Jon FJELDSÅ. 2013: The global diversification of songbirds (Oscines) and the build-up of the Sino-Himalayan diversity hotspot. Avian Research, 4(2): 132-143. DOI: 10.5122/cbirds.2013.0014
Citation: Jon FJELDSÅ. 2013: The global diversification of songbirds (Oscines) and the build-up of the Sino-Himalayan diversity hotspot. Avian Research, 4(2): 132-143. DOI: 10.5122/cbirds.2013.0014

The global diversification of songbirds (Oscines) and the build-up of the Sino-Himalayan diversity hotspot

More Information
  • Corresponding author:

    Jon FJELDSÅ, jfjeldsaa@snm.ku.dk

  • Received Date: 03 Dec 2012
  • Accepted Date: 16 Feb 2013
  • Available Online: 23 Apr 2023
  • Over the last decade, molecular phylogenetic studies have provided the foundation for a comprehensive analysis of the global diversification of songbirds (Oscines), which comprise nearly half of all the birds of the world. By comparing the spatial distribution of species representing basal and terminal root-path groups, this paper provides graphical illustrations of the global pattern of diversification for the major songbird clades. The worldwide expansion of songbirds started as an island radiation in the area where New Guinea is now located, but the mountains of southern China represent a principal center for more recent diversification. The paper suggests priorities and perspectives for further research aiming to understand what determines the variation in biodiversity on different spatial scales.

  • The Three-Toed Woodpecker is circumpolal distributed across the Northern Hemisphere. This vast distribution area results in eight subspecies, which are currently divided into two separate species based on mitochondrial DNA: Picoides tridactylus in Eurasia and P. dorsalis in North America (Zink et al., 1995, 2002). The subspecies P. t. funebris (Fig. 1) is endemic to the Qinghai-Tibet plateau in China. No research is being ever conducted since its discovery in 1870 (Verreaux, 1870). Thus, P. t. funebris is a subspecies for which we are not aware of any reports on life history details including foraging behavior.

    Figure  1.  The Three-toed Woodpecker subspecies Picoides tridactylus funebris

    Foraging behavior in Three-toed Woodpeckers is strongly related to the availability of food which was shown to be the driving factor for selection of foraging sites (Hogstad, 1976, 1977, 1991; Pechacek, 2006). Bark beetles and wood boring beetle larvae that are both confined to the subsurface of dead and dying trees are reported to be the most important prey of Three-toed Woodpeckers (Pechacek and Kristin 2004). Morphological adaptations especially with regard to the shape of the chisel-like bill are the basic precondition to excavate these prey from foraging substrates.

    Measurements of 12 museum specimens of P. t. funebris (6 males and 6 females, Y.Z. Zhu unpublished data) suggested that the differences in bill length between the sexes are less developed than in P. t. alpinus (< 4% vs > 8%) (Pechacek, 2006). This may have resulted in evolution of more serious competition between males and females because bill length differences are related to the pronounced foraging niche partitioning. Niche partitioning helps to prevent conflicts in cases when both sexes are foraging close to each other and was well described in P. t. tridactylus (Hogstad, 1976, 1977, 1991) and P. t. alpinus (Pechacek, 2006).

    We therefore conducted field observations on P. t. funebris in Gansu Province, China to compare its foraging behavior with that of other subspecies we particularly aimed for 1) exploring foraging sites and foraging techniques, and 2) assessing the niche partitioning between the sexes.

    The study was conducted at the Kache Forest Farm, Zhuoni County, Gansu Province, China (34°10′7″–34°38′20″N, 103°12′49″–103°48′50″E), with altitude ranging from 2500 to 4500 m above sea level. The Kache Forest Farm is composed of coniferous forests that are dominated by spruces (Picea asperata, P. wilsonii) and firs (Abies fargesii, A. faxoniana). Two large-scale logging operations were conducted in the area between 1949 and 1998, and afforestation took place in recent years.

    A female P. t. funebris was caught in a mist net on 21 March 2007. It was banded and fitted with a 2 g radio transmitter (type BD 2G, Holohil, Canada). We followed the female by radio-tracking and collected foraging observation. The mated male individual was observed travelling together with the female frequently during the breeding season, and we therefore conducted observations on the foraging male as well.

