The In-Plume Emission Test Stand (IPETS) characterizes gaseous and particulate matter (PM) emissions from combustion sources in real time. Carbon dioxide (CO 2 ), carbon monoxide (CO), nitric oxide (NO), nitrogen dioxide (NO 2 ), and other gases are quantified with a closed-path Fourier transform infrared spectrometer (FTIR). Particle concentrations, chemical composition, and other particle properties are characterized with an electrical lowpressure impactor (ELPI), a light-scattering particle detector, an optical particle counter, and filter samples amenable to different laboratory analysis. IPETS measurements of fuel-based emission factors for a diesel generator are compared with those from a Mobile Emissions Laboratory (MEL). IPETS emission factors ranged from 0.3 to 11.8, 0.2 to 3.7, and 22.2 to 32.8 g/kg fuel for CO, NO 2 , and NO, respectively. IPETS PM emission factors ranged from 0.4 to 1.4, 0.3 to 1.8, 0.3 to 2.2, and 1 to 3.4 g/kg fuel for filter, photoacoustic, nephelometer, and impactor measurements, respectively. Observed linear regression statistics for IPETS versus MEL concentrations were as follows: CO slope ϭ 1.1, r 2 ϭ 0.99; NO slope ϭ 1.1, r 2 ϭ 0.92; and NO 2 slope ϭ 0.8, r 2 ϭ 0.96. IPETS versus MEL PM regression statistics were: filter slope ϭ 1.3, r 2 ϭ 0.80; ELPI slope ϭ 1.7, r 2 ϭ 0.87; light-scattering slope ϭ 2.7, r 2 ϭ 0.92; and photoacoustic slope ϭ 2.1, r 2 ϭ 0.91. Lower temperatures in the dilution air (ϳ25°C for IPETS vs. ϳ50°C for MEL) may result in greater condensation of semi-volatile compounds on existing particles, thereby explaining the 30% difference for filters. The other PM measurement devices are highly correlated with the filter, but their factorydefault PM calibration factors do not represent the size and optical properties of diesel exhaust. They must be normalized to a simultaneous filter measurement.
INTRODUCTIONGas and particle emissions from power generators, gasoline engines, and diesel engines affect attainment of air quality standards, 1 human health, 2 visibility, 3 and climate. 4 Real-world emission estimates from these sources are needed to improve air quality management strategies.Engine certification emission factors (EFs) are determined from chassis or engine dynamometer tests following test protocols that vary vehicle operating conditions over time. 5 Only a few vehicles or engines can be tested on dynamometers because of the time and effort required. Other methods can determine EFs for large vehicle fleets. Tunnel studies yield fleet EFs averaged over many vehicles, but these tests are unable to determine individual vehicle EFs and their distribution across vehicle type and age. 6 Vehicle emission remote sensing systems (VERSS) and in-plume systems can measure fuel-based EFs for many individual vehicles over a wide range of real-world operating conditions. 7,8 Fuel-based EFs are calculated as 9,10