Effects of restoration and fire : simplebooklet.com

Alexander J D Williams E J Gillespie C R Contreras Mart nez S Finch D M 2020 Effects of restoration and fire on habitats and populations of western hummingbirds a literature review Gen Tech Rep RMRSGTR 408 Fort Collins CO U S Department of Agriculture Forest Service Rocky Mountain Research Station 64 p Abstract To inform future restoration efforts we reviewed the known effects of fire and habitat management and restoration on hummingbirds in four key habitat types in North America We examined seven species that most commonly occur west of the Rocky Mountains Rufous Selasphorus rufus Calliope Selasphorus calliope Broad tailed Selasphorus platycercus Costa s Calypte costae Black chinned Archilochus alexandri Anna s Calypte anna and Allen s Selasphorus sasin Our review found that most western hummingbird species respond positively to wild or prescribed fire in forested and chaparral habitats of the western United States although some hummingbird occurrence declines following fire possibly due to the loss of preferred nesting habitat in mature forests Restoration practices that eradicate exotic plants encourage the regeneration of native shrubs and flowering plants especially understory vegetation and promote early and midsuccessional habitats connected with native stand trees will benefit hummingbirds by providing foraging habitat in migration and on breeding grounds Restoration practices that encourage the regeneration of native shrubs understory vegetation and native epiphytes while maintaining forest canopy can also benefit hummingbirds We also identify many critical research questions and needs which if addressed would improve the quantification of pre and postfire and habitat management impacts on hummingbirds especially Allen s and Rufous populations which are experiencing steep population declines _____________________________ Keywords Keywords Hummingbirds fire prescribed fire restoration climate change Cover Photo 1 Broad tailed hummingbird Selasphorus platycercus pollinates a variety of flowering plants in different seasons Calder et al 2013 Photo by Mark Chappell Photo 2 inset Wholeleaf Indian Paintbrush Castilleja integra in Arizona is frequently pollinated by the Blackchinned Hummingbird Archilochus alexandri Brown and Kodric Brown 1979 Photo by Robert Sivinski All Rocky Mountain Research Station publications are published by U S Forest Service employees and are in the public domain and available at no cost Even though U S Forest Service publications are not copyrighted they are formatted according to U S Department of Agriculture standards and research findings and formatting cannot be altered in reprints Altering content or formatting including the cover and title page is strictly prohibited ii

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Author John D Alexander Executive Director Klamath Bird Observatory Ashland Oregon Elizabeth J Williams Outreach and Education Coordinator Klamath Bird Observatory Ashland Oregon Caitlyn R Gillespie Research Biologist Klamath Bird Observatory Ashland Oregon Sarahy Contreras Mart nez Jefe del Laboratorio de Zoolog a DERN IMECBIO Universidad de Guadalajara CUCSUR Autl n de Navarro Jalisco M xico Deborah M Finch Program Manager and Biological Scientist USDA Forest Service Rocky Mountain Research Station Albuquerque New Mexico Acknowledgments We wish to thank the USDA Forest Service Rocky Mountain Research Station and the Western Hummingbird Partnership for providing funding for this project and Greg Butcher USDA Forest Service International Programs Susan Bonfield and Carol Lively Environment for the Americas for their support Reviewer recommendations from Karl Malcolm Forest Service and Christine Bishop Environment and Climate Change Canada greatly improved this manuscript Mike McDonald USDA Forest Service Pacific Southwest Research Station David Hawksworth USDA Forest Service Rocky Mountain Research Station Felicity Newell Klamath Bird Observatory and Nate Trimble Klamath Bird Observatory provided valuable feedback and editorial assistance iii

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Table of Contents Introduction and Scope 1 Region of Interest 3 Hummingbird Biology and Habitat Relationships 4 Species of Interest 5 Anna s Hummingbird Calypte anna 6 Allen s Hummingbird Selasphorus sasin 8 Black chinned Hummingbird Archilochus alexandri 10 Broad tailed Hummingbird Selasphorus platycercus 12 Calliope Hummingbird Stellula calliope 14 Costa s Hummingbird Calypte costae 16 Rufous Hummingbird Selasphorus rufus 18 Fire Restoration and Hummingbirds Key Findings By Region 20 Southwestern Desert and Riparian 20 Habitats and Fire Regimes 20 Wildfire and Hummingbirds 22 Restoration and Hummingbirds 24 Management Implications 25 Coastal California Sierra Nevada and Great Basin 26 Habitats and Fire Regimes 26 Wildfire and Hummingbirds 29 Restoration and Hummingbirds 31 Management Implications 32 Pacific Northwest Northern Rockies 34 Habitats and Fire Regimes 34 Wildfire and Hummingbirds 36 Restoration and Hummingbirds 37 Management Implications 38 Southern Rockies Colorado Plateau 39 Habitats and Fire Regimes 39 Wildfire and Hummingbirds 40 Restoration and Hummingbirds 40 Management Implications 41 Conclusion 42 Research Inventory and Monitoring Priorities 44 Improve Hummingbird Monitoring and Data Sharing Techniques 44 Address Information Gaps Regarding Hummingbird Biology and Life History 45 iv

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Introduction and Scope Hummingbirds are one of the most diverse families of birds in the world with 338 recorded species McGuire et al 2014 They are exclusive to the western hemisphere with the highest diversity of species occurring in the tropics Greenewalt 1960 Although hummingbirds breed as far north as Canada and Alaska their highest diversity in the United States occurs in the pine oak woodlands of southeastern Arizona Wethington and Finley 2009 Hummingbirds use a variety of habitats throughout their range including second growth forests alpine meadows desert habitats and riparian woodlands They have been found at elevations from 0 to 4 800 m 15 748 ft Stolz et al 1996 Hummingbirds are specialized nectar feeders and play an important ecological role in plant pollination Brown and Bowers 1985 Gegear and Burns 2007 Stiles 1981 Temeles and Kress 2003 Due to a number of factors including their small size limited energy reserves rapid movements high pitched vocalizations timing of migration and polygynous mating systems it is thought that hummingbirds cannot be monitored as easily as many other landbirds Wethington and Finley 2009 Because of this population data are limited to results from North American Breeding Bird Surveys and relatively little is known about the basic biology and life history of many hummingbirds Nests have not been described for over 60 percent of the 48 known vulnerable threatened or endangered hummingbird species on the International Union for the Conservation of Nature s Red List Wethington and Finley 2009 Available data suggest declines in many species of hummingbirds although the causes of these declines are unknown In 2009 48 of the 338 known species of hummingbirds or over 14 percent of the hummingbird family were listed as vulnerable threatened or endangered Twenty three species were listed as critically endangered or endangered on the International Union for the Conservation of Nature s Red List and an additional 25 species are listed as near threatened or vulnerable Wethington and Finley 2009 As of 2019 60 of 367 Trochilidae species are listed as either vulnerable near threatened or endangered Schumann et al 1999 Partners in Flight PIF has identified Rufous Hummingbird Selasphorus rufus and Allen s Hummingbird Selasphorus sasin as Watch List species of continental concern Rosenberg et al 2016 Watchlist species are of concern due to small populations declining population trends narrow distribution high threats restricted distributions or some combination of these Rich et al 2004 In order to advance hummingbird conservation it is important to identify key information gaps related to hummingbird biology movements and habitat relationships All species in the western United States genera Archilochus Calypte and Selasphorus migrate long distances annually between temperate and tropical regions facing thermogenic demand Five are endemic to the western North America area Archilochus alexandri Calypte costae Selasphorus rufus Selasphorus sasin and Selasphorus calliope In 2002 the Hummingbird Monitoring Network was developed to inform hummingbird management and conservation In 2009 a group of scientists land managers and conservation professionals convened for the first major meeting of the Western Hummingbird Partnership WHP a multi party network with the goal to advance hummingbird conservation through science based monitoring research habitat restoration enhancement and education outreach efforts with an initial focus on western North America Wethington et al 2010 USDA Forest Service RMRS GTR 408 2020 1

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The WHP identified the study of fire and restoration effects on populations of hummingbirds as a key priority Wethington et al 2010 While a number of studies have addressed avian responses to fire fuel reduction thinning and other restoration practices e g Bock and Block 2005 Huff et al 2005 Kotliar et al 2002 Saab and Powell 2005 Saab et al 2005 Saab et al 2007 virtually none have focused on hummingbirds There is concern that changes in forest or plant community structure as a result of wildfire prescribed fire or other restoration practices will alter habitats and change the availability of nectar resources thus impacting hummingbird populations Contreras Mart nez 2015 In turn as hummingbirds are important pollinators in western ecosystems impacts that result in changes in their abundance and distribution are likely to affect hummingbird pollinated plants many of which are endemic or endangered The WHP also identified global climate change invasive species and habitat loss as significant threats to hummingbird populations Wethington et al 2010 Because hummingbirds are specialized nectar feeders they are likely to be particularly vulnerable to effects of climate change that cause shifts in plant communities or floral phenology Croonquist and Brooks 1991 Some species like Anna s Hummingbird Calypte anna have demonstrated an ability to quickly adapt to human development and food sources while other species like Allen s and Costa s Hummingbird are more restricted in their movements and habitats Some hummingbird species may persist in the face of climate change while others with more sensitive habitat or food requirements will decline in population size or occurrence and possibly face extirpation In order to slow or prevent these declines it is critical to understand the limiting factors on hummingbird populations and the potential impacts both positive and negative of climate change In order to reduce fuel loads and fire risk and to increase the resiliency of forest and aridland habitats to potential climate change impacts land managers across the western United States are initiating a variety of restoration projects For example the USDA Forest Service is currently initiating a series of adaptive restoration projects on National Forest lands through the Collaborative Landscape Restoration Program USDA Forest Service 2012 In an effort to inform these restoration efforts and to address information gaps in our understanding of hummingbirds this review presents the results of studies examining the known or potential impacts of fire and restoration on hummingbirds that breed primarily in the western United States This review first provides an overview of the region of interest and of general hummingbird biology and habitat relationships before describing the range habitat relationships key plant species and conservation status of the seven hummingbird focus species It then provides a summary organized by geographical region of literature related to fire restoration and hummingbirds along with preliminary management implications Where appropriate relevant inferences are drawn from studies of fire and avian ecology fire effects on vegetation or climate change effects on vegetation These sections are followed by a discussion and a summary of research inventory and monitoring priorities for western hummingbirds It is important to note that the results presented in this review of fire restoration effects and avian ecology studies are not comprehensive Instead this review is focused on results that include detections of western hummingbirds or results that can potentially inform an understanding of hummingbirds responses to fire restoration and climate change For a more complete treatment of the fire and avian ecology literature consult reviews such as Bock 2 USDA Forest Service RMRS GTR 408 2020

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and Block 2005 Huff et al 2005 Kotliar et al 2002 Saab and Powell 2005 Saab et al 2005 and Saab et al 2007 Or refer to the sources cited within this review Region of Interest The region of interest is the western United States with the following States considered Washington Oregon California Idaho Montana Wyoming Arizona Colorado New M xico Utah and Nevada In order to organize relevant findings and facilitate their integration into North American Bird Conservation Initiative NABCI and other bird conservation planning contexts we utilized Bird Conservation Regions BCRs BCRs were developed by NABCI to facilitate bird conservation planning throughout North America Rich et al 2004 They are large ecologically distinct units that share relatively homogenous bird communities habitats and resource management issues fig 1 Within the region and States of interest the following nine BCRs were identified BCR 5 Northern Pacific Rainforest BCR 9 Great Basin BCR 10 Northern Rockies BCR 15 Sierra Nevada BCR 16 Southern Rockies Colorado Plateau BCR 32 Coastal California BCR 33 Sonoran and Mojave Deserts BCR 34 Sierra Madre Occidental BCR 35 Chihuahuan Desert Figure 1 Bird Conservation Regions of North America included in this review USDA Forest Service RMRS GTR 408 2020 3

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The Fire Restoration and Hummingbirds section below provides an overview of the habitats historic fire regimes and priority management issues for each of the nine BCRs In compiling results from the literature it became clear that some BCRs are well represented in the fire and restoration literature while others have received little to no study In order to aggregate information in a regional context as well as provide a broad organizational framework for the review we grouped the BCRs of interest into four geographical regions as follows Southwestern Desert and Riparian BCRs 33 34 and 35 Coastal California Sierra Nevada Great Basin BCRs 9 15 32 Pacific Northwest Northern Rockies BCRs 5 10 Southern Rockies BCR 16 These regions broadly correspond to the core breeding ranges of each of the seven focus species for this review Hummingbird Biology and Habitat Relationships All North American hummingbirds belong to the subfamily Trochilinae and the order Apodiformes The hummingbird order has many genera most of which contain only a few species Hummingbird hybridization is relatively common Banks and Johnson 1961 Hummingbirds have a number of unique adaptations that set them apart from other birds They are the smallest birds with weights of North American species ranging from 2 5 to about 5 0 g Calder and Calder 1994 Russell 1996 They have long slender bills and are adapted primarily to feeding on nectar from flowers but they will also feed on a variety of small insects The figure eight motion of their wings allows them to hover while feeding as well as to fly up down sideways and even upside down for brief periods Elphick et al 2001 Hummingbirds have the ability to lower their body temperature to 13 C 55 F to conserve energy Hiebert 1990 Hummingbirds play an important role in plant pollination and are thought to have played a role in the speciation of several plants Grant and Grant 1966 Hummingbird and plant co evolution is especially notable in the tropics Wolf et al 1976 Although they are often associated with red tubular flowers hummingbirds will feed on a variety of flower shapes and colors Grant 1966 Being highly mobile hummingbirds can quickly exploit new food sources and most species feed from a variety of flower species Feinsinger 1978 Snow and Snow 1972 Wolf 1970 Wolf et al 1976 Hummingbirds are known to visit flowers in a predictable sequence called traplining and some defend territories of food resources In a study in Arizona Brown and Kodric Brown 1979 found that hummingbirds were not selective in the flowers they visited and that some individuals carried four or more types of pollen The flowers in this study were all convergent in flower size shape and color Hummingbird movements and the timing of hummingbird migration are not well understood but are thought to relate to flowering plant phenology Baltosser 1989 As described in the species descriptions the Rufous Allen s and Calliope Hummingbird all of which breed in latitudes north of Arizona are thought to migrate following an elliptical route flying south along the Rocky Mountain flyway postbreeding and north in the spring farther west and at lower elevations Calder 1993 Calder and Calder 1994 Phillips 1975 Other species such as 4 USDA Forest Service RMRS GTR 408 2020

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the Black chinned Archilochus alexandri and Broad tailed Hummingbird migrate through Arizona in the fall but their timing and routes are poorly understood Baltosser and Russell 2000 Calder and Calder 1992 Migration is also thought to vary with the age and sex of individuals Adult male Rufous Hummingbirds typically migrate before adult females and in the fall females precede the juveniles Calder 1993 Phillips 1975 Male Black chinned and Costa s Hummingbirds precede females but the young migrate at approximately the same time as females Baltosser and Russell 2000 Baltosser and Scott 1996 Citizen science data from eBird has revealed evidence of seasonal geographic variation in migratory routes for Rufous Black chinned Calliope and Broad tailed Hummingbirds although more research is needed to understand how hummingbird species respond to environmental change and conditions en route Supp et al 2015 Hummingbirds are territorial and will actively defend their feeding and nest sites against conspecifics and potential predators They usually do so through performing an elaborate dive display which is repeated several times Males warn off intruders with a variety of tactics including vocalizations flashing of the gorget and or the crown feathers or even a physical assault punctuated with diving displays Elphick et al 2001 Both male and female hummingbirds establish territories usually in different locations Hummingbirds do not maintain pair bonds and males will try to mate with as many females as possible It is thought that males set up territories in relation to food supplies although other factors may influence territory selection such as proximity to females nest sites or open views of the surrounding area Armstrong 1987 Pitelka 1942 Powers 1987 Female hummingbirds build an open cup shaped nest on a branch or other supporting structure They typically nest in the canopy or sub canopy less than 15 m above the ground Saab and Powell 2005 They construct their nest out of soft silky materials like spider webs caterpillar silk feathers down bark or lichen Predation is a major cause of nest failure for many hummingbirds Baltosser 1986 Greeney and Wethington 2009 however found that nests within 300 m of active accipiter nests had significantly higher probabilities of successfully fledging young It is thought that the presence of accipiters kept away potential hummingbird nest predators like jays Species of Interest It is outside of the scope of this review to consider all of the hummingbird species that occur within the region of interest Instead we chose to focus on those species that have much of their global distribution in the western United States In managing habitats for these species other hummingbird species that occur in the same habitats should benefit In order to determine the focus species the Partners in Flight PIF Landbird Population Estimates Database was queried to determine the percent of global distribution and estimated population of western hummingbirds within the States and BCRs of interest Blancher et al 2007 The following seven species were identified as having 40 percent or more of their global distribution in the region of interest Allen s Hummingbird Anna s Hummingbird Black chinned Hummingbird Broad tailed Hummingbird USDA Forest Service RMRS GTR 408 2020 5

