404Birds of the Brazilian state of <strong>Acre</strong>: diversity, zoogeography, and conservationEdson GuilhermeContact and hybridization zonesTwo contact zones were i<strong>de</strong>ntified within the studyarea (<strong>Acre</strong>) based on the distribution of parapatric taxa(Table 2). I have <strong>de</strong>noted these zones as the (a) westerncontact zone and (b) eastern contact zone (Figures 5, 6,and 7). The western contact zone is based on the presenceof the following sister taxa – Pipra filicauda/P. fasciicauda(Figure 6), Dendrocincla fuliginosa neglecta/D. f. atrirostris(Figure 5), and Pteroglossus castanotis castanotis/P. c.australis (Guilherme 2009). The eastern zone is <strong>de</strong>finedby the occurrence of Xiphorhynchus chunchotambo/ocellatus, Hypocnemis subflava/peruviana (Figure 7), andGlyphorhynchus spirurus castelnaudii/G. s. albigularis(Guilherme 2009).Two possible hybridization zones were i<strong>de</strong>ntifiedwithin the study area, coinciding with the contact zones.The western hybridization zone is <strong>de</strong>fined on the basis ofthe presence of specimens with intermediate characteristicsbetween Pteroglossus castanotis castanotis/P. c. australisand Dendrocolaptes certhia juruanus/D. c. polyzonus,whereas the eastern zone is characterized by the presenceof morphologically intermediate specimens betweenBrotogeris cyanoptera cyanoptera/B. c. beniensis and Momotusmomota cf. nattereri/M. m. simplex (Guilherme 2009).DISCUSSIONBird diversity in <strong>Acre</strong>The large number of bird species recor<strong>de</strong>d in theBrazilian state of <strong>Acre</strong> further emphasizes the biologicaldiversity of southwestern Amazonia (Haffer 1990). Infact, the number of species recor<strong>de</strong>d for <strong>Acre</strong> – 667 –represents more than half of the total recor<strong>de</strong>d for thewhole of the Amazon basin (Marini & Garcia, 2005;Mittermeier et al. 2003), and if only the fauna of thesouthern basin (south of the Solimões/Amazon channel)is consi<strong>de</strong>red (Stotz et al. 1996), 74.4% of the specieswere recor<strong>de</strong>d in <strong>Acre</strong>.The avifauna of <strong>Acre</strong> is composed primarily ofresi<strong>de</strong>nt species, but also inclu<strong>de</strong>s migrants and inva<strong>de</strong>rs.Five of the nine new species ad<strong>de</strong>d to the list of Brazilianbirds since 2005 were recor<strong>de</strong>d in <strong>Acre</strong> (Guilherme et al.2005, Guilherme & Aleixo 2008, Aleixo et al. 2008, Regoet al. 2009, Zimmer et al. 2010, CBRO 2011). Anotherspecies – Cacicus koepckeae – should also be ad<strong>de</strong>d to thislist, based on the recent record from the Chandless River(Buzetti 2008). Of the 1832 bird species known to occurin Brazil (CBRO, 2011), 22 have been recor<strong>de</strong>d only in<strong>Acre</strong> (Appendix 1), which testifies to the singularity ofthis state. <strong>Acre</strong> is located entirely within the Inambaricenter of en<strong>de</strong>mism, the largest such area in the lowlandsof the southern Amazon basin (Silva et al. 2005b).According to Cracraft (1985), the geographic rangesof the 57 bird taxa en<strong>de</strong>mic to the southwestern Amazonbasin <strong>de</strong>fine the limits of the Inambari center. Almostthree quarters (73.6%) of these en<strong>de</strong>mic taxa have beenrecor<strong>de</strong>d in <strong>Acre</strong>, with four new species (all <strong>de</strong>scribed since1985) being ad<strong>de</strong>d to the list subsequently (Appendix 1).