The principal site of ground and/or airborne data acquisition relevant to the FED project were International Paper's Northern Experimental Forest (NEF) located near Howland, Maine.
In 1989, NASA Headquarters initiated the Multisensor Airborne Campaign (MAC) philosophy of coordinating aircraft deployments, in which FED was an active participant. Prior to conducting our first official FED MACs in 1990, an unofficial MAC was conducted over the NEF in September '89. This included extensive ground-based data collection and overflights by NASA's DC-8 carrying JPL's Airborne Synthetic Aperture Radar (AIRSAR), NASA's C-130 carrying Thematic Mapper Simulator (TMS) and Goddard's Advanced Solid-state Array Spectroradiometer (ASAS), and a NASA helicopter equipped with a Barnes Modular Multiband Radiometer (MMR), a Spectron Engineering SE-590 spectroradiometer, and an Airborne Laser Polarimetry System (ALPS). A detailed description of this field experiment, as well as the type of data sets which were collected during this intensive field campaign can be found in Smith et al. (1990).
As a follow-on to the September '89 unofficial MAC, official FED MAC's were held in July (microwave) and September (passive, optical), 1990, and in June, 1991 (passive, optical).
Phase I data acquisition during the July microwave component of the 1990 FED MAC included:
Phase I data acquisition during the September optical-reflective component of the 1990 FED MAC included concurrent and coordinated overflights of the NEF under extremely clear atmospheric conditions, as well as supporting ground measurements:
Phase I data acquisition during the June 1991 FED MAC included:
A soil survey (1:120,000) of the Northern Experimental Forest was performed by the USDA Soil Conservation Service including field and laboratory characterization of representative pedons. The final soil survey map has been digitized and rasterized, along with a topographic map of the NEF, for use in the FED GIS.
Trace gas flux (CO2, CH4, N2O) was measured from surface horizons within varying soil drainage classes and under varying vegetation types using amended and non-amended treatments (see Groffman, 1989).
Soil temperature and matric potential within 4 soil horizons are being continuously monitored with data loggers at 2 sites (excessively drained deciduous dominated esker site, and somewhat poorly drained spruce-dominated tower site).
A 3 km east-west transect was surveyed along the Howland and Edinburgh town line and mapped according to soil drainage classes. Horizontal point sampling techniques were used to characterize forest properties within each of the soil drainage classes, including species, diameter breast height, tree height and canopy position. Soil samples were also obtained and analyzed for particle size, pH, nitrogen, iron, aluminum, organic carbon, heavy metals, cation exchange capacity, and sulfate adsorption. Results of transect vegetation and soil characteristics have been correlated with the canopy Normalized Difference Vegetation Index [Levine et al., 1994}
Gravimetric soil moisture content within 4 soil horizons during the June 1990 aircraft overflights was acquired at sixteen 25m X 25m interval gridded plots in both the spruce and hemlock sites. Similar sampling was repeated in June 1991 at 52 locations within the spruce site at 2 soil depths for analysis using spatial statistics and comparison with AIRSAR data.
Soil samples from the June 1991 MAC are presently being prepared and analyzed for organic carbon, total nitrogen, particle size, available phosphorus, total phosphorus, and phosphate adsorption potential.