utah juniper
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2021 ◽  
Vol 480 ◽  
pp. 118639
Author(s):  
Steven A. Kannenberg ◽  
Avery W. Driscoll ◽  
Danielle Malesky ◽  
William R.L. Anderegg

Fire ◽  
2020 ◽  
Vol 3 (1) ◽  
pp. 6
Author(s):  
Scott M. Frost ◽  
Martin E. Alexander ◽  
R. Justin DeRose ◽  
Michael J. Jenkins

The planning of fuel treatments for ecological or societal purposes requires an in-depth understanding of the conditions associated with the occurrence of free-burning fire behavior for the area of concern. Detailed fire-environment analysis for Army Garrison Camp Williams (AGCW) in north-central Utah was completed as a prerequisite for fuel treatment planning, using a procedure that could be generally applied. Vegetation and fuels data, topographic and terrain features, and weather and climate data, were assessed and integrated into predictive fuel models to aid planning. A fire behavior fuel model map was developed from biophysical variables, vegetation type, and plot survey data using random forests, and resulted in an overall classification rate of 72%. The predominate vegetation type-fuel complex was grass, followed by lesser amounts of Gambel oak, Wyoming big sagebrush and Utah juniper. The majority of AGCW is mountainous in nature, characterized by slopes less than 40% in steepness with slightly more northerly and easterly aspects than south and west, and elevations that ranged from 1650 to 1950 m above mean sea level. Local fire weather data compiled from the three nearest remote automated weather stations indicated that average temperature maxima (32 °C) and relative humidity minima (12%) usually occurred between 1400 to 1500 h daily, and from July to August, seasonally. The semi-arid climate at AGCW, coupled with the corresponding preponderance of flashy fuel types and sloping terrain, constitutes a formidable fire environment in which to plan for mitigating against adverse fire behavior.


Geosites ◽  
2019 ◽  
Vol 1 ◽  
pp. 1-7
Author(s):  
Carl Ege

Why take your kids to the neighborhood playground, when you can visit a playground that inspires their sense of geologic adventure? Devils Playground is not your ordinary community playground, but a wonderland of granitic rock weathered into fantastic forms and weird shapes. Occupying an assortment of Bureau of Land Management, state, and private land in the Bovine Mountains, Devils Playground is a relatively unknown geologic curiosity found in a remote corner of northwestern Utah. Devils Playground is situated in the physiographic region known as the Great Basin province that extends across western Utah, Nevada, and to the Sierra Nevada Mountains in eastern California. The area is composed mostly of granitic rocks of the Emigrant Pass intrusion. A combination of granitic rock, faulting, and weathering under a semiarid climate created favorable conditions for the creation of Devils Playground. Desert plants such as sagebrush,Utah juniper, pinyon pine, Mormon tea, and cheatgrass are common throughout the area.


2018 ◽  
Vol 71 (3) ◽  
pp. 327-335 ◽  
Author(s):  
Tamzen K. Stringham ◽  
Keirith A. Snyder ◽  
Devon K. Snyder ◽  
Samuel S. Lossing ◽  
Craig A. Carr ◽  
...  

2016 ◽  
Vol 72 (1) ◽  
pp. 1-14 ◽  
Author(s):  
R. Justin Derose ◽  
Matthew F. Bekker ◽  
Roger Kjelgren ◽  
Brendan M. Buckley ◽  
James H. Speer ◽  
...  

2015 ◽  
Vol 61 (1) ◽  
pp. 162-168
Author(s):  
Wesley Sprinkle ◽  
John Klepac
Keyword(s):  

2015 ◽  
Vol 24 (2) ◽  
pp. 236 ◽  
Author(s):  
Kert R. Young ◽  
Bruce A. Roundy ◽  
Stephen C. Bunting ◽  
Dennis L. Eggett

Juniper (Juniperus spp.) and piñon (Pinus spp.) trees have encroached millions of hectares of sagebrush (Artemisia spp.)–bunchgrass communities. Juniper–piñon trees are treated to reduce canopy fuel loads and crown fire potential. We measured the effects of juniper–piñon infilling and fuel-reduction treatments on fuel load characteristics at four locations in Utah. At each location, treatment areas were burned, left untreated, or trees were cut or masticated in a randomised complete-block design. We measured standing and downed fuels by size and type along 30-m transects on 15 subplots (30 × 33 m) per location before and 1–3 years after treatment. Increased tree cover was associated with decreased shrub and herbaceous fuel loads (P < 0.01). By 2 years post-treatment, herbaceous fuel loads were greater than pretreatment in all treated areas (P < 0.01). Cut and mastication treatments increased surface woody 10- and 100-h fuel loads and wood/bark cover (P < 0.01). Masticated-tree depth was a good estimator of fuel loads (R2 = 92). The conversion of canopy fuels to surface fuels reduced fuels that enable crown fire and extreme fire intensity. Cool-season prescribed fire may need to follow mechanical treatments to reduce surface fuel and the potential for wildfire damage to perennial understorey vegetation.


2014 ◽  
Vol 113 (4) ◽  
pp. A21
Author(s):  
Richard W. Weber
Keyword(s):  

2014 ◽  
Vol 2014 ◽  
pp. 1-10 ◽  
Author(s):  
Kert R. Young ◽  
Bruce A. Roundy ◽  
Dennis L. Eggett

Juniper (Juniperusspp.) has encroached on millions of hectares of sagebrush (Artemisiaspp.) steppe. Juniper mechanical mastication increases cover of understory species but could increase resource availability and subsequently invasive plant species. We quantified the effects of juniper mastication on soil resource availability by comparing total C, total N, C : N ratio, Olsen extractable P, sulfate S, and pH using soil samples and inorganic N (NO3-+NH4+) using ion exchange membranes. We compared resource availability in paired masticated and untreated areas in three juniper-dominated sagebrush and bunchgrass ecosystems in the Utah portion of the Great Basin. Inorganic N was 4.7 times higher in masticated than in untreated areas across seasons (P<0.001). Within masticated areas, tree mounds of juniper leaf scales and twigs served as resource islands with 1.9 times higher inorganic N and total C, and 2.8 times higher total N than bare interspaces across seasons (P<0.01). Bare interspaces had 3.0–3.4 times higher inorganic N than interspaces covered with masticated trees during late-summer through winter (P<0.01). Soil fertility changes associated with mastication were not considered sufficient to favor establishment of annual over perennial grasses, and we expect both to increase in cover following juniper mastication.


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