    Following field protocols by Pechacek (2006), foraging data was recorded every 15 s during an observed foraging bout. We recorded foraging behavior and associated parameters of foraging substrates. Foraging bout was considered as effective only if the woodpecker was observed foraging on a tree for more than 45 s and we could therefore record observations more than three times. Collected data reflected behavior or substrate use as a percentage of each foraging bout (i.e. percentage of time spent by displaying a particular foraging behavior or using a particular foraging substrate). To ensure the independency of foraging bouts, the next foraging bout was recorded after minimally one hour (Swihart and Slade, 1985), or alternatively, if the woodpecker moved at least 100 m from the previous location (Pechacek, 2006).

    According to the sampling classification developed by Remsen and Robinson (1990) and Pechacek (2006), we distinguished nine types of behavior associated with foraging: pecking, peeling, sap-sucking, preening, territory defence, climbing, freezing, head swinging, and other. We summarized pecking, tapping and probing from the original classification (Remsen and Robinson, 1990; Pechacek, 2006) as pecking which represented foraging for prey hidden relatively deep in the foraging substrate. Scaling and gleaning from the original classification were summarized as peeling which represented foraging for prey available close to the substrate surface.

    Parameters of foraging substrates were categorized and measured according to Pechacek (2006). We considered parameters that included foraging zone (i.e. base of the trunk, trunk, branches), substrate thickness, foraging height (i.e. lower, central and middle third of the foraging tree) and condition of the foraging substrate (i.e. alive, dead with and without bark). The thickness of foraging substrate was assessed referring to the bird itself (about 5.5 cm width). Additionally, we randomly placed 100 plots of 10 m × 10 m throughout the foraging area (i.e. home-range) of the male and female to assess the amount of snags (i.e. standing dead trees) in the foraging territory.

    After recording a foraging bout, the nearest tree of random direction was selected as a reference. Tree species and diameter at breast height (DBH) were recorded for both foraging and reference tree, and then the feeding preference index (PI) was calculated to express the foraging preference, using the equation from Kells et al. (2001):

    PI=(Vk/Vt)/(Ak/At)

    where Vk is the number of foraging visits of kth site, Vt the total number of visits to all sites, Ak the total number of kth reference, and At the total number of all references.

    Analyses were conducted in SPSS 13.0. Wilcoxon Signed Ranks Test was used to test the difference between DBH of foraging and reference trees. Mann-Whitney U-Test was used to test for differences in foraging behavior between the sexes. Results were considered significant at p < 0.05. Standard deviations (SD) are given with means.

    We collected 117 observations on a foraging pair of P. t. funebris during the breeding season between April and August 2007. Of them, 89 accounted for the female and 28 for the male. Both partners were found foraging close to each other at 56 (47.8%) out of 117 occasions.

    The volume of snags in the foraging territory amounted 4.3 m3·ha–1 (6 and 2.1 m3·ha–1 for the male's and female's home ranges, respectively).

    P. t. funebris preferred live spruces and snags over other available sites (Table 1). Foraging trees had by 26% bigger DBH than the reference trees, whereas the mean DBH of the female's foraging trees was larger than that of reference trees (32.6 ± 8.8 vs 22.2 ± 9.2), and the DBH of the male's foraging trees was similar to the reference ones (33.1 ± 10.4 vs 30.2 ± 10.6) (Table 2). The main foraging technique of P. t. funebris was pecking (39.8 ± 27.0% of the foraging time) followed by the peeling (13.2 ± 15.0%).

    Table  1.  Preferences for foraging trees in a pair of P. t. funebris during the breeding season in Kache Forest Farm, Zhuoni County, Gansu Province, 2007. A reference tree was selected as the nearest tree of random direction to the foraging tree.
    Site Foraging tree (%) Reference tree (%) Preference index
    Fir 65.8 83.2 0.791
    Spruce 18.8 10.3 1.825
    Snag a 14.5 3.4 4.265
    Other 0.9 3.4 0.265
    Total 100 100
    n 117 117
    a Unidentified species.
     | Show Table
    DownLoad: CSV
    Table  2.  Diameter of foraging trees used by a pair of P. t. funebris during the breeding season in Kache Forest Farm, Zhuoni County, Gansu Province, 2007, including diameter of associated reference trees. A reference tree was selected as the nearest tree of random direction to the foraging tree.
    Foraging tree (cm) Reference tree (cm) Z a p a n
    Male 33.1 ± 10.4 30.2 ± 10.6 –0.1 0.996 28
    Female 32.6 ± 8.8 22.2 ± 9.2 –6.4 0.000 89
    Z b –0.2 –3.7
    p b 0.858 0.000
    Total 32.7 ± 9.2 24.1 ± 10.1 –5.8 0.000 117
    a Results derived from Wilcoxon Signed Ranks Test;
    b Results derived from Mann-Whitney U-Test.
     | Show Table
    DownLoad: CSV