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Calliope Hummingbird Costa s Hummingbird Rufous Hummingbird In this section we briefly describe the range movements habitat relationships key plant species and conservation status of the seven focus species Anna s Hummingbird Calypte anna The Anna s Hummingbird fig 2 breeds from southern British Columbia to the Baja Peninsula of California Russell 1996 although it is likely the range has expanded northward Battey 2019 Davidson et al 2015 During the postbreeding period it is found along the Pacific Coast from southeastern Alaska to northern M xico Its postbreeding movements are not well understood but are thought to take advantage of localized seasonal blooms In California individuals are thought to move to higher elevations postbreeding coinciding with the flowering of high elevation plants as well as to the south and east where movements coincide with the onset of summer rains and the availability of flowering plants and insects Russell 1996 Figure 2 Anna s Hummingbird photo Jim Livaudais used with permission 6 USDA Forest Service RMRS GTR 408 2020

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The Anna s Hummingbird feeds on a variety of flowering plants including chaparral currant Ribes malvaceum fuchsia flowered gooseberry Ribes speciosum monkeyflower Mimulus spp penstemon Keckiella cordifolia fig 3 fuchsia Epilobium cana woolly blue curls Trichostema lanatum manzanita Arctostaphylos spp pitcher sage Salvia spathacea western columbine Aquilegia formosa and Indian warrior Pedicularis densiflora Grant and Grant 1966 Russell 1996 Stiles 1973 It is considered an important pollinator throughout its range Breeding coincides with the onset of winter rains as chaparral currant begins to bloom In California nesting begins as early as mid November and usually ends in May although both earlier and later nesting have been recorded Broods fledge from March through June coinciding with the blooming of fuchsia flowered gooseberry and other flowers Russell 1996 Figure 3 Keckiella cordifolia photo Tim Miller used with permission The Anna s Hummingbird breeds primarily in chaparral habitats interspersed with open woodlands Pitelka 1951 Stiles 1973 Males set up territories on slopes in chaparral while females typically nest in live oak Quercus agrifolia woodlands in canyon bottoms with nests located 2 to 20 m above the ground Grinnell and Wythe 1927 Anna s Hummingbirds also use riparian woodlands coastal scrub and urban and suburban areas with exotic flowering plants for breeding Shuford 1993 Small 1994 Its range is thought to have expanded significantly since the 1930s as urban and suburban development have introduced new year round food sources Because of its expanded range the Anna s Hummingbird is not currently of conservation concern Russell 1996 USDA Forest Service RMRS GTR 408 2020 7

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Allen s Hummingbird Selasphorus sasin The Allen s Hummingbird fig 4 is a short to medium distance migrant that breeds in a narrow strip along the Pacific Coast of California and southwestern Oregon and winters in a small area of central M xico Mitchell 2000 It is rarely found in Mojave Desert scrub habitats Cody 1968 Rosenberg et al 1991 There are two known subspecies the migratory Selasphorus sasin sasin and the resident S s sedentarius found on the Channel Islands of California and on adjacent small sections of the mainland although the mainland range has expanded in southern California since 1970 Clark 2017 The Allen s Hummingbird breeds in coastal scrub or riparian shrub woodland habitat generally within 30 km of the coast and occasionally uses coastal pine forests or live oak woodlands Grinnell and Miller 1944 In western M xico it is a rare species in cloud forests and coniferous oak forests and its abundance is influenced by floral abundance after a fire It prefers sites with a scrub layer and a thin canopy adjacent to territories with native trees It starts to arrive during the second week of November and departs in March Contreras Mart nez 2015 There is a large population at the Sierra de Manantl n in December Santana 2000 Figure 4 Allen s Hummingbird photo Mark Chappell used with permission 8 USDA Forest Service RMRS GTR 408 2020

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Most migratory hummingbird species reduce their ranges in winter compared to their breeding ranges however Allen s Hummingbird increases its range in winter ContrerasMart nez and Schondube 2009 using the Neovolcanic Transverse Belt an important overwintering region with flowering plants at high elevations as the season progresses Allen s Hummingbirds use this region to move from eastern to western M xico Contreras Mart nez 2015 but more study is needed to understand the habitat use and distribution of Allen s Hummingbird in winter The Allen s Hummingbird is known for the extremely early timing of its migration Northbound migration begins as early as December and southward migration can begin as early as mid May Northbound migration follows the Pacific Coast corresponding to the flowering of winter blooming plants while southward movements are thought to follow an inland route through the coast range or the Sierra Nevada mountains corresponding to higher elevation blooms Phillips 1975 Nesting usually takes place from early to mid February through June Pitelka 1951 Male Allen s Hummingbirds establish territories in open coastal scrub or riparian shrub habitat Females select their nest sites in areas of dense vegetation and nests are usually 5 to 15 m above the ground Legg and Pitelka 1956 The migratory sasin subspecies feeds on a variety of flowers including bush monkeyflower Mimulus aurantiacus Indian paintbrush Castilleja spp columbine Aquilegia formosa currants and gooseberries Ribes spp Indian pink Silene laciniata S californica Indian warrior Pedicularis densiflora twinflower Lonicera involucrata penstemon Penstemon and Keckia spp ceanothus Ceanothus spp pitcher sage Salvia spathacea madrone Arbutus menziesii and manzanita Arctostaphylos spp Bent 1940 Grant and Grant 1966 It is also known to pollinate several lily species along the coast of California including the federally endangered western lily Lilium occidentale fig 5 The sedentarius subspecies feeds on a number of endemic plant species on the Channel Islands including island snapdragon Galvezia speciosa island monkeyflower Mimulus flemingii and Indian paintbrush Castilleja lanata hololeuca Mitchell 2000 Figure 5 Lilium occidentale photo 2000 John Game used with permission USDA Forest Service RMRS GTR 408 2020 9

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The Allen s Hummingbird is a PIF Watchlist species due to its small geographic range particularly the range of S s sedentarius Rosenberg et al 2016 It is also listed as a U S Fish and Wildlife Service USFWS 2008 Bird of Conservation Concern Breeding Bird Survey data suggest potential declines in the Allen s Hummingbird although the reasons for these declines are unknown Sauer et al 2008 The mainland range of S s sedentarius has expanded more than 23 percent in mainland California since 1970 primarily in urban areas Clark 2017 The Allen s Hummingbird is difficult to distinguish from the Rufous Hummingbird which presents a challenge for field identification based on physical appearance but other indicators such as dive type and sonation are distinctive between species Calder 1993 Mitchell 2000 The expansion of the Anna s Hummingbirds range in recent decades is also of some concern as the Allen s Hummingbird is thought to be at a competitive disadvantage to the Anna s Hummingbird Mitchell 2000 Black chinned Hummingbird Archilochus alexandri The Black chinned Hummingbird fig 6 breeds in a variety of habitats throughout the western United States Texas and northeastern M xico and winters in west central M xico Baltosser and Russell 2000 Karr and Freemark 1983 During breeding it is most abundant in the southern portion of its range particularly in riparian habitats of southern Arizona and southern New M xico but it also breeds throughout the southern central and northern Rocky Mountains Males arrive on breeding grounds from mid March to May depending on latitude and typically depart in July and August before the females and young migrate Russell 1996 Figure 6 Black chinned Hummingbird photo Jim Livaudais used with permission 10 USDA Forest Service RMRS GTR 408 2020

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The Black chinned Hummingbird nests in riparian or woodland habitats that include oaks Quercus spp sycamores Platanus spp cottonwoods Populus spp and willow Salix spp Strong and Bock 1990 found that in southeastern Arizona Black chinned Hummingbirds used lowland areas with relatively large riparian trees especially Arizona sycamore Platanus wrightii and that they selected drier areas than other species It also uses a variety of altered habitats including urban environments and in the lower Colorado River Valley it nests almost exclusively in introduced tamarisk Tamarix ramosissima or salt cedar habitats Rosenberg et al 1987 Females often nest in canyon bottoms floodplains or dry washes while males are often found on adjacent drier slopes Nests are typically less than 4 m above the ground Baltosser 1989 In the Sonoran Desert nesting is usually limited to a single brood Strong and Bock 1990 Postbreeding habitat is thought to be similar to breeding habitat and postbreeding movements appear to follow food availability Baltosser and Russell 2000 The Black chinned Hummingbird is an important pollinator throughout its range In the mountains of Arizona it pollinates beard lip penstemon Penstemon barbatus and squawfeather Castilleja integra fig 7 Brown and Kodric Brown 1979 The Black chinned Hummingbird s range has expanded as artificial food sources and nesting habitats especially tamarisk habitats have grown There is little conservation concern for the species rangewide although it is thought that the loss or severe alteration of riparian habitats could affect local populations Baltosser and Russell 2000 Population growth is thought to be limited due to high levels of nest predation Baltosser 1986 Figure 7 Castilleja integra photo 2004 Robert Sivinski used with permission USDA Forest Service RMRS GTR 408 2020 11

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Broad tailed Hummingbird Selasphorus platycercus The Broad tailed Hummingbird fig 8 breeds throughout the southern and central Rocky Mountains and uses a variety of habitats in upper Sonoran and montane habitats of eastcentral California Arizona New M xico Colorado western Texas Nevada Utah and Wyoming Calder and Calder 1992 It is also found year round in oak and oak pine forests throughout central M xico In California it breeds in upper Sonoran habitats containing pinyon Pinus monophylla juniper Juniperus californica and mountain mahogany Cercocarpus spp in willow thickets and in riparian areas Grinnell and Miller 1944 In Arizona it breeds in ponderosa pine Pinus ponderosa Douglas fir Pseudotsuga menziesii Engelmann spruce Picea engelmannii and fir Abies concolor A lasiocarpa forests as well as in oak woodlands and riparian habitats Phillips et al 1964 In Colorado Utah and Wyoming it breeds in foothill and montane environments containing aspen Populus tremuloides ponderosa pine Engelmann spruce subalpine fir and Douglas fir as well as in shrub patches within woodlands Finch 1989 In western M xico it is restricted to higher elevations in the mountains and some individuals breed in winter sites Contreras Mart nez 2015 Its presence coincides with the flowering peak of plants in the genera Salvia Lobelia Calliandra Ipomea and Senecio Schondube et al 2004 Figure 8 Broad tailed Hummingbird photo Mark Chappell used with permission 12 USDA Forest Service RMRS GTR 408 2020

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The Broad tailed Hummingbird is thought to prefer moderately to heavily disturbed habitats for breeding and is often found in or near meadows or in shrubby habitats along forest edges Szaro and Balda 1982 It is known to nest to 3 230 m 10 597 ft Bagne and Finch 2005 Bock and Block 2005 Nests are usually located 0 3 to 1 5 m above the ground and nest sites often have an overhanging branch or other object to shield the nest and conserve heat Calder 1973 Successful nesting corresponds to peaks in flower blossoms and late nests have lower success rates Calder 1973 Waser 1976 The Broad tailed Hummingbird arrives on its breeding grounds between early March and late May depending on latitude and departs on its postbreeding migration in August or September Although its migration is not well understood it is thought to follow an elliptical migration similar to other Selasphorus hummingbirds traveling north in the spring then east to its breeding grounds then south along the Rocky Mountain flyway postbreeding Calder and Calder 1994 Phillips 1975 The Broad tailed Hummingbird feeds on a variety of red tubular flowers including penstemon Penstemon spp delphinium Delphinium spp columbine Aquilegia elegantula A triternata scarlet gilia Ipomopsis aggregata Mexican fire pink Silene laciniata fig 9 Indian paintbrush Castilleja spp sage Salvia spp bouvardia Bouvardia ternifolia scarlet mint Stachys coccinea and manzanita Arctostaphylos spp Waser 1978 At lower elevations in southeastern Arizona it uses ocotillo Fouquieria splendens The Broad tailed Hummingbird also feeds on a variety of flowers that are not typical for hummingbirds including pussy willow Salix spp glacier lily Erythronium grandiflorum ball head waterleaf Hydrophyllum capitatum and mountain cowslip Mertensia oblongifolia Brown and Kodric Brown 1979 Waser 1978 Figure 9 Silene laciniata photo Tim Miller used with permission USDA Forest Service RMRS GTR 408 2020 13

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There are concerns over declines in Broad tailed Hummingbirds Norvell et al 2005 noted significant declines in riparian areas of Utah from 1992 to 2001 and Hejl 1994 reported declines in western coniferous forests Bagne and Finch 2005 reported a 15 to 49 percent decline in the southern Rockies of New M xico The reasons for these declines are not well understood It has been suggested that the large scale provision of feeders may artificially elevate populations and contribute to large scale mortality in the winter months It is also thought that land use practices like fire suppression timber harvest and grazing may be contributing to declines Brawn and Balda 1988 Hejl 1994 Contreras Mart nez 2015 suggested that the species can be associated with a mix of factors such as temperature basal area of trees and the availability of flowers Phenological mismatch between early spring food resources from flowering plants and spring arrival of Broad tailed Hummingbirds has also shifted and may contribute to reduced nest success in the future McKinney et al 2012 Broadtailed Hummingbirds are not on the 2016 Partners in Flight Watch List but are noted as one of many species that have experienced population declines Rosenberg et al 2016 Calliope Hummingbird Stellula calliope The Calliope Hummingbird fig 10 breeds in montane habitats of western North America from British Columbia and Alberta through California and winters in southern M xico It is the smallest breeding bird in North America known for breeding in high elevation habitats and undertaking a long distance migration despite its small size It is thought that the Calliope Hummingbird migrates in an elliptical pattern similar to the Rufous and Broad tailed Hummingbird flying north along the Pacific Coast in spring then east to its breeding grounds and then south along the Rocky Mountain flyway postbreeding Calder and Calder 1994 Recent analysis of eBird data demonstrates annual east west variation in western hummingbird migration paths including Calliope Hummingbirds that suggests that they may be able to adjust their routes due to weather and resource distribution while still moving north south at similar rates across years Supp et al 2015 The Calliope Hummingbird breeds in forested montane environments of British Columbia the Pacific Northwest the central and northern Rocky Mountains Nevada and California s Sierra Nevada mountains It selects open montane forests and early successional forests for breeding Marcot 1984 During fall migration it uses primarily subalpine and alpine montane meadows but is also seen at low elevation feeders In both California and Oregon it is known to nest in forests in the shrub sapling stage of succession 8 to 15 years after clearcutting or burning Marcot 1984 Meslow and Wight 1975 In winter it is restricted to the higher parts of the mountains in coniferous oak forest edges forest and shrub but it is an uncommon species in the wintering habitat in M xico During its northward spring migration the Calliope Hummingbird uses desert washes and low coastal mountains as well as coastal riparian habitats It feeds on red tubular flowers as well as a variety of other flowers including larkspur Delphinium spp fig 11 columbine Aquilegia spp squaw currant Ribes cereum paintbrush and bearded tongues Penstemon spp Armstrong 1987 Bent 1940 Martin 1988 Male Calliope Hummingbirds set up breeding territories in open areas such as forest openings meadows or clearings while females nest in forests or in aspen or willow thickets along streams Ryser 1985 Nests are usually positioned under an overhanging branch to shield from precipitation and heat loss Bent 1940 Calder 1973 14 USDA Forest Service RMRS GTR 408 2020

