Research article Special Issues

Climate change and land management impact rangeland condition and sage-grouse habitat in southeastern Oregon

  • Received: 10 December 2014 Accepted: 18 March 2015 Published: 06 April 2015
  • Contemporary pressures on sagebrush steppe from climate change, exotic species, wildfire, and land use change threaten rangeland species such as the greater sage-grouse (Centrocercus urophasianus). To effectively manage sagebrush steppe landscapes for long-term goals, managers need information about the potential impacts of climate change, disturbances, and management activities. We integrated information from a dynamic global vegetation model, a sage-grouse habitat climate envelope model, and a state-and-transition simulation model to project broad-scale vegetation dynamics and potential sage-grouse habitat across 23.5 million acres in southeastern Oregon. We evaluated four climate scenarios, including continuing current climate and three scenarios of global climate change, and three management scenarios, including no management, current management and a sage-grouse habitat restoration scenario. All climate change scenarios projected expansion of moist shrub steppe and contraction of dry shrub steppe, but climate scenarios varied widely in the projected extent of xeric shrub steppe, where hot, dry summer conditions are unfavorable for sage-grouse. Wildfire increased by 26% over the century under current climate due to exotic grass encroachment, and by two- to four-fold across all climate change scenarios as extreme fire years became more frequent. Exotic grasses rapidly expanded in all scenarios as large areas of the landscape initially in semi-degraded condition converted to exotic-dominated systems. Due to the combination of exotic grass invasion, juniper encroachment, and climatic unsuitability for sage-grouse, projected sage-grouse habitat declined in the first several decades, but increased in area under the three climate change scenarios later in the century, as moist shrub steppe increased and rangeland condition improved. Management activities in the model were generally unsuccessful in controlling exotic grass invasion but were effective in slowing woodland expansion. Current levels of restoration treatments were insufficient to prevent some juniper expansion, but increased treatment rates under the restoration scenario maintained juniper near initial levels in priority treatment areas. Our simulations indicate that climate change may have both positive and negative implications for maintaining sage-grouse habitat.

    Citation: Megan K. Creutzburg, Emilie B. Henderson, David R. Conklin. Climate change and land management impact rangeland condition and sage-grouse habitat in southeastern Oregon[J]. AIMS Environmental Science, 2015, 2(2): 203-236. doi: 10.3934/environsci.2015.2.203

    Related Papers:

  • Contemporary pressures on sagebrush steppe from climate change, exotic species, wildfire, and land use change threaten rangeland species such as the greater sage-grouse (Centrocercus urophasianus). To effectively manage sagebrush steppe landscapes for long-term goals, managers need information about the potential impacts of climate change, disturbances, and management activities. We integrated information from a dynamic global vegetation model, a sage-grouse habitat climate envelope model, and a state-and-transition simulation model to project broad-scale vegetation dynamics and potential sage-grouse habitat across 23.5 million acres in southeastern Oregon. We evaluated four climate scenarios, including continuing current climate and three scenarios of global climate change, and three management scenarios, including no management, current management and a sage-grouse habitat restoration scenario. All climate change scenarios projected expansion of moist shrub steppe and contraction of dry shrub steppe, but climate scenarios varied widely in the projected extent of xeric shrub steppe, where hot, dry summer conditions are unfavorable for sage-grouse. Wildfire increased by 26% over the century under current climate due to exotic grass encroachment, and by two- to four-fold across all climate change scenarios as extreme fire years became more frequent. Exotic grasses rapidly expanded in all scenarios as large areas of the landscape initially in semi-degraded condition converted to exotic-dominated systems. Due to the combination of exotic grass invasion, juniper encroachment, and climatic unsuitability for sage-grouse, projected sage-grouse habitat declined in the first several decades, but increased in area under the three climate change scenarios later in the century, as moist shrub steppe increased and rangeland condition improved. Management activities in the model were generally unsuccessful in controlling exotic grass invasion but were effective in slowing woodland expansion. Current levels of restoration treatments were insufficient to prevent some juniper expansion, but increased treatment rates under the restoration scenario maintained juniper near initial levels in priority treatment areas. Our simulations indicate that climate change may have both positive and negative implications for maintaining sage-grouse habitat.


