Thresholds and hotspots for shrub restoration following a heterogeneous megafire
Context Reestablishing foundational plant species through aerial seeding is an essential yet challenging step for restoring the vast semiarid landscapes impacted by plant invasions and wildfire-regime shifts. A key component of the challenge stems from landscape variability and its effects on plant...
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| Veröffentlicht in: | Landscape ecology Jg. 33; H. 7; S. 1177 - 1194 |
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| Format: | Journal Article |
| Sprache: | Englisch |
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Dordrecht
Springer Netherlands
01.07.2018
Springer Nature B.V |
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| ISSN: | 0921-2973, 1572-9761 |
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| Abstract | Context
Reestablishing foundational plant species through aerial seeding is an essential yet challenging step for restoring the vast semiarid landscapes impacted by plant invasions and wildfire-regime shifts. A key component of the challenge stems from landscape variability and its effects on plant recovery.
Objectives
We assessed landscape correlates, thresholds, and tipping points for sagebrush presence from fine-scale sampling across a large, heterogeneous area burned the previous year, where we were able to quantify soil surface features that are typically occluded yet can strongly affect recovery patterns.
Methods
Hypothesis testing and binary-decision trees were used to evaluate factors affecting initial sagebrush establishment, using 2171 field plots (totaling ~ 2,000,000 m
2
sampled) over a 113,000-ha region.
Results
Sagebrush established in 50% of plots where it was seeded, a > 12-fold greater establishment frequency than in unseeded areas. Sagebrush establishment was enhanced in threshold-like ways by elevation (> 1200 m ASL), topographic features that alter heatload and soil water, and by soil-surface features such as “fertile islands” that bore the imprint of pre-fire sagebrush. Sagebrush occupancy had a negative, linear relationship with exotic-annual grass cover and parabolic relationship with perennial bunchgrasses (optimal at 40% cover).
Conclusions
Our approach revealed interactive, ecological relationships such as novel soil-surface effects on first year establishment of sagebrush across the burned landscape, and identified “hot spots” for recovery. The approach could be expanded across sites and years to provide the information needed to explain past seeding successes or failures, and in designing treatments at the landscape scale. |
|---|---|
| AbstractList | Context
Reestablishing foundational plant species through aerial seeding is an essential yet challenging step for restoring the vast semiarid landscapes impacted by plant invasions and wildfire-regime shifts. A key component of the challenge stems from landscape variability and its effects on plant recovery.
Objectives
We assessed landscape correlates, thresholds, and tipping points for sagebrush presence from fine-scale sampling across a large, heterogeneous area burned the previous year, where we were able to quantify soil surface features that are typically occluded yet can strongly affect recovery patterns.
Methods
Hypothesis testing and binary-decision trees were used to evaluate factors affecting initial sagebrush establishment, using 2171 field plots (totaling ~ 2,000,000 m
2
sampled) over a 113,000-ha region.
Results
Sagebrush established in 50% of plots where it was seeded, a > 12-fold greater establishment frequency than in unseeded areas. Sagebrush establishment was enhanced in threshold-like ways by elevation (> 1200 m ASL), topographic features that alter heatload and soil water, and by soil-surface features such as “fertile islands” that bore the imprint of pre-fire sagebrush. Sagebrush occupancy had a negative, linear relationship with exotic-annual grass cover and parabolic relationship with perennial bunchgrasses (optimal at 40% cover).
