Contributions of wood smoke and vehicle emissions to ambient concentrations of volatile organic compounds and particulate matter during the Yakima wintertime nitrate study

A multiple linear regression (MLR) chemical mass balance model was applied to data collected during an air quality field experiment in Yakima, WA, during January 2013 to determine the relative contribution of residential wood combustion (RWC) and vehicle emissions to ambient pollutant levels. Acetonitrile was used as a chemical tracer for wood burning and nitrogen oxides (NOx) as a chemical tracer for mobile sources. RWC was found to be a substantial source of gas phase air toxics in wintertime. The MLR model found RWC primarily responsible for emissions of formaldehyde (73%), acetaldehyde (69%), and black carbon (55%) and mobile sources primarily responsible for emissions of carbon monoxide (CO; 83%), toluene (81%), C2-alkylbenzenes (81%), and benzene (64%). When compared with the Environmental Protection Agency’s 2011 winter emission inventory, the MLR results suggest that the contribution of RWC to CO emissions was underestimated in the inventory by a factor of 2. Emission ratios to NOx from the MLR model agreed to within 25% with wintertime emission ratios predicted from the Motor Vehicle Emissions Simulator (MOVES) 2010b emission model for Yakima County for all pollutants modeled except for CO, C2-alkylbenzenes, and black carbon. The MLR model results suggest that MOVES was overpredicting mobile source emissions of CO relative to NOx by a factor of 1.33 and black carbon relative to NOx by about a factor of 3

Field and Laboratory Measurements of Biomass Burning and Vehicle Exhaust Using a PTR-MS

The Proton Transfer Reaction Mass Spectrometer (PTR-MS) is a powerful tool for analyzing organic compounds in air and has been applied in field and laboratory applications to assess emissions from biomass burning and vehicles. Biomass burning is an important source of air pollution globally in the form of wild fires, burning of crop stubble, and combustion of organic material for home energy. In the United States, residential wood combustion combined with low inversion heights in winter time has caused air quality problems. Through field deployment of the PTR-MS in Xi’an China during August of 2011, it was determined that 27%, 16%, 26%, and 12% of ambient carbon monoxide (CO), acetaldehyde, benzene, and toluene could be attributed to biomass burning. The PTR-MS was also deployed to Yakima, Washington in January of 2013, finding that residential wood combustion was a substantial source of air toxics and PM. Residential wood combustion contributed 100%, 73%, 69%, 55%, 36%, 19%, 19%, and 17% of organic PM1, formaldehyde, acetaldehyde, black carbon, benzene, toluene, C2-alkylbenzenes, and CO respectively.Diesel vehicles are becoming a larger fraction of the vehicle fleet and can be held responsible for a substantial fraction of air pollution emissions from on and off road mobile sources. Diesel engines are a source of low volatility products that are difficult to measure and are thought to be important in the formation of secondary organic aerosol (SOA). This work focuses on measuring important diesel exhaust compounds with the PTR-MS and assessing oxidation processes of these compounds. When the PTR-MS was deployed to the field along with a thermal desorption preconcentration system, we estimated that diesel vehicles were about 3-15% of the vehicle activity influencing our study site in Yakima, WA using the ratio of m/z 157 to m/z 129. SOA yields of diesel exhaust compounds were assessed and about 48% of the SOA was attributed to compounds measured by the PTR-MS; with 21% attributed to alkylbenzenes, 20% attributed to alkanes, 3% attributed to alkylnaphthalenes, 3% attributed to molecular weight 178 polycyclic aromatic hydrocarbons, and 1% attributable to cycloalkanes

SOA formation potential of emissions from soil and leaf litter.

Soil and leaf litter are significant global sources of small oxidized volatile organic compounds, VOCs (e.g., methanol and acetaldehyde). They may also be significant sources of larger VOCs that could act as precursors to secondary organic aerosol (SOA) formation. To investigate this, soil and leaf litter samples were collected from the University of Idaho Experimental Forest and transported to the laboratory. There, the VOC emissions were characterized and used to drive SOA formation via dark, ozone-initiated reactions. Monoterpenes dominated the emission profile with emission rates as high as 228 μg-C m(-2) h(-1). The composition of the SOA produced was similar to biogenic SOA formed from oxidation of ponderosa pine emissions and α-pinene. Measured soil and litter monoterpene emission rates were compared with modeled canopy emissions. Results suggest surface soil and litter monoterpene emissions could range from 12 to 136% of canopy emissions in spring and fall. Thus, emissions from leaf litter may potentially extend the biogenic emissions season, contributing to significant organic aerosol formation in the spring and fall when reduced solar radiation and temperatures reduce emissions from living vegetation

SOA Formation Potential of Emissions from Soil and Leaf Litter

Soil and leaf litter are significant global sources of small oxidized volatile organic compounds, VOCs (e.g., methanol and acetaldehyde). They may also be significant sources of larger VOCs that could act as precursors to secondary organic aerosol (SOA) formation. To investigate this, soil and leaf litter samples were collected from the University of Idaho Experimental Forest and transported to the laboratory. There, the VOC emissions were characterized and used to drive SOA formation via dark, ozone-initiated reactions. Monoterpenes dominated the emission profile with emission rates as high as 228 μg-C m^–2 h^–1. The composition of the SOA produced was similar to biogenic SOA formed from oxidation of ponderosa pine emissions and α-pinene. Measured soil and litter monoterpene emission rates were compared with modeled canopy emissions. Results suggest surface soil and litter monoterpene emissions could range from 12 to 136% of canopy emissions in spring and fall. Thus, emissions from leaf litter may potentially extend the biogenic emissions season, contributing to significant organic aerosol formation in the spring and fall when reduced solar radiation and temperatures reduce emissions from living vegetation