Influences on the Insular Distribution of Montane Lincoln's Sparrows (Melospiza Lincolnii Alticola)

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Influences on the Insular Distribution of Montane Lincoln's Sparrows (Melospiza Lincolnii Alticola) Great Basin Naturalist Volume 57 Number 2 Article 2 5-7-1997 Boggy meadows, livestock grazing, and interspecific interactions: influences on the insular distribution of montane Lincoln's Sparrows (Melospiza lincolnii alticola) Carla Cicero University of California, Berkeley Follow this and additional works at: https://scholarsarchive.byu.edu/gbn Recommended Citation Cicero, Carla (1997) "Boggy meadows, livestock grazing, and interspecific interactions: influences on the insular distribution of montane Lincoln's Sparrows (Melospiza lincolnii alticola)," Great Basin Naturalist: Vol. 57 : No. 2 , Article 2. Available at: https://scholarsarchive.byu.edu/gbn/vol57/iss2/2 This Article is brought to you for free and open access by the Western North American Naturalist Publications at BYU ScholarsArchive. It has been accepted for inclusion in Great Basin Naturalist by an authorized editor of BYU ScholarsArchive. For more information, please contact [email protected], [email protected]. Great Basin Nahiralist 57(2), C 1997, pp. 104-115 BOGGY MEADOWS, LIVESTOCK GRAZING, AND INTERSPECIFIC INTERACTIONS: INFLUENCES ON THE INSULAR DISTRIBUTION OF MONTANE LINCOLN'S SPARROWS (MEWSPlZA LINCOLNII ALTICOLA) Carla Cicerol ABSTRACT.-I surveyed 34 meadows in California and Oregon to count Lincoln's Sparrows (Nelospb,a lincolnli alt/oola) uod to identify habitat features that might influence their local, insular occurrence. Lincoln's Sparrows were found at 72% of the sites surveyed. Counts of singing males were low and uncorrelated with meadow size. Lincoln's SpatTOWS were most t:ommon in wet meadows with little damago by gra:.r.ing. Singing males were ooncentrated in flooded or boggy areas near meadow edges, where pines (PUlUS .~p.) provided c1evated pcrdles fOr .~inging and vigilance. Patche..~ ofwillows (Salix sp.) wen; often present nearby. Numbers of male Lincoln's Sparrows were strongly and negatively correlated with ahun­ dance ofsympatric Song Sparrows (M melodroff$lwreUa). Lincoln's Sparrows breeding in montane meadows are poten­ tially vulnemble to local extirpation because of their im:ular distribution, low population density, and fluctuating habitat conditions. Heavy damage from liv~10cJc grazing drastically increase" the probability oflocal extirpation. Key words: Melospiza lincolnii, Lincoln's Sparrou>, montane meadow, insular populatwns, habitat ussocf.atKm., live­ stock grazing, conservation biology, MclospWi. melodia, Scn~ Sparrow. Mcadows form ecological islands through­ fragments (e.g., Forman et al. 1976). However, out montane forests of the western United detailed studies ofspecifIC taxa occupying nat­ States. Although these systems generally sup­ ural insular habitats such as meadows are port a rich avifauna, they are highly variahle in scarce. terms of physiographic, hydrologic, edaphic, The montane form of Lincoln's Sparrow vegetative, and floristic characteristics (e,g., (Melospi:w lincolnii alticolo.; Miller and McCahe see Kuramoto and Bliss 1970, Benedict and 1935, American Ornithologists' Union 1957) is Major 1982, Ratliff 1982, 1985, Allen 1987). well suited to such a study. This taxon breeds Grazing and fire history also shape meadow insularly in particular kinds of meadows from environments (Kuramoto and Bliss 1970, Oregon to California and from Idaho to New DeBenedetti aod Parsons 1979, 1984, Parsons Mexico. Such sites are separated from other 1981, Ratliff 1985). Changes in grazing and suitable islands nf habitat by unoccupied coni­ fire management practices, combined with cli· ferous forest Two other subspecies (M. I. lin­ mate, further influence the ecology and stability colnii and M. I. gracili8) occur more broadly of meadows by promoting invasion of lodge­ in broshy bogs from central Alaska through pole pine and other conifers (Franklin et al. Canada to the northern contiguous United 1971, Dunwiddie 1977, Vale 1981a, 1981b, States. Despite the widespread distribution of Ratliff 1985). Lincoln's Sparrows, the species has been poorly Because of their mobility, birds respond studied compared with either ofits congeners, quickly to habitat change aod thus are model the Song Sparrow (M. melodia) or Swamp orgaoisms for illustrating the effect of habitat Sparrow (M. georgiana). Information on the dis­ on the distribution and abundance of insular tribution and natural history ofM. I. alticola is as well as cootioental populations (Cody 1981, especially lacking. In this study I provide hase­ Wiens 1989). Numerous researchers have exam­ line data on occurrence, abundance, habitat ined total avifaunal distribution and abundance association, and other factors potentially related on montane islands (e.g., Johnson 