Conclusions
Our approach revealed interactive, ecological relationships such as novel soil-surface effects on first year establishment of sagebrush across the burned landscape, and identified “hot spots” for recovery. The approach could be expanded across sites and years to provide the information needed to explain past seeding successes or failures, and in designing treatments at the landscape scale. ContextReestablishing foundational plant species through aerial seeding is an essential yet challenging step for restoring the vast semiarid landscapes impacted by plant invasions and wildfire-regime shifts. A key component of the challenge stems from landscape variability and its effects on plant recovery.ObjectivesWe assessed landscape correlates, thresholds, and tipping points for sagebrush presence from fine-scale sampling across a large, heterogeneous area burned the previous year, where we were able to quantify soil surface features that are typically occluded yet can strongly affect recovery patterns.MethodsHypothesis testing and binary-decision trees were used to evaluate factors affecting initial sagebrush establishment, using 2171 field plots (totaling ~ 2,000,000 m2 sampled) over a 113,000-ha region.ResultsSagebrush established in 50% of plots where it was seeded, a > 12-fold greater establishment frequency than in unseeded areas. Sagebrush establishment was enhanced in threshold-like ways by elevation (> 1200 m ASL), topographic features that alter heatload and soil water, and by soil-surface features such as “fertile islands” that bore the imprint of pre-fire sagebrush. Sagebrush occupancy had a negative, linear relationship with exotic-annual grass cover and parabolic relationship with perennial bunchgrasses (optimal at 40% cover).ConclusionsOur approach revealed interactive, ecological relationships such as novel soil-surface effects on first year establishment of sagebrush across the burned landscape, and identified “hot spots” for recovery. The approach could be expanded across sites and years to provide the information needed to explain past seeding successes or failures, and in designing treatments at the landscape scale. CONTEXT: Reestablishing foundational plant species through aerial seeding is an essential yet challenging step for restoring the vast semiarid landscapes impacted by plant invasions and wildfire-regime shifts. A key component of the challenge stems from landscape variability and its effects on plant recovery. OBJECTIVES: We assessed landscape correlates, thresholds, and tipping points for sagebrush presence from fine-scale sampling across a large, heterogeneous area burned the previous year, where we were able to quantify soil surface features that are typically occluded yet can strongly affect recovery patterns. METHODS: Hypothesis testing and binary-decision trees were used to evaluate factors affecting initial sagebrush establishment, using 2171 field plots (totaling ~ 2,000,000 m² sampled) over a 113,000-ha region. RESULTS: Sagebrush established in 50% of plots where it was seeded, a > 12-fold greater establishment frequency than in unseeded areas. Sagebrush establishment was enhanced in threshold-like ways by elevation (> 1200 m ASL), topographic features that alter heatload and soil water, and by soil-surface features such as “fertile islands” that bore the imprint of pre-fire sagebrush. Sagebrush occupancy had a negative, linear relationship with exotic-annual grass cover and parabolic relationship with perennial bunchgrasses (optimal at 40% cover). CONCLUSIONS: Our approach revealed interactive, ecological relationships such as novel soil-surface effects on first year establishment of sagebrush across the burned landscape, and identified “hot spots” for recovery. The approach could be expanded across sites and years to provide the information needed to explain past seeding successes or failures, and in designing treatments at the landscape scale. |