    加载中
    [1] Jones A (2000) Effects of cattle grazing on North American ecosystems: a quantitative review. West N Am Naturalist 60: 155-164.
    [2] DiTomaso JM (2000) Invasive weeds in rangelands: Species, impacts, and management. Weed Sci 48: 255-265. doi: 10.1614/0043-1745(2000)048[0255:IWIRSI]2.0.CO;2
    [3] Miller RF, Bates JD, Svejcar TJ, et al. (2005) Biology, ecology, and management of western juniper. Tech Bull 152. Corvallis, OR: Oregon State University, Agricultural Experiment Station. 82 p.
    [4] Miller RF, Eddleman LE (2001) Spatial and temporal changes of sage grouse habitat in the sagebrush biome. Tech Bull 151. Corvallis, OR: Oregon State University Agricultural Experiment Station.
    [5] Schroeder MA, Aldridge CL, Apa AD, et al. (2004) Distribution of sage-grouse in North America. Condor 106: 363-376. doi: 10.1650/7425
    [6] Connelly JW, Knick ST, Schroeder MA, et al. (2004) Conservation assessment of Greater sage-grouse and sagebrush habitats. Cheyenne, WY: Western Association of Fish and Wildlife Agencies. 610 p.
    [7] Braun CE, Connelly JW, Schroeder MA (2005) Seasonal habitat requirements for sage-grouse: spring, summer, fall, and winter. In: Shaw NL, Pellant M, Monsen SB, editors. Sage-grouse habitat restoration symposium proceedings: June 4-7, Boise, ID Proc RMRS-P-38. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station Proceedings RMRS-P-38. pp. 130.
    [8] Knick ST, Connelly JW, editors (2011) Greater sage-grouse: ecology and conservation of a landscape species and its habitats. Studies in Avian Biology 38. Berkeley, CA: University of California Press.
    [9] Crawford JA, Olson RA, West NE, et al. (2004) Ecology and management of sage-grouse and sage-grouse habitat. J Range Manage 57: 2-19.
    [10] US Department of the Interior (2010) Endangered and threatened wildlife and plants; 12-month findings for petitions to list the greater sage-grouse (Centrocercus urophasianus) as threatened or endangered. Federal Register 75:13910-14014 (23 March 2010).
    [11] Mack RN (1981) Invasion of Bromus tectorum L. into western North America: an ecological chronicle. Agro-Ecosystems 7: 145-165.
    [12] Soulé PT, Knapp PA (1999) Western juniper expansion on adjacent disturbed and near-relict sites. J Range Manage 52: 525-533. doi: 10.2307/4003782
    [13] Miller RF, Svejcar TJ, Rose JA (2000) Impacts of western juniper on plant community composition and structure. J Range Manage 53: 574-585. doi: 10.2307/4003150
    [14] Pellant M (1996) Cheatgrass: the invader that won the West. Bureau of Land Management, Idaho State Office. 23 p.
    [15] Whisenant SG (1990) Changing fire frequencies on Idaho's Snake River Plains: ecological and management implications. In: McArthur ED, Romney EM, Smith SD et al., editors. Proceedings: symposium on cheatgrass invasion, shrub die-off, and other aspects of shrub biology and management. Gen Tech Rep INT-276. Gen Tech Rep INT-276 ed. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station. pp. 4-10.
    [16] Miller RF, Rose JA (1995) Historic expansion of Juniperus occidentalis (western juniper) in southeastern Oregon. Great Basin Nat 55: 37-45.
    [17] Burkhardt JW, Tisdale EW (1976) Causes of juniper invasion in southwestern Idaho. Ecology 57: 472-484. doi: 10.2307/1936432
    [18] Bunting SC, Kingery JL, Strand E (1999) Effects of succession on species richness of the western juniper woodland/sagebrush steppe mosaic. In: Monsen SB, Richards S, Tausch RJ et al., editors. Proceedings: Ecology and management of piñon-juniper communities within the Interior West: USDA Forest Service, Rocky Mountain Research Station-P-9.
    [19] Mote P, Snover AK, Capalbo S, et al. (2014) Ch. 21: Northwest. In: Melillo JM, Richmond TC, Yohe GW, editors. Climate Change Impacts in the United States: The Third National Climate Assessment: U.S. Global Change Research Program.
    [20] Abatzoglou JT, Kolden CA (2011) Climate change in western US deserts: potential for increased wildfire and invasive annual grasses. Rangeland Ecol Manag 64: 471-478. doi: 10.2111/REM-D-09-00151.1
