scholarly journals Long-term changes in sage grouse Centrocercus urophasianus populations in western North America

1997 ◽  
Vol 3 (1) ◽  
pp. 229-234 ◽  
Author(s):  
John W. Connelly ◽  
Clait E. Braun
The Condor ◽  
1991 ◽  
Vol 93 (1) ◽  
pp. 130-137 ◽  
Author(s):  
Leonard A. Brennan ◽  
Michael L. Morrison

2019 ◽  
Vol 15 (6) ◽  
pp. 20190011 ◽  
Author(s):  
Jesse L. Morris ◽  
R. Justin DeRose ◽  
Thomas Brussel ◽  
Simon Brewer ◽  
Andrea Brunelle ◽  
...  

As important centres for biological diversity, aspen forests are essential to the function and aesthetics of montane ecosystems in western North America. Aspen stands are maintained by a nuanced relationship with wildfire, although in recent decades aspen mortality has increased. The need to understand the baseline environmental conditions that favour aspen is clear; however, long-term fire history reconstructions are rare due to the scarcity of natural archives in dry montane settings. Here, we analyse a high-resolution lake sediment record from southwestern, Utah, USA to quantify the compositional and burning conditions that promote stable (or seral) aspen forests. Our results show that aspen presence is negatively correlated with subalpine fir and that severe fires tend to promote persistent and diverse aspen ecosystems over centennial timescales. This information improves our understanding of aspen disturbance ecology and identifies the circumstances where critical transitions in montane forests may occur.


2016 ◽  
Vol 5 (2) ◽  
pp. 129
Author(s):  
Krystle A. Wengreen ◽  
Michael Frisina ◽  
Julie L. Hager ◽  
Bok F. Sowell

<p class="emsd-body"><span lang="EN-GB">Greater sage-grouse <span class="search1">(<em>Centrocercus urophasianus)</em> is</span> a high priority species for federal and state land management agencies in the Western United States. Sage-grouse<span class="search1"> are sagebrush (<em>Artemisia spp</em>.) obligates requiring sagebrush for their survival throughout the year. Sagebrush has been removed and replaced with crested wheatgrass </span>(<em>Agropyron</em><em>cristatum</em><span class="search1"> &amp; </span><em>A.</em><em>desertorum</em><span class="search1">) throughout the West. The objectives of this paper were to review the literature (100 papers), as well as consult experts, to determine which methods are most likely to eliminate crested wheatgrass and establish sagebrush. No technique eliminates crested wheatgrass in a single application but research suggests it should not comprise more than 14% cover for successful reseeding of other species. Grazing and fire have no long-term impacts on crested wheatgrass. Mechanical treatments, such as plowing, disking, and cultivating reduce and eradicate crested wheatgrass, but a flush of invasive annual grasses following mechanical disturbance can make establishment of seeded species difficult. </span><span class="search1"><span>If invasive plant establishment is a problem with mechanical treatments, crested wheatgrass stands should be treated with </span>glyphosate in early spring for two consecutive years at a rate of 1.1 kg/ha of active ingredient. Then, sagebrush should be seeded in the late fall using a compact row seeder or Brillion cultipacker at a rate of 0.22 kg/ha pure live seed. </span></span></p>


The Condor ◽  
10.1650/7131 ◽  
2003 ◽  
Vol 105 (4) ◽  
pp. 737 ◽  
Author(s):  
Grant Ballard ◽  
Geoffrey R. Geupel ◽  
Nadav Nur ◽  
Thomas Gardali

The Condor ◽  
2004 ◽  
Vol 106 (2) ◽  
pp. 363-376 ◽  
Author(s):  
Michael A. Schroeder ◽  
Cameron L. Aldridge ◽  
Anthony D. Apa ◽  
Joseph R. Bohne ◽  
Clait E. Braun ◽  
...  

Abstract We revised distribution maps of potential presettlement habitat and current populations for Greater Sage-Grouse (Centrocercus urophasianus) and Gunnison Sage- Grouse (C. minimus) in North America. The revised map of potential presettlement habitat included some areas omitted from previously published maps such as the San Luis Valley of Colorado and Jackson area of Wyoming. Areas excluded from the revised maps were those dominated by barren, alpine, and forest habitats. The resulting presettlement distribution of potential habitat for Greater Sage-Grouse encompassed 1 200 483 km2, with the species' current range 668 412 km2. The distribution of potential Gunnison Sage-Grouse habitat encompassed 46 521 km2, with the current range 4787 km2. The dramatic differences between the potential presettlement and current distributions appear related to habitat alteration and degradation, including the adverse effects of cultivation, fragmentation, reduction of sagebrush and native herbaceous cover, development, introduction and expansion of invasive plant species, encroachment by trees, and issues related to livestock grazing. Distribución de Centrocercus spp. en América del Norte Resumen. Revisamos los mapas de distribución potencial precolombino y de poblaciones actuales de Centrocerus urophasianus y C. minimus en América del Norte. El mapa modificado de hábitat potencial precolombino incluyó algunas áreas omitidas de mapas anteriormente publicados, como el Valle San Luis de Colorado y el área de Jackson, Wyoming. Las áreas excluídas de los mapas modificados fueron las dominadas por hábitats forestales, alpinos y estériles. La distribución precolombina resultante para C. urophasianus abarcó 1 200 483 km2, con un territorio actual de 668 412 km2. La distribución de habitat potencial para C. minimus abarcó 46 521 km2, con un territorio actual de 4787 km2. Estos contrastes tan marcados parecen estar relacionados con la modificación y degradación del hábitat, incluyendo los efectos nocivos de la agricultura, la fragmentación de hábitat, la disminución de Artemisia spp. y otras coberturas herbáceas nativas, el desarollo, la introducción y la expansión de especies de plantas invasoras, la invasión de árboles y cuestiones relacionadas con pastoreo de ganado.


Sign in / Sign up

Export Citation Format

Share Document