraction (SPE) is the most frequently-used approach for simultaneous concentration and fractionation of HULIS from other dissolved constituents (Kiss et al., 2002; Salma et al., 2007, 2008, 2013; Samburova et al., 2007) and was also applied in this work. For SPE, C-18 cartridges were chosen; organics that represent HULIS were retained on C-18 cartridges (SEP-PAK VAC, 3 mL, 500 mg, Waters), afterwards they were eluted with methanol, dried gently with N2, and re-dissolved in 14.8 mL of Milli-Q. Aliquots of HULIS were then used for organic carbon analysis.
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