Sobre a possível extinção de aves da planície alagável do Alto Rio Paraná, Brasil

bjb Brazilian Journal of Biology Braz. J. Biol. 1519-6984 1678-4375 Instituto Internacional de Ecologia São Carlos, SP, Brazil A planície alagável do Alto Rio Paraná (ARP) representa o último trecho do Rio Paraná em território brasileiro em que ainda existe um extensivo ecossistema do tipo rio-planície alagável. No entanto, a região sofreu intenso processo de desmatamento nas décadas passadas e mais da metade da extensão original da planície foi perdida com a formação do lago da usina hidrelétrica de Porto Primavera, o que pode ter resultado na extinção local de espécies. No presente estudo, comparou-se a lista de espécies de aves registradas no ARP antes da construção da referida usina (1926-1996) com aquelas registradas após este período (1999-2007) no âmbito do programa de Pesquisas Ecológicas de Longa Duração (PELD-sítio 6), com o objetivo de investigar características biogeográficas e ecológicas das espécies potencialmente extintas no local. Endemismo, proximidade das espécies de seus limites de distribuição geográfica, baixa tolerância a habitats alterados e especificidade de habitat podem estar associados à perda de espécies no ARP. A região representa uma importante oportunidade para a conservação e deve receber esforços para evitar a perda futura de espécies e de processos ecológicos. On the possible extinction of bird species in the Upper Paraná River floodplain, Brazil Sobre a possível extinção de aves da planície alagável do Alto Rio Paraná, Brasil Mendonça, LB.I,*; Lopes, EV.I; Anjos. L.II IPrograma de Pós-Graduação em Ecologia de Ambientes Aquáticos Continentais, Universidade Estadual de Maringá - UEM, Av. Colombo, 5790, PEA, Bloco G90, CEP 87020-900, Maringá, PR, Brazil IIDepartamento de Biologia Animal e Vegetal, Universidade Estadual de Londrina - UEL, CP 6001, CEP 86051-970, Londrina, PR, Brazil ABSTRACT The Upper Paraná River floodplain (UPR) represents the last stretch of the Paraná River in Brazilian territory where a river-floodplain ecosystem still exists. However, the region had been subjected to intense deforestation in previous decades, and more than half of the original floodplain has been lost due to the construction of the Porto Primavera dam, which may have resulted in the local extinction of species. In the present study, we compared the list of bird species recorded before the construction of Porto Primavera dam (1926-1996) to that gotten afterwards (1999-2007) under the Long-Term Ecological Research program (LTER-site 6). We aim to investigate biogeographical and ecological traits of species potentially lost in the UPR. Endemism, proximity to the edge of species' geographic range, low tolerance to human-altered habitats and habitat specificity were associated to the potential extinction of birds in the UPR. The region represents an important opportunity for conservation, and should be target of conservation efforts to avoid further loss of species and ecological processes. Keywords: local extinction, birds, Atlantic Forest, floodplain. RESUMO A planície alagável do Alto Rio Paraná (ARP) representa o último trecho do Rio Paraná em território brasileiro em que ainda existe um extensivo ecossistema do tipo rio-planície alagável. No entanto, a região sofreu intenso processo de desmatamento nas décadas passadas e mais da metade da extensão original da planície foi perdida com a formação do lago da usina hidrelétrica de Porto Primavera, o que pode ter resultado na extinção local de espécies. No presente estudo, comparou-se a lista de espécies de aves registradas no ARP antes da construção da referida usina (1926-1996) com aquelas registradas após este período (1999-2007) no âmbito do programa de Pesquisas Ecológicas de Longa Duração (PELD-sítio 6), com o objetivo de investigar características biogeográficas e ecológicas das espécies potencialmente extintas no local. Endemismo, proximidade das espécies de seus limites de distribuição geográfica, baixa tolerância a habitats alterados e especificidade de habitat podem estar associados à perda de espécies no ARP. A região representa uma importante oportunidade para a conservação e deve receber esforços para evitar a perda futura de espécies e de processos ecológicos. Palavras-chave: extinção local, avifauna, Floresta Atlântica, planície alagável. 