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The Interior Columbia Basin assessment area in the Western United States, encompassing eastern Washington (WA), eastern Oregon (OR), most of Idaho (ID), northwestern Montana (MT), and adjacent areas of northwestern Wyoming (WY), northwestern Utah (UT), and northern Nevada (NV), and the historical habitats of greater sage-grouse within the species' historical range in the Basin (from Wisdom and others 2000).

The Interior Columbia Basin assessment area in the Western United States, encompassing eastern Washington (WA), eastern Oregon (OR), most of Idaho (ID), northwestern Montana (MT), and adjacent areas of northwestern Wyoming (WY), northwestern Utah (UT), and northern Nevada (NV), and the historical habitats of greater sage-grouse within the species' historical range in the Basin (from Wisdom and others 2000).

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Habitats and populations of greater sage-grouse (Centrocercus urophasianus) have declined throughout western North America in response to a myriad of detrimental land uses. Successful restoration of this species' habitat, therefore, is of keen interest to Federal land agencies who oversee management of most remaining habitat. To illustrate the chal...

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Context 1
... this paper, we summarize results of recent landscape evaluations to restore habitats for sage-grouse on lands administered by the U.S. Department of Agriculture, Forest Service, and U.S. Department of the Interior, Bureau of Land Management (FS-BLM) in the Interior Columbia Ba- sin and adjacent portions of the Great Basin (Basin) ( fig. 1). The 58 million-ha Basin encompasses a major portion of current and historical range of greater sage-grouse ( fig. 1) (Wisdom and others 2002a). Proposed management of the Basin's sagebrush steppe will therefore substantially affect sage-grouse and other sagebrush obligates. That as context, our goals were to summarize the conditions ...
Context 2
... lands administered by the U.S. Department of Agriculture, Forest Service, and U.S. Department of the Interior, Bureau of Land Management (FS-BLM) in the Interior Columbia Ba- sin and adjacent portions of the Great Basin (Basin) ( fig. 1). The 58 million-ha Basin encompasses a major portion of current and historical range of greater sage-grouse ( fig. 1) (Wisdom and others 2002a). Proposed management of the Basin's sagebrush steppe will therefore substantially affect sage-grouse and other sagebrush obligates. That as context, our goals were to summarize the conditions projected for greater sage-grouse from a previous study within the Basin (Raphael and others 2001) in relation to two ...