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The Calliope Hummingbird was a 2004 PIF Watch List Species and a USFWS 2008 Bird of Conservation Concern Rich et al 2004 but was not a 2016 PIF Watch List Species Rosenberg et al 2016 Current species assessment scores rank Calliope Hummingbird as a Yellow Watch list species due to range restriction PIF Partners in Flight 2017 It is thought that the provision of feeders may artificially elevate populations and contributing to high mortality during winter The distribution of Calliope Hummingbird is more limited in M xico and it displays strong site fidelity Contreras Mart nez and Schondube 2009 but habitat loss may be related to threats from agricultural development Contreras Mart nez personal observation 2019 Costa s Hummingbird Calypte costae The Costa s Hummingbird fig 12 breeds in Sonoran Desert scrub habitats of Arizona southern and Baja California Nevada Utah and Sonora M xico Baltosser and Scott 1996 It is less common but widespread during breeding in Mojave Desert habitats of Nevada southwestern Utah northeastern Arizona and parts of eastern California as well as in California coastal shrub and chaparral habitats Johnsgard 1983 In the Sonoran Desert breeding takes place from February to May after which most individuals are thought to migrate to the Pacific Coast of southern and Baja California Phillips et al 1964 These individuals are thought to return to Arizona and California deserts beginning in October coinciding with the blooming of chuparosa Justicia californica or desert lavender Hyptis emoryi fig 13 where they remain through the breeding season Weathers 1983 Individuals that breed in the Mojave Desert arrive there between February and April and remain into May or June after which most are thought to winter in M xico although some individuals overwinter Baltosser and Scott 1996 In southern California breeding occurs in coastal sage and chaparral habitats from March through September and most individuals are thought to winter in M xico In the Sonoran Desert the Costa s Hummingbird breeds in dry low elevation scrubby habitats In the Mojave Desert it breeds near springs and in riparian woodlands washes and canyons In California it breeds in chaparral and sage scrub habitats Stiles 1973 During migration it uses xeric habitats although it may follow riparian corridors or canyons Baltosser and Scott 1996 Nests are usually built in a tree or shrub 1 to 2 m above the ground and vegetative cover around the nest is often sparse Along the Colorado River Costa s Hummingbird nests were located in catclaw acacia Acacia greggii graythorn Condalia globosa and in flowering stalks of Utah agave Agave globosa Brown 1992 The Costa s Hummingbird feeds on nectar from a variety of flowering shrubs trees cacti and agaves Chuparosa is a reliable source of midwinter nectar while ocotillo is used in March and April during breeding Scott 1994 Waser 1976 Other nectar sources include desert lavender Hyptis emoryi creosote bush Larrea tridentata fairy duster Calliandra eriophylla paloverde Parkinsonia spp saguaro Carnegiea gigantea bladderpod Peritoma arborea desert willow Chilopsis linearis ironwood Olneya tesota barestem larkspur Delphinium scaposum bush penstemon Keckiella antirrhinoides desert honeysuckle Anisacanthus thurberi squaw cabbage Stanleya spp black sage Salvia mellifera white sage Salvia apiana tree tobacco Nicotiana glauca woolly bluecurl Trichostema lanatum bush monkeyflower Diplacus longiflorus Mojave beardtongue Penstemon pseudospectabilis and heart leaved penstemon Penstemon cordifolius Baltosser and Scott 1996 Grinnell and Miller 1944 16 USDA Forest Service RMRS GTR 408 2020

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The Costa s Hummingbird was listed as a PIF Watch List Species in 2004 and a USFWS 2008 Bird of Conservation Concern Rich et al 2004 but is not a PIF Watch List Species in 2016 Rosenberg et al 2016 It is listed as threatened in New M xico Its greatest threat is habitat alteration and loss especially in California desert scrub coastal scrub and chaparral habitats but also in Sonoran Desert scrub habitats In many areas of the southwestern United States it is thought that human development has favored the Anna s Hummingbird which readily uses urban and suburban habitats at the expense of the Costa s Hummingbird Bolger et al 1997 Intensive cattle grazing and the invasion of buffelgrass Pennisetum ciliare and other exotic grasses into Sonoran Desert scrub habitats are also thought to be negatively affecting the Costa s Hummingbird Baltosser and Scott 1996 Yetman and B rquez 1994 Rufous Hummingbird Selasphorus rufus The Rufous Hummingbird fig 14 has the northernmost range and the longest migration of any western hummingbird It utilized the greatest number of BCRs during the spring and fall migrations It breeds from southeastern Alaska through British Columbia Washington Oregon northern California western Alberta and the northern Rockies of Idaho and western Montana It winters throughout Baja California and northern and central M xico Calder 1993 The Rufous Hummingbird is known for its use of high elevation habitats and has been observed in alpine meadows at 3 840 m 12 600 ft in the Sierra Nevada of California Small 1994 Like other Selasphorus hummingbirds the Rufous Hummingbird is thought to have an elliptical migration following a lowland coastal route north in the spring and a highelevation route south in the summer and fall along the Rocky Mountain flyway or through the Coast Range and Sierra Nevada mountains Phillips 1975 The Rufous Hummingbirds movements are thought to correspond to floral phenology Calder 1993 Migrants arrive on their breeding grounds from February to May depending on latitude and depart in July or Figure 14 Rufous Hummingbird photo Jim Livaudais used with permission 18 USDA Forest Service RMRS GTR 408 2020

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August The Rufous Hummingbird breeds in second growth forests and forest openings as well as in mature forests riparian areas parks fields meadows and other open areas In western Oregon nests were found in second growth forests from 16 to 120 years old Meslow and Wight 1975 Nests are usually well concealed in trees and shrubs and colonies of up to 20 nests within a small area have been found Bent 1940 During summer and fall migration the Rufous Hummingbird uses primarily high elevation meadows and other openings and during late winter and spring it uses low coastal mountains and coastal riparian habitats Calder 1993 The Rufous Hummingbird feeds on a variety of red tubular flowers including red columbine Aquilegia formosa scarlet gilia Ipomopsis aggregata fig 15 bearded tongues Penstemon spp and paintbrushes Castilleja spp It also feeds on a variety of other flowers including sage Salvia spp bouvardia Bouvardia ternifolia mint Stachys coccinea lilies Erythronium grandiflorum Lilium columbianum purple larkspur Delphinium barbeyi and D geranioides heath Vaccinium ovatum Menziesia ferruginea currant Ribes sanguineum salmonberry Rubus spectabilis honeysuckle Lonicera spp fireweed Epilobium angustifolium horsemint Monarda menthifolia toad flax Linaria vulgaris snapdragon Scrophularia montana and bee flower Cleome serrulata Calder 1993 The Rufous Hummingbird is a PIF and Audubon Watch List Species and is listed as a USFWS 2008 Bird of Conservation Concern Rich et al 2004 It is a Partners in Flight Focal Species for nectar producing plants in early seral forests Altman 2005 Breeding bird survey data show an estimated 63 percent decline in Rufous Hummingbird since the 1960s although reasons for these declines are unknown Berlanga et al 2010 The Rufus Hummingbird is a 2016 PIF Watch List species of continental concern Rosenberg et al 2016 Figure 9 Ipomopsis aggregata bridgesii photo Tim Miller used with permission USDA Forest Service RMRS GTR 408 2020 19

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Fire Restoration and Hummingbirds Key Findings By Region Southwestern Desert and Riparian Habitats and Fire Regimes The Sonoran and Mojave Deserts BCR 33 cover much of the southwestern United States The Mojave Desert region extends from southeastern California through southern Nevada and portions of Arizona and Utah Dominant Mojave Desert scrub vegetation includes creosote bush Joshua tree Yucca brevifolia and mesquite Prosopis spp while juniper Juniperus spp and white fir Abies concolor forests are found at higher elevations The Sonoran Desert extends through much of southern Arizona and southwestern New M xico as well as into Baja California and Sonora M xico The Sonoran Desert region is dominated by cacti including saguaro Carnegiea gigantea and cholla Cylindropuntia spp as well as shrubs like creosote bush and bursage Ambrosia dumosa and small trees like mesquite Prosopis spp paloverde Parkinsonia florida desert ironwood Olneya tesota desert willow Chilopsis linearis ssp arcuata and ocotillo Fouquieria splendens Shreve and Wiggins 1964 At higher elevations Sonoran Desert scrub transitions into chaparral or desert grasslands in the north and desert thornscrub to the south B rquez et al 1992 Fires were historically rare in Sonoran and Mojave Desert habitats and many native desert plants are not fire adapted Humphrey 1974 In recent decades exotic grasses and shrubs like buffelgrass which is planted for cattle forage and red brome Bromus rubens have invaded southwestern desert habitats Yetman and B rquez 1994 These fire prone exotic plants have increased fuel loads leading to more frequent high severity fires that cause mortality of non fire adapted desert plants Bock and Block 2005 D Antonio and Vitousek 1992 Schmid and Rogers 1988 Population estimates for BCR 33 are presented in table 1 Table 1 Western hummingbird percent global population and population estimates for BCR 33 Sonoran and Mojave Deserts Species Costa s Hummingbird Total Global population 31 3 Population estimate 900 000 900 000 Source Partners in Flight Landbird Population Estimates Database http pif birdconservancy org PopEstimates Database aspx The Sierra Madre Occidental BCR 34 is a mountain range that extends from southeastern Arizona through central M xico It is characterized by pine pine oak and fir forests at higher elevations and by semiarid scrub habitats on the eastern slopes NABCI 2012 Little is known about historic fire regimes in these habitats but it is thought that the pine and pine oak forests of the Sierra Madre Occidental historically experienced frequent low to mid severity fires similar to ponderosa pine forests of the southwestern United States Fule and Covington 1997 20 USDA Forest Service RMRS GTR 408 2020

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Wildfires are the most important environmental disturbances in this region and are known to trigger the succession process in forested areas Jardel Pel ez et al 2006 However fire exclusion largely as a result of grazing is thought to have increased the volume of woody vegetation leading to more intense fires and mortality of mature oaks Johnson et al 1962 Population estimates for hummingbirds in BCR 34 are presented in table 2 Table 2 Western hummingbird percent global population and population estimates for BCR 34 Sierra Madre Occidental Species Anna s Hummingbird Black chinned Hummingbird Broad tailed Hummingbird Costa s Hummingbird Total Global population 2 2 Population estimate 100 000 8 9 4 1 4 1 400 000 400 000 120 000 1 020 000 Source Partners in Flight Landbird Population Estimates Database http pif birdconservancy org PopEstimates Database aspx The Chihuahuan Desert BCR 35 borders the Sierra Madre Occidental to the east extending from southern New M xico and extreme southeastern Arizona through central M xico Lower elevations are dominated by desert scrub vegetation including creosote bush mesquite and tarbush Flourensia cernua as well as desert grasslands dominated by native black grama Bouteloua eriopoda with evergreen pinyon juniper and pine oak woodlands at higher elevations Bock and Block 2005 Like the Sonoran and Mojave Deserts fire was likely rare historically in Chihuahuan desert and grassland habitats Due to the combined effects of grazing and fire exclusion native Chihuahuan desert grasslands have experienced extensive conversion to exotic shrublands Bock and Block 2005 Climate change is expected to increase aridity and the frequency of fire in Chihuahuan desert habitats which will accelerate the decline in range and occurrence of native desert grasses like black grama Kilgore et al 2009 Population estimates for hummingbirds in BCR 35 are presented in table 3 Southwestern riparian habitat is not identified as a BCR but we include it as a habitat type within the Southwestern Desert and Riparian region due to its high importance for breeding birds including hummingbirds in the southwestern United States Riparian habitats are found throughout the southwestern United States and comprise a major source of vegetative and biological diversity in these habitats Stamp 1978 Strong and Bock 1990 Native southwestern riparian vegetation includes cottonwood Arizona sycamore Platanus wrightii willow and netleaf hackberry Celtis reticulata These trees provide important breeding habitat for many resident and migratory birds including several endangered or threatened species Powell and Steidl 2000 Skagen et al 1998 Szaro and Jakle 1985 Riparian habitats in the southwestern United States provide breeding habitat for many bird species in this region including rare or declining species that are not found elsewhere Carothers et al 1974 Cartron et al 1999 Johnson et al 1977 Naiman et al 1993 Rosenberg et al 1991 Strong and Bock 1990 USDA Forest Service RMRS GTR 408 2020 21

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Table 3 Western hummingbird percent global population and population estimates for BCR 35 Chihuahuan Desert Species Black chinned Hummingbird Broad tailed Hummingbird Total Global Population population estimate 15 8 5 4 700 000 500 000 1 200 000 Source Partners in Flight Landbird Population Estimates Database http pif birdconservancy org PopEstimates Database aspx Over the past century southwestern riparian habitats have been altered extensively through changes to hydrological regimes fire suppression grazing and invasion by exotic plants especially tamarisk Tamarix spp Fleischner 1994 estimates that 90 to 95 percent of the original riparian habitat in the southwestern United States has been lost or degraded These alterations have changed natural disturbance regimes increasing fuel loads and the incidence of wildfires in riparian habitats Bock and Block 2005 Schmid and Rogers 1988 The invasion of drought resistant tamarisk into riparian habitats of the southwestern United States is thought to be contributing to more frequent intense wildfires that are destructive to native vegetation Busch 1995 Finch et al 2006 Wildfire and Hummingbirds Fire was historically rare in southwestern desert habitats and many desert plants are not well adapted to frequent fire Humphrey 1974 McLaughlin and Bowers 1982 Because many desert bird species including hummingbirds rely on native vegetation for nesting and foraging the loss or alteration of native vegetation due to fire and the spread of exotics is likely to have a profound effect on these species Bock and Block 2005 A study of plant communities and birds following fire in the Sonoran Desert in Arizona found reduced bird species richness compared with unburned areas both immediately and 4 years postfire Esque et al 2013 Because so few studies exist the potential effects of fire on birds in desert habitats must be surmised from studies of the effects of fire on vegetation Esque and Schwalbe 2002 There is a strong correlation between native vegetation volume complexity and bird diversity and abundance in Sonoran and Mojave Desert scrub habitats The destruction of native vegetation through fire will likely have a negative effect on hummingbirds that breed in these habitats for example the Costa s and Black chinned Hummingbird Mills et al 1991 Tomoff 1974 While chuparosa responds well to fire in southern Arizona many other desert plants that are used for both foraging and nesting by the Costa s Hummingbird such as paloverde agave and many cacti species are destroyed by fire Baltosser and Scott 1996 Yetman and B rquez 1994 Therefore increases in the frequency and intensity of wildfire in desert scrub habitats are likely to negatively affect the Costa s Hummingbird and other hummingbirds that use these habitats Climate change particularly decline in rainfall is correlated to overall declines and collapse of bird communities in the Mojave Desert since the early 20th century Iknayan and Beissinger 2018 Climate change may also negatively impact hummingbirds through its impacts on native 22 USDA Forest Service RMRS GTR 408 2020

