NASA - National Aeronautics and Space Administration

Langley Aerosol Research Group Experiment (LARGE).  The "classic" suite of instrumenation measures in-situ aerosol micrphysical and optical properties. The package can be tailored for specific science objectives and to operate on a variety of aircraft. Depending on the aircraft, measurments are made from either a shrouded single-diffuser "Clarke" inlet, from a BMI (Brechtel Manufacturing Inc.) isokinetic inlet, or from a HIML inlet. Primary measurements include:

1.) total and non-volatile particle concentrations (3nm and 10nm nominal size cuts),
2.) dry size distributions from 3nm to 5µm diameter using a combination of mobilty-optical-aerodynamic sizing techniques,
3.) dry and humidified scattering coefficients (at 450, 550, and 700nm wavelength), and
4.) dry absorption coefficients (470, 532, and 670nm wavelength). 

LARGE derived products include particle size statistics (integrated number, surface area, and volume concentrations for ultrafine, accumulation, and coarse modes), dry and ambient aerosol extinction coefficients, single scattering albedo, angstrom exponent coefficients, and scattering hygroscopicity parameter f(RH).

As part of the measurement team on the NASA DC-8 we operate two related installations: a mist chamber/ion chromatograph (MC/IC) sampling/analysis system providing near real time results for selected species, and a bulk aerosol system that collects particulates onto filters for subsequent analysis. We use ion chromatography on aqueous extracts of the bulk aerosol samples collected on Teflon filters to quantify soluble ions (Cl^-, Br^-, NO3^-, SO4^2-, C2O4^2-, Na⁺, NH4⁺, K⁺, Ca⁺, and Mg⁺). Filters are exposed on all level flight legs. Below 3 km exposure times are 5 minutes or less, increasing at higher altitudes to a maximum sample time of 15 minutes. Aerosols participate in heterogeneous chemistry, impact radiative transfer, and can be detected from space. Our measurements help to validate and extend retrievals of aerosol distributions and properties by MODIS, MISR and CALIPSO. In addition, several of the particle-associated ions are tracers of sources of gas and aerosol pollutants (e.g., SO4^2- from industrial emissions of SO2, enhancements of C2O4^2-, K⁺, and NH4⁺ indicate encounters with biomass burning plumes, Na⁺, and Cl^- are tracers of seasalt, Mg²⁺ and Ca²⁺ are tracers of dust). Our system has two inlets, allowing collection of paired samples simultaneously.

POPS measures CH2O, H2O2, and CH3OOH.

CH2O is measured by aqueous collection followed by enzyme fluorescence detection.

H2O2 and CH3OOH is measured by aqueous collection followed by HPLC separation and enzyme fluorescence detection.

NO is measured using a chemiluminescence detector. One of the four NO detectors is used for the NO measurements. NOy is measured simultaneously by catalytically converting it to NO on the surface of gold tubes heated to ±° C, with carbon monoxide (CO) acting as a reducing agent. The converter system is contained in a pod mounted outside the cabin to minimize the length of the inlet tubes. Gas phase-NOy measurements are made by sampling air through the rearward facing inlet which discriminates against particles of diameter larger than 1 mm. The mixing ratios of total NOy (gas phase-NOy + amplified particulate-NOy) are measured by sampling air through the forward facing inlet which is heated to 100° C. The mixing ratios of gas phase and total NOy are measured independently. A humidifier maintains the H2O mixing ratio in sample flows at a few % in order to stabilize the instrument background against humidity variations in the ambient air. The absolute sensitivities of the NO and NOy channels are measured every 80 minutes by adding NO or NO2 standard gases. The pressure in the gold catalytic converter for gas-phase NOy is maintained at a constant value of about 50 hPa, independent of the ambient pressure. The pressure is held constant by controlling the sample flow using a servo-controlled Teflon valve mounted upstream of the converter tube. All parts of the inlet system upstream of the gold catalyst are made of Perfluoroalkoxy (PFA) Teflon which is temperature controlled at 40˚C. The NO2 conversion efficiency is 99.0611%. The HCN conversion efficiency is lower than 5% for dry air with O3 mixing ratios lower than 100 ppbv. It decreases to 2% for humid air with an H2O mixing ratio of 0.1% and O3 mixing ratios lower than 100 ppbv. This instrument is also equipped with an NO2 photolytic converter combined with an NO detector in our first attempt to access the accuracy of the NO2 measurements.

The FSSP is of that general class of instruments called optical particle counters (OPCs) that detect single particles and size them by measuring the intensity of light that the particle scatters when passing through a light beam. A Helium Neon laser beam is focused to a diameter of 0.2 mm at the center of an inlet that faces into the oncoming airstream. This laser beam is blocked on the opposite side of the inlet with an optical stop, a "dump spot" to prevent the beam from entering the collection optics. Particles that encounter this beam scatter light in all directions and some of that scattered in the forward direction is directed by a right angle prism though a condensing lens and onto a beam splitter. The "dump spot" on the prism and aperture of the condensing lens define a collection angle from about 4º - 12º.

The beam splitter divides the scattered light into two components, each of which impinge on a photodetector. One of these detectors, however, is optically masked to receive only scattered light when the particles pass through the laser beam displaced greater than approximately 1.5 mm either side of the center of focus. Particles that fall in that region are rejected when the signal from the masked detector exceeds that from the unmasked detector. This defines the sample volume needed to calculate particle concentrations.