    [21] Abatzoglou JT, Rupp DE, Mote PW (2014) Seasonal climate variability and change in the Pacific Northwest of the United States. J Climate 27: 2125-2142. doi: 10.1175/JCLI-D-13-00218.1
    [22] Bradley BA, Oppenheimer M, Wilcove DS (2009) Climate change and plant invasions: restoration opportunities ahead? Global Change Biol 15: 1511-1521. doi: 10.1111/j.1365-2486.2008.01824.x
    [23] Beschta RL, Donahue DL, DellaSala DA, et al. (2013) Adapting to climate change on western public lands: addressing the ecological effects of domestic, wild, and feral ungulates. Environ Manage 51: 474-491. doi: 10.1007/s00267-012-9964-9
    [24] Chambers JC, Bradley BA, Brown CS, et al. (2014) Resilience to stress and disturbance, and resistance to Bromus tectorum L. invasion in cold desert shrublands of western North America. Ecosystems 17: 360-375.
    [25] McIver J, Starr L (2001) Restoration of degraded lands in the interior Columbia River basin: passive vs. active approaches. For Ecol Manage 153: 15-28.
    [26] Creutzburg MK, Halofsky JE, Halofsky JS, et al. (2014) Climate change and land management in the rangelands of central Oregon. Environ Manage 55: 43-55.
    [27] Halofsky JS, Halofsky JE, Burcsu T, et al. (2014) Dry forest resilience varies under simulated climate-management scenarios in a central Oregon, USA landscape. Ecol Appl 24:1908-1925. doi: 10.1890/13-1653.1
    [28] Yospin GI, Bridgham SD, Neilson RP, et al. (2014) A new model to simulate climate change impacts on forest succession for local land management. Ecol Appl 25: 226-242.
    [29] Bachelet D, Lenihan JM, Daly C, et al. (2001) MC1, a dynamic vegetation model for estimating the distribution of vegetation and associated carbon and nutrient fluxes, Technical Documentation Version 1.0. Portland, Oregon, USA: USDA Forest Service, Pacific Northwest Station.
    [30] Neilson RP (1995) A model for predicting continental-scale vegetation distribution and water balance. Ecol Appl 5: 352-385.
    [31] Parton WJ, Scurlock JMO, Ojima DS, et al. (1993) Observations and modeling of biomass and soil organic-matter dynamics for the grassland biome worldwide. Global Biogeochem Cy 7: 785-809. doi: 10.1029/93GB02042
    [32] Lenihan JM, Daly C, Bachelet D, et al. (1998) Simulating broad-scale fire severity in a dynamic global vegetation model. Northwest Sci 72: 91-103.
    [33] Halofsky JE, Hemstrom MA, Conklin DR, et al. (2013) Assessing potential climate change effects on vegetation using a linked model approach. Ecol Model 266: 131-143. doi: 10.1016/j.ecolmodel.2013.07.003
    [34] Breiman L, Priedman J, Stone CJ, et al. (1984) Classification and Regression Trees. Boca Raton, FL: Chapman & Hall. 359 p.
    [35] Bestelmeyer BT, Tugel AJ, Peacock Jr. GL, et al. (2009) State-and-transition models for heterogeneous landscapes: a strategy for development and application. Rangeland Ecol Manag 62: 1-15. doi: 10.2111/08-146
    [36] Westoby M, Walker B, Noy-Mier I (1989) Opportunistic management for rangelands not at equilibrium. J Range Manage 42: 66-274. doi: 10.2307/3899661
    [37] Briske DD, Fuhlendorf SD, Smeins FE (2005) State-and-transition models, thresholds, and rangeland health: a synthesis of ecological concepts and perspectives. Rangeland Ecol Manag 58: 1-10. doi: 10.2111/1551-5028(2005)58<1:SMTARH>2.0.CO;2
    [38] Briske DD, Bestelmeyer BT, Stringham TK, et al. (2006) Recommendations for development of resilience-based state-and-transition models. Rangeland Ecol Manag 61: 359-367.
    [39] Provencher L, Forbis TA, Frid L, et al. (2007) Comparing alternative management strategies of fire, grazing, and weed control using spatial modeling. Ecol Model 209: 249-263. doi: 10.1016/j.ecolmodel.2007.06.030
    [40] Forbis TA, Provencher L, Frid L, et al. (2006) Great Basin land management planning using ecological modeling. Environ Manage 38: 62-83. doi: 10.1007/s00267-005-0089-2