<strong>Acre</strong> can be consi<strong>de</strong>red to be an excellent sample of theInambari center, given that it covers only 12% of its area,but contains more that 70% of its en<strong>de</strong>mic species. Giventhis, <strong>Acre</strong> is an excellent natural laboratory for the studyof historic biogeography.The migratory species were recor<strong>de</strong>d in both of thegeographic sub-regions (Appendix 1). However, some ofthe species arriving from south-central South Americawere only observed in eastern <strong>Acre</strong> (Appendix 1). Australand intratropical migrants such as Myiopagis viridicata,Tyrannus albogularis, Casiornis rufus, and Turdusamaurochalinus, arrived in the state from the southeast(e.g., Bolivian Chaco), where they breed (Davis 1993;Jahn et al. 2002, Appendix 1). Some migratory species,in particular tyrannids, tend to occupy the forest edges,secondary vegetation, and open areas (Chesser 1997). Asthe forest cover of easternmost <strong>Acre</strong> has been extensivelydisturbed, the resulting open and regenerating habitatscontribute to an increase in the probability of recordingother forest edge species such as Micrococcyx cinereus,Contopus cinereus, and Elaenia flavogaster (Appendix 1). Itseems likely that the occurrence of these species will alsobe confirmed for the central-western sub-region of thestate as new surveys are carried out in these areas duringthe migration season.A group of species, previously known only from thefoothills of the An<strong>de</strong>s and lowlands in Peru and Bolivia,was recor<strong>de</strong>d in the central eastern sub-region of <strong>Acre</strong>.For some species, such as Picumnus subtilis, Xiphorhynchuschunchotambo, and Cacicus koepckeae, these records<strong>do</strong> not represent either migrations or recent shifts indistribution, but rather, these species are resi<strong>de</strong>nts thathad simply not been recor<strong>de</strong>d previously, due to thelack of surveys in the area adjacent to the bor<strong>de</strong>rs withPeru and Bolivia. Other species, such as Conothraupisspeculigera and Pseu<strong>do</strong>colopteryx acutipennis neverthelessappear to migrate from the Pacific slope and An<strong>de</strong>s to thelowlands of Amazonia.Vagrancy also plays a role in the <strong>Acre</strong> avifauna.Phoenicoparrus jamesi, which is typical of the salt lakesof the An<strong>de</strong>an altiplano, was observed in <strong>Acre</strong> on a singleoccasion, and was consi<strong>de</strong>red to be an acci<strong>de</strong>ntal visitorby Guilherme et al. (2005). The nearest record of thisspecies is from the Manu National Park in southwesternPeru, at an altitu<strong>de</strong> of 350 m asl, where it was alsoconsi<strong>de</strong>red to be an vagrant (Walker et al. 2006), giventhat this lowland area is equally distant from the naturaldistribution of the species (<strong>de</strong>l Hoyo et al. 1992). Anotherspecies consi<strong>de</strong>red to be a vagrant here is Heliomaster<strong>Revista</strong> <strong>Brasileira</strong> <strong>de</strong> <strong>Ornitologia</strong>, 20(4), 2012
Birds of the Brazilian state of <strong>Acre</strong>: diversity, zoogeography, and conservationEdson Guilherme405FIGURE 6. Geographic distributions of Pipra filicauda and P. fasciicauda according to Natureserve (2007). The arrows point from the core to theperiphery of the ranges of the respective species. The red triangles and black <strong>do</strong>ts indicate the parapatric occurrence, respectively, of Pipra filicauda andP. fasciicauda in western <strong>Acre</strong>.FIGURE 7. Geographic distribution of the parapatric species Hypocnemis peruviana and H. subflava in eastern <strong>Acre</strong> showing the estimated “secondarycontact zone”. The arrows point from the core to the periphery of the ranges of the respective species<strong>Revista</strong> <strong>Brasileira</strong> <strong>de</strong> <strong>Ornitologia</strong>, 20(4), 2012