| Author | Pilliod, David S. Applestein, Cara Arkle, Robert S. Germino, Matthew J. Davidson, Bill E. Fisk, Matthew R. Barnard, David M. |
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| References | Hulvey KB, Leger EA, Porensky LM, Roche LM, Veblen KE, Fund A, Shaw J, Gornish ES (2017) Restoration islands: at tool for efficiently restoring dryland ecosystems? Restor Ecol. Online first McCuneBKeonDMarrsREquations for potential annual direct incident radiation and heatloadJ Veg Sci20021360360610.1111/j.1654-1103.2002.tb02087.x BrudvigLABarakRSBauerJTCaughlinTTLaughlinDCLariosLMatthewsJWStubleKLTurleyNEZirbelCRInterpreting variation to advance predictive restoration scienceJ Appl Ecol2017541018102710.1111/1365-2664.12938 DiCristinaKGerminoMCorrelation of neighborhood relationships, carbon assimilation, and water status of sagebrush seedlings establishing after fireWest N Am Nat20066644144910.3398/1527-0904(2006)66[441:CONRCA]2.0.CO;2 Burkett LM, Bestelmeyer BT, Tugel AJ (2011) A field guide to pedoderm and pattern classes. Version 2.2. http://jornada.nmsu.edu/files/FieldGuidePedodermPattern.pdf CopelandSMMunsonSMPilliodDSWeltyJLBradfordJBButterfieldBJLong-term trends in restoration and associated land treatments in the southwestern United StatesRestor Ecol20172631132210.1111/rec.12574 SchlaepferDRLauenrothWKBradfordJBModeling regeneration responses of big sagebrush (Artemisia tridentata) to abiotic conditionsEcol Model2014286667710.1016/j.ecolmodel.2014.04.021 BatesDMaechlerMBolkerBWalkerSlme4: linear mixed-effects models using Eigen and S4R Package Version20141123 KnutsonKCPykeDAWirthTAArkleRSPilliodDSBrooksMLChambersJCGraceJBLong-term effects of seeding after wildfire on vegetation in Great Basin shrubland ecosystemsJ Appl Ecol2014511414142410.1111/1365-2664.12309 EiswerthMEKrauterKSwansonSRZielinskiMPost-fire seeding on Wyoming big sagebrush ecological sites: regression analyses of seeded nonnative and native species densitiesJ Environ Manag2009901320132510.1016/j.jenvman.2008.07.009 RottlerCMBurkeICPalmquistKABradfordJBLauenrothWKReclamation after oil and gas development does not speed up succession or plant community recovery in big sagebrush ecosystems in WyomingRestor Ecol20172611412310.1111/rec.12543 HooverANGerminoMJA common-garden study of resource-island effects on a native and an exotic, annual grass after fireRangel Ecol Manag20126516017010.2111/REM-D-11-00026.1 GerminoMJReinhardtKDesert shrub responses to experimental modification of precipitation seasonality and soil depth: relationship to the two-layer hypothesis and ecohydrological nicheJ Ecol201410298999710.1111/1365-2745.12266 D’AntonioCMVitousekPMBiological invasions by exotic grasses, the grass/fire cycle, and global changeAnnu Rev Ecol Syst199223638710.1146/annurev.es.23.110192.000431 HassanMAWestNEDynamics of soil seed pools in burned and unburned sagebrush semi-desertsEcology19866726927210.2307/1938531 BolkerBMBrooksMEClarkCJGeangeSWPoulsenJRStevensMHHWhiteJSSGeneralized linear mixed models: a practical guide for ecology and evolutionTrends Ecol Evolut20092412713510.1016/j.tree.2008.10.008 SchlaepferDRLauenrothWKBradfordJBNatural regeneration processes in big sagebrush (Artemisia tridentata)Rangel Ecol Manag20146734435710.2111/REM-D-13-00079.1 BevenKKirkbyMJA physically based, variable contributing area model of basin hydrologyHydrol Sci J197924436910.1080/02626667909491834 BochetEGarcía-FayosPAlborchBTormoJSoil water availability effects on seed germination account for species segregation in semiarid roadslopesPlant Soil200729517919110.1007/s11104-007-9274-91:CAS:528:DC%2BD2sXmsFKjtb0%3D RinellaMJHammondDHBryantA-EMKozarBJHigh precipitation and seeded species competition reduce seeded shrub establishment during