    The mean DBH of the foraging trees showed no difference between male and female (p = 0.858). However, we observed the following differences between the sexes with regard to parameters of foraging substrates (Table 3): the female foraged more often in the upper third of a tree (p = 0.010), while the male was more frequently seen foraging in the lower third (p = 0.003). The thickness of the male foraging substrate was significantly larger than that of the female's (p = 0.013). The male foraged more often on the dead substrates covered with bark (p = 0.021). On the other hand, the female spent more time on living parts of trees (p = 0.017). Additionally, male used pecking more often than the female (p = 0.035; Table 4).

    Table  3.  Parameters of foraging sites used by a pair of P. t. funebris during the breeding season in Kache Forest Farm, Zhuoni County, Gansu Province, 2007. The numbers reflect substrate use as a percentage of foraging bouts, i.e. percentage of time spent using a particular substrate parameter (except of thickness which is expressed in cm).
    Male Female Z p All
    Foraging zone
    Base of the trunk 14.3 ± 35.6 3.8 ± 18.3 –1.5 0.141 6.3 ± 23.8
    Trunk 46.4 ± 50.8 37.4 ± 45.2 –0.96 0.926 39.6 ± 46.5
    Branches 39.2 ± 49.7 57.7 ± 46.3 –1.2 0.248 53.3 ± 47.6
    Foraging height
    Lower third 28.6 ± 46.0 5.8 ± 23.2 –3.1 0.003 11.3 ± 31.6
    Central third 33.8 ± 46.6 28.6 ± 44.4 –0.4 0.651 29.8 ± 44.8
    Upper third 33.7 ± 47.8 65.5 ± 47.0 –2.6 0.010 58.9 ± 48.5
    Condition
    Alive 15.1 ± 35.6 28.9 ± 42.3 –2.4 0.017 25.6 ± 41.1
    Dead with bark 78.9 ± 38.1 63.9 ± 41.2 –2.3 0.021 67.5 ± 40.9
    Dead without bark 5.9 ± 15.3 7.3 ± 16.5 –0.1 0.893 6.9 ± 16.2
    Total 100 100 100
    Mean thickness of foraging substrates (cm) 17.0 ± 11.6 11.0 ± 8.2 –2.4 0.013 12.6 ± 9.9
    n 28 89 117
     | Show Table
    DownLoad: CSV
    Table  4.  Foraging techniques and behavior associated with foraging observed in a pair of P. t. funebris during the breeding season in Kache Forest Farm, Zhuoni County, Gansu Province, 2007. The numbers reflect behavior as a percentage of foraging bouts, i.e. percentage of time spent using a particular foraging technique.
    Foraging behavior Male Female Z p All
    Pecking 46.2 ± 29.5 37.8 ± 26.0 –1.8 0.035 39.8 ± 27.0
    Peeling 13.0 ± 14.5 13.2 ± 15.3 –0.2 0.430 13.2 ± 15.0
    Sap-sucking 3.4 ± 18.0 4.3 ± 17.0 –0.6 0.474 4.1 ± 17.2
    Preening 6.1 ± 17.7 5.1 ± 16.5 –1.1 0.142 5.3 ± 16.8
    Territory defense 0.4 ± 1.9 1.1 ± 6.0 –0.4 0.370 0.9 ± 5.3
    Climbing 8.9 ± 13.3 9.7 ± 12.7 –0.3 0.374 9.5 ± 12.8
    Freezing 3.8 ± 10.8 9.5 ± 18.9 –0.8 0.208 8.1 ± 17.4
    Head swinging 7.5 ± 8.2 10.8 ± 11.9 –1.1 0.139 10.0 ± 11.2
    Other 10.5 ± 13.7 6.2 ± 6.7 –1.4 0.079 7.2 ± 9.0
    Total 100 100 100
    n 28 89 117
     | Show Table
    DownLoad: CSV

    P. t. funebris preferred foraging on live spruces and snags that were bigger than surrounding reference trees with an average DBH of 32.7 ± 9.2 cm. We found differences between the sexes with respect to foraging height, substrate thickness and condition of the substrate. The most frequent foraging technique was pecking (39.8% of foraging time) followed by the peeling (13.2%). The male pecked more often than the female, and the female preferred foraging on trees that were larger than those available in female's foraging territory. Although the fir was the dominant tree species in our study area by amounting for 83.2% of the randomly selected reference trees, P. t. funebris preferred spruces and snags which had higher population density of bark beetles than firs (Liu et al., 1994). The observed foraging on trees with relatively large DBH was likely also related to the more abundant beetle prey that typically occurs in large substrates (Hanula et al., 2000).

