Mowing Wyoming Big Sagebrush (Artemisia tridentata ssp. wyomingensis) Cover Effects Across Northern and Central Nevada

2016 ◽  
Vol 69 (5) ◽  
pp. 360-372 ◽  
Author(s):  
Sherman R. Swanson ◽  
John C. Swanson ◽  
Peter J. Murphy ◽  
J. Kent McAdoo ◽  
Brad Schultz
2016 ◽  
Vol 25 (9) ◽  
pp. 933 ◽  
Author(s):  
Douglas J. Shinneman ◽  
Susan K. McIlroy

Sagebrush steppe of North America is considered highly imperilled, in part owing to increased fire frequency. Sagebrush ecosystems support numerous species, and it is important to understand those factors that affect rates of post-fire sagebrush recovery. We explored recovery of Wyoming big sagebrush (Artemisia tridentata ssp. wyomingensis) and basin big sagebrush (A. tridentata ssp. tridentata) communities following fire in the northern Columbia Basin (Washington, USA). We sampled plots across 16 fires that burned in big sagebrush communities from 5 to 28 years ago, and also sampled nearby unburned locations. Mixed-effects models demonstrated that density of large–mature big sagebrush plants and percentage cover of big sagebrush were higher with time since fire and in plots with more precipitation during the winter immediately following fire, but were lower when precipitation the next winter was higher than average, especially on soils with higher available water supply, and with greater post-fire mortality of mature big sagebrush plants. Bunchgrass cover 5 to 28 years after fire was predicted to be lower with higher cover of both shrubs and non-native herbaceous species, and only slightly higher with time. Post-fire recovery of big sagebrush in the northern Columbia Basin is a slow process that may require several decades on average, but faster recovery rates may occur under specific site and climate conditions.


2015 ◽  
Vol 5 (1) ◽  
pp. 17
Author(s):  
Karen A. Kitchen ◽  
Brittany Goldsmith ◽  
Jim Robison-Cox ◽  
Michael Frisina ◽  
Bok Sowell

<p class="emsd">Sagebrush habitat is declining throughout the United States. This can have negative impacts for big game as well as other wildlife species. The purpose of our research was to analyze the relationship between several abiotic factors and the cover of two conifer species, Douglas-fir (<em>Pseudotsuga menziesii</em>) and Rocky Mountain juniper (<em>Juniperus scopulorum</em>), on the cover of Wyoming (<em>Artemisia tridentata spp. wyomingensis</em>) and mountain (<em>Artemisia tridentata spp. Vaseyana</em>) big sagebrush. Abiotic factors, percent cover of sagebrush and conifers, and individual conifer age and canopy area were recorded at 40 Wyoming and 40 mountain big sagebrush plots at each of three study sites in southwest Montana (n = 240). No correlation was found between any abiotic factor and live sagebrush cover over all sites (p&gt;0.05). A model of the relationship between the combined cover of the two conifer species and the two subspecies of big sagebrush was developed. The best-fit model included the terms: study site, sagebrush subspecies,  and the interaction, study site by sagebrush subspecies as the independent variables, with as the dependent variable (  = Intercept<sub>i</sub>– 0.401 ; R<sup>2</sup> = 0.61). There was a negative relationship between conifer cover and sagebrush cover and no difference in the effects of conifer cover on the two sagebrush subspecies. Validation trials were successful at one of three locations outside the study area and suggested that the model is better suited to lower elevation, less productive sites. Individual Douglas-fir have a 3 fold larger canopy area than Rocky Mountain juniper at comparable ages (p&lt;0.001). Controlling conifers to increase Wyoming big sagebrush does not appear to be effective due to the low level of sagebrush cover. If conifer control is desired, Douglas-fir should be targeted over Rocky Mountain juniper on mountain big sagebrush sites, but not on Wyoming big sagebrush sites.</p>


1989 ◽  
Vol 3 (4) ◽  
pp. 640-645 ◽  
Author(s):  
Myles J. Watts ◽  
Carl L. Wambolt

The economic feasibility of four Wyoming big sagebrush control methods: burning, spraying with 2,4-D, plowing and seeding, and rotocutting was analyzed. Perennial grass response to big sagebrush treatment was measured to estimate a treatment response function for each control method which provided the biological informational base to develop cost and benefits. Annualized present values of net additional returns for single 2,4-D and burning treatments were $1.10/ha and $1.16/ha, respectively. When big sagebrush was retreated at optimal intervals, 2,4-D and burning generated annualized net additional returns of $2.88/ha and $2.57/ha, respectively. Rotocutting was marginally feasible, and plowing was not feasible.


2013 ◽  
Vol 14 (1) ◽  
pp. 60-70 ◽  
Author(s):  
R. P. Karrfalt ◽  
N. Shaw

2011 ◽  
Vol 12 (3) ◽  
pp. 263-267 ◽  
Author(s):  
R. D. Cox ◽  
L. H. Kosberg ◽  
N. L. Shaw ◽  
S. P. Hardegree

Oecologia ◽  
2001 ◽  
Vol 126 (2) ◽  
pp. 239-246 ◽  
Author(s):  
John H. Graham ◽  
E. Durant McArthur ◽  
D. Carl Freeman

2006 ◽  
Vol 20 (3) ◽  
pp. 183-194 ◽  
Author(s):  
Ann L. Hild ◽  
Gerald E. Schuman ◽  
Laurel E. Vicklund ◽  
Mary I. Williams

Sign in / Sign up

Export Citation Format

Share Document