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vegetation in southwestern desert habitats although this needs more study Smith et al 2000 predicted that exotic grass seed production will be enhanced under projected climate change scenarios White et al 2011 modeled bird occurrence in northern Chihuahuan desert habitats using simulated vegetation changes associated with climate change The model projected increases in the relative abundance of shrubland birds and decreases in the abundance of bird species associated with grassland yucca Yucca spp and ocotillo Fouquieria splendens habitats The model predicted increases in shrubland because leaf area index values were lower in shrubland These results have potentially negative implications for the Costa s Hummingbird which feeds on ocotillo flowers Because hummingbirds are not generally found in desert grasslands this review does not address the results of studies examining avian responses to fire in grassland habitats in detail In general studies of postfire desert grassland bird habitat associations indicate declines in bird species that require dense cover and increases in ground foraging birds Bock and Bock 1978 Bock and Bock 1988 Bock and Bock 1992 In the Sierra Madre Occidental mountains of western M xico fires are important for maintaining plant species diversity in the pine and pine oak forest Jardel Pel ez et al 2009 Fires are part of the historical regime and many plant species survive the effects of surface fires and regenerate quickly following severe fires Jardel Pel ez et al 2006 Llamas Casillas 2009 However when several fires occur in a short timeframe regeneration in forests is inhibited and is replaced by secondary scrub Jardel Pel ez et al 2006 found that pines dominate early successional stages of tree regeneration whereas broadleaf species dominate in later stages In the understory flowering herbaceous plants dominate in early postfire successional stages and are gradually replaced by woody plants with fewer flowers in later successional stages Long distance migratory hummingbirds respond to the successional stages of forest regeneration as they depend on the abundance of plants that regenerate after the fires for example abundant Salvia iodantha and S mexicana Arizmendi 2001 In Jalisco Contreras Mart nez 2015 and Contreras Mart nez and Santana 1995 reported that hummingbird responses to postfire conditions varied Out of the 10 common hummingbird species in pine oak forest 60 percent are migratory and occur within the regions included in this review Hummingbirds are most abundant in the earlier successional stage after a fire but changes in diversity of hummingbird species are not always correlated with the diversity of food plants at any given point in time but are correlated with overall flower abundance Contreras Mart nez 2015 Contreras Mart nez and Santana 1995 In southwestern riparian habitats native vegetation structure and diversity correlate with breeding bird diversity and abundance as well as to nest success Carothers et al 1974 Powell and Steidl 2000 Strong and Bock 1990 Szaro and Jakle 1985 Avian diversity is also correlated to the presence of native cottonwoods in riparian habitats and native Arizona sycamore is an important nest substrate Carothers et al 1974 Powell and Steidl 2000 Stamp 1978 In recent decades there have been significant declines in bird abundance and diversity in many southwestern riparian habitats Rosenburg et al 1991 Skagen et al 1998 Strong and Bock 1990 Southwestern riparian habitats are not adapted to frequent or intense fire and recent wildfires in these habitats have caused the mortality of native trees including cottonwood Populus fremontii and sycamore Platanus wrightii Bock and Bock 1988 Stuever 1997 In one of the few studies of the impacts of fire on birds in southwestern riparian habitats Smith et al 2006 studied breeding bird and native vegetation responses to wildfire USDA Forest Service RMRS GTR 408 2020 23

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along the Middle Rio Grande River in New M xico Black chinned Hummingbirds were more abundant at control sites than at burned sites suggesting a decrease in abundance after wildfire Restoration and Hummingbirds Few studies have examined avian responses to restoration treatments in southwestern desert scrub habitats More study is needed on the impacts of restoration treatments including fencing to exclude grazing replanting of native species and exotic plant removal on breeding bird species in these habitats Prescribed fire is not indicated as a management tool due to the destructive effects of fire on native vegetation Herbicide application has shown some promise in killing buffelgrass but its long term effectiveness as well as its effects on native plants and birds are not well studied Bovey et al 1984 Tjelmeland et al 2008 Few studies have examined hummingbird responses following fire in western M xico In Sierra Madre Occidental fire is one of the most common natural and anthropogenic disturbances to wildlife habitats Fire management in Mexican forested areas is a controversial issue as many do not view fires as part of the normal dynamic nature of these ecosystems Jardel Pel ez 2000 In addition fire regimes have changed over time and fires are becoming more frequent more severe and larger Despite the importance and growing incidences of fire no studies on vegetation restoration food resources such as flowering shrubs and hummingbirds have been conducted in western M xico In general the abiotic factors that affect the abundance of hummingbird species are the presence frequency and severity of the fire altitude and temperature Contreras Mart nez 2015 The biotic factors that affect the abundance of hummingbirds are mainly the abundance of hummingbird pollinated flowers and canopy cover The challenges of habitat management and restoration following fire are different at the sites that hummingbirds use throughout their life cycles Regardless of the location fire can affect the diversity and density of floral nectar resources in turn impacting hummingbird foraging both positively and negatively and thus limit hummingbird populations Contreras Mart nez 2015 Contreras Mart nez and Santana 1995 More study is needed to address the timing of prescribed fires and the restoration of postfire habitat Few studies have examined avian responses to restoration treatments in southwestern riparian habitats Still many species of birds use invasive tamarisk as breeding habitat without any loss to productivity or nest success suggesting that restoration projects focused on the removal of tamarisk should ensure it is replaced with high quality native vegetation to mitigate the potential effects of restoration treatments on breeding birds Sogge et al 2008 From 2000 to 2005 vertebrate responses to a variety of restoration treatments designed to reduce fuel and remove invasive plants in riparian forests were studied along the Middle Rio Grande River in New M xico Treatments included mechanical removal along with herbicide treatment partial mechanical removal and herbicide treatment followed by prescribed fire and mechanical removal followed by herbicide treatment and revegetation Bateman et al 2008 Finch 2008 Finch et al 2006 Smith et al 2009 Finch et al 2006 found that Black chinned Hummingbirds were the most abundant species on all sites across all years of the study but they declined in response to the treatment likely due to reductions in nesting and foraging habitat Finch 2008 Finch et al 2006 Black chinned Hummingbird nest success was slightly lower in native substrates than in exotic 24 USDA Forest Service RMRS GTR 408 2020

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substrates but the analysis revealed nest success was not significantly related to exotic versus native plant use and Black chinned Hummingbirds appeared to readily switch to native nesting substrates after exotics were removed during the first year following treatment Finch et al 2006 Smith et al 2009 further examined the effects of the treatments described above on nestsite selection and nest survival of Black chinned Hummingbirds Similar to the results of Finch et al 2006 nest survival was higher in pretreatment plots and in exotic substrates than in posttreatment plots and native cottonwoods however treatments were not found to have a statistically significant effect on nest survival Nest survival was found to be negatively associated with nest height indicating that higher nests were more susceptible to predation These results are similar to those of Baltosser 1983 who found an inverse relationship between nest height and nest survival for Black chinned Hummingbirds Both Smith et al 2009 and Finch et al 2006 found that nest survival rates varied significantly from year to year and across locations indicating high variability in hummingbird abundance movements and habitat selection from year to year Finch et al 2006 Additional work examining nest success of Black chinned Hummingbirds in riparian areas dominated by either nonnative or native plant species found similar or better nest success in nonnative Russian olive Elaeagnus angustifolia and salt cedar Tamarix spp suggesting that some nonnative shrub and tree species can still provide important habitat structure for nesting hummingbirds Smith et al 2014 These results suggest that while the removal of exotic vegetation may have a short term negative impact on Black chinned Hummingbird abundance and nest success the species will readily adapt to nesting in native vegetation The relative importance of nest height to Blackchinned Hummingbird nest success indicates that structural diversity in riparian vegetation is an important component of nesting habitat quality Management Implications In Sonoran and Mojave Desert scrub habitats the invasion of exotic grasses particularly buffelgrass and the subsequent risk for more frequent intense fires destructive of native desert vegetation are serious management issues Marshall et al 2012 Increases in fire frequencies and the loss of native vegetation have potentially serious consequences for hummingbirds that nest and forage in desert scrub habitats like the Costa s and Black chinned Hummingbird They also have potentially negative implications for species that use these habitats during migration including Anna s Calliope and possibly Allen s Hummingbird Prescribed fire is not considered an appropriate management strategy in southwestern desert scrub habitats due to the destructive effects of fire on native desert vegetation Manual or mechanical removal of exotic grasses may be effective but the long term effectiveness of these methods has not been assessed Manual removal efforts should be monitored diligently to ensure success Herbicide application has shown some promise in killing buffelgrass but its long term effectiveness as well as its effects on native plants and wildlife are not well studied Bovey et al 1984 Tjelmeland et al 2008 More study is also needed on the viability of propagating and replanting native species in these habitats CalPIF 2009 According to Contreras Mart nez 2015 most specialist hummingbirds in pine oak forests of the Sierra Madre Occidental are adapted to the conditions created after a fire It is important to maintain the historical disturbance regime caused by forest fires The landscape USDA Forest Service RMRS GTR 408 2020 25

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matrix caused by diverse perturbation natural and human activities and the resulting mosaic of habitats can maintain hummingbird diversity However it is necessary to maintain burned areas with mostly low severity fire and some small areas of high severity fire 3 hectares surrounded with forest cover of advanced successional stages 80 percent Contreras Mart nez personal observation 2019 and a fire return interval between 11 and 30 years Jardel Pel ez et al 2009 Bird species such as Rufous Hummingbird Calliope Hummingbird and Allen s Hummingbird benefit from high severity fire with a positive response detected during the first 10 years after the fire Contreras Mart nez 2015 In southwestern riparian habitats dense vegetation structure is correlated with nest success and nest height is inversely related to nest success for many avian species including the Black chinned Hummingbird Baltosser 1986 Finch et al 2006 Mills et al 1991 Powell and Steidl 2000 There are indications that native riparian species including cottonwood and willow are able to resprout after fire although native plants may take longer to reestablish than exotics Bateman et al 2008 Finch et al 2006 For example cottonwoods may take up to 10 years to resprout after fire Ellis 2001 Therefore the challenge in riparian restoration is to reduce the risk of wildfire and the extent of exotic vegetation while retaining sufficient understory vegetation to ensure adequate nest success A study of the effects of alternative understory management practices on bird abundance in the Middle Rio Grande found hand thinning approaches to remove exotics resulted in no impact or greater abundance of understory nesting bird species including Black chinned Hummingbirds while mechanical clearing treatments had negative effects on bird abundance Brand et al 2013 Prescribed fire in combination with mechanical and herbicide treatments and the planting of native species may help to reduce fuels and retard the spread of exotics Finch et al 2006 Fuel removal efforts should include planting of native species and the continued monitoring of restoration sites to ensure adequate native plant regeneration Finch 2008 Coastal California Sierra Nevada and Great Basin Habitats and Fire Regimes The Coastal California region BCR 32 is characterized by mixed chaparral and coastal scrub habitats oak pine woodlands and California Central Valley wetland and associated upland habitats This review focuses on California coastal scrub and chaparral habitats as they provide important breeding habitat for Allen s Anna s and Costa s Hummingbird Coastal California has a Mediterranean climate of hot dry summers and wet mild winters California chaparral habitats support a variety of plant species including chamise Adenostoma fasciculatum California lilac Ceanothus spp manzanita Arctostaphylos spp and mountain mahogany Cercocarpus betuloides CalPIF 2004 California coastal scrub habitats are comprised of plants such as coyote brush Baccharis pilularis yellow bush lupine Lupinus arboreus salal Gaultheria shallon and evergreen huckleberry Vaccinium ovatum CalPIF 2004 Munz 1959 Both California chaparral and coastal sage scrub habitats are fire adapted and many plants found in these habitats including gooseberries and currants Ribes spp trefoils Lotus spp and blackberries Rubus spp depend on fire to resprout Brown and DeByle 1989 Keeley 1991 Lyon and Stickney 1976 Morgan and Neuenschwander 1988 In California 57 of 58 herbaceous perennial species resprouted after a wildfire in chaparral Keeley 1998 California 26 USDA Forest Service RMRS GTR 408 2020

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chaparral habitats historically experienced high severity fire every 20 to 40 years although some more southern areas historically experienced longer fire return intervals of 100 years or more Hanes 1988 Keeley and Safford 2005 Kilgore 1981 California coastal scrub habitats are fire adapted but are thought to have had a longer historic fire return interval O Leary 1990 Many coastal scrub plants are capable of resprouting or germinating after fire but the persistence of some coastal scrub plant species is thought to be threatened by fires that occur every 40 years or less Malanson 1985 Too frequent fire intervals of less than 10 years can cause the conversion of California coastal shrub habitats to exotic grasslands Keeley and Safford 2005 Malanson 1985 Fire suppression in California coastal scrub habitats can result in conversion to live oak woodland although this is considered a lesser threat than grassland conversion Callaway and Davis 1993 Table 4 Western hummingbird percent global population and population estimates for BCR 32 Coastal California Species Allen s Hummingbird Anna s Hummingbird Costa s Hummingbird Black chinned Hummingbird Calliope Hummingbird Total Global population 57 5 76 2 12 2 Population estimate 400 000 4 000 000 400 000 4 4 0 2 200 000 5 000 4 605 000 Source Partners in Flight Landbird Population Estimates Database http pif birdconservancy org PopEstimates Database aspx The greatest threats to California coastal scrub and chaparral habitats are loss conversion and fragmentation due to human development California coastal scrub habitats have been virtually eliminated California and chaparral habitats have declined significantly as well CalPIF 2004 Increases in fire frequency due to climate change and human activities also represent a significant threat Keeley et al 1999 Population estimates for hummingbirds in BCR 32 are presented in table 4 The mountain range of the Sierra Nevada BCR 15 rises sharply from the Great Basin on the east and slopes toward the Central Valley of California on the west Mixed conifer forests of sugar pine Pinus lambertiana white fir Douglas fir giant sequoia Sequoiadendron giganteum ponderosa pine and incense cedar Calocedrus decurrens dominate the lower and mid elevations on the west side while red fir Abies magnifica Jeffrey pine Pinus jeffreyi whitebark pine Pinus albicaulis western white pine Pinus monticola and mountain hemlock Tsuga mertensiana dominate the montane and subalpine zones The eastern Sierra is dominated by lodgepole pine Pinus contorta western white pine and whitebark pine at high elevations with pinyon juniper forests at lower elevations USDA Forest Service RMRS GTR 408 2020 27

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Because of its Mediterranean climate of hot dry summers and mild wet winters the Sierra Nevada region evolved with frequent fire It is thought that Sierra Nevada forests historically experienced a patchy mixed severity fire regime with a typical fire return interval of less than 50 years Agee 1993 Kilgore 1973 Skinner and Chang 1996 Fire suppression in Sierra Nevada forests is thought to have created a disproportionate amount of decadent latesuccessional forest stands and an increase in fuels contributing to more frequent high severity fires Brown and Kapler Smith 2000 Husari and Hawk 1994 Population estimates for hummingbirds in BCR 15 are presented in table 5 Table 5 Western hummingbird percent global population and population estimates for BCR 15 Sierra Nevada Species Anna s Hummingbird Black chinned Hummingbird Calliope Hummingbird Rufous Hummingbird Total Global Population population estimate 7 3 300 000 0 2 5 0 0 1 8 000 120 000 6 000 434 000 Source Partners in Flight Landbird Population Estimates Database http pif birdconservancy org PopEstimates Database aspx The Great Basin region BCR 9 includes the northern Basin and Range the Columbia plateau and the eastern slopes of the Cascade and Sierra Nevada mountain ranges in Oregon California Nevada and Utah The Great Basin receives little precipitation mostly in the form of snow Grasslands sagebrush Artemisia spp and other xeric shrubs dominate the lower elevations while pinyon juniper woodlands and open ponderosa pine forests are found at higher elevations Lodgepole pine Pinus contorta and subalpine fir forests are found at higher elevations on north facing slopes Cottonwoods and quaking aspen are found in riparian habitats Great Basin habitats are thought to have been characterized by a low to moderate severity fire regime with seasonal burning by Native Americans Kitchen 2010 Grazing fire suppression and the invasion of exotic grasses in these habitats have resulted in increased fire frequencies more incidences of crown fires and the expansion of woodland habitats into adjacent shrub grasslands Bock and Block 2005 Brooks and Pyke 2001 Keane et al 2002 Population estimates for hummingbirds in BCR 9 are presented in table 6 28 USDA Forest Service RMRS GTR 408 2020

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Table 6 Western hummingbird percent global population and population estimates for BCR 9 Great Basin Species Calliope Hummingbird Rufous Hummingbird Black chinned Hummingbird Anna s Hummingbird Costa s Hummingbird Broad tailed Hummingbird Total Global population 31 6 6 6 Population estimate 800 000 700 000 3 4 0 8 0 2 2 9 160 000 40 000 5 000 300 000 2 005 000 Source Partners in Flight Landbird Population Estimates Database http pif birdconservancy org PopEstimates Database aspx Wildfire and Hummingbirds While California coastal scrub habitats are sensitive to fire California chaparral habitats evolved with frequent fire and it is thought that the bird species associated with these habitats are adapted to fire as well CalPIF 2004 There are indications that bird responses to fire in California chaparral habitats are relatively short lived and that recolonization occurs during the first few years postfire Moriarty et al 1985 Other studies suggest that recently burned chaparral habitats support higher avian species richness and diversity than unburned habitats Longhurst 1978 Wirtz 1982 Overall fire appears to have a neutral to positive effect on bird species richness and abundance in California chaparral Several studies suggest that Anna s Hummingbird populations decline postfire in coastal sage scrub and chaparral habitats In a study of avian responses to a wildfire in a variety of habitats in southern California Mendelsohn et al 2008 found that Anna s Hummingbirds declined significantly in low elevation chaparral habitats 2 years postfire The study found that overall species diversity increased postfire in low elevation coastal sage scrub habitats Shrub and tree covers were reduced significantly postfire in the coastal sage scrub and chaparral habitats Anna s Hummingbird may have declined due to a loss of tree and shrub cover for nesting or perching Moriarty et al 1985 compared bird populations in burned and unburned coastal sage scrub habitats following a wildfire in southern California After an initial drop the number of species at the burned site increased during the first year postfire recovering 70 to 90 percent of the original species richness and abundance Species associated with open habitats preferred the burned area while birds associated with thick shrubby areas favored the unburned area Anna s Hummingbird declined postfire Stanton 1986 studied avian community dynamics 2 and 3 years after the same fire While bird abundance remained relatively constant throughout the year in the control habitat it fluctuated in the burned habitat with higher abundances during the breeding season USDA Forest Service RMRS GTR 408 2020 29