    We found that P. t. funebris extensively foraged on dead branches (53.3% of the foraging time), while P. t. alpinus rarely did so (13%, Pechacek, 2006). This may have been adaptation to the small amount of snags available in the foraging territory in our study area (4.3 m3·ha–1). In contrast, snag amount was much higher in habitats of P. t. alpinus in the European Alps (30 m3·ha–1 of combined volume of snags and downed logs, Konnert, 2000). Woodpeckers may have therefore compensated for the lack of snags to obtain prey on another form of dead wood, the dead branches. We noted that sap-sucking was observed more often in P. t. funebris than in P. t. alpinus (4.1% vs 1.2% of the foraging time) (Pechacek, 2006), suggesting that P. t. funebris was more dependent on the tree sap than the other subspecies.

    P. t. funebris showed pronounced vertical niche partitioning between the sexes. This was consistent with observations on Three-Toed Woodpeckers elsewhere (Hogstad 1977, 1991; Pechacek, 2006). We found distinct differences between the sexes with respect to use of three out of four investigated parameters of the foraging substrates. The male occupied for most of the foraging time the lower third of coniferous trees and thicker substrates, where beetle prey is typically more abundant than in the upper third and on branches (Chen et al., 1999; Liu et al., 2007). Excavation of prey from the substrates composed of large DBH and thick bark required more time investment by extensive pecking. This may have explained the higher proportion of the male's pecking behavior compared to female. Conversely, the female used more often dead substrates with bark already peeled off, and living substrates. These sites presumably contained less abundant food. We also found that the volume of snags was higher within the male's home range compared to that of the female (6 vs 2.1 m3·ha–1). Moreover, we detected the male driving away the female for five times, which accounted for 8.9% of all records when both partners were found travelling together. We therefore concluded that the male dominated over the female by occupying prey-richer resources also in P. t. funebris despite of less obvious competitive advantages as demonstrated by little differences in the bill length between the sexes in comparison with P. t. alpinus (Pechacek, 2006).

    We confirmed that P. t. funebris displayed foraging behavior and niche partitioning that showed similar patterns to those reported for other studied subspecies of the Three-toed Woodpecker. The observed niche partitioning, however, did not reflect well the expected strong competition for the best foraging sites based on less pronounced sexual dimorphism (here represented by bill length) in P. t. funebris.