    [41] Hemstrom MA, Merzenich J, Reger A, et al. (2007) Integrated analysis of landscape management scenarios using state and transition models in the upper Grande Ronde River subbasin, Oregon, USA. Landscape Urban Plan 80: 198-211. doi: 10.1016/j.landurbplan.2006.10.004
    [42] Hemstrom MA, Wisdom MJ, Hann WJ, et al. (2002) Sagebrush-steppe vegetation dynamics and restoration potential in the interior Columbia Basin, U.S.A. Con Bio 16: 1243-1255. doi: 10.1046/j.1523-1739.2002.01075.x
    [43] Creutzburg MK, Halofsky JS, Hemstrom MA (2012) Using state-and-transition models to project cheatgrass and juniper invasion in eastern Oregon sagebrush steppe. In: Kerns BK, Shlisky A, Daniel CJ, editors. Proceedings of the First State-and-Transition Landscape Modeling Conference, June 15-16, 2011. Gen Tech Rep PNW-869. Portland, OR: U.S. Department of Agriculture, Forest Service, Pacific Northwest Forest and Range Experiment Station.
    [44] Littell JS, Oneil EE, McKenzie D, et al. (2010) Forest ecosystems, disturbance, and climatic change in Washington State, USA. Climatic Change 102: 129-158. doi: 10.1007/s10584-010-9858-x
    [45] U.S. Geological Survey and U.S. Department of Agriculture NRCS (2011) Federal Standards and Procedures for the National Watershed Boundary Dataset (WBD) (2d ed.). U.S. Geological Survey Techniques and Methods. pp. 62 p.
    [46] Burcsu TK, Halofsky JS, Bisrat SA, et al. (2014) Chapter 2: Dynamic Vegetation Modeling of Forested, Woodland, Shrubland, and Grassland Vegetation Communities in the Pacific Northwest and Southwest Regions of the United States. In: Halofsky JE, Creutzburg MK, Hemstrom MA, editors. Integrating Social, Economic, and Ecological Values across Large Landscapes. Gen Tech Rep PNW-GTR-896. Portland, OR: U.S. Department of Agriculture, Forest Service, Pacific Northwest Research Station. 216 pp..
    [47] Taylor KE, Stouffer RJ, Meehl GA (2012) An overview of CMIP5 and the experiment design. B Am Meteorol Soc 93: 485-498. doi: 10.1175/BAMS-D-11-00094.1
    [48] Connelly JW, Schroeder MA, Sands AR, et al. (2000) Guidelines to manage sage grouse populations and their habitats. Wildlife Soc B 28: 967-985.
    [49] Anderson JE, Inouye RS (2001) Landscape-scale changes in plant species abundance and biodiversity of a sagebrush steppe over 45 years. Ecol Monogr 71: 531-556. doi: 10.1890/0012-9615(2001)071[0531:LSCIPS]2.0.CO;2
    [50] Cook JG, Irwin LL (1992) Climate-Vegetation Relationships between the Great-Plains and Great-Basin. Am Midl Nat 127: 316-326. doi: 10.2307/2426538
    [51] Nagler PL, Glenn EP, Kim H, et al. (2007) Relationship between evapotranspiration and precipitation pulses in a semiarid rangeland estimated by moisture flux towers and MODIS vegetation indices. J Arid Environ 70: 443-462. doi: 10.1016/j.jaridenv.2006.12.026
    [52] Bates JD, Svejcar T, Miller RF, et al. (2006) The effects of precipitation timing on sagebrush steppe vegetation. J Arid Environ 64: 670-697. doi: 10.1016/j.jaridenv.2005.06.026
    [53] Bradley BA (2009) Regional analysis of the impacts of climate change on cheatgrass invasion shows potential risk and opportunity. Global Change Biol 15: 196-208. doi: 10.1111/j.1365-2486.2008.01709.x
    [54] Chambers JC, Roundy BA, Blank RR, et al. (2007) What makes Great Basin sagebrush ecosystems invasible by Bromus tectorum? Ecol Monogr 77: 117-145. doi: 10.1890/05-1991
    [55] Parton WJ, Anderson DW, Cole CV, et al. (1983) Simulation of soil organic matter formation and mineralization in semiarid agroecosystems. Special Publication No. 23. In: Lowrance RR, Todd RL, Asmussen LE et al., editors. Nutrient cycling in agricultural ecosystems. Athens, Georgia: The University of Georgia, College of Agriculture Experiment Stations.
    [56] Rogers BM, Neilson RP, Drapek R, et al. (2011) Impacts of climate change on fire regimes and carbon stocks of the U.S. Pacific Northwest. J Geophys Res-Biogeo 116: G03037.
    [57] Michalak JL, Withey JC, Lawler JJ, et al. (2014) Climate vulnerability and adaptation in the Columbia Plateau, WA. Report prepared for the Great Northern Landscape Conservation Cooperative. Available from:https://www.sciencebase.gov/catalog/item/533c5408e4b0f4f326e3a15e.
