Allometric Modeling of Bunchgrasses in Big Sagebrush Plant Communities

2021 ◽  
Vol 79 ◽  
pp. 77-86
Author(s):  
Alexandra J. Smith ◽  
Daniel R. Schlaepfer ◽  
Kyle A. Palmquist ◽  
Ingrid C. Burke ◽  
William K. Lauenroth
2011 ◽  
Vol 144 (11) ◽  
pp. 2573-2584 ◽  
Author(s):  
Kirk W. Davies ◽  
Chad S. Boyd ◽  
Jeffrey L. Beck ◽  
Jon D. Bates ◽  
Tony J. Svejcar ◽  
...  

2019 ◽  
Vol 79 (2) ◽  
pp. 233 ◽  
Author(s):  
Lacey Wilder ◽  
Kari E. Veblen ◽  
Eugene W. Schupp ◽  
Thomas A. Monaco

Weed Science ◽  
1970 ◽  
Vol 18 (1) ◽  
pp. 89-97 ◽  
Author(s):  
James A. Young ◽  
Raymond A. Evans

We characterized soil and vegetation assemblages, many of which are infested with medusahead (Taeniatherum asperum(Sim.) Nevski), on the margin of the Great Basin. Interpretations of these assemblages provide an index of the validity of the basic environmental unit of this ecosystem which can be manipulated through weed control and revegetation techniques. Vertisol (churning clay soils) sites with sparse native plant communities are more susceptible to medusahead invasion than more complex low sagebrush (Artemisia arbusculaNutt.) or low sagebrush-woodland communities on related clay soils. If the more complex communities are degraded to a low seral state, medusahead can invade and occupy the site. Wet meadows and burned coniferous forest sites at high elevations were the only sites where medusahead occurred on soils with textures other than clay. Big sagebrush (Artemisia tridentataNutt.) communities on medium to coarse textured soils were very resistant to medusahead invasion. The restriction of medusahead to certain sites controls the mechanism of invasion and interacts with the breeding system of the species to influence its evolution.


2016 ◽  
Vol 69 (3) ◽  
pp. 179-184 ◽  
Author(s):  
K.W. Davies ◽  
A.M. Nafus ◽  
C.S. Boyd ◽  
A. Hulet ◽  
J.D. Bates

2015 ◽  
Vol 24 (4) ◽  
pp. 527 ◽  
Author(s):  
Chad S. Boyd ◽  
Kirk W. Davies ◽  
April Hulet

Maintenance and post-fire rehabilitation of perennial bunchgrasses is important for reducing the spread of exotic annual grass species in big sagebrush plant communities. Post-fire rehabilitation decisions are hampered by a lack of tools for determining extent of fire-induced perennial grass mortality. Our objective was to correlate post-fire characteristics with perennial bunchgrass mortality at the plant and plant community scales. We recorded basal area, percent char, depth of burn and soil colour for 174 bunchgrasses across four ecological sites after a 65 000 ha wildfire in south-east Oregon and assessed plant mortality. Mortality was correlated with post-fire soil colour and ecological site; soil colours (black and grey) associated with pre-fire shrub presence had up to five-fold higher mortality than brown soils typical of interspace locations. Models incorporating depth of burn and soil colour correctly predicted mortality for 90% of individual plants; cover of brown soil explained 88% of the variation in bunchgrass mortality at the plant community scale. Our results indicate that soil colour and depth of burn are accurate predictors of bunchgrass mortality at individual plant and plant community scales and could be used to spatially allocate post-fire bunchgrass rehabilitation resources.


2010 ◽  
Vol 3 (3) ◽  
pp. 294-300 ◽  
Author(s):  
Roger L. Sheley ◽  
Jeremy James

AbstractUnderstanding the relative importance of various functional groups in minimizing invasion by medusahead is central to increasing the resistance of native plant communities. The objective of this study was to determine the relative importance of key functional groups within an intact Wyoming big sagebrush–bluebunch wheatgrass community type on minimizing medusahead invasion. Treatments consisted of removal of seven functional groups at each of two sites, one with shrubs and one without shrubs. Removal treatments included (1) everything, (2) shrubs, (3) perennial grasses, (4) taprooted forbs, (5) rhizomatous forbs, (6) annual forbs, and (7) mosses. A control where nothing was removed was also established. Plots were arranged in a randomized complete block with 4 replications (blocks) at each site. Functional groups were removed beginning in the spring of 2004 and maintained monthly throughout each growing season through 2009. Medusahead was seeded at a rate of 2,000 seeds m−2 (186 seeds ft−2) in fall 2005. Removing perennial grasses nearly doubled medusahead density and biomass compared with any other removal treatment. The second highest density and biomass of medusahead occurred from removing rhizomatous forbs (phlox). We found perennial grasses played a relatively more significant role than other species in minimizing invasion by medusahead. We suggest that the most effective basis for establishing medusahead-resistant plant communities is to establish 2 or 3 highly productive grasses that are complementary in niche and that overlap that of the invading species.


Plant Ecology ◽  
2017 ◽  
Vol 218 (8) ◽  
pp. 957-970 ◽  
Author(s):  
Victoria E. Pennington ◽  
Kyle A. Palmquist ◽  
John B. Bradford ◽  
William K. Lauenroth

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