  • Alström P, Fregin S, Norman JA, Ericson PGP, Christidis L, Olsson U. 2011a. Multilocus analysis of a taxonomically densely sampled dataset reveal extensive non-monophyly in the avian family Locustellidae. Mol Phyl Evol, 58: 513–526.
    Alström P, Höhna S, Gelang M, Ericson PGP, Olsson U. 2011b. Non-monophyly and intricate morphological evolution within the avian family Cettiidae revealed by multilocus analysis of a taxonomically densely sampled dataset. BMC Evol Biol, 11: 352.
    Barker FK, Cibois A, Schikler P, Feinstein J, Cracraft J. 2004. Phylogeny and diversification of the largest avian radiation. Proc Natl Acad Sci USA, 101: 11040–11045.
    Barker FK. 2011. Phylogeny and diversification of modern passerines. In: Dyke G, Kaiser G (eds) Living Dinosaurs. WileyBlackwell, Oxford, pp 235–256
    Byrne M, Steane D, Joseph L, Yeates D, Jordan GJ, Crayn D, Aplin K, Cantrill D, Cook LG, Crisp MD, Keogh JS, Melville J, Moritz C, Porch N, Sniderman JMK, Sunnucks P, Weston PH. 2011. Decline of a biome: evolution, contraction, fragmentation, extinction and invasion of the Australian mesic zone biota. J Biogeogr, 38: 1035–1056.
    Chen X, Huang S, Guo P, Colli GT, Montes de Oca AN, Vitt LJ, Alexander Pyron R, Burbrink FT. 2012. Understanding the formation of ancient intertropical disjunct distributions using Asian and Neotropical hinged-teeth snakes (Sibynophis and Scaphiodontophis: Serpentes: Colubridae). Mol Phyl Evol, 66: 254–261.
    Connor EF, Simberloff D. 1979. The assembly of species communities: chance or competition? Ecology, 60: 1132–1140.
    Derryberry EP, Claramunt S, Derryberry R, Chesser RT, Cracraft J, Aleixo A, Pérez-Emán J, Remsen JV, Brumfield RT. 2011. Lineage diversification and morphological evolution in a largescale continental radiation: the Neotropical ovenbirds and woodcreepers (Aves: Furnariidae). Evolution, 65: 2973–2986.
    Diamond JM. 1974. Colonization of exploded volcanic islands by birds: the supertramp strategy. Science, 183: 803–806.
    Diamond JM. 1975. Assembly of species communities. In: Cody ML, Diamond JM (eds) Ecology and Evolution of Communities. Belknap Press, Cambridge, MA.
    Dynesius M, Jansson R. 2000. Evolutionary consequences of changes in species' geographical distributions driven by Milankovitch climate oscillations. Proc Natl Acad Sci USA, 97: 9115–9120.
    Ericson PGP, Christidis L, Cooper A, Irestedt M, Jackson J, Johansson US, Norman JA. 2002. A Gondwanan origin of passerine birds supported by DNA sequences of the endemic New Zealand wrens. Proc R Soc B, 269: 235–241.
    Ericson PGP, Jansén A-L, Johansson US, Ekman J. 2005. Intergeneric relationships of the crows, jays, magpies, and allied groups (Aves: Corvidae) based on nucleotide sequence data. J Avian Biol, 36: 222–234.
    Fabre P-H, Irestedt M, Fjeldså J, Bristol R, Groombridge JJ, Irham M, Jønsson KA. 2012. Dynamic colonization exchanges between continents and islands drive diversification in paradiseflycatchers (Terpsiphone, Monarchidae). J Biogeogr, 39: 1900–1918.
    Filardi CE, Moyle RG. 2005. Single origin of a pan-Pacific bird group and upstream colonization of Australasia. Nature, 438: 216–219.
    Fjeldså J, Bowie RCK, Rahbek C. 2012. The role of mountain ranges in the diversification of birds. Ann Rev Ecol Evol Syst, 43: 249–265.
    Fleischer RC, James HF, Olson SL. 2008. Convergent evolution of Hawaiian and Australo-Pacific honeyeaters from distant songbird ancestors. Curr Biol, 18: 1–5.
    Fregin S, Haase M, Olsson U, Alström P. 2012. New insights into family relationships within the avian superfamily Sylvioidea (Passeriformes) based on seven molecular markers. BMC Evol Biol, 12: 157.
    Fritz SA, Jønsson KA, Fjeldså J, Rahbek C. 2011. Diversification and biogeographic patterns of four island radiations of passerine birds. Evolution, 66: 179–190.
    Fuchs J, Fjeldså J, Bowie RCK, Voelker G, Pasquet E. 2006. The African warbler genus Hyliota as a lost lineage in the Oscine songbird tree: Molecular support for an African origin of the Passerida. Mol Phyl Evol, 39: 186–197.