1975, Kratter to their local. distribution in western montane 1992, Lentz 1993), in natural habitat patches meadows. Secondarily, I evaluate the potential (e.g., aspen; Flack 1976), or in disrnrbed forest impact livestock grazing has on this taxon. IMuseum ,,(~dlf1lle lDoIO!D', U,.M:nity ufCaliforn.iil, Berkeley, C.... lt4721I. 104 1997] LINCOLN'S SI'ARROWS IN MEADOWS 105 Range ecologists have shown unequivocally dance may reveal degradation of meadows by that grazing occurs unevenly across montane livestock. vegetation types and that meadows and other riparian areas receive disproportionately heavy STUDY AREAS AND METHODS use relative to their total acreage (Cook 1966, Roath and Krueger 1982a, 1982b, Gillen et aI. I surveyed meadows for Lincoln's Sparrows 1984, Platts and Nelson 1985). Numerous stud­ from mid-May to early July 1987-1989. A total ies have assessed the impact of such use on of 34 meadows belonging to 29 systems were riparian habitats and associated wildlife (e.g., visited, including 1 in northern Oregon and 28 Leege et aI. 1981, Kauffman et a1. 1983, Kauff­ in California from the southern Cascade Moun­ man and Krueger 1984, Ihylor 1986, Ohmart tains (Lassen County) through the Sierra Nevada 1994). Montane Lincobis Sparrows are paten· to the San Bernardino Mountains (Fig. 1). Ele­ tially vulnerable to disturbance by heavy graz­ vations ranged from 1365 to 2470 m, with ing because oftheir tendency to nest on or near lodgepole pine (Pinus contorta) forest dominat­ swampy ground in wet meadows (Grinnell ing the surrounding vegetation. Size, land own­ and Miller 1944, Austin 1968). Consequently, ership, and type and intensity oflivestock graz­ changes in their local occurrence or abun- ing varied among meadows. Although several -'-'-'_'_0_.• -----'-'1 ..... " 10" ~ ... •• " ... ·~4.5 ... 2-v ~~6-7 • ~. 6·12 13..., 14••015 016 • , ( 17-18,-21· ". "0· '. 19-20--\..22 ' , ~24"'=-25-26 ", ..._.. '., .. , , • , • , ,I , • , I 35 " • \ , / / • ) • o, 100 mi. ( , , L.\ o 200 km. J:i'ig. L Breeding distribution of Lincoln's Sparrows in Califomia. The general locations of 28 meadow systems sur­ veyed in California are indicated; an additional me-d.dow in Oregon is not shown. Closed circles denote meadows where Lincoln's Sparrows were present; open circles, meadows where Lincoln's Sparrows were absent. Closed. squares show other known breeding localities based on specimens depo!>iled in the Museum ofVertebrate Zoology, Berkeley, Califor­ nia.; published records (Grinnell and Miller 1944, Lentz 1993); records obtained during ~l survey ofmeadows for Willow Flycatchers (Empidonm: traillU., M. A. Flett and J. Harris unpublished data). 106 GREAT BASIN NATURAUST [Volume 57 groups of meadows were clustered geographi­ grazing. Surveys took longer in large meadows cally, differences in habitat characteristics, ele­ or at sites 'vith high numbers of Lincoln's vatioIl, and/or grazing regime occurred between Sparrows. Because the amount of time spent even the most proximal sites. Consequently, at each site varied, count values were stan­ each meadow was treated as an independent dardized by dividing the number of singing sample point. nventy-five sites consisted ofsin­ males observed per visit by the length of the gle meadows without any connection to other survey. As with all count methods, some silent sites. Another meadow (Beasore Meadow [site males may bave been overlooked. Thus, these 22]) was divided by a fence into 2 parts with counts represent minimal estimates of total strikingly different grazing regimes; because abundance. the 2 sides also contrasted dramatically in The geographic scope of tbis study pre­ abundance of Lincoln's Sparrows, they were cluded surveying all meadows simultaneously. separated for purposes of analysis and discus­ To verify the reliability of counts conducted at sion. Three meadow systems (Lacey [8], Hay­ different times, I surveyed 17 meadows (50%) press Creek [9], and Sagehen Creek [12]) con­ twice or more during the same or subsequent tained multiple meadows witbin 1 drainage or seasons. Counts of singing males in the same basin that were separated from each other by meadow at different stages of the breeding a distance of at least 0.8 km. Because these cycle were identical. Because annual climatic were visited only during the breeding season, differences might also influence counts taken when males were singing and thus territorial, in different years, I obtained data on mean presumably there was no movement ofLincoln's temperature and precipitation during May and Sparrows between meadows. This was con­ June 1987-1989 (National Oceanic and Atmos­ firmed by multiple visits to the same meadow pheric Administration 1987, 1988, 1989) from system (e.g., Haypress Creek) during a single weather stations located near 3 main clusters breeding season, when individual singing males
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