dryland restorationEcol Appl2015251044105310.1890/14-1110.126465041 HardegreeSPAbatzoglouJTBrunsonMWGerminoMJHegewischKCMoffetCAPilliodDSRoundyBABoehmARMeredithGRWeather-centric rangeland revegetation planningRangel Ecol Manag20177111110.1016/j.rama.2017.07.003 PrevéyJSGerminoMJHuntlyNJInouyeRSExotic plants increase and native plants decrease with loss of foundation species in sagebrush steppePlant Ecol2010207395110.1007/s11258-009-9652-x Applestein C, Germino MJ, Fisk MJ (accepted) Vegetation community response to landscape scale post-fire herbicide (imazapic) application. Invasive Plant Sci Manag R Core TeamR: a language and environment for statistical computing2017Vienna, AustriaR Foundation for Statistical Computing ReisnerMDGraceJBPykeDADoescherPSConditions favouring Bromus tectorum dominance of endangered sagebrush steppe ecosystemsJ Appl Ecol2013501039104910.1111/1365-2664.12097 GerminoMJBelnapJStarkJMAllenEBRauBMGerminoMJChambersJCBrownCEcosystem impacts of exotic annual invaders in the genus BromusExotic Brome-grasses in arid and semiarid ecosystems of the western US2016BerlinSpringer619510.1007/978-3-319-24930-8_3 BoydCSDaviesKWLemosJAInfluence of soil color on seedbed microclimate and seedling demographics of a perennial bunchgrassRangel Ecol Manag20177062162410.1016/j.rama.2017.03.004 DonatoDCFontaineJBCampbellJLRobinsonWDKauffmanJBLawBEPost-wildfire logging hinders regeneration and increases fire riskScience2006311575935210.1126/science.1122855164001111:CAS:528:DC%2BD28XntlyqsA%3D%3D ThompsonJRSpiesTAGanioLMReburn severity in managed and unmanaged vegetation in a large wildfireProc Natl Acad Sci200710425107431074810.1073/pnas.0700229104175633701:CAS:528:DC%2BD2sXnt1ylurk%3D McArthurEDPlummerAPBiogeography and management of native western shrubs—a case study, section Tridentatae of ArtemisiaGreat Basin Naturalist Memoirs19782229243 DaviesKWBoydCSNafusAMRestoring the sagebrush component in crested wheatgrass–dominated communitiesRangel Ecol Manag20136647247810.2111/REM-D-12-00145.1 PilliodDSWeltyJLToevsGRSeventy-five years of vegetation treatments on public rangelands in the Great Basin of North AmericaRangelands2017391910.1016/j.rala.2016.12.001 ChambersJCBradleyBABrownCSD’AntonioCGerminoMJGraceJBHardegreeSPMillerRFPykeDAResilience to stress and disturbance, and resistance to Bromus tectorum L. invasion in cold desert shrublands of western North AmericaEcosystems20141736037510.1007/s10021-013-9725-51:CAS:528:DC%2BC2cXjslWntrc%3D JamesJJSvejcarTJRinellaMJDemographic processes limiting seedling recruitment in arid grassland restorationJ Appl Ecol20114896196910.1111/j.1365-2664.2011.02009.x SankeyJBGerminoMJSankeyTTHooverANFire effects on the spatial patterning of soil properties in sagebrush steppe, USA: a meta-analysisInt J Wildland Fire20122154555610.1071/WF11092 SeefeldtSSGerminoMJDiCristinaKPrescribed fires in Artemisia tridentata ssp. Vaseyana steppe have minor and transient effects on vegetation cover and compositionAppl Veg Sci20071024925610.1111/j.1654-109X.2007.tb00523.x WijayratneUCPykeDABurial increases seed longevity of two Artemisia tridentata (Asteraceae) subspeciesAm J Bot20129943844710.3732/ajb.100047722301894 NelsonZJWeisbergPJKitchenSGInfluence of climate and environment on post-fire recovery of mountain big sagebrushInt J Wildland Fire20142313114210.1071/WF13012 RodhouseTJIrvineKMSheleyRLSmithBSHohSEspositoDMMata-GonzalezRPredicting foundation bunchgrass species abundances: model-assisted decision-making in protected-area sagebrush steppeEcosphere20145911610.1890/ES14-00169.1 OttJECoxRDShawNLComparison of postfire seeding practices for wyoming big sagebrushRangel Ecol Manag20177062563210.1016/j.rama.2017.03.005 SólymosPLeleSRRevisiting resource selection probability functions and single-visit methods: clarification and extensionsMethods Ecol