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Black chinned Hummingbirds were more abundant in the burned habitat than in the control habitat by a ratio of 13 1 Anna s Hummingbirds were more abundant in the control habitat by a ratio of 95 60 and showed a statistically significant preference for the unburned habitat These results align with those of Mendelsohn et al 2008 and Moriarty et al 1985 The reasons for declines in Anna s Hummingbirds after fire are unknown but they possibly relate to the loss of tree and shrub cover in burned habitats because the Anna s Hummingbird nests up to 20 m and males often perch on tree branches overlooking their foraging territories Anna s Hummingbirds also rapidly exploit new habitats and food sources so it is possible that individuals disperse to new habitats after fire Limited information suggests that Costa s Hummingbirds may prefer burned habitats in both chaparral and coastal sage scrub habitats Baltosser and Scott 1996 cited a study Cogswell 1962 in which Costa s Hummingbirds reached their maximum density on plots that had burned 3 to 5 years earlier in coastal scrub and chaparral habitats in southern California During this period they were much more abundant than Anna s Hummingbirds The reasons for this are unknown It is possible that postfire habitats offer more food resources to Costa s Hummingbirds or that the species which nests low to the ground prefers habitats in the stage of early shrub regeneration for nesting Burned habitats may also present less territorial competition from Anna s Hummingbirds Unfortunately no information exists on the effects of wildfire on Allen s Hummingbird Studies of avian responses to wildfire in Sierra Nevada forests have found results similar to other studies of fire and avian ecology in western forests Overall studies have found that after fire the abundance of ground and canopy foraging birds as well as timber drilling birds increases while the abundance of foliage gleaning birds decreases Bock and Lynch 1970 Burnett et al 2011 Raphael et al 1987 Responses to high and low mixed severity fire tend to be positive for Broad tailed and Calliope Hummingbirds Fontaine and Kennedy 2012 A number of studies indicate that Calliope Hummingbirds select early to mid successional postfire habitats in the Sierra Nevada In a 2011 study of bird communities after wildfires in the northern Sierra Nevada that took place in 2000 2007 and 2008 Burnett et al 2011 found that Calliope Hummingbirds were most abundant on plots within the 2000 and 2007 fire areas although they were not detected on plots that burned in the 2008 fire The authors noted that Calliope Hummingbirds were rarely detected on private lands after fire possibly because of the practice of removing shrubs to encourage conifer regeneration on these lands Raphael et al 1987 summarized breeding bird censuses that were completed between 1966 and 1985 after a 1960 Sierra Nevada wildfire In this study Calliope Hummingbirds reached their highest mean densities on burned plots between 1975 and 1979 15 to 19 years postfire although their densities were also relatively high on unburned plots during the same period Their abundance remained relatively high 21 to 25 years after fire on the burned plots Raphael et al 1987 Marcot 1984 found that Calliope Hummingbirds were associated with Douglas fir forests in the shrub sapling stage of succession 14 years after fire in northwestern California It is likely that postfire habitats provide important stopover habitat for Rufous Hummingbirds in the Sierra Nevada during their postbreeding migration In late summer of 2009 and 2011 Ryan Burnett Director Sierra Nevada Group PRBO Conservation Science personal communication 2012 observed high numbers thousands of Rufous Hummingbirds foraging in open areas that had burned in a large 2007 wildfire These areas contained many blooming wildflowers 30 USDA Forest Service RMRS GTR 408 2020

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Little is known about the effects of wildfire on hummingbirds in Great Basin habitats It is thought that fire exclusion and grazing have contributed to the expansion of pinyon juniper woodlands into adjacent shrub grasslands which may affect Black chinned Broad tailed or Calliope Hummingbird all of which breed in the Great Basin The expansion of woodlands in Great Basin habitats may benefit the Black chinned Hummingbird which is known to nest in juniper trees Balda 1969 although this has not been studied Restoration and Hummingbirds Studies that have examined the effects of prescribed fire or other restoration practices on birds in California coastal scrub and chaparral habitats have not addressed hummingbird responses specifically Lawrence 1966 found that bird densities increased during the first spring following a prescribed fire in a southern California foothill chaparral habitat but leveled off to prefire levels by the fourth year of the study These results are similar to those of studies of avian responses to wildfire in chaparral There are indications that mechanical fuel reduction treatments like mastication result in lower diversities and abundances of birds than prescribed fire A preliminary report of results from a study comparing prescribed fire and mastication treatments in California chaparral found that 40 bird species used postfire habitats while only 14 species and many fewer individuals used postmastication habitat Potts and Stephens 2007 The mastication plots also contained higher abundances of nonnative grasses A study of chaparral bird community responses in coastal California to either prescribed fire treatments or mechanical mastication found that while bird communities recovered 3 years posttreatment following prescribed fire mechanical treatments resulted in reduced species richness even 5 years following treatment Newman et al 2018 The effects of prescribed fire on songbirds in Sierra Nevada forests are not well studied but results are similar to those of wildfire and avian ecology studies in other habitats Finch et al 1997 Kotliar et al 2002 Saab and Powell 2005 Bagne and Purcell 2011 studied the effects of prescribed fire applied to managed fire suppressed mixed conifer forests in the Sierra Nevada Aerial foraging and riparian associated birds increased 1 year postfire while conifer associated birds declined during the same period Bark foraging and cavity nesting birds increased 3 to 6 years postfire Anna s Hummingbirds decreased by 65 percent immediately postfire in this study a result that aligns with Anna s Hummingbirds responses to wildfire in chaparral An examination of avian responses in the Sierra Nevada found that an interaction of time since fire and burn severity often interacted to predict response in a bird community Taillie et al 2018 While the analysis did not address hummingbird responses specifically it highlighted the need to consider interacting effects when predicting avian response to mixed severity fire Little to no information exists on the effects of restoration practices specifically for hummingbirds in the Great Basin but studies examining restoration and management in pinyon juniper woodlands on bird communities provide useful insights In some pinyonjuniper woodland habitats mechanical removal or chaining techniques have been applied to reduce the encroachment of woodland trees The effects of these practices on birds have not been well studied One study suggested that birds that depend on woodland trees for nesting and foraging responded negatively to the removal of trees through chaining Balda and Masters 1980 The effects of these techniques on hummingbirds are not known Black chinned USDA Forest Service RMRS GTR 408 2020 31

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Broad tailed and Calliope Hummingbirds are known to nest in pinyon juniper woodlands in the Great Basin so these practices have the potential to affect breeding habitat quality for these species In two studies of bird community response to management in pinyon juniper woodlands bird communities remained relatively stable following disturbance though the response varied Knick et al 2014 2017 A study of woodland reduction using mechanical treatments including chaining resulted in either no change or reduction in abundance of several species of birds for up to 2 years following treatment although Black chinned and Broad tailed Hummingbirds did not show a significant decrease in habitat use following treatments relative to controls Bombaci et al 2017 Management Implications Studies indicate that many bird species are able to rapidly recolonize chaparral habitats postfire and that these habitats return to preburn levels of avian abundance and richness within a few years Moriarty et al 1985 Furthermore there is some indication that Costa s Hummingbird a species of conservation concern that breeds in California chaparral and coastal sage scrub habitats responds positively to fire Therefore management practices that encourage the restoration of fire to California chaparral habitats are likely to help maintain avian species richness and diversity in these habitats and will likely benefit the Costa s Hummingbird Anna s Hummingbirds appear to decline in burned habitats postfire however there is little overall conservation concern for this species which is thought to be able to rapidly exploit new habitats and food sources provided through human development The ability of birds including the Costa s Hummingbird to recolonize burned coastal scrub and chaparral habitats likely depends on the availability of suitable refugia within burned habitats or of unburned habitat nearby to escape to during and immediately after fire Mayer and Wirtz 1995 Therefore fire may be detrimental to birds in small or highly fragmented patches of chaparral or coastal scrub that are not adjacent to unburned habitat Many species including the Costa s Hummingbird are thought to be highly sensitive to habitat fragmentation Crooks et al 2004 found a higher diversity of birds sensitive to urbanization in unfragmented sage scrub and chaparral habitats of coastal southern California Bolger et al 1997 found that Costa s Hummingbirds declined in response to fragmentation in coastal scrub and chaparral habitats in southern California and had significantly lower densities in habitats within 500 m of an edge In contrast Anna s Hummingbird was among the four species that increased in response to fragmentation The study concluded that fragmentation was beneficial for species associated with human development and edge habitats like the Anna s Hummingbird and detrimental for species dependent on larger patches of unfragmented habitat like the Costa s Hummingbird Management efforts that focus on preserving existing large intact stands of coastal shrub and chaparral and on restoring natural fire regimes within these habitats are likely to be beneficial to the Costa s Hummingbird as well as other birds Management practices should promote the development of a patchwork of habitats in various successional stages from early to late seral across the landscape to maximize the diversity and abundance of birds CalPIF 2004 Chase et al 2000 In areas with greater habitat fragmentation efforts should focus on creating or maintaining intact corridors between habitat patches as well as buffers between habitat patches and developed areas to reduce the risks of fire predation and the invasion of exotic plants When possible restoration sites should be located adjacent to intact floristically 32 USDA Forest Service RMRS GTR 408 2020

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diverse habitats in order to promote the germination of native herbs Allen et al 2000 When fuel buffers to protect human development are necessary small but effective fuel buffers are recommended over graded buffers that cover a large area CalPIF 2004 In chaparral prescribed fire is recommended over mechanical removal or mastication because fire promotes the regeneration of flowering plants and because mechanical mastication promotes the reseeding of exotic grasses at much higher rates than prescribed fire Potts and Stephens 2007 Conversion to exotic grasslands is one of the greatest threats to California coastal scrub and chaparral habitats Allen et al 2000 CalPIF 2004 While some extent of mixed grassland chaparral habitat may provide habitat heterogeneity and be beneficial for birds homogenous exotic grasslands support a much lower diversity and abundance of birds than chaparral habitats For example in a study comparing southwestern chaparral habitats with adjacent grassland and riparian habitats that had been repeatedly burned and seeded with exotic grasses Szaro 1981 found that bird densities were significantly lower in the burned grassland habitats When necessary mastication should be followed with mulching to discourage the reseeding of exotic grasses Allen et al 2000 Prescribed fire should be applied outside of the breeding seasons of hummingbirds and songbirds which begins as early as February and ends around mid August CalPIF 2004 However some evidence suggests that spring burns in coastal sage scrub may be more likely to promote native plant diversity than fall burns Allen et al 2000 More research is needed on the timing of prescribed fire in these habitats Several studies indicate that the Calliope Hummingbird which breeds in the Sierra Nevada selects early to mid successional postfire habitats for nesting Rufous Hummingbirds have been observed in large numbers in early postfire habitats in the Sierra Nevada during fall migration Managing Sierra Nevada mixed conifer forests for a mixed severity fire regime as was characteristic historically should benefit these species Management should allow for fires to burn at a variety of severities including high severities to promote flowering plant regeneration and provide habitat for a diversity of bird species Many flowering plants in the Sierra Nevada are adapted to resprout after fire For example lupine can regenerate even when the entire crown of the plant is consumed McLean 1969 Golden brodiaea a perennial forb found in the Sierra Nevada flowers when stimulated by increased light Stone 1951 In Sierra Nevada forests prescribed fire is recommended as a management strategy alone or in combination with thinning logging or mastication Prescribed fire will encourage flowering plant regeneration as well as create spatial heterogeneity that will benefit a variety of bird species Postfire habitat should be managed for the growth of a variety of native shrubs and forbs rather than encouraging only conifer regeneration to provide adequate nesting and forging habitat for Calliope and Rufous Hummingbird Burnett et al 2010 In foothill and montane chaparral habitats in the Sierra Nevada restoring a fire return interval of 20 30 years as was characteristic historically will likely be beneficial to species that use these habitats Barbour and Major 1988 Large decadent patches of chaparral shrub can be treated with prescribed fire or mastication applied in small areas over several years to reduce the risk of catastrophic fire USDA Forest Service RMRS GTR 408 2020 33

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Birds in the Great Basin are thought to select habitats along elevational as well as successional gradients Pavlacky 2004 Rosenstock and Van Riper 2001 The effects of fire or fire exclusion on hummingbirds in Great Basin habitats are unknown but fire exclusion is thought to have altered successional processes and led to the encroachment of woodlands into adjacent grassland habitats Bock and Block 2005 Brooks and Pyke 2001 Keane et al 2002 Mechanical fuel reduction techniques like chaining may reduce woodland encroachment into grasslands but some birds including possibly hummingbirds respond negatively to chaining Balda and Masters 1980 The restoration of fire to Great Basin habitats will promote a variety of successional stages across the landscape that will benefit a variety of bird species Pavlacky 2004 More study is needed on the effects of prescribed fire and on the potential effects of the reintroduction of fire into Great Basin habitats There is evidence that grazing particularly in riparian habitats of the Great Basin may negatively affect breeding birds that are associated with these habitats including the Blackchinned and Broad tailed Hummingbird Dickson et al 2009 Dobkin et al 1998 A study of avian abundance in riparian and aspen woodlands in the Great Basin following livestock removal found an overall increase in bird abundance 10 12 years following removal although there was a nonsignificant decrease in hummingbird species abundance Earnst et al 2012 More study is also needed in this area Pacific Northwest Northern Rockies Habitats and Fire Regimes The Northern Pacific Rainforest region BCR 5 in the northwestern United States encompasses the western portions of Washington Oregon and northern California and is characterized by high precipitation and mild temperatures Along the Pacific Coast western hemlock Sitka spruce and balsam fir forests dominate the northern regions while Douglas fir and coast redwood dominate the southern regions NABCI 2012 Montane forests of western hemlock Tsuga heterophylla Douglas fir evergreen hardwood white fir grand fir Abies grandis and Pacific silver fir Abies amabilis dominate inland regions along with oak woodland Quercus spp oak savannah and shrublands Huff et al 2005 Historically wet coastal forests in the Pacific Northwest experienced infrequent highseverity fire with a fire return interval of over 100 years while drier inland and montane forests were characterized by a mixed severity fire regime with a fire return interval of 5 to 75 years Agee 1991 1993 1998 Huff et al 2005 In southwestern Oregon and northwestern California it is thought that the mixed conifer hardwood forests that characterize this region historically burned frequently supporting a variety of seral shrubs and fire adapted hardwoods Agee 1993 Due to the long historic fire return interval in wet coastal forests fire suppression is not currently of management concern In drier montane forests and lowland habitats however fire suppression is believed to have led to an accumulation of fuels increased incidences of high severity fires and conifer encroachment in oak woodland and savannah habitats Huff et al 2005 In southwestern Oregon and northwestern California fire suppression has altered forest structure in favor of conifers and at the expense of hardwood and mixed conifer hardwood forests Betts et al 2010 Population estimates for hummingbirds in BCR 5 are presented in table 7 34 USDA Forest Service RMRS GTR 408 2020