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... Forest Service scientists led the development and implementation of a variety of groundbreaking conceptual models for sage-grouse habitat restoration and recovery as part of the Interior Columbia Basin Ecosystem Management Project (ICBEMP), and later in ecoregional assessments in the Great Basin and across the entire range of Greater Sage-Grouse. Conceptual models developed by FS scientists for sage-grouse restoration and recovery for application across the 58-million ha ICBEMP area include (1) novel state-and-transitions models for sagebrush to evaluate future sagebrush habitat trajectories ; (2) innovative Bayesian belief network models developed and applied by Wisdom et al. (2002a) for evaluating current and future sage-grouse habitats; (3) development of a new habitat network approach for sagebrush-dependent species, including sage-grouse, and demonstration of this conceptual model in restoration planning (Wisdom et al. 2002b); and (4) additional integration and synthesis of sage-grouse models for restoration planning (Wisdom et al. 2005a). ...
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The primary purpose of this FS R&D Sage-Grouse Conservation Science Strategy is to promote understanding and recognition of FS strengths, science leadership and collaborative opportunities in key areas of sagebrush and sage-grouse science, identify Research Priorities and Goals based on a review of existing knowledge and future needs, stimulate increased development and delivery of sage-grouse conservation knowledge, and serve as a communication and planning guide for managers, staff, and scientists working on or concerned about sage-grouse related issues. The strategy aims to improve awareness of our collective expertise, partnerships, and existing facility resources by summarizing the sage-grouse conservation science conducted by FS R&D.
... scientists for sage-grouse restoration and recovery for application across the 58-million ha ICBEMP area include: 1) novel state-and-transitions models for sagebrush to evaluate future sagebrush habitat trajectories (Hemstrom et al. 2002); 2) innovative Bayesian belief network models developed and applied by Wisdom et al. (2002a) for evaluating current and future sage-grouse habitats; 3) development of a new habitat network approach for sagebrushdependent species, including sage-grouse, and demonstration of this conceptual model in Figure 15-Fruiting bodies of the seed pathogen Pyrenophora semeniperda, which illustrate why the pathogen was given its nickname "black fingers of death" (Photo by Susan Meyer, USDA Forest Service). restoration planning (Wisdom et al. 2002b); and 4) additional integration and synthesis of sage-grouse models for restoration planning (Wisdom et al. 2005a). ...
... Rowland and Wisdom (2009) also developed and applied new habitat network approaches for sagebrush-dependent vertebrate species in the Great Basin, including sage-grouse. FS-led conceptual models for sagebrush habitat restoration and sage-grouse recovery across the historical range of the species include those by Wisdom et al. (2005a), which introduced novel modeling paradigms and management approaches for prioritizing landscape conservation and restoration. ...
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... greater sage-grouse and its habitat). Conceptual models developed by FS scientists for sage-grouse restoration and recovery for application across the 58-million ha ICBEMP area include: (1) novel state-and-transitions models for sagebrush to evaluate future sagebrush habitat trajectories (Hemstrom et al. 2002); (2) innovative Bayesian belief network models developed and applied by Wisdom et al. (2002a) for evaluating current and future sage-grouse habitats; (3) development of a new habitat network approach for sagebrush-dependent species, including sage-grouse, and demonstration of this conceptual model in restoration planning (Wisdom et al. 2002b); and (4) additional integration and synthesis of sage-grouse models for restoration planning (Wisdom et al. 2005a). ...
... Rowland and Wisdom (2009) also developed and applied new habitat network approaches for sagebrush-dependent vertebrate species in the Great Basin, including sage-grouse. FS-led conceptual models for sagebrush habitat restoration and sage-grouse recovery across the historical range of the species include those by Wisdom et al. (2005a), which introduced novel modeling paradigms and management approaches for prioritizing landscape conservation and restoration. ...
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A recurrent challenge in the conservation of wide-ranging, imperiled species is understanding which habitats to protect and whether we are capable of restoring degraded landscapes. For Greater Sage-grouse (Centrocercus urophasianus), a species of conservation concern in the western United States, we approached this problem by developing multi-scale empirical models of occupancy in 211 randomly located plots within a 40 million ha portion of the species' range. We then used these models to predict sage-grouse habitat quality at 826 plots associated with 101 post-wildfire seeding projects implemented from 1990 to 2003. We also compared conditions at restoration sites to published habitat guidelines. Sage-grouse occupancy was positively related to plot- and landscape-level dwarf sagebrush (Artemisia arbuscula, A. nova, A. tripartita) and big sagebrush steppe prevalence, and negatively associated with non-native plants and human development. The predicted probability of sage-grouse occupancy at treated plots was low on average (0.09) and not substantially different from burned areas that had not been treated. Restoration sites with quality habitat tended to occur at higher elevation locations with low annual temperatures, high spring precipitation, and high plant diversity. Of 313 plots seeded after fire, none met all sagebrush guidelines for breeding habitats, but approximately 50% met understory guidelines, particularly for perennial grasses. This pattern was similar for summer habitat. Less than 2% of treated plots met winter habitat guidelines. Restoration actions did not increase the probability of burned areas meeting most guideline criteria. The probability of meeting guidelines was influenced by a latitudinal gradient, climate, and topography. Our results suggest that sage-grouse are relatively unlikely to use many burned areas within 20 years of fire, regardless of treatment. Understory habitat conditions are more likely to be adequate than overstory conditions, but in most climates, establishing forbs and reducing cheatgrass dominance is unlikely. Reestablishing sagebrush cover will require more than 20 years using past restoration methods. Given current fire frequencies and restoration capabilities, protection of landscapes containing a mix of dwarf sagebrush and big sagebrush steppe, minimal human development, and low non-native plant cover may provide the best opportunity for conservation of sage-grouse habitats.
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... Tying population monitoring and ecological indicators together will enable managers to identify indicators associated with population change across broad spatial scales and to ameliorate negative effects with appropriate conservation actions (Burgman et al. 2005, Turner 2005). Moreover, this process will help integrate monitoring efforts by states with those of federal agencies, who are required to assess the effectiveness of land management at achieving desired population objectives in sagebrush habitats (Wisdom et al. 2005). Standardization of field methods and implementation of a defensible monitoring approach is vital if we are to use the resulting information to guide implementation of conservation activities. ...
... Previously widespread, the species has been extirpated from ~50% of its original range (), with an estimated range-wide population decline of 45-80% and local declines of 17-92% (, Braun 1998, Aldridge and Brigham 2003). Loss and degradation of habitat from anthropogenic change are the most important historical and current factors leading to isolation, reduction and extirpation of populations (Braun 1998,b, Aldridge and Brigham 2002, Knick et al. 2003, Wisdom et al. 2005). Concerns such as West Nile virus (Naugle et al. 2004, Walker et al. 2004) and genetic isolation (Oyler-McCance et al. 2005) led the U.S. Fish and Wildlife Service (USFWS) to consider protecting sage-grouse populations under the Endangered Species Act in 2004. ...
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This review summarizes the fire effects information and relevant ecology of greater sage-grouse and Gunnison sage-grouse in North America that was available in the scientific literature as of 2016. It is available at: https://www.fs.fed.us/database/feis/animals/bird/cent/all.html