Evolut2016719620510.1111/2041-210X.12432 PalmquistKASchlaepferDRBradfordJBLauenrothWKMid-latitude shrub steppe plant communities: climate change consequences for soil water resourcesEcology2016972342235410.1002/ecy.145727859085 BrabecMMGerminoMJShinnemanDJPilliodDSMcIlroySKArkleRSChallenges of establishing big sagebrush (Artemisia tridentata) in rangeland restoration: effects of herbicide, mowing, whole-community seeding, and sagebrush seed sourcesRangel Ecol Manag20156843243510.1016/j.rama.2015.07.001 ChambersJCSeed movements and seedling fates in disturbed sagebrush steppe ecosystems: implications for restorationEcol Appl20001014001413 DaviesKWBatesJDRestoring big sagebrush after controlling encroaching western juniper with fire: aspect and subspecies effectsRestor Ecol201725334110.1111/rec.12375 DaviesKWBatesJDJamesJJMicrosite and herbaceous vegetation heterogeneity after burning Artemisia tridentata steppeOecologia200915959760610.1007/s00442-008-1231-719066972 BrabecMMGerminoMJRichardsonBAClimate adaption and post-fire restoration of a foundational perennial in cold desert: insights from intraspecific variation in response to weatherJ Appl Ecol20165429330210.1111/1365-2664.12679 Therneau TM, Atkinson B, Ripley MB (2010) The rpart package De’athGFabriciusKEClassification and regression trees: a powerful yet simple technique for ecological data analysisEcology2000813178319210.1890/0012-9658(2000)081[3178:CARTAP]2.0.CO;2 MD Reisner (662_CR37) 2013; 50 JE Ott (662_CR33) 2017; 70 BM Bolker (662_CR4) 2009; 24 CM D’Antonio (662_CR13) 1992; 23 DC Donato (662_CR19) 2006; 311 TJ Rodhouse (662_CR39) 2014; 5 ME Eiswerth (662_CR20) 2009; 90 E Bochet (662_CR3) 2007; 295 UC Wijayratne (662_CR48) 2012; 99 JR Thompson (662_CR47) 2007; 104 SS Seefeldt (662_CR44) 2007; 10 CS Boyd (662_CR5) 2017; 70 662_CR27 SP Hardegree (662_CR23) 2017; 71 MJ Germino (662_CR21) 2016 R Core Team (662_CR888) 2017 ZJ Nelson (662_CR32) 2014; 23 D Bates (662_CR1) 2014; 1 SM Copeland (662_CR12) 2017; 26 JS Prevéy (662_CR36) 2010; 207 JC Chambers (662_CR10) 2000; 10 P Sólymos (662_CR45) 2016; 7 K DiCristina (662_CR18) 2006; 66 KW Davies (662_CR16) 2013; 66 DR Schlaepfer (662_CR42) 2014; 286 K Beven (662_CR2) 1979; 24 KC Knutson (662_CR29) 2014; 51 MM Brabec (662_CR7) 2015; 68 G De’ath (662_CR17) 2000; 81 JC Chambers (662_CR11) 2014; 17 DR Schlaepfer (662_CR43) 2014; 67 CM Rottler (662_CR40) 2017; 26 JJ James (662_CR28) 2011; 48 ED McArthur (662_CR30) 1978; 2 KW Davies (662_CR14) 2017; 25 MM Brabec (662_CR6) 2016; 54 MJ Rinella (662_CR38) 2015; 25 MA Hassan (662_CR25) 1986; 67 662_CR49 B McCune (662_CR31) 2002; 13 662_CR46 JB Sankey (662_CR41) 2012; 21 AN Hoover (662_CR26) 2012; 65 DS Pilliod (662_CR35) 2017; 39 MJ Germino (662_CR22) 2014; 102 KA Palmquist (662_CR34) 2016; 97 KW Davies (662_CR15) 2009; 159 LA Brudvig (662_CR8) 2017; 54 662_CR9 |
| References_xml | – reference: De’athGFabriciusKEClassification and regression trees: a powerful yet simple technique for ecological data analysisEcology2000813178319210.1890/0012-9658(2000)081[3178:CARTAP]2.0.CO;2 – reference: Hulvey KB, Leger EA, Porensky LM, Roche LM, Veblen KE, Fund A, Shaw J, Gornish ES (2017) Restoration islands: at tool for efficiently restoring dryland ecosystems? Restor Ecol. Online first – reference: KnutsonKCPykeDAWirthTAArkleRSPilliodDSBrooksMLChambersJCGraceJBLong-term effects of seeding after wildfire on vegetation in Great Basin shrubland ecosystemsJ Appl Ecol2014511414142410.1111/1365-2664.12309 – reference: RottlerCMBurkeICPalmquistKABradfordJBLauenrothWKReclamation after oil and gas development does not speed up succession or plant community recovery in big sagebrush ecosystems in WyomingRestor Ecol20172611412310.1111/rec.12543 – reference: BolkerBMBrooksMEClarkCJGeangeSWPoulsenJRStevensMHHWhiteJSSGeneralized linear mixed models: a practical guide for ecology and