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Table 7 Western hummingbird percent global population and population estimates for BCR 5 Northern Pacific Rainforest Species Allen s Hummingbird Anna s Hummingbird Rufous Hummingbird Calliope Hummingbird Black chinned Hummingbird Total Global population 42 1 6 6 75 3 1 2 Population estimate 300 000 300 000 8 000 000 30 000 0 0 1 500 8 631 500 Source Partners in Flight Landbird Population Estimates Database http pif birdconservancy org PopEstimates Database aspx The Northern Rockies region BCR 10 includes the Rocky Mountains and outlying ranges of Montana Idaho and northwestern Wyoming This region is dominated by ponderosa pine Douglas fir and lodgepole pine forests at lower elevations with Engelmann spruce Picea engelmannii and subalpine fir forests at higher elevations The mesic north and west edges of the Rockies are dominated by western larch Larix occidentalis grand fir western red cedar Thuja plicata and western hemlock forests Northern Rockies forests historically experienced a range of fire frequencies and severities Schoennagel et al 2004 It is thought that lower elevation ponderosa pine forests historically experienced a frequent low to midseverity fire regime while mid to high elevation forests experienced less frequent higher severity fires Brown and Kapler Smith 2000 Veblen et al 2000 It is thought that fire suppression in northern Rockies forests has led to heavy accumulations of dead and living fuels uniform stands of late successional forests and an increased likelihood of uncharacteristically severe wildfires Barrett et al 1991 Population estimates for hummingbirds in BCR 10 are presented in table 8 Table 8 Western hummingbird percent global population and population estimates for BCR 10 Northern Rockies Global population 61 8 Species Calliope Hummingbird Black chinned Hummingbird 2 8 Broad tailed Hummingbird 1 2 Rufous Hummingbird 17 8 Total Population estimate 1 500 000 130 000 110 000 2 000 000 3 740 000 Source Partners in Flight Landbird Population Estimates Database http pif birdconservancy org PopEstimates Database aspx USDA Forest Service RMRS GTR 408 2020 35

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Wildfire and Hummingbirds Few studies have examined the effects of wildfire on birds in Pacific Northwest forests Huff et al 1985 studied postfire bird communities in montane forests of Olympic National Park Washington In this study bird species richness and diversity were highest 19 years after fire A higher percentage of species bred only in forests in the stand initiation stage from 1 to 19 years after fire and during this period there were higher abundances of ground and shrub associated species and lower abundances of canopy feeding species Fontaine et al 2009 found that in northwestern California and southwestern Oregon repeatedly burned habitats were characterized by shrub nesting and ground foraging species while unburned mature forests were characterized by conifer nesting and foliage gleaning species These results are similar to those from other forest types in the western United States Bock and Lynch 1970 Raphael et al 1987 Saab et al 2007 More recent studies have noted that fire severity plays an important role in individual species and community level responses following wildfire Stephens et al 2015 Betts et al 2010 noted that Rufous Hummingbirds were positively associated with early seral broadleaf forests in the Pacific Northwest These habitats which historically experienced frequent fire are in decline across the region likely due to combined effects of fire suppression and conifer intensive management practices Kennedy and Spies 2005 In Huff s 1985 study Rufous Hummingbird was one of the most abundant species 19 years after fire In the same paper however Huff 1985 described the results of a chronosequence study of seven forested plots in Olympic National Park ranging from 1 to 515 years postfire In this analysis Rufous Hummingbird was found to have a mixed response to fire Calder 1993 cites a study from Meslow and Wight 1975 which found that Rufous Hummingbirds nested in second growth forests from 16 to 120 years old as well as in mature forests greater than 120 years old These results suggest that Rufous Hummingbirds use primarily mid successional to mature forest habitats for nesting Little information is available on the response of the Calliope Hummingbird to fire in Pacific Northwest forests Marcot 1984 found that Calliope Hummingbirds were associated with Douglas fir forests in the shrub sapling stage of succession 14 years after fire in northwestern California This suggests that Calliope Hummingbirds may prefer shrubby habitats in early succession 8 to 15 years postfire for nesting Results from fire and avian ecology studies in the Sierra Nevada also indicate that Calliope Hummingbirds prefer shrubby early successional postfire habitats for nesting Burnett et al 2011 Raphael et al 1987 Studies of avian ecology and wildfire in the northern Rockies indicate that wildfire including high severity fire is beneficial for many birds and that a range of fire severities and frequencies across the landscape provide for a diversity of bird species Hutto 1995 Kotliar et al 2002 Saab and Powell 2005 Smucker et al 2005 Taylor and Barmore 1980 Smucker et al 2005 demonstrated that avian responses to fire can vary significantly with fire severity and that postfire bird communities after high severity fire were unique Hutto 1995 also found that bird communities after high severity fire were unique with seed eating timber drilling and insectivorous birds being most abundant While detections of hummingbirds in fire and avian ecology studies in the northern Rockies are low available data indicate that Calliope Hummingbirds increase in abundance in early successional postfire forests especially in forests that burned at moderate to high severities Hutto 1995 Smucker et al 2005 Smucker et al 2005 studied avian responses to 36 USDA Forest Service RMRS GTR 408 2020

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a 125 000 hectare wildfire in mixed conifer forests that burned at variety of severities across the Bitterroot National Forest in Montana in 2000 In this study nearly twice as many bird species increased as decreased in response to fire Rufous Hummingbirds declined slightly postfire at unburned points and were not detected at burned points before or after the fire Calliope Hummingbirds increased in abundance postfire at both previously burned and previously unburned points although the increase was greater at previously unburned points Slightly more Calliope Hummingbirds were detected at points that burned at moderate to high severities than at points that burned at low severity or did not burn Rufous Hummingbirds declined slightly postfire at unburned points and were not detected at burned points before or after the fire These results are similar to those of fire and avian ecology studies in the Pacific Northwest which indicate that Calliope Hummingbirds prefer early successional forests for nesting while Rufous Hummingbirds may decline after fire Marcot 1984 Meslow and Wight 1975 Caution is needed in interpreting these results however as detection rates were low In a study of bird community composition following a series of wildfires in northern Wyoming and western Montana Hutto 1995 detected Calliope Hummingbirds at six burned sites and Rufous Hummingbirds at four burned sites These detection rates are too low to draw meaningful conclusions however combining these data with bird survey data from throughout the northern Rockies Hutto 1995 found that Calliope Hummingbirds were most abundant 10 to 40 years postfire Saab et al 2005 cited a study from Harris 1982 indicating that Calliope Hummingbirds had a positive response to wildfire from 1 to 4 years after a 120 480 hectare fire in a mixed conifer forest in the northern Rockies Bird species including Calliope Hummingbird benefit from high severity fire even though the positive response may not be detected for 10 30 years Hutto and Patterson 2016 Overall results from fire and avian ecology studies in the northern Rockies indicate that Calliope Hummingbirds prefer early successional postfire habitats for nesting while Rufous Hummingbirds possibly decline or have variable responses to fire Restoration and Hummingbirds Several studies from Pacific Northwest forests indicate that Rufous Hummingbirds increase in abundance in managed stands immediately after logging and prescribed fire Bettinger 1996 studied bird communities in Douglas fir forests in western Oregon that had been managed through logging and prescribed fire Rufous Hummingbirds were significantly more abundant in managed open canopy stands although no habitat variables were significantly associated with their abundance Morrison and Meslow 1983 found similar results in a study of bird communities after logging and prescribed fire in western Oregon In this study Rufous Hummingbirds were one of the most abundant species on early clearcuts and their presence was associated with a low shrub herb layer and low deciduous tree cover Rufous Hummingbirds decreased in abundance with increasing stand age in this study Betts et al 2010 noted that Rufous Hummingbirds are positively associated with early seral mixed conifer hardwood forests in the Pacific Northwest These results conflict somewhat with those fire and avian ecology studies which indicate that Rufous Hummingbirds may decline after fire and that they may prefer forests from 16 to 20 years into secondary succession as well as mature forests for nesting Huff 1985 Meslow and Wight 1975 It is possible that Rufous Hummingbirds use early clearcuts and burned habitats for foraging while they nest primarily in mid successional to mature forested habitats with slightly more canopy cover in USDA Forest Service RMRS GTR 408 2020 37

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the Pacific Northwest Rufous Hummingbirds have been observed in large numbers in postfire habitats in the Sierra Nevada during migration Burnett et al 2011 indicating that these habitats are likely important to the species for foraging as well as during migration Therefore it is possible that both early to mid successional forests as well as mature forests are important for Rufous Hummingbirds The majority of studies of the effects of management practices on birds in the northern Rockies focus on silvicultural treatments and few have examined the effects of prescribed fire In a review of the effects of silvicultural treatments on birds in the Rocky Mountains Hejl et al 1995 compared bird abundances in unlogged forests with early successional forests after clearcutting In this synthesis Calliope Hummingbirds were always more abundant in partially logged forests than in unlogged forests Rufous Hummingbirds were associated with tall shrub clearcuts but the species was equally abundant in recent clearcuts and unlogged forests These results align with wildfire studies indicating that Calliope Hummingbirds consistently prefer open habitats while Rufous Hummingbirds are more variable in their habitat selection In this study Broad tailed Hummingbirds were most abundant in tall shrub clearcuts a result that aligns with those of fire restoration and avian ecology studies in the southern Rockies where they primarily breed Management Implications Rufous and Calliope Hummingbirds use early to mid successional forests for nesting and foraging in the Pacific Northwest Calder 1993 Calder and Calder 1994 In inland montane and mixed conifer hardwood forests of the Pacific Northwest fire suppression and other management practices have altered forest structure and reduced the amount of hardwoods and early successional habitat across the region Agee 1993 The loss of these habitats as well as increases in forest stand densities has likely had detrimental effects on both the Rufous and Calliope Hummingbird Huff et al 2005 Restoration efforts that increase the amount of early and mid successional forest habitats and encourage the regeneration of hardwoods are likely to benefit these species Early successional forest habitat availability following timber harvest may provide habitat for Rufous Hummingbirds but in a study of herbicide treatments in early seral forests Rufous hummingbirds were significantly sensitive to intensive management herbicide treatments Betts et al 2013 More research is needed to determine how timber management practices may alter important habitat characteristics in early seral forests for Rufous hummingbirds In inland montane forests the restoration of a mixed severity fire regime as was characteristic historically with a fire return interval of 5 to 75 years will likely benefit both Rufous and Calliope Hummingbird by increasing the amount of early successional habitats In habitats that were historically characterized by mixed conifer hardwood forest types the restoration of a mixed severity fire regime that incorporates high severity fires will likely benefit Rufous Hummingbirds and other birds that use these forest types Fontaine et al 2009 Swetnam et al 1999 Prescribed fire can be used as a management strategy to increase the amount of early to mid successional habitat and to encourage the regeneration of hardwoods and will be beneficial for hummingbirds through encouraging the regeneration of flowering plants Both Rufous and Calliope Hummingbird use open shrubby habitats created through fire and logging therefore both of these species should be able to tolerate some forest harvest in the context of larger restoration objectives Because these species use open habitats for 38 USDA Forest Service RMRS GTR 408 2020

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foraging management that promotes the restoration and maintenance of natural forest openings like meadows across the landscape will be beneficial Hagar and Stern 2001 Huff et al 2005 Wildfire and avian ecology studies indicate that fire at a variety of frequencies scales and severities is critical to maintaining avian diversity and abundance as well as vegetative diversity in northern Rockies forests Agee 1993 Hutto 1995 Hutto et al 2008 Kotliar et al 2002 In this region burned habitats including those that burned at high severities support a high diversity of bird species and unique bird communities Saab et al 2005 Many flowering plants in the northern Rockies including heartleaf arnica Arnica cordifolia broadleaf arnica Arnica latifolia showy aster Eurybia conspicua and fireweed Chamaenerion spp are adapted to resprout after fire Frye 1934 Moss 1936 In the northern Rockies Calliope Hummingbirds demonstrate a clear preference for the open shrubby habitats characteristic of early postfire habitats Rufous Hummingbirds demonstrate a mixed response to fire Management that aims to restore historic fire regimes and promote the development of a mosaic of successional stages across the landscape will likely benefit both Calliope and Rufous Hummingbird These goals can be achieved through the reintroduction of frequent low to mixed severity fire at lower elevations and infrequent stand replacing fire at higher elevations Hejl et al 1995 Hutto 1995 Saab et al 2005 Smucker et al 2005 Based on limited information both species appear to be tolerant of some forest harvest in the context of these management objectives The effects of prescribed fire on hummingbirds in northern Rockies habitats are unknown but are likely to be comparable to the effects of wildfire Southern Rockies Colorado Plateau Habitats and Fire Regimes The Southern Rockies Colorado Plateau region BCR 16 extends through southern Wyoming central and western Colorado eastern Utah and northern Arizona and New M xico It includes the Wasatch and Uinta mountains to the west and the southern Rocky Mountains to the east separated by the tableland of the Colorado Plateau NABCI 2012 Engelmann spruce subalpine fire and lodgepole pine forests dominate the higher elevations while pinyon juniper woodlands are found at lower elevations Ponderosa pine forests dominate higher elevations of the Colorado Plateau above 6 000 ft as well as much of northern Arizona New M xico eastern Utah and western Colorado It is thought that mid to high elevation mixed conifer forests of the southern Rockies historically experienced infrequent high severity fires while ponderosa pine forests of the Colorado Plateau Arizona and New M xico historically experienced frequent low to mid severity fires Brown and Kapler Smith 2000 Fischer and Bradley 1987 Shinneman and Baker 1997 Fire suppression is thought to have altered forest composition in the southern Rockies While historically ponderosa pine forests in this region were open and parklike with a low accumulation of fuels many of these forests are now crowded with large accumulations of fuel Brown and Davis 1973 Fire suppression at higher elevations may have also led to accumulations of fuel and to even aged decadent forest stands at risk for uncharacteristically severe fire Barrett et al 1991 Population estimates for hummingbirds in BCR 16 are presented in table 9 USDA Forest Service RMRS GTR 408 2020 39

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Table 9 Western hummingbird percent global population and population estimates for BCR 16 Southern Rockies Colorado Plateau Species Black chinned Hummingbird Broad tailed Hummingbird Anna s Hummingbird Total Global Population population estimate 17 7 48 4 0 9 800 000 4 700 000 30 000 5 530 000 Source Partners in Flight Landbird Population Estimates Database http pif birdconservancy org PopEstimates Database aspx Wildfire and Hummingbirds Studies of avian ecology and wildfire in the southern Rockies indicate that many avian species do not change in abundance after low to moderate severity fire but that highseverity fire may affect bird abundance and community composition For example Kotliar et al 2007 found that after wildfire in a mixed conifer forest in New M xico pre and postfire bird communities were similar except in areas of high severity fire and species richness was similar pre and postfire across all fire severities Four species demonstrated significant effects of fire severity and their densities were all higher in burned compared to unburned forests A comparison study of bird responses to fire severity in Arizona with historical low severity fire regime and Idaho with historical mixed severity fire regime found that more species responded negatively to wildfire in Arizona and positively to wildfire in Idaho The study highlighted the importance of considering individual species life history and regional differences in historical fire regimes when predicting bird responses to mixed severity fires Latif et al 2016 Broad tailed Hummingbirds demonstrate a positive response to moderate and highseverity fire in the southern Rockies In Kotliar et al s 2007 study Broad tailed Hummingbird densities were slightly lower postfire except at the high severity burn level where their densities were higher postfire Broad tailed Hummingbirds mean densities were highest on high severity plots both one and two years after fire The authors attributed these high densities to an increase in flowering plants in areas that burned at high severities Kotliar et al 2007 In a review of avian responses to fire in the southwestern United States Bock and Block 2005 indicated that Broad tailed Hummingbirds showed a positive response 3 years after moderate severity wildfire in a ponderosa pine forest in Arizona Restoration and Hummingbirds Studies indicate that many birds are tolerant of low to moderate severity prescribed fire as well as thinning practices in ponderosa pine forests of the southern Rockies In a study of avian responses to prescribed fire in ponderosa pine forests of Arizona and New M xico Dickson et al 2009 found most breeding birds to be tolerant of low to moderate severity fire Bagne and Finch 2005 studied avian responses to thinning in ponderosa pine forests in 40 USDA Forest Service RMRS GTR 408 2020

