Canopy coverage and frequency were recorded in 20 circular 10 sq m plots. Six treatments were sampled, three ungrazed and three to grazed by native grazers. In each case one of the three watersheds was unburned, another burned annually in April, the third burned every four years in April. In each treatment two soils were sampled: a lower-slope deep fertile nonrocky soil (tully silty clay loam), and a shallow rocky soil (florence cherty silt loam) on level to gently sloping ridges. In 1983 another ungrazed annual burn area (1c) was added (both tully and florence soils) because original area (1d) appeared aberrant.
To determine long-term changes in canopy cover, frequency, richness, and diversity in watersheds from different burn treatments in grazed and ungrazed watersheds.
Location of Sampling Stations: Plant composition is determined on upland topographic locations (Florence soils), lowland topographic locations (Tully soils), and slope locations. Maps of sampling locations are available as following PVC Map.
Collection of plant composition data began in 1983 in watersheds 1c, 1d, 4b, 20b, N1b, N4d, and N20b. Since then, numerous other watersheds have been added and an annual plant census is currently conducted in: 1d, 2c, 2d, 4a, 4b, 20b, N1a, N1b, N4a, N4d, N20a, N20b, Fa, Fb, Wa, Wb, Spa, Spb, Sua, Sub, R1a, R1b, R20a, R20b, Ca, Cb, Cc, Cd, Sa, Sb, Sc, and Texas Hog. Sampling in the eight seasonally burned watersheds began in 1994 and sampling in the Shane and Cattle Units began in 2008. Four reversal watersheds were established in 2001 in which 1a became R20a, 20a became R1a, 1c became R20b, and 20d became R20b. Only Florence soils (f) are sampled in 2c and 2d, whereas only Tully soils (t) are sampled in R1a and R20a. Sampling on slope sites (s) in 1d, 1c, 4a, 4b, 20b, 20d, N4a, N4d, N20a, and N20b were conducted from 1991-2001, but are currently sampled only in the bison-grazed watersheds.
Frequency of Sampling: Initially, plots were surveyed 3 times each year. Beginning in 1991, however, sampling frequency was changed to twice a year (late-May to Mid-June for the spring census, and mid- August to early-September for the summer census). Generally, cool-season species are sampled in the spring census whereas warm-season species are sampled in the summer census when they are more developed.
Variable Measured: Canopy cover of all vascular plant species in each plot are estimated.
Methods: In each watershed, four 50-m long transects (A, B, C, and D) were established on each topographic position. In each transect, five evenly spaced, permanently marked plots are located (n = 20 plots for each topographic position in a watershed). A surveyor’s pin with a 1.78 m long chain is placed in the conduit marking each plot. Canopy cover of all vascular plant species in a 10-m2 circular area within each conduit are estimated using a modified Daubenmire cover scale (Bailey and Poulton, 1968. Ecology 49:1-13). Cover categories are:
Form of Data Output: Raw data contains the cover class value for each species detected in the plot. For species that are sampled on both census dates, the highest cover class of each plot is used for analyses. Percentage cover for each species is computed by averaging the mid-points of the cover classes for the 20 plots. The presence or absence of a species in the 20 plots can be used to estimate frequency of occurrence.
Summary of All Changes:
Pasture c01b was called Texas Hog (thp) in 2009.
Vegetation species composition from 1983. The transects were permanently layed out in the current format of 4 transects (A-D), each with 5 plots. Transect E only occurred on watershed N20B florence in 1986 and 1987. This transect is the same as the current transect D for this watershed and soil type. The old transect D was abandoned in 1987 prior to bison reintroduction. Seven cover classes were used to estimate species canopy coverage. 1 - 0-1% cover; 2 - 2-5% cover; 3 - 5-25% cover; 4 - 25-50% cover; 5 - 50-75%; 6 - 75-95% cover; 7 - 95-100% cover. (Note: for the watershed r20b, no data were collected in the transect A & B in the fall of 2011 due to wildfire occurred.)
*Transect ‘E’ occurred only on the N20b florence site in 1986 and 1987 and was renamed the new ‘D’ transect in 1988. The old ‘D’ transect was sampled from 1983 to 1987 and then abandoned when the bison fence was constructed. Thus, plots d1-d5 from 1983-1987 are NOT the same d1-d5 plots in subsequent years.
Codes used in the data set:
t = tully (lowland) soil
f = florence (upland) soil
s = slopes
For list of Species codes used, please check species list (PDF), or species list in Excel version
For the PVC Experiment Map, please check PVC map
For additional metadata information see: http://lter.konza.ksu.edu/sites/default/files/DC.pdf
For additional methods information see: http://lter.konza.ksu.edu/sites/default/files/MM.pdf