    Fuchs J, Irestedt M, Fjeldså J, Couloux A, Pasquet E, Bowie RCK. 2012. Molecular phylogeny of African bush-shrikes and allies: Tracing the biogeographic history of an explosive radiation of corvoid birds. Mol Phyl Evol, 64: 93–105.
    Fuchs J, Pasquet E, Couloux A, Fjeldså J, Bowie RCK. 2009. A new Indo-Malayan member of the Stenostiridae (Aves: Passeriformes) revealed by multi-locus sequence data: biogeographic implications for a morphologically diverse clade of flycatchers. Mol Phyl Evol, 53(2): 384–393.
    Gelang M, Cibois A, Pasquet E, Olsson U, Alström P, Ericson PGP. 2009. Phylogeny of babblers (Aves, Passeriformes): major lineages, family limits and classification. Zool Scripta, 38: 225–236.
    Graham CH, Parra JL, Rahbek C, McGuire JA. 2009. Phylogenetic structure in tropical hummingbird communities. Proc Natl Acad Sci USA, 106: 19673–19678.
    Hall R. 2011. Australia-SE Asia collision: plate tectonics and crustal flow. In: Hall R, Cottam MA, Wilson MEJ (eds) The SE Asian Gateway: History and Tectonics of Australia-Asia Collision. The Geological Society, London, pp 75–109.
    Hawkins BA, Diniz-Filho JAF. 2006. Beyond Rapoport's rule: evaluating range size patterns of New World birds in a twodimensional framework. Global Ecol Biogeogr, 15: 461–469.
    Holt BG, Lessard J-P, Borregaard MK, Fritz SA, Araújo MB, Dimitrov D, Fabre P-H, Graham CH, Graves GR, Jønsson KA, Nogués-Bravo D, Wang Z, Whittaker RJ, Fjeldså J, Rahbek C. 2013. An update of Wallace's zoogeographic regions of the world. Science, 339: 74–78.
    Houle D, Govindaraju DR, Omholt S. 2010. Phenomics: the next challenge. Nat Rev Genet, 11: 856–866.
    Irestedt M, Fuchs J, Jønsson KA, Ohlson JI, Pasquet E, Ericson PGP. 2008. The systematic affinity of the enigmatic Lamprolia victoriae (Aves: Passeriformes) – An example of avian dispersal between New Guinea and Fiji over Miocene intermittent landbridges. Mol Phyl Evol, 48: 1218–1222.
    Jetz W, Thomas GH, Jo JB, Hartmann K, Mooers AO. 2012. The global diversity of birds in space and time. Nature, 491: 444–448.
    Johansson US, Fjeldså J, Bowie RCK. 2008. Phylogenetic relationships within Passerida (Aves: Passeriformes): a review and a new molecular phygeny based on three nuclear intron markers. Mol Phyl Evol, 48: 858–876.
    Jønsson KA, Bowie RCK, Moyle RG, Christidis L, Norman JA, Benz BW, Fjeldså J. 2010c. Historical biogeography of an IndoPacific passerine bird family (Pachycephalidae): different colonization patterns in the Indonesian and Melanesian archipelagos. J Biogeogr, 37: 245–257.
    Jønsson KA, Bowie RCK, Moyle RG, Irestedt M, Christidis L, Norman JA, Fjeldså J. 2010d. Phylogeny and biogeography of Oriolidae (Aves: Passeriformes). Ecography, 33: 1–10.
    Jønsson KA, Bowie RCK, Nylander JAA, Christidis L, Norman JA, Fjeldså J. 2010b. Biogeographical history of cuckoo-shrikes (Aves: Passeriformes): transoceanic colonization of Africa from Australo-Papua. J Biogeogr, 37: 1767–1781.
    Jønsson KA, Fabre P-H, Fritz SA, Etienne RS, Ricklefs R, Jorgensen TB, Fjeldså J, Rahbek C, Ericson PGP, Woog F, Pasquet E, Irestedt M. 2012. Ecological and evolutionary determinants for the adaptive radiation of the Madagascan vangas. Proc Natl Acad Sci USA, 109: 20–25.
    Jønsson KA, Fabre P-H, Ricklefs RE, Fjeldså J. 2011. Major global radiation of corvoid birds originated in the proto-Papuan archipelago. Proc Natl Acad Sci USA, 108: 2328–2333.
    Jønsson KA, Fjeldså J. 2006. Determining biogeographic patterns of dispersal and diversification in oscine passerine birds in Australia, Southeast Asia and Africa. J Biogeogr, 33: 1155–1165.
    Jønsson KA, Irestedt M, Ericson PGP, Fjeldså J. 2007. Systematic placement of an enigmatic Southeast Asian taxon Eupetes macrocercus and implications for the biogeography of a main songbird radiation, the Passerida. Biol Lett, 3: 323–326.
    Jønsson KA, Irestedt M, Ericson PGP, Fjeldså J. 2010a. A molecular phylogeny of minivets (Passeriformes: Campephagidae: Pericrocotus): Implications for biogeography and convergent plumage evolution. Zool Scripta, 39: 1–8.
