USGS - science for a changing world

Northern Prairie Wildlife Research Center

  Home About NPWRC Our Science Staff Employment Contacts Common Questions About the Site

Dynamics of Green Ash Woodlands
in Theodore Roosevelt National Park


Vegetation measurement

In 1985, we selected 12 representative stands in the Green Ash – Common Choke Cherry Habitat Type (Hansen et al. 1995) for measurement. In each stand, a 20-m baseline was established in the center of the stand parallel to the drainage on which the stand was located. We attempted to minimize heterogeneity within sampled areas by including only interior areas of stands and excluding stands in which we could not locate a 20 by 3 m strip with tree cover. We measured vegetation in three strata. The ground stratum was sampled by estimating canopy coverage of all grasses, forbs, shrubs, and nonliving ground cover less than 50 cm in height at 1-m intervals along the transect baseline in 20 by 50-cm (1985 and 1986) or 25 by 51-cm (1988 to 1996) plots. Cover estimates in individual plots were based on a modification of a canopy coverage rating system developed by Daubenmire (1959). Canopy coverage for each category over the entire transect was calculated by using the median percentage value within each coverage class (I = 0; II [less than 1%] = 0.5%; III [1 to 5%] = 2.5%; IV [greater than 5 to 25%] = 15%; V [greater than 25 to 50%] = 38%; VI [greater than 50% to 75%] = 62%; VII [greater than 75 to 95%] = 85%; and VIII [greater than 95%] = 98%) as a point estimate and averaging the values recorded in 20 individual plots per transect. Density of plants in the shrub stratum (woody species less than or equal to 2 m in height) was calculated by counting shrub stems by height class (less than 50 cm, 50 to 100 cm, and greater than 100 to 200 cm) in seven 1-m² plots placed at 3-m intervals along the transect baseline. Density of plants in the tree stratum (woody plants greater than 2 m in height) was measured in a 20 by 3-m plot parallel to each transect baseline. Plants with multiple stems were counted as separate trees if the stem branching occurred at ground level or lower.

Baselines were marked with metal posts to aid in relocation. A tape measure stretched between end points of the baseline allowed us to resample the same plots in different years. Plant species nomenclature follows the Flora of the Great Plains (Great Plains Flora Association 1986). Our analyses were limited to a subset of species and groups of species that we regarded as potential indicators of change (Table 1).

Table 1.  Vegetation parameters included in analyses of change in green ash stands during 1985 to 1996 in Theodore Roosevelt National Park, North Dakota.
Category Definition/expected trend
Tree stratum (stem counts)
  Green ash ( > 2 m) Expected to decrease under heavy grazing or drought
  Choke cherry ( > 2 m)
  Saskatoon service-berry
  All trees and saplings ( > 2 m)
Shrub stratum (stem counts)
  Green ash (≤ 2 m) Expected to decrease under heavy grazing by livestock or native ungulates and drought.
  Choke cherry (≤ 2 m)
  Saskatoon service-berry (≤ 2 m)
  Snowberry (≤ 2 m) Includes Symphoricarpos albus (L.) and S. occidentalis (Hook.). Expected to increase under heavy grazing by gramivores.
  All species (0 - 50 cm) Expected to decrease under heavy grazing or drought but possible increase under gramivore grazing.
  All species ( > 50 - 100 cm) Expected to decrease under heavy grazing, drought, or severe winters.
  All species ( > 100 - 200 cm) Expected to decrease under heavy grazing, drought, or severe winters.
Ground stratum (% cover)
  Bare ground Expected to increase under heavy grazing or drought.
  Litter Expected to decrease under heavy grazing or drought but could also decrease if hidden under heavy herbaceous living plant cover.
  Shrubs 0 - 50 cm Expected to decrease under heavy grazing or drought but could increase under heavy use by gramivores.
  Graminoids Expected to decrease under heavy grazing and drought.
  Climax graminoids Includes only the three most common species (Virginia wild rye [Elymus virginicus L.], little-seed ricegrass [Oryzopsis micrantha (Trin. & Rupr.) Thurb.], and Sprengel's sedge [Carex sprengelii Dew. ex Spreng.]) in stands. Expected to decrease under heavy grazing and drought.
  Exotic grasses Includes all introduced grass species, but Kentucky bluegrass (Poa pratensis L.) and smooth brome (Bromus inermis Leyss.) comprised > 90% of exotics in stands. Expected to increase under heavy grazing and decrease under drought.
  All forbs Includes all forb species identified in stands. Expected to increase under heavy grazing by gramivores and decrease under drought conditions.
  Palatable forbs Includes all native forb species/genera that were found in stands and identified as comprising > 2% of seasonal diets of elk or deer in TRNP (Genera included: Achillea L., Astragalus L., Campanula L., Fragaria L., Galium L., Glycyrrhiza L., Heuchera L., Monarda L., Oxalis L., Thalictrum L., Toxicodendron P.Mill., Vicia L., and Viola L.
  Invasive forbs Exotic forbs that had demonstrated potential to dominate ground cover in green ash stands in southwestern North Dakota. Included: Arctium minus Bernh., Cirsium arvense (L.) Scop., Euphorbia esula L., Convolvulus arvensis L., and Polygonum convolvulus L.