1. Introduction The rate at which humans are changing natural land-scapes, in general terms, is much higher than that seen through the dynamics of disturbance in natural ecosystems (Tabarelli and Gascon, 2005), and habitat loss and fragmentation are perhaps the main factors associated to loss in biodiversity (Marini and Garcia, 2005; Tabarelli and Gascon, 2005; IUCN, 2008). The floodplain located at the border of the States of Paraná and Mato Grosso do Sul (Brazil), is within the last non-dammed section of the Paraná River in Brazil. This area, called in the present study as the Upper Paraná River floodplain (UPR), represents the last stretch of the Paraná River in Brazilian territory where a river-floodplain ecosystem still exists, and is one of the last well preserved areas of the Paraná River wetlands (Agostinho et al., 2004). However, the local extinction of species is potential, given that the region had been subjected to intense deforestation in previous decades due to human colonization (Agostinho, 1997; Campos and Souza, 1997). Moreover, the construction of the Porto Primavera hydroelectric plant has created a large water reservoir, which has possible implications on the dynamics of local plant and animal populations. Originally, the UPR stretched over nearly 480 km, especially over the right bank system of the river in the State of Mato Grosso do Sul. With the formation of the reservoir lake of the Porto Primavera hydroelectric plant (1998-2001), more than half of this ecosystem was lost. Even so, the remaining portion, extending roughly 230 km, represents a biodiverse ecosystem, which is considered a priority for conservation (MMA, 2003; Agostinho et al., 2004). This region has been designated a conservation unit by the Federal Government: the "Área de Proteção Ambiental das Ilhas e Várzeas do Rio Paraná". The mouth of the Ivinhema River (an important tributary of the Paraná River), also included in the area, belongs to the "Parque Estadual das Várzeas do Rio Ivinhema", a state park. The UPR is also included in the Atlantic Forest Biosphere Reserve, of the Unesco-MAB program. Since 1999, this area has been studied under the Long Term Ecological Research program identified as site 6 (LTER-site 6; Agostinho et al., 2004). LTER-site 6 comprises a large group of researchers studying social, physical and biological aspects of UPR; the avifauna is one of the groups of organisms studied. The avifauna of the UPR and adjacent areas is highly diverse due to the mosaic of habitats in the region; the aquatic, terrestrial and transitional environments form a complex mosaic. In addition, the UPR is located is a transition zone between the Atlantic Forest and the Cerrado (Ab'Sáber, 2003; Souza et al., 2004), and their respective endemic areas (Porzecanski and Cracraft, 2005). It is also influenced by the Chaco (Campos and Souza, 1997). The first ornithological records in the UPR date from 1920s (Sztolcman, 1926). Aftewards, Straube et al. (1996) organized an annotated checklist of the avifauna of the northwestern Paraná and bordering areas, including the UPR region. The paper of Straube et al. brings together previously information on species records, based on literature, museum specimens and their own field observations. In addition, short-term surveys of bird species were conduced as part of the environmental diagnostic for the construction of the Porto Primavera hydroelectric plant (Themag and Engea, 1994). After the construction of Porto Primavera dam (1998-2001), ornithological studies in the UPR have been carried out, under the LTER-site 6 program, since 1999 (Gimenes and Anjos, 2004; 2006; 2007; Loures-Ribeiro and Anjos, 2004; 2006; Mendonça et al., 2004; Mendonça and Anjos, 2006; ongoing studies). The list of birds recorded in those studies is presented in Gimenes et al. (2007), together with additional records made by Gimenes and collaborators; this list encompasses all records of bird species obtained under the LTER-site 6. Considering all inventories, 372 bird species are accounted for the UPR. Comparisons between historical data and recent inventories are important when assessing extinction processes (Ribon et al. 2003). In the present study, we compared the list of bird species recorded in the period from 1926-1996 to that gotten from 1999-2007 (referred here as currently recorded species; CR species). We aim to investigate biogeographical and ecological traits of species potentially lost (referred here as PL species), when these two lists are compared. 