Abstract

Abstract. An integral part of air quality management is knowledge of the impact of pollutant sources on ambient concentrations of particulate matter (PM). There is also a growing desire to directly use source impact estimates in health studies; however, source impacts cannot be directly measured. Several limitations are inherent in most source apportionment methods motivating the development of a novel hybrid approach that is used to estimate source impacts by combining the capabilities of receptor models (RMs) and chemical transport models (CTMs). The hybrid CTM–RM method calculates adjustment factors to refine the CTM-estimated impact of sources at monitoring sites using pollutant species observations and the results of CTM sensitivity analyses, though it does not directly generate spatial source impact fields. The CTM used here is the Community Multiscale Air Quality (CMAQ) model, and the RM approach is based on the chemical mass balance (CMB) model. This work presents a method that utilizes kriging to spatially interpolate source-specific impact adjustment factors to generate revised CTM source impact fields from the CTM–RM method results, and is applied for January 2004 over the continental United States. The kriging step is evaluated using data withholding and by comparing results to data from alternative networks. Data withholding also provides an estimate of method uncertainty. Directly applied (hybrid, HYB) and spatially interpolated (spatial hybrid, SH) hybrid adjustment factors at withheld observation sites had a correlation coefficient of 0.89, a linear regression slope of 0.83 ± 0.02, and an intercept of 0.14 ± 0.02. Refined source contributions reflect current knowledge of PM emissions (e.g., significant differences in biomass burning impact fields). Concentrations of 19 species and total PM2.5 mass were reconstructed for withheld observation sites using HYB and SH adjustment factors. The mean concentrations of total PM2.5 at withheld observation sites were 11.7 (± 8.3), 16.3 (± 11), 8.59 (± 4.7), and 9.2 (± 5.7) μg m−3 for the observations, CTM, HYB, and SH predictions, respectively. Correlations improved for concentrations of major ions, including nitrate (CMAQ–DDM (decoupled direct method): 0.404, SH: 0.449), ammonium (CMAQ–DDM: 0.454, SH: 0.492), and sulfate (CMAQ–DDM: 0.706, SH: 0.730). Errors in simulated concentrations of metals were reduced considerably: 295 % (CMAQ–DDM) to 139 % (SH) for vanadium; and 1340 % (CMAQ–DDM) to 326 % (SH) for manganese. Errors in simulated concentrations of some metals are expected to remain given the uncertainties in source profiles. Species concentrations were reconstructed using SH results, and the error relative to observed concentrations was greatly reduced as compared to CTM-simulated concentrations. Results demonstrate that the hybrid method along with a spatial extension can be used for large-scale, spatially resolved source apportionment studies where observational data are spatially and temporally limited.

Highlights

  • IntroductionMany past epidemiological studies focused on associating particulate matter (PM) mass (e.g., PM2.5/10: PM with aerodynamic diameters less than 2.5 or 10 μm) with the health outcomes, as opposed to individual species or the sources of the PM due to limited data availability or difficulties in quantifying source impacts

  • Variations in ambient pollutant species concentrations, including particulate matter (PM) and gases, are correlated with health outcomes – such as lower birth weight (Darrow et al, 2011; Wang et al, 1997), higher occurrences of bradycardia and central apnea (Campen et al, 2001; Peel et al, 2011), decreased peak expiratory flows and increased respiratory symptoms in non-smoking asthmatics (Peters et al, 1997)Published by Copernicus Publications on behalf of the European Geosciences Union.C

  • The original Community Multiscale Air Quality (CMAQ)–decoupled direct method (DDM), directly applied hybrid (CTM–receptor models (RMs)), and spatial hybrid (SH) concentrations are compared to measurements at withheld observation locations to evaluate the performance of each method in simulating concentrations

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Summary

Introduction

Many past epidemiological studies focused on associating PM mass (e.g., PM2.5/10: PM with aerodynamic diameters less than 2.5 or 10 μm) with the health outcomes, as opposed to individual species or the sources of the PM due to limited data availability or difficulties in quantifying source impacts. Epidemiological studies are examining the associations between individual species and health outcomes using data from ground observation networks, such as the Chemical Speciation Network (CSN) and the Southeastern Aerosol Research and Characterization Network (SEARCH) (Dominici et al, 2010; Samet et al, 2000; Sarnat et al, 2008; Tolbert et al, 2007). Attributing individual component concentrations and the overall mixture of observed air pollution to specific sources, as well as linking those sources with adverse health impacts, is challenging. Receptor models (RMs) are used to generate source apportionment (SA) results for epidemiological studies because longer time series are required (e.g., greater than 2 years) (Sarnat et al, 2008)

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