Abstract

Abstract. A size-resolved submicron organic aerosol composition dataset from a high-resolution time-of-flight mass spectrometer (HR-ToF-AMS) collected in Mexico City during the MILAGRO campaign in March 2006 is analyzed using 3-dimensional (3-D) factorization models. A method for estimating the precision of the size-resolved composition data for use with the factorization models is presented here for the first time. Two 3-D models are applied to the dataset. One model is a 3-vector decomposition (PARAFAC model), which assumes that each chemical component has a constant size distribution over all time steps. The second model is a vector-matrix decomposition (Tucker 1 model) that allows a chemical component to have a size distribution that varies in time. To our knowledge, this is the first report of an application of 3-D factorization models to data from fast aerosol instrumentation, and the first application of this vector-matrix model to any ambient aerosol dataset. A larger number of degrees of freedom in the vector-matrix model enable fitting real variations in factor size distributions, but also make the model susceptible to fitting noise in the dataset, giving some unphysical results. For this dataset and model, more physically meaningful results were obtained by partially constraining the factor mass spectra using a priori information and a new regularization method. We find four factors with each model: hydrocarbon-like organic aerosol (HOA), biomass-burning organic aerosol (BBOA), oxidized organic aerosol (OOA), and a locally occurring organic aerosol (LOA). These four factors have previously been reported from 2-dimensional factor analysis of the high-resolution mass spectral dataset from this study. The size distributions of these four factors are consistent with previous reports for these particle types. Both 3-D models produce useful results, but the vector-matrix model captures real variability in the size distributions that cannot be captured by the 3-vector model. A tracer m/z-based method provides a useful approximation for the component size distributions in this study. Variation in the size distributions is demonstrated in a case study day with a large secondary aerosol formation event, in which there is evidence for the coating of HOA-containing particles with secondary species, shifting the HOA size distribution to larger particle sizes. These 3-D factorizations could be used to extract size-resolved aerosol composition data for correlation with aerosol hygroscopicity, cloud condensation nuclei (CCN), and other aerosol impacts. Furthermore, other fast and chemically complex 3-D datasets, including those from thermal desorption or chromatographic separation, could be analyzed with these 3-D factorization models. Applications of these models to new datasets requires careful construction of error estimates and appropriate choice of models that match the underlying structure of those data. Factorization studies with these 3-D datasets have the potential to provide further insights into organic aerosol sources and processing.

Highlights

  • Fine particles have important effects on human health, climate forcing, visibility, as well as deposition of nutrients and acids to crops and ecosystems

  • To allow for differences between the HR-MS and Particle Time-of-Flight (PToF) mass spectra, we introduce a regularization parameter that allows the intensity, c, at each m/z in each reference factor to deviate from its starting value

  • In the 3-vector model (Fig. 1a), each factor is composed of a characteristic chemical composition, a characteristic size distribution, and the time series of the mass concentration of that component

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Summary

Introduction

Fine particles have important effects on human health, climate forcing, visibility, as well as deposition of nutrients and acids to crops and ecosystems. The extent and impact of these effects depend on both particle size and chemistry, with particles with submicron diameters being especially important. These aerosol effects are complex because aerosol size distributions are dynamic. Many processes can change the size distributions of aerosols, including creation of new particles by nucleation; growth by coagulation and condensation; decrease in size by evaporation of semivolatile species upon dilution, heating, or chemical reaction; and removal of particles by wet or dry deposition (Whitby, 1978). Measured ambient size distributions do not reflect the original sources directly, but represent aerosols transformed by atmospheric processes. Aerosol size and chemical composition are directly linked, and ideally should be measured simultaneously

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