    Lessard J-P, Belmaker J, Myers JA, Chase JM, Rahbek C. 2012. Inferring local ecological processes amid species pool influences. TREE, 27: 600–607.
    Lovette IJ, McCleery BV, Talaba AL, Rubinstein DR. 2008. A complete species-level molecular phylogeny for the "Eurasian" starlings (Sturnidae: Sturnus, Acridotheres, and allies): recent diversification in a highly social and dispersive avian group. Mol Phyl Evol, 47: 251–260.
    Lovette IJ, Rubenstein DR. 2007. A comprehensive molecular phylogeny of the starlings (Aves: Sturnidae) and mockingbirds (Aves: Mimidae): congruent mtDNA and nuclear trees for a cosmopolitan avian radiation. Mol Phyl Evol, 44: 1031–1056.
    MacArthur RH, Wilson EO. 1967. The Theory of Island Biogeography. Princeton University Press, Princeton, N.J.
    Moyle RG, Andersen MJ, Oliveros CH, Steinheimer F, Reddy S. 2012. Phylogeny and biogeography of the core babblers (Aves: Timaliidae). Syst Biol, 61: 631–651.
    Nyári ÁS, Benz BW, Jønsson KA, Fjeldså J, Moyle RG. 2009. Phylogenetic relationships of fantails (Aves: Rhipiduridae). Zool Scripta, 38: 553–561.
    Olsson U, Alström P, Ericson PGP, Sundberg P. 2005. Non-monophyletic taxa and cryptic species — Evidence from a molecular phylogeny of leaf-warblers (Phylloscopus, Aves). Mol Phyl Evol, 36: 261–276.
    Olsson U, Irestedt M, Sangster G, Ericson PGP, Alström P. 2012. Systematic revision of the avian family Cisticolidae based on a multi-locus phylogeny of all genera. Mol Phyl Evol, 66(3): 790–799.
    Päckert M, Martens J, Sun Y-H, Severinghaus LL, Nazarenko AA, Ting J, Töpfer T, Tietze DT. 2011. Horizontal and elevational phylogeographic patterns of Himalayan and Southeast Asian forest passerines (Aves: Passeriformes). J Biogeogr, 39: 556–573.
    Päckert M, Martens J, Sun Y-H. 2010. Phylogeny of long-tailed tits and allies inferred from mitochondrial and nuclear markers (Aves: Passeriformes, Aegithalidae). Mol Phyl Evol, 56: 952–967.
    Price T. 2010. The role of time and ecology in the continental radiation of the Old World leaf-warblers (Phylloscopus and Seicercus). Phil Trans R Soc B, 365: 1749–1762.
    Rabosky SL, Lovette IJ. 2009. Density-dependent diversification in North American wood warblers. Proc Roy Soc B, 275: 2363–2371.
    Reddy S. 2008. Systematics and biogeography of the shrike-babblers (Pteruthius): Species limits, molecular phylogenetics, and diversification patterns across southern Asia. Mol Phyl Evol, 47: 54–72.
    Ricklefs RE. 2011. A biogeographical perspective on evological systems: some personal reflections. J Biogeogr, 38: 2045–2056.
    Rosenzweig ML. 1995. Species Diversity in Space and Time. Cambridge University Press.
    Sangster G, Alström P, Forsmark E, Olsson U. 2010. Multi-locus phylogenetic analysis of Old World chats and flycatchers reveals extensive paraphyly at family, subfamily and genus level (Aves: Muscicapidae). Mol Phyl Evol, 57: 380–392.
    Sibley CG, Ahlquist JE. 1990. Phylogeny and Classification of Birds: a study in Molecular Evolution. Yale University Press, New Haven.
    Voelker G, Rohwer S, Outlaw D, Bowie RCK. 2009. Repeated trans-Atlantic dispersal catalyzed a global songbird radiation. Global Ecol Biogeogr, 18: 41–49.
    Wallace AR. 1876. The Geographical Distribution of Animals; with a Study of The Relations of Living and Extinct Faunas as Elucidating the Past Changes of the Earth's Surface. Macmillan & Co., London.
    Wetmore A. 1957. The classification of the oscine Passeriformes. Condor, 59: 207–209.
    Zuccon D, Ericson PGP. 2010. A multi-gene phylogeny disentangles the chat-flycatcher complex (Aves: Muscicapidae). Zool Scripta, 39: 213–224.
    Zuccon D, Prys-Jones R, Rasmussen PC, Ericson PGP. 2011. The phylogenetic relationships and generic limits of finches (Fringillidae). Mol Phyl Evol, 62: 581–596.
  • Related Articles

Catalog

    Figures(3)

    Article Metrics

    Article views (3815) PDF downloads (2022) Cited by()

    /

    DownLoad:  Full-Size Img  PowerPoint
    Return
    Return