evolutionTrends Ecol Evolut20092412713510.1016/j.tree.2008.10.008 – reference: NelsonZJWeisbergPJKitchenSGInfluence of climate and environment on post-fire recovery of mountain big sagebrushInt J Wildland Fire20142313114210.1071/WF13012 – reference: SólymosPLeleSRRevisiting resource selection probability functions and single-visit methods: clarification and extensionsMethods Ecol Evolut2016719620510.1111/2041-210X.12432 – reference: DaviesKWBatesJDJamesJJMicrosite and herbaceous vegetation heterogeneity after burning Artemisia tridentata steppeOecologia200915959760610.1007/s00442-008-1231-719066972 – reference: DonatoDCFontaineJBCampbellJLRobinsonWDKauffmanJBLawBEPost-wildfire logging hinders regeneration and increases fire riskScience2006311575935210.1126/science.1122855164001111:CAS:528:DC%2BD28XntlyqsA%3D%3D – reference: SchlaepferDRLauenrothWKBradfordJBNatural regeneration processes in big sagebrush (Artemisia tridentata)Rangel Ecol Manag20146734435710.2111/REM-D-13-00079.1 – reference: BevenKKirkbyMJA physically based, variable contributing area model of basin hydrologyHydrol Sci J197924436910.1080/02626667909491834 – reference: GerminoMJBelnapJStarkJMAllenEBRauBMGerminoMJChambersJCBrownCEcosystem impacts of exotic annual invaders in the genus BromusExotic Brome-grasses in arid and semiarid ecosystems of the western US2016BerlinSpringer619510.1007/978-3-319-24930-8_3 – reference: PalmquistKASchlaepferDRBradfordJBLauenrothWKMid-latitude shrub steppe plant communities: climate change consequences for soil water resourcesEcology2016972342235410.1002/ecy.145727859085 – reference: ThompsonJRSpiesTAGanioLMReburn severity in managed and unmanaged vegetation in a large wildfireProc Natl Acad Sci200710425107431074810.1073/pnas.0700229104175633701:CAS:528:DC%2BD2sXnt1ylurk%3D – reference: DiCristinaKGerminoMCorrelation of neighborhood relationships, carbon assimilation, and water status of sagebrush seedlings establishing after fireWest N Am Nat20066644144910.3398/1527-0904(2006)66[441:CONRCA]2.0.CO;2 – reference: BrabecMMGerminoMJShinnemanDJPilliodDSMcIlroySKArkleRSChallenges of establishing big sagebrush (Artemisia tridentata) in rangeland restoration: effects of herbicide, mowing, whole-community seeding, and sagebrush seed sourcesRangel Ecol Manag20156843243510.1016/j.rama.2015.07.001 – reference: SankeyJBGerminoMJSankeyTTHooverANFire effects on the spatial patterning of soil properties in sagebrush steppe, USA: a meta-analysisInt J Wildland Fire20122154555610.1071/WF11092 – reference: McArthurEDPlummerAPBiogeography and management of native western shrubs—a case study, section Tridentatae of ArtemisiaGreat Basin Naturalist Memoirs19782229243 – reference: McCuneBKeonDMarrsREquations for potential annual direct incident radiation and heatloadJ Veg Sci20021360360610.1111/j.1654-1103.2002.tb02087.x – reference: Applestein C, Germino MJ, Fisk MJ (accepted) Vegetation community response to landscape scale post-fire herbicide (imazapic) application. Invasive Plant Sci Manag – reference: Therneau TM, Atkinson B, Ripley MB (2010) The rpart package – reference: PrevéyJSGerminoMJHuntlyNJInouyeRSExotic plants increase and native plants decrease with loss of foundation species in sagebrush steppePlant Ecol2010207395110.1007/s11258-009-9652-x – reference: HardegreeSPAbatzoglouJTBrunsonMWGerminoMJHegewischKCMoffetCAPilliodDSRoundyBABoehmARMeredithGRWeather-centric rangeland revegetation planningRangel Ecol Manag20177111110.1016/j.rama.2017.07.003 – reference: RinellaMJHammondDHBryantA-EMKozarBJHigh precipitation and seeded species competition reduce seeded shrub establishment during dryland restorationEcol Appl2015251044105310.1890/14-1110.126465041 – reference: BatesDMaechlerMBolkerBWalkerSlme4: linear mixed-effects models using Eigen and S4R Package Version20141123 – reference: HassanMAWestNEDynamics of soil