Field methods
Measurements were made in July and again in September 2019, which
is typically near peak annual biomass in the region (Huenneke et
al. 2002).
Vegetation cover
We recorded vegetation cover (grass+shrub vs litter+soil) using
line point intercept (LPI) measurements along the transects at
every half meter. Start and stop lat/lon coordinates for these
transect are included with the dataset.
Mesquite (PRGL) height
The height of shrubs that intersected the LPI transects were
measured using the disk-drop method (Li et al. 2013).
Grass root exposure and green shoots
A belt transect was centered along the same transect tape as LPI
to characterize patterns of root exposure recording a grass if it
was within 50-cm from the transect. Grasses with overlapping
canopies were considered a single patch because they function as a
single roughness element for the wind. For each patch, we noted if
a grass had any green shoots and whether roots were exposed.
UAV Imagery
Between September 5th and 12th, 2019, we captured high resolution
aerial imagery of the transects. We flew a Phantom 4 quadcopter
(DJI, Shenzen, China), over the established 18 transects at a
height of 10-m with 80% overlap between each flight path. Flights
were between 10 AM to 2 PM to establish similar lighting
conditions and limit canopy shadow.
UAV data reduction
Approximately 120 images per transect were collected to generate
orthomosaics of 3.5 mm/pixel resolution using PhotoScan (Agisoft
Metashape Pro 1.6). In ENVI 5.5 (L3Harris Geospatial, Boulder,
CO), we placed region of interest (ROI) polygons covering every
grass patch within one meter of the transect tape, which was
visible in the orthomosaic. These ROIs were used to estimate grass
cover. For each ROI, we calculated the Green Chromatic Coordinate
(GCC):
$GCC = \frac{DN_{green}}{DN_{red} + DN_{green} + DN_{blue}}$
where DN is the digital number for each of the three color
channels (red, green, and blue) (Richardson et al. 2007). The GCC
is a greenness index that is a measure of the proportion of the
reflected light that is green, irrespective of total amount of
visible light reflected (i.e., irrespective of total brightness)
References
Huenneke, L. F., J. P. Anderson, M. Remmenga, and W. H.
Schlesinger. 2002. Desertification alters patterns of aboveground
net primary production in Chihuahuan ecosystems. Global Change
Biology 8:247-264.
Li, J., G. S. Okin, J. E. Herrick, J. Belnap, M. E. Miller, K.
Vest, and A. E. Draut. 2013. Evaluation of a new model of aeolian
transport in the presence of vegetation. Journal of Geophysical
Research: Earth Surface 118:288-306.
Richardson, A. D., J. P. Jenkins, B. H. Braswell, D. Y. Hollinger,
S. V. Ollinger, and M. L. Smith. 2007. Use of digital webcam
images to track spring green-up in a deciduous broadleaf forest.
Oecologia 152:323-334.