Independent variables

Changes in vegetation during the monitoring period were related to indices of ungulate utilization of monitored stands, seasonal temperatures, and seasonal precipitation. None of our monitored stands was burned during the 12-year. So we were unable to assess the effects of fire. We never saw pronghorn, bison, or horses or any evidence of their presence within the plots we measured. Elk and deer had access to our sites and were considered the most likely ungulates to have an impact on vegetation at sampling sites. Fecal pellets at sample sites and duration of exposure to ungulate foraging were used to assess elk and deer impacts.

Forty-seven elk were introduced into the South Unit of TRNP in 1985. Numbers increased to approximately 400 by 1993 (Theodore Roosevelt National Park, Unpubl. data). In January 1993, 200 elk were removed from the population. The estimate in 1996 was 300 to 400. Between 1985 and 1992, elk distribution in TRNP expanded from the introduction site to cover all areas of the South Unit that were inside the boundary game fence (approximately 95% of the South Unit). Potential duration of use by elk in stands we sampled at the time of the 1996 vegetation measurements varied from 0 to 12 years.

White-tailed and/or mule deer had access to all of our sample sites from 1985 to 1996. Fall surveys conducted by the North Dakota State Game and Fish Department indicated that mule deer numbers declined by more than 50% between 1985 and 1996 (North Dakota State Game and Fish Department, Unpubl. data). No data were available for white-tailed deer numbers in TRNP, but white-tailed deer were much less common than mule deer in areas where our stands were located.

Weather, especially precipitation and temperature, exert major influences on green ash stands (Girard et al. 1987). Temperatures during 1985 to 1996 were well within historic norms. The warmest and coolest summers of the monitoring period were 1988 and 1993, respectively (Fig. 2). Winter temperatures were generally milder than average with the mildest winter before the 1992 growing season and the coldest before the 1996 growing season. Precipitation during the growing season was greater than 20% below the 30-year average in 1984, 1985, 1988, 1989, and 1990 (Fig. 3). Precipitation was greater than 20% above average in 1986, 1987, and 1993. We included 11 variables related to weather (Table 2) in our analyses. Weather data were obtained from a weather station maintained by TRNP in the South Unit. We attempted to measure all stands before herbaceous plants became desiccated, but in some years we were forced to measure one or more stands after the optimal mid-July to mid-August sampling period. We included month of vegetation measurement as an index to phenology to determine if deviations from our optimal sampling period had detectable impacts on values.

Figure 2: Line graph showing mean temperatures for the summer and winter.
Figure 2.  Mean temperatures for the summer (June - August) and winter (November - March) recorded at the South Unit of Theodore Roosevelt National Park, 1984 to 1996.

Figure 3: Line graph showing precipitation during the growing season and winter.
Figure 3.  Precipitation during the growing season (March - September) and winter (November - March) recorded at the South Unit of Theodore Roosevelt National Park, 1984 to 1996. Means for 1950 to 1996 are displayed as dashed lines in the figure.

Table 2.  Independent variables used in analyses of changes in green ash stands in Theodore Roosevelt National Park during 1985 to 1996.
Variable acronym Definition
Short term effects
  Month Month in which vegetation measurements were taken ( > n = later phenology).
  Pptmo Precipitation (mm) in month vegetation measurements were taken
  Tempmo Mean temperature (°C) of month of vegetation measurement.
One-year effects
  Pptgro Precipitation (mm) in current growing season up to month of vegetation measurement.
  Snow Total precipitation (mm) in winter (Nov - Mar) preceding vegetation measurement.
  Temsum Mean temperature (°C) for growing season up to month of vegetation measurement.
  Temwin Mean temperature (°C) for winter (Nov - Mar) preceding vegetation measurement.
Two-year effects
  Pptprev Precipitation (mm) during growing season (Mar - Oct) one year before vegetation measurement.
  Ppt2y Precipitation in current and previous growing season.
  Snow2y Precipitation in past two winters.
  Temsum2y Sum of summer mean temperatures for current and previous year.
  Temwin2y Sum of winter mean temperatures for two winters prior to measurement.
Ungulate effects
  Elkpel Mean ground cover (%) for elk pellets in 20 ground stratum plots/site.
  Deerpel Mean ground cover (%) for deer pellets in 20 ground stratum.