seed pools in burned and unburned sagebrush semi-desertsEcology19866726927210.2307/1938531 – reference: SchlaepferDRLauenrothWKBradfordJBModeling regeneration responses of big sagebrush (Artemisia tridentata) to abiotic conditionsEcol Model2014286667710.1016/j.ecolmodel.2014.04.021 – reference: DaviesKWBoydCSNafusAMRestoring the sagebrush component in crested wheatgrass–dominated communitiesRangel Ecol Manag20136647247810.2111/REM-D-12-00145.1 – reference: CopelandSMMunsonSMPilliodDSWeltyJLBradfordJBButterfieldBJLong-term trends in restoration and associated land treatments in the southwestern United StatesRestor Ecol20172631132210.1111/rec.12574 – reference: ReisnerMDGraceJBPykeDADoescherPSConditions favouring Bromus tectorum dominance of endangered sagebrush steppe ecosystemsJ Appl Ecol2013501039104910.1111/1365-2664.12097 – reference: D’AntonioCMVitousekPMBiological invasions by exotic grasses, the grass/fire cycle, and global changeAnnu Rev Ecol Syst199223638710.1146/annurev.es.23.110192.000431 – reference: BrabecMMGerminoMJRichardsonBAClimate adaption and post-fire restoration of a foundational perennial in cold desert: insights from intraspecific variation in response to weatherJ Appl Ecol20165429330210.1111/1365-2664.12679 – reference: WijayratneUCPykeDABurial increases seed longevity of two Artemisia tridentata (Asteraceae) subspeciesAm J Bot20129943844710.3732/ajb.100047722301894 – reference: HooverANGerminoMJA common-garden study of resource-island effects on a native and an exotic, annual grass after fireRangel Ecol Manag20126516017010.2111/REM-D-11-00026.1 – reference: ChambersJCSeed movements and seedling fates in disturbed sagebrush steppe ecosystems: implications for restorationEcol Appl20001014001413 – reference: JamesJJSvejcarTJRinellaMJDemographic processes limiting seedling recruitment in arid grassland restorationJ Appl Ecol20114896196910.1111/j.1365-2664.2011.02009.x – reference: Burkett LM, Bestelmeyer BT, Tugel AJ (2011) A field guide to pedoderm and pattern classes. Version 2.2. http://jornada.nmsu.edu/files/FieldGuidePedodermPattern.pdf – reference: EiswerthMEKrauterKSwansonSRZielinskiMPost-fire seeding on Wyoming big sagebrush ecological sites: regression analyses of seeded nonnative and native species densitiesJ Environ Manag2009901320132510.1016/j.jenvman.2008.07.009 – reference: BrudvigLABarakRSBauerJTCaughlinTTLaughlinDCLariosLMatthewsJWStubleKLTurleyNEZirbelCRInterpreting variation to advance predictive restoration scienceJ Appl Ecol2017541018102710.1111/1365-2664.12938 – reference: PilliodDSWeltyJLToevsGRSeventy-five years of vegetation treatments on public rangelands in the Great Basin of North AmericaRangelands2017391910.1016/j.rala.2016.12.001 – reference: ChambersJCBradleyBABrownCSD’AntonioCGerminoMJGraceJBHardegreeSPMillerRFPykeDAResilience to stress and disturbance, and resistance to Bromus tectorum L. invasion in cold desert shrublands of western North AmericaEcosystems20141736037510.1007/s10021-013-9725-51:CAS:528:DC%2BC2cXjslWntrc%3D – reference: DaviesKWBatesJDRestoring big sagebrush after controlling encroaching western juniper with fire: aspect and subspecies effectsRestor Ecol201725334110.1111/rec.12375 – reference: SeefeldtSSGerminoMJDiCristinaKPrescribed fires in Artemisia tridentata ssp. 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Reestablishing foundational plant species through aerial seeding is an essential yet challenging step for restoring the vast semiarid landscapes... ContextReestablishing foundational plant species through aerial seeding is an essential yet challenging step for restoring the vast semiarid landscapes... CONTEXT: Reestablishing foundational plant species through aerial seeding is an essential yet challenging step for restoring the vast semiarid landscapes... |
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