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New M xico The study found that avian responses generally only lasted 1 or 2 years and that many species had no response to the treatments In a study of bird responses to thinning treatments in ponderosa pine forests in Arizona occupancy for several songbird species and species richness was generally higher in sites with larger trees and higher snag density and lower in sites with greater canopy cover Kalies and Rosenstock 2013 Several studies indicate that the Broad tailed Hummingbird responds positively to logging thinning or other treatments that create open habitats in the southern Rockies Blake 1982 studied bird communities on burned and unburned plots in ponderosa pine forests in northern Arizona in 1973 and 1974 Logging had occurred on two burned and two unburned plots In this study 14 species had positive responses to thinning five had negative responses seven had no responses and one had a mixed response Broad tailed Hummingbirds were most abundant on sites that were burned and clearcut and were not detected on unburned uncut sites In a synthesis of studies comparing bird abundances in unlogged forests with early successional forests after clearcutting in the Rocky Mountains Hejl et al 1995 found that Broad tailed Hummingbirds were generally more abundant in clearcuts than in unlogged areas Szaro and Balda 1982 1986 found that in southwestern ponderosa pine forests Broad tailed Hummingbirds preferred moderately to heavily disturbed areas and that the species reached its highest population densities on treated plots Management Implications Studies of avian responses to fire and restoration in the southern Rockies indicate Broadtailed Hummingbirds increase in abundance after high severity fire These increases are likely due to the profusion of flowering plants in these postfire habitats Kotliar et al 2007 Broadtailed Hummingbirds are also thought to prefer nesting in open and shrubby habitats that are prevalent after fire Calder 1992 Hejl 1994 suggested that declines in the Broad tailed Hummingbird may be due to decreases in the prevalence of burned forests Therefore Broadtailed Hummingbirds are likely to benefit from treatments that increase the amount of early successional postfire habitats in the southern Rockies including areas that burned at high severities Block and Finch 1997 Broad tailed Hummingbirds are also likely compatible with some degree of timber harvest and or thinning in the southern Rockies Blake 1982 Hejl et al 1995 The application of low to moderate severity prescribed fire in ponderosa pine forests of the southern Rockies is likely to benefit Broad tailed Hummingbirds through increasing the amount of early successional habitat and flowering plants Due to a long history of fire suppression in these habitats it is thought that prescribed fire efforts will have to be scaled up significantly in order to restore southwestern ponderosa pine forests to historic conditions Finch et al 2007 However it will be important to ensure that fire both wild and prescribed remain within the range of historical variation both in frequency and intensity In a study of understory plant responses to restoration treatments including no treatment thinning thinning and prescribed fire prescribed fire and wildfire of varying intensity in northern Arizona ponderosa pine forests Griffis et al 2001 found that exotic plants increased in richness and abundance with treatment intensity while the abundance of native shrub species decreased with treatment intensity especially after wildfire To prevent the spread of exotic shrubs techniques like prefire forest thinning may be required to reintroduce fire to areas where it has been excluded for long periods of time Covington et al 1997 USDA Forest Service RMRS GTR 408 2020 41

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In mixed conifer forests of the southern Rockies the restoration of a mixed severity fire regime with areas of high severity fire will create landscape scale heterogeneity as well as provide habitat for species dependent on heavily disturbed habitats including the Broad tailed Hummingbird Restoring high severity fire to mixed conifer forests of the southern Rockies may help to reverse declines in Broad tailed Hummingbird and other species dependent on these habitats Brawn and Balda 1988 Hejl 1994 Conclusion Disturbance is a major driver of biological and structural diversity at habitat stand and landscape scales Brawn et al 2001 Fire is a natural disturbance that has shaped the ecosystems of western North America for millennia Policies of fire suppression throughout much of the 20th century are thought to have led to increased fuel loads and shifts in forest stand composition leading to more frequent large scale and higher severity wildfires that are damaging to human communities as well as forest health and wildlife populations Schoennagel et al 2004 The combined effects of fire suppression and the introduction of exotic grasses in arid habitats of the western United States are thought to be altering habitat structure and increasing fire frequencies in these habitats Trends toward a warmer drier climate are also thought to be influencing the pattern and scale of wildfires with a trend toward more frequent and severe fires Trouet et al 2010 These changes have caused concern among land managers charged with maintaining forest and ecosystem health as well as among scientists landowners and the public As land managers design implement and scale up restoration projects that aim to improve forest and aridland health and increase the resilience of western ecosystems to a changing climate it is important to understand the impacts of fire and fire adapted ecosystem restoration on wildlife populations The literature presented in this review suggests that while hummingbirds face a variety of potential challenges on their breeding grounds in the western United States their persistence is compatible with many fire adapted ecosystem restoration efforts Hummingbirds evolved in the context of wildfire and are adapted to feeding on nectar from flowering plants which flourish in open disturbed areas especially after fire Brown and Kapler Smith 2000 hummingbirds can quickly take advantage of new food resources from disturbances following fire Many flowering plants are adapted to resprout or germinate after fire In southwestern desert scrub and riparian habitats the control of exotic plants is a critical management issue and is likely to pose a continued challenge under climate warming scenarios Smith et al 2000 The invasion of buffelgrass and the subsequent conversion of southwestern desert scrub habitats to homogenous grassland has potentially serious implications for hummingbirds that nest in desert scrub including the Costa s and Black chinned Hummingbird as well as for hummingbirds that use these habitats during migration In southwestern riparian habitats the spread of tamarisk and the subsequent increased risk of catastrophic fire pose a serious threat to breeding birds that use these habitats including the Black chinned Hummingbird While prescribed fire is not advised in desert scrub it may have a role in riparian restoration in the Southwest when used in careful combination with mechanical treatment herbicide application and the replanting of native species In desert scrub 42 USDA Forest Service RMRS GTR 408 2020

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manual and mechanical treatments to remove buffelgrass along with herbicide application should continue on an experimental scale with monitoring to ensure the successful reduction or eradication of exotics In California coastal scrub and chaparral habitats the Costa s Hummingbird is thought to use postfire habitats although data are limited and Anna s Hummingbirds appear to decline immediately after fire Unfortunately virtually nothing is known about Allen s Hummingbirds response to fire or restoration but their restricted range and specific habitat requirements indicate that this species is highly sensitive to habitat fragmentation Costa s Hummingbirds are also thought to be highly sensitive to habitat fragmentation therefore the preservation of existing large undisturbed stands of coastal scrub and chaparral is likely of critical importance to both the Allen s and Costa s Hummingbirds both species of conservation concern Management efforts in intact coastal scrub and chaparral stands should focus as much as possible on allowing natural fires to burn and on restoring a diversity of successional stages to maximize bird abundance and diversity CalPIF 2004 Westman 1987 In habitats that are fragmented or degraded management efforts should focus on the removal of exotics and on the development of intact corridors between habitats as well as buffers between habitat patches and developed areas Eliason and Allen 1997 Allen et al 2000 In forested ecosystems of the western United States several hummingbird species including Rufous Calliope and Broad tailed Hummingbird show a clear preference for the open disturbed early successional habitats created through fire Wethington and Finley 2009 Broad tailed Hummingbirds abundance has been positively correlated to areas of high severity fire and Calliope Hummingbirds are consistently more abundant in habitats that have been disturbed through fire Bock and Block 2005 Kotliar 2007 Smucker et al 2005 Rufous Hummingbirds are also known to use postfire and clearcut habitats although they may prefer mature forests for nesting Huff 1985 Meslow and Wight 1975 Morrison and Meslow 1983 Studies of avian ecology and fire indicate that wildfire benefits aerial foraging and insectivorous birds which share similar foraging strategies to hummingbirds Bagne and Purcell 2011 Hutto 1995 Therefore restoration efforts that aim to increase the amount of early and mid seral habitat in forested ecosystems in the western United States are likely to benefit hummingbirds as well as other birds that use these habitats Whenever possible prescribed fire alone or in combination with thinning or mechanical treatments is preferred to logging or thinning alone in forested habitats Prescribed fire stimulates germination and growth in flowering plants and creates spatial heterogeneity Imbeau et al 1999 As land managers move forward with planned restoration projects there are many opportunities to continue to broaden our understanding of hummingbirds habitat selection movements and responses to fire and fire adapted ecosystem restoration efforts While more research is needed and warranted the existing fire and avian ecology literature provides a strong conceptual framework from which to move forward with needed restoration efforts despite uncertainty Land managers should strive to integrate bird monitoring into restoration projects in the early planning stages with a Before After Control Impact approach As fire and avian ecology research methodologies and hummingbird monitoring techniques continue to improve so will our ability to draw inferences about the factors limiting hummingbird populations and the potential effects of planned restoration efforts Close cooperation between land managers and the scientific community will be key to developing and prioritizing management actions that will benefit western hummingbirds throughout their migratory ranges USDA Forest Service RMRS GTR 408 2020 43

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Research Inventory and Monitoring Priorities There is a need for Before After Control Impact approach studies to understand the impact of fire on hummingbird populations Long term monitoring of hummingbird population trends are available through North American Breeding Bird Surveys Rosenberg et al 2017 Trends in occurrence and inventory of some North American species can be acquired through Christmas Bird Counts National Audubon Society 2010 or eBird https ebird org Still there are limits to those methodologies for studying hummingbirds due to the timing of the migration polygynous mating system and other unique life history traits The following research inventory and monitoring priorities were identified through this review Many align with those set forth in the Western Hummingbird Partnership Action Plan Contreras Mart nez 2015 Contreras Mart nez et al 2017 Wethington et al 2010 Bird monitoring should be incorporated into land management and restoration efforts before during and after the treatments to assure that the ecological objectives of restoration are being met Improve Hummingbird Monitoring and Data Sharing Techniques There is a critical need to improve and expand upon existing hummingbird population monitoring techniques as well as to encourage and facilitate the sharing of data among cooperators Improvement in monitoring techniques are needed to determine hummingbird responses to fire effects and postfire restoration The following steps are recommended 1 Expand hummingbird banding locations to replicate sites and sample a broader range of ecotypes The expansion of hummingbird banding efforts is valuable for understanding hummingbird demographics population trends migration routes and timing However there is a need to establish banding locations that have replicated sites that are representative of a spectrum of habitats within ecozones and conditions e g exposed vs not exposed to fire fragmented vs unfragmented forested vs meadow a spectrum of successional habitat and altitudinal variation migration versus breeding locations Training and support should be provided for existing and new hummingbird banding efforts and existing bird banding stations should be provided with the training and resources necessary to accurately identify age and band hummingbirds 2 Explore new monitoring methods for hummingbirds When typical breeding bird survey techniques are applied hummingbirds are challenging to monitor compared to passerines for which many survey methods have been developed Field identification requires specialized training due to the unique vocalizations timing of breeding and polygynous mating systems of hummingbirds Existing monitoring techniques should be refined or improved or new monitoring strategies should be developed to improve hummingbird monitoring data collection particularly adjusting the timing of surveys to identify migration phenology and breeding densities 3 Streamline hummingbird monitoring data collection and reporting techniques among cooperators 44 USDA Forest Service RMRS GTR 408 2020

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4 Encourage the sharing of hummingbird data among cooperators through the use of data sharing portals e g the Avian Knowledge Network Address Information Gaps Regarding Hummingbird Biology and Life History Basic information gaps remain in our understanding of hummingbird movements populations and habitat selection The following are key areas requiring study 1 Abundance and distribution at landscape and regional scales 2 Habitat selection and specific habitat requirements 3 Migration and seasonal movement patterns 4 Site fidelity and adult dispersal 5 Reproductive strategies Understand Hummingbird Demographics and Factors Limiting Populations There are many gaps in our understanding of the factors limiting hummingbird populations including 1 Population trends 2 Estimates of population size 3 Where populations are limited 4 Reproductive success including factors related to nesting success 5 Estimates of adult and juvenile survivorship 6 Source sink dynamics dispersal and recruitment Synthesize Predicted Climate Change Impacts on Phenology of Key Plant Species for Hummingbirds There is a critical need to understand the potential impacts of climate change on the phenology of flowering plants especially those plants that are key nectar sources for hummingbirds Variations in precipitation snowpack timing of snowmelt and drought cycles are likely to seriously impact flowering plant phenology and in turn hummingbirds As a starting point we recommend the development of a matrix of key flowering plants for western hummingbirds on their breeding migration and wintering grounds accompanied by a synthesis of known or anticipated climate change impacts on these plants Study the Effects of Changing Fire Frequencies and Severities on Hummingbirds Food Sources Fire suppression and climate change are likely leading to alterations in historic fire regimes and forest stand structures leading to fire frequencies and intensities that are outside of the range of historic variation There is a need to understand how these changes are affecting hummingbird food sources For example Keeley and Zedler 1978 suggested that shorter fire frequencies may over time favor resprouting plant species over reseeding species Carpenter and Recher 1979 noted that resprouting species generally produce fewer and smaller flowers that produce less nectar and are less fragrant than reseeding species which allocate more USDA Forest Service RMRS GTR 408 2020 45

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resources to flower production and pollination Fulton and Carpenter 1979 Resprouting species also tend to grow more slowly and reach smaller sizes during the first 10 to 20 years after fire Carpenter and Recher 1979 Furthermore very intense fires may kill the regenerative structures of resprouting plants even those that are adapted to fire How hummingbirds will be affected by these potential changes is unknown Assess the Long Term Impacts of Restoration on Hummingbird Populations Most of the studies in this review assess the short term 1 to 5 years impacts of fire and restoration In general avian responses to fire are complex due to variation in ecological conditions fire severity and time since fire making species and context specific studies important for assessing management and restoration impacts Hutto et al 2015 It is recommended that restoration efforts when possible incorporate monitoring prior to fire events and thereafter for 5 to 10 years to control for variation in hummingbird movements and site selection from year to year and to assess the medium to long term impacts of restoration Assess Seasonal Timing of Prescribed Fire in Relation to Hummingbirds It is generally recommended that managers avoid burning during the nesting season for migratory birds For hummingbirds in North America this period can extend from February through July Therefore to minimize impacts to nesting hummingbirds fall burning is recommended although prescribed burning in the spring may help promote the growth of flowering plants which could possibly benefit hummingbirds Allen et al 2000 Huff et al 2005 Thies et al 2005 More study is needed in this area Study the Effects of Herbicide Application on Hummingbirds in Southwestern Desert Scrub and Riparian Habitats Herbicide application to control exotics in southwestern desert scrub and riparian habitats has found some success experimentally but the short or long term effects of herbicide application on hummingbirds as well as other birds is unknown 46 USDA Forest Service RMRS GTR 408 2020

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References Agee J K 1991 Fire history along an elevational gradient in the Siskiyou Mountains Oregon Northwest Science 65 188 199 Agee J K 1993 Fire ecology of Pacific Northwest forests Washington DC Island Press 511 p Agee J K 1998 The landscape ecology of western forest fire regimes Northwest Science 72 24 34 Allen E B Eliason S A Marquez V J et al 2000 What are the limits to restoration of coastal sage scrub in Southern California In Keeley J E Baer Keeley M Fotheringharn C J eds 2nd Interface between ecology and land development in California Open File Report 00 62 Sacramento CA U S Geological Survey Western Ecological Research Center 253 262 Altman B 2005 Conservation priorities for landbirds of the Pacific Coast of Oregon and Washington In Ralph C J Rich T D eds Bird conservation implementation and integration in the Americas proceedings of the third international Partners in Flight conference 2002 March 20 24 Asilomar CA Volume 1 Gen Tech Rep PSW GTR 191 Albany CA U S Dept of Agriculture Forest Service Pacific Southwest Research Station 143 148 Arizmendi M C 2001 Multiple ecological interactions Nectar robbers and hummingbirds in a highland forest in M xico Canada Journal of Zoology 79 997 1 006 Armstrong D P 1987 Economics of breeding territoriality in male Calliope Hummingbirds The Auk 104 242 253 Bagne K E Finch D M 2005 Small scale response in an avian community to a large scale thinning project in the southwestern United States In Rich T D Arizmendi C Demarest D D et al eds Proceedings of the fourth international Partners in Flight conference tundra to tropics McAllen TX Partners in Flight 669 678 Bagne K E Purcell K L 2011 Short term responses of birds to prescribed fire in firesuppressed forests of California The Journal of Wildlife Management 75 1 051 1 060 Balda R P 1969 Foliage use by birds of the oak juniper woodland and ponderosa pine forest in southeastern Arizona The Condor 71 399 412 Balda R P Masters N L 1980 Avian communities in the pinyon juniper woodlands a descriptive analysis Workshop proceedings Managing western forests and grasslands for nongame birds Gen Tech Rep INT 86 Ogden UT U S Department of Agriculture Forest Service Intermountain Forest and Range Experiment Station and Rocky Mountain Forest and Range Experiment Station 146 167 Baltosser W H 1983 Nesting ecology of sympatric hummingbirds in Guadalupe Canyon Las Cruces NM New M xico State University PhD dissertation 103 p Baltosser W H 1986 Nesting success and productivity of hummingbirds in southwestern New M xico and southeastern Arizona Wilson Bulletin 98 353 357 USDA Forest Service RMRS GTR 408 2020 47