We used Wilcoxin's ranked sum tests to determine if values for individual vegetation categories (Table 1) changed across all sampled stands between 1985 and 1996 in directions consistent with deer population changes (a greater than 50% decline during 1985 to 1996) or cumulative weather trends (eight of the 12 years had below average growing season precipitation). If deer were negatively affecting vegetation in 1985, the population decline should have lead to increases in palatable shrubs and herbaceous plants by 1996. If below average precipitation negatively affected stands, we should have seen a decline in stem density of woody plants and/or canopy coverage of climax herbaceous species between 1985 and 1996.

We could not do a simple test of vegetation measurements in 1985 versus vegetation measurements in 1996 to identify changes that might be associated with elk impacts on green ash stands because the opportunity for elk to impact green ash communities varied among stands. Elk distribution within TRNP expanded from an area that included four of our sample sites in 1985 to 11 of the 12 sites by 1996. We hypothesized that changes in vegetation and ground cover associated with elk use of stands should increase with the number of years elk had access to a stand. We developed 18 vegetation and ground cover categories from our vegetation data that, based on food habits studies in TRNP (Sullivan 1988, Westfall 1989) and impacts on vegetation reported in other areas (Lyon and Ward 1982, Singer and Harter 1996, Singer et al. 1998, Wambolt 1998, White et al. 1998), we expected to decline following intensive use of a site by elk. Differences between values recorded for these categories in 1985 and 1996 were converted to percent change (V1996 - V1985 /V1985 x 100) and truncated to a range of -100% to +101% to normalize the data and decrease the influence of large proportionate changes in low absolute cover or density measurements. Truncation affected only 11% of the vegetation measurements but reduced the average skew of variables by 53% to -0.38 and the average kurtosis by 21% to 3.69. Truncated percent change between 1985 and 1996 was tested using multiple t-tests on categories paired across sites. If elk did have impacts on green ash stands in TRNP, we expected to see significant differences in mean percent change among a set of stands with zero to 12 years of elk use, and we expected stands with the most years of elk use to have lower average values (i.e. greater negative changes between 1985 and 1996) than stands with the fewest years of elk use.

The changes in vegetation we measured between the 1985 and 1996 sampling periods could also reflect the impacts of short-term (one month to two years) rather than long-term factors. We used two approaches to determine if recent weather patterns or recent ungulate use influenced the changes we observed from one sampling period to another. The strength of association between individual explanatory variables (weather indices and percent ground coverage of elk and deer fecal pellets in stands) and response variables (truncated percent change between measurements in vegetation/ground coverage categories taken at two-year intervals between 1986 and 1996) was determined using Pearson's correlations. The second approach, multivariate analysis, was an attempt to develop a more realistic model for explaining changes in vegetation. Changes in vegetation are highly variable, usually not linear, seldom occur at consistent rates among different species, and frequently involve responses to multiple causative factors. Of the multivariate analytical methods available, we selected logistic regression as the most appropriate for our data based on guidelines presented by Morrison et al. (1998). We used logistic regression to determine if combinations of weather variables and ungulate fecal pellet indices would be useful in predicting the direction of change between sampling periods. Percent changes in vegetation categories between sampling periods were converted to class variables (1 = no change or increase, 2 = decline), and a step-up procedure (P < 0.05 to enter) was applied to identify the variable sets that could best distinguish between positive and negative changes. The MSUSTAT package (Lund 1989) was used for multiple t-tests and correlation analysis. SAS (1994) was used in the logistic regression analysis.

Previous Section -- Study Area
Return to Contents
Next Section -- Results

Accessibility FOIA Privacy Policies and Notices

Take Pride in America logo logo U.S. Department of the Interior | U.S. Geological Survey
Page Contact Information: Webmaster
Page Last Modified: Saturday, 02-Feb-2013 06:29:20 EST
Menlo Park, CA [caww54]