    [58] Aldridge CL, Nielsen SE, Beyer HL, et al. (2008) Range-wide patterns of greater sage-grouse persistence. Divers Distrib 14: 983-994. doi: 10.1111/j.1472-4642.2008.00502.x
    [59] Innes RJ (2013) Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available from: http://www.fs.fed.us/database/feis.
    [60] McKenzie D, Gedalof Z, Peterson DL, et al. (2004) Climatic change, wildfire, and conservation. Conserv Biol 18: 890-902. doi: 10.1111/j.1523-1739.2004.00492.x
    [61] Brooks ML, D'Antonio CM, Richardson DM, et al. (2004) Effects of invasive alien plants on fire regimes. BioScience 54: 677-688. doi: 10.1641/0006-3568(2004)054[0677:EOIAPO]2.0.CO;2
    [62] Connelly JW, Arthur WJ, Markham OD (1981) Sage grouse leks on recently disturbed sites. 34: 153-154.
    [63] Davies G, Bakker J, Dettweiler-Robinson E, et al. (2012) Trajectories of change in sagebrush steppe vegetation communities in relation to multiple wildfires. Ecol Appl 22: 1562-1577.
    [64] Holloran MJ, Anderson SH (2005) Spatial distribution of greater sage-grouse nests in relatively contiguous sagebrush habitats. Condor 107: 742-752.
    [65] Kremer RG, Hunt ER, Running SW, et al. (1996) Simulating vegetational and hydrologic responses to natural climatic variation and GCM-predicted climate change in a semi-arid ecosystem in Washington, USA. J Arid Environ 33: 23-38. doi: 10.1006/jare.1996.0043
    [66] Ziska LH, Reeves JB, Blank B (2005) The impact of recent increases in atmospheric CO2 on biomass production and vegetative retention of Cheatgrass (Bromus tectorum): implications for fire disturbance. Global Change Biol 11: 1325-1332. doi: 10.1111/j.1365-2486.2005.00992.x
    [67] Smith SD, Huxman TE, Zitzer SF, et al. (2000) Elevated CO2 increases productivity and invasive species success in an arid ecosystem. Nature 408: 79-82. doi: 10.1038/35040544
    [68] Bradley BA, Wilcove DS (2009) When invasive plants disappear: transformative restoration possibilities in the western United States resulting from climate change. Restor Ecol 17: 715-721. doi: 10.1111/j.1526-100X.2009.00586.x
    [69] Baruch-Mordo S, Evans JS, Severson JP, et al. (2013) Saving sage-grouse from the trees: A proactive solution to reducing a key threat to a candidate species. Biol Conserv 167: 233-241. doi: 10.1016/j.biocon.2013.08.017
    [70] Boyd CS, Johnson DD, Kerby J, et al. (2014) Of grouse and golden eggs: can ecosystems be managed within a species-based regulatory framework? Range Ecol Manag 57: 358-368.
    [71] Davies KW, Sheley RL (2011) Promoting native vegetation and diversity in exotic annual grass infestations. Restor Ecol 19: 159-165. doi: 10.1111/j.1526-100X.2009.00548.x
    [72] Pyke DA, Wirth TA, Beyers JL (2013) Does seeding after wildfires in rangelands reduce erosion or invasive species? Restor Ecol 21: 415–421. doi: 10.1111/rec.12021
    [73] Davies KW, Johnson DA (2011) Are we “missing the boat” on preventing the spread of invasive plants in rangelands? Invasive Plant Sci Manag 4: 166-171. doi: 10.1614/IPSM-D-10-00030.1
    [74] Drut MS, Pyle WH, Crawford JA (1994) Technical note: Diets and food selection of sage grouse chicks in Oregon. J Range Manage 47: 90-93. doi: 10.2307/4002848
    [75] Knutti R, Sedlacek J (2013) Robustness and uncertainties in the new CMIP5 climate model projections. Nat Clim Change 3: 369-373.
    [76] Huntley B (1991) How plants respond to climate change - migration rates, individualism and the consequences for plant-communities. Ann Bot-London 67: 15-22.
  • Reader Comments
  • © 2015 the Author(s), licensee AIMS Press. This is an open access article distributed under the terms of the Creative Commons Attribution License (http://creativecommons.org/licenses/by/4.0)
通讯作者: 陈斌, bchen63@163.com
  • 1. 

    沈阳化工大学材料科学与工程学院 沈阳 110142

  1. 本站搜索
  2. 百度学术搜索
  3. 万方数据库搜索
  4. CNKI搜索

Metrics

Article views(7037) PDF downloads(1706) Cited by(21)

Article outline

Figures and Tables

Figures(8)  /  Tables(4)

/

DownLoad:  Full-Size Img  PowerPoint
Return
Return

Catalog