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Baltosser W H 1989 Nectar availability and habitat selection by hummingbirds in Guadalupe Canyon Wilson Bulletin 101 559 578 Baltosser W H Russell S M 2000 Black chinned hummingbird Archilochus alexandri Poole A Gill F eds The Birds of North America Online http bna birds cornell edu bna species 495 articles introduction Accessed 2010 December 9 Baltosser W H Scott P E 1996 Costa s hummingbird Calypte costae Poole A Gill F eds The Birds of North America Online http bna birds cornell edu bna species 251 articles introduction Accessed 2010 December 9 Banks R C Johnson N K 1961 A review of North American hybrid hummingbirds The Condor 63 3 28 Barbour M G Major J eds 1988 Terrestrial vegetation of California Special Publication No 9 Sacramento CA California Native Plant Society 1 020 p Barrett S W Arno S F Key C H 1991 Fire regimes of western larch lodgepole pine forests in Glacier National Park Canadian Journal of Forest Research 21 1711 1720 Bateman H L Chung MacCoubrey A Finch D M et al 2008 Impacts of non native plant removal on vertebrates along the middle Rio Grande New M xico Ecological Restoration 26 193 195 Battey C J 2019 Ecological release of the Anna s hummingbird during a northern range expansion The American Naturalist 194 3 Bent A C 1940 Life histories of North American cuckoos goatsuckers hummingbirds and their allies U S Nat Mus Bull 176 Berlanga H Kennedy J A Rich T D et al 2010 Saving our shared birds Partners in Flight tri national vision for landbird conservation Ithaca NY Cornell Lab of Ornithology 49 p Bettinger K A 1996 Bird communities in 5 to 34 year old managed Douglas fir stands on the Willamette National Forest Oregon Cascades Corvallis OR Oregon State University Thesis 109 p Betts M G Hagar J C Rivers J W et al 2010 Thresholds in forest bird occurrence as a function of the amount of early seral broadleaf forest at landscape scales Ecological Applications 20 2116 2130 Betts M G Verschuyl J Giovanini J et al 2013 Initial experimental effects of intensive forest management on avian abundance Forest Ecology and Management 310 1036 1044 Blake J G 1982 Influence of fire and logging on nonbreeding bird communities of ponderosa pine forests The Journal of Wildlife Management 46 404 415 Blancher P J Rosenberg K V Panjabi A O et al 2007 Guide to the Partners in Flight 48 USDA Forest Service RMRS GTR 408 2020

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population estimates database Version North American landbird conservation plan 2004 Partners in Flight Technical Series No 5 26 p http rmbo org pif_db laped download Guide 20to 20PIF 20Population 20Estimates 20Database 202 pdf Block W M Finch D M 1997 Songbird ecology in southwestern ponderosa pine forests A literature review Gen Tech Rep RM 292 Fort Collins CO U S Department of Agriculture Forest Service Rocky Mountain Research Station 152 p Bock C E Block W M 2005 Response of birds to fire in the American southwest In Ralph C J Rich T D eds Bird conservation implementation and integration in the Americas Proceedings of the third international Partners in Flight conference 2002 March 20 24 Asilomar CA Volume 2 Gen Tech Rep PSW GTR 191 Albany CA U S Department of Agriculture Forest Service Pacific Southwest Research Station 1 093 1 099 Bock C E Bock J H 1978 Response of birds small mammals and vegetation to burning sacaton grasslands in southeastern Arizona Journal of Range Management 31 296 300 Bock C E Bock J H 1988 Effects of fire on wildlife in Southwestern lowland habitats In Effects of fire management of southwestern natural resources Proceedings of the symposium 1988 November 15 17 Tucson AZ Gen Tech Rep RM 191 Fort Collins CO U S Department of Agriculture Forest Service Rocky Mountain Forest and Range Experiment Station 50 64 Bock C E Bock J H 1992 Response of birds to wildfire in native versus exotic Arizona grassland The Southwestern Naturalist 37 73 81 Bock C E Lynch J F 1970 Breeding bird populations of burned and unburned conifer forest in the Sierra Nevada The Condor 72 182 189 Bolger D T Scott T A Rotenberry J T 1997 Breeding bird abundance in an urbanizing landscape in coastal southern California Conservation Biology 11 406 421 Bombaci S P Gallo T Pejchar L 2017 Small scale woodland reduction practices have neutral or negative short term effects on birds and small mammals Rangeland Ecology and Management 70 363 373 Bovey R W Hein H Meyer R E 1984 Effect of herbicides on the production of common buffelgrass Cenchrus ciliaris Weed Science 32 8 12 Brand L A Dixon M D Fetz T et al 2013 Projecting avian responses to landscape management along the Middle Rio Grande New M xico The Southwestern Naturalist 58 150 162 Brawn J D Balda R P 1988 Population biology of cavity nesters in northern Arizona Do nest sites limit breeding densities The Condor 90 61 71 Brooks M L Pyke C R 2001 Invasive plants and fire in the deserts of North America In Galley K E M Wilson T P eds Proceedings of the invasive species workshop The role of fire in the control and spread of invasive species Miscellaneous Publications No 11 Tallahassee FL Tall Timbers Research Station 1 14 USDA Forest Service RMRS GTR 408 2020 49

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Brown A A Davis K P 1973 Forest fire Control and use Second edition New York NY McGraw Hill Brown B T 1992 Nesting chronology density and habitat use of Black chinned Hummingbirds along the Colorado River Arizona Journal of Field Ornithology 63 393 400 Brown J H Bowers M A 1985 Community organization in hummingbirds relationships between morphology and ecology The Auk 102 251 269 Brown J H Kodric Brown A 1979 Convergence competition and mimicry in a temperate community of hummingbird pollinated flowers Ecology 60 1 022 1 035 Brown J K DeByle N V 1989 Effects of prescribed fire on biomass and plant succession in western aspen Res Pap INT 412 Ogden UT U S Department of Agriculture Forest Service Intermountain Research Station 16 p Brown J K Kapler Smith J eds 2000 Wildland fire in ecosystems Effects of fire on flora Gen Tech Rep RMRS GTR 42 vol 2 Ogden UT U S Department of Agriculture Forest Service Intermountain Research Station 257 p Brown J H Kodric Brown A 1979 Convergence competition and mimicry in a temperate community of hummingbird pollinated flowers Ecology 60 1 022 1 035 Burnett R D Seavy N Taillie P 2011 Plumas Lassen administrative study 2010 post fire avian monitoring report PRBO Conservation Science 45 p B rquez A A Martinez Y Martin P S 1992 From the High Sierra Madre to the coast changes in vegetation along Highway 16 In Clark K F Quintana J R Schmidt R H eds Geology and mineral resources of the northern Sierra Madre Occidental M xico Guidebook for the 1992 field conference El Paso Geological Society 1992 September 18 21 El Paso TX El Paso Geological Survey 239 252 Busch D E 1995 Effects of fire on southwestern riparian plant community structure The Southwestern Naturalist 40 259 267 Calder W A 1973 Microhabitat selection during nesting of hummingbirds in the Rocky Mountains Ecology 54 127 134 Calder W A 1993 Rufous hummingbird Selasphorus rufus Poole A Gill F eds The Birds of North America Online http bna birds cornell edu bna species 053 articles introduction Accessed 2010 December 9 Calder W A Calder L L 1992 Broad tailed hummingbird Selasphorus platycercus Poole A Stettenheim P Gill F eds The Birds of North America Online http bna birds cornell edu bna species 016 articles introduction Accessed 2010 December 9 Calder W A Calder L L 1994 Calliope hummingbird Stellula calliope Poole A Gill F eds The Birds of North America Online http bna birds cornell edu bna species 135 articles introduction Accessed 2011 Oct 31 Callaway R M Davis F W 1993 Vegetation dynamics fire and the physical environment in coastal central California Ecology 74 1 567 1 578 50 USDA Forest Service RMRS GTR 408 2020

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CalPIF California Partners in Flight 2009 The desert bird conservation plan A strategy for protecting and managing desert habitats and associated birds in California California Partners in Flight http www prbo org calpif plans html CalPIF California Partners in Flight Lovio J 2004 The coastal scrub and chaparral bird conservation plan A strategy for protecting and managing coastal scrub and chaparral habitats and associated birds in California Stinson Beach CA PRBO Conservation Science Camfield A F Calder W A Calder L L 2013 Broad tailed Hummingbird Selasphorus platycercus version 2 0 In Pool A F ed The birds of North America Ithaca NY Lab of Ornithology https doi org 10 2173 bna 16 Carothers S W Johnson R R Aitchison S W 1974 Population structure and social organization of southwestern riparian birds American Zoologist 14 97 108 Carpenter F L Recher H F 1979 Pollination reproduction and fire The American Naturalist 113 871 879 Cartron J E Stoleson S H Johnson R R 1999 Riparian dependence biogeographic status and likelihood of endangerment in landbirds of the Southwest In Finch D M Whitney J C Kelly J F et al eds Rio Grande ecosystems Linking land water and people toward a sustainable future for the Middle Rio Grande Basin 1998 June 2 5 Albuquerque NM Proc RMRS P 7 Ogden UT U S Department of Agriculture Forest Service Rocky Mountain Research Station 211 215 Chase M K Kristan W B Lynam A J et al 2000 Single species as indicators of species richness and composition in California coastal sage scrub birds and small mammals Conservation Biology 14 474 487 Clark C J 2017 eBird records show substantial growth of the Allen s Hummingbird Selasphorus sasin sedentarius population in urban Southern California The Condor 119 122 130 Cody M L 1968 Interspecific territoriality among hummingbird species The Condor 70 270 271 Cogswell H L 1962 Territory size in three species of chaparral birds in relation to vegetation density and structure Berkeley CA University of California 567 p Contreras Mart nez S 2015 Din mica espacio temporal de colibr es Trochilidae en bosques de pino encino post incendio en la Reserva de la Biosfera Sierra de Manantl n Jalisco M xico Doctoral Thesis Ciencias en Biosistem tica Ecolog a y Manejo de Recursos Naturales y Agr colas Departamento de Ecolog a y Recursos Naturales Universidad de Guadalajara CUCSUR M xico Contreras Mart nez S Pacheco Contretras C Hijar Tejeda C et al 2017 Grandes Guerreros Colibr es y Fuego Scientific documentary MUNIC CONACyT Filmoteca de la UNAM USDA Forest Service RMRS GTR 408 2020 51

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Contreras Mart nez S Santana E 1995 The effect of forest fires on migratory birds in the Sierra de Manantl n Jalisco M xico In Conservation of neotropical migratory birds in M xico Miscellaneous Publication 727 Orono ME Maine Agricultural and Forest Experiment Station 113 122 Contreras Mart nez S Santana Castell n S E Schondube J 2009 Dynamics of overwintering populations of hummingbirds in M xico A summary and current research from Jalisco In The 79th meeting of the Cooper Ornithological Society Part of the Hummingbird Conservation Symposium S01 and Western Hummingbird Project Workshop April 16 19 2009 Tucson AZ http www birdmeetings org COS2009 viewabstract2 asp AbstractID 5242 Covington W W Fule P Z Moore M M et al 1997 Restoring ecosystem health in ponderosa pine forests of the southwest Journal of Forestry 95 23 29 Crooks K R Suarez A V Bolger D T 2004 Avian assemblages along a gradient of urbanization in a highly fragmented landscape Biological Conservation 115 451 462 Croonquist M J Brooks R P 1991 Use of avian and mammalian guilds as indicators of cumulative impacts in riparian wetland areas Environmental Management 15 701 714 D Antonio C M Vitousek P M 1992 Biological invasions by exotic grasses the grass fire cycle and global change Annual Review of Ecology and Systematics 23 63 87 Davidson P J A Cannings R J Couturier A R Lepage D Di Corrado C M eds 2015 The Atlas of the Breeding Birds of British Columbia 2008 2012 Bird Studies Canada Delta B C http www birdatlas bc ca e Accessed 2019 August 11 Dickson B G Fleishman E Dobkin D S et al 2009 Relationship between avifaunal occupancy and riparian vegetation in the central Great Basin Nevada USA Restoration Ecology 17 722 730 Dickson B G Noon B R Flather C H et al 2009 Quantifying the multi scale response of avifauna to prescribed fire experiments in the southwest United States Ecological Applications 19 608 621 Dobkin D S Rich A C Pyle W H 1998 Habitat and avifaunal recovery from livestock grazing in a riparian meadow system of the northwestern Great Basin Conservation Biology 12 209 221 Earnst S L Dobkin D S Ballard J A 2012 Changes in avian and plant communities of aspen woodlands over 12 years after livestock removal in the northwestern Great Basin Bird abundance after cattle removal Conservation Biology 26 862 872 Eliason S A Allen E B 1997 Exotic grass competition in suppressing native shrubland reestablishment Restoration Ecology 5 245 255 Ellis L M 2001 Short term response of woody plants to fire in a Rio Grande riparian forest central New M xico USA Biological Conservation 97 159 170 52 USDA Forest Service RMRS GTR 408 2020

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Elphick C Dunning J B Sibley D A eds 2001 The Sibley guide to bird life and behavior 1st edition New York Alfred A Knopf 608 p Esque T C Schwalbe C R 2002 Alien annual grasses and their relationship to fire and biotic change in Sonoran Desert scrub In Tellman B ed Invasive exotic species in the Sonoran region Tucson AZ University of Arizona Press and the Arizona Sonora Desert Museum 194 Esque T C Webb R H Wallace C S A et al 2013 Desert fires fueled by native annual forbs Effects of fire on communities of plants and birds in the lower Sonoran Desert of Arizona The Southwestern Naturalist 58 223 233 Feinsinger P 1978 Ecological interactions between plants and hummingbirds in a successional tropical community Ecological Monographs 48 269 287 Finch D M 1989 Habitat use and habitat overlap of riparian birds in three elevational zones Ecology 70 866 880 Finch D M 2008 Pentimento Fuels reduction and restoration in the bosque of the Middle Rio Grande Fire Science Brief 7 1 6 Boise ID Joint Fire Science Program https www fs fed us rm pubs_other rmrs_2008_finch_d003 pdf Finch D M Galloway J Hawksworth D 2006 Monitoring bird populations in relation to fuel loads and fuel treatments in riparian woodlands with tamarisk and Russian olive understories In Aguirre Bravo C Pellicane P J Burns D P et al eds 2006 Monitoring science and technology symposium unifying knowledge for sustainability in the western hemisphere Proceedings RMRS P 42CD Fort Collins CO U S Department of Agriculture Forest Service Rocky Mountain Research Station 113 120 Finch D M Ganey J L Yong W et al 1997 Effects and interactions of fire logging and grazing In Block W M Finch D M tech eds Songbird ecology in southwestern ponderosa pine forests A literature review Gen Tech Rep RM 292 Fort Collins CO U S Department of Agriculture Forest Service Rocky Mountain Forest and Range Experiment Station 103 136 Fischer W C Bradley A F 1987 Fire ecology of western Montana forest habitat types Gen Tech Rep INT 223 Ogden UT U S Department of Agriculture Forest Service Intermountain Research Station 95 p Fleischner T L 1994 Ecological costs of livestock grazing in western North America Conservation Biology 8 629 644 Fontaine J B Donato D C Robinson W D et al 2009 Bird communities following high severity fire Response to single and repeat fires in a mixed evergreen forest Oregon USA Forest Ecology and Management 257 1 496 1 504 Fontaine J B Kennedy P L 2012 Meta analysis of avian and small mammal response to fire severity and fire surrogate treatments in U S fire prone forests Ecological Applications 22 1 547 1 561 Frye T C 1934 Ferns of the Northwest Portland OR Binfords and Mort 177 p USDA Forest Service RMRS GTR 408 2020 53

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