2. Material and Methods 2.1. Study area The section of the UPR and bordering areas considered in the present study, corresponds to the segment between the reservoir lake of the Porto Primavera hydroelectric plant and the upper mouth of the Ivinhema River (22º 32'S to 22º 59' S and 53º 08' W to 53º 4' W; 230 m a. s. l.). The region's climate is classified as Cfa (tropical-subtropical), with a mean annual temperature of 22 ºC (26 ºC in summer and 19 ºC in winter) and a mean annual rainfall of 1,500 mm (Centrais Elétricas do Sul do Brasil, 1986). Currently, the original forest cover of the UPR (seasonal semi-deciduous forest) is reduced to small remnants located in areas close to the Paraná River and its islands (Campos and Souza, 1997), in a matrix dominated by agricultural and pasture lands. The landscape of UPR is a complex mosaic that includes forest remnants (rarely exceeding 300 ha), stretches of riparian vegetation, marsh forests, buriti palm groves, shrubby vegetation, grasslands, and wetlands. Besides the segments of large rivers - such as the Paraná, Ivinhema and Baía (the latter situated completely within the floodplain) - floodplain lakes, secondary channels, over 100 islands, sandy and swampy beaches are found in the region. 2.2. Ornithological data The list of bird species found in the UPR and bordering areas prior to the formation of the Porto Primavera reservoir (1926-1996) was obtained in Themag and Engea (1994) and Straube et al. (1996). The list of birds recorded after this period (1999-2007) was obtained in Gimenes et al. (2007). Two features of the biogeographical distribution of birds were considered: 1) endemism and 2) the position of the UPR in relation to the edge of species' geographic range. Species with geographic distribution restricted either to the Atlantic Forest (ATL) or the Central South American (CSA) zoogeographical regions according to Parker III et al. (1996) were considered endemics. The position of UPR in relation to the edge of species' range was defined considering the following classes of distance: up to 100 km, 100-200 km, 200-500 km and over 500 km. Distances were estimated from species' range maps (Ridgely et al., 2007), by measuring the distance between the approximate central point of the area studied and the closest edge of species' range. This estimate was performed using the software ArcExplorer 9.2. For species whose distributions do not include the UPR (Ridgely et al., 2007), a zero value was adopted for the distance to their edge of geographic range, assuming that the recording of the species at the location represents a new limit for its range. The ecological traits considered were: 1) habitat use, 2) tolerance to habitat alteration, 3) habitat specificity, and 4) diet. Habitat use: species were classified as forest species, which occur in the interior and/or edges of forests; semi-open species, observed more often in non-forest habitats such as shrubby vegetation and open areas; species that inhabit both forests and semi-open habitats; aquatic species, whose feeding or reproduction depends directly on aquatic habitats. Classification was based mostly on Parker III et al. (1996). Tolerance to habitat alteration: species that can occur in human-altered habitats, such as second-growth forest and woodlands, pastures and agricultural lands, and second-growth scrub (habitats F15, N13 and N14 sensu Parker III et al., 1996) were considered tolerant to human-altered habitats. Habitat restriction: species that occur in only one habitat type according to Parker III et al. (1996) were considered habitat restricted. Diet: species were classified as omnivores, insectivores, carnivores, frugivores, or nectarivores according to Del Hoyo et al. (1992-2005). For species not included in Del Hoyo et al. (1992-2005), we considered diets reported by Ridgely and Tudor (1989, 1994), Sick (1997), and Isler and Isler (1999). A RxC test for independency (Chi-square test) was used to evaluate significance (alfa = 0.05) between species number in different categories when the expected frequencies were equal ot geater than five (Fowler and Cohen, 1986). We compared the proportions of each category for the CR bird species with the PL ones. 3. Results From the total of 372 bird species recorded to the UPR, 77 (21%) were not recorded in the period from 1999-2007. Those 77 bird species were considered here as possibly locally extinct (Appendix). The rates of endemic/non endemic species were significantly different for the CR and PL bird species groups (Chi-square = 14.2; DF = 1; P < 0.0001); endemic species are more likely to become extinct, as they were better represented in the PL group (Table 1). Regarding the position of the UPR in relation to the edge of species' range, there was a significant difference in the proportions of species in classes of distance (up to 100 km, 100-200 km, 200-500 km, and over 500 km) comparing CR and PL species (Chi-square = 52.8; DF = 3; P < 0.0001). Bird species close to the edge of their geographical range (up to 100 km) seem to be more extinction prone. In contrast, those that are far from their range limit (>500 km) seem more likely to persist in the UPR landscape (Table 1). The distribution of species within habitat categories differed between PL and CR groups (Chi-square = 9.36; DF = 3; P = 0.025). Species associated to semi-open habitats seem to be the ones more negatively affected by landscape alteration in the UPR; a higher proportion of species in this category was observed in the PL group (Table 1). The rates of species that are tolerant/not tolerant to human-altered habitats were also different between the PL and RC groups (Chi-square = 43.7; DF = 1; P < 0.0001). The PL group was composed mostly of not tolerant species while the CR group had a greater proportion of species that are tolerant to altered habitats (Table 1). Similarly, habitat specificity differed between PL and CR groups (Chi-square = 6.72; DF = 1; P < 0.01), with a greater proportion of habitat restricted species being observed in the former group (Table 1). The only ecological trait that did not show a significant difference between the two groups of species was diet (Chi-square = 0.838; DF = 4; P = 0.93). Similar proportions of frugivores, insectivores, carnivores, nectarivores and omnivores were observed in the PL and CR groups (Table 1). These tendencies (tolerance to human-altered habitats, habitat specificity, and diet) were also observed for each class of habitat use (forest, forest to semi-open, semi-open, and aquatic) individually (Chi-square; p < 0.05 for all tests). Species that displayed at least two of the traits considered in the present investigation (endemism, proximity to the edge of species' range, low tolerance to human-altered habitats, and habitat specificity) were frequent in the PL group (60%; Appendix). Four species, Tinamus solitarius (Vieillot, 1819), Philydor lichsteinsteini Cabanis and Heine, 1859, Charitospiza euscoma Oberholser, 1905, and Geositta poiciloptera (Wied, 1830) displayed all four traits. Only 8% of species in the PL group did not show any of these traits. With the exception of Tachyphonus coronatus (Vieillot, 1822), endemism was combined with other traits for all PL species: 61% of endemic birds analyzed were close to the edge of their ranges, 94% were considered not tolerant to human-altered habitats, 27% were habitat-restricted, and for 39%, endemism was combined with the first two traits. All habitat-restricted species and 81% of those found close to the edge of their ranges appeared to be not tolerant of human-altered habitats (Appendix). 4. Discussion The present study has demonstrated that endemism, proximity to the edge of species' geographic range, low tolerance to human-altered habitats and habitat specificity are all traits associated to the potential loss of species in the UPR. These features are frequently mentioned in the literature as being associated with increased extinction risk in birds (Stotz et al., 1996; Christiansen and Pitter, 1997; Goerk, 1997; Ribon et al., 2003; Gage et al., 2004; Kattan et al., 1994; Sodhi et al., 2004; Anjos, 2006; Lees and Peres, 2008). The fact that the study area is quite large makes it difficult to confirm extinction, particularly for some bird species that are difficult to detect. However, we believe that the species listed in the present study are probably locally extinct, or had their populations considerably reduced. Most species displayed at least two of the traits considered here; three of the four species that displayed all four traits (Tinamus solitarius, Charitospiza euscoma, and Geositta poiciloptera) are Near Threatened at the global level (IUCN, 2008). Endemism can be used as a criterion for identifying species at risk. Moreover, areas with a high number of endemic species (e.g. Atlantic Forest) are often considered priorities for conservation (Stotz at al., 1996; Myers et al., 2000; Silva et al., 2004; Bencke et al., 2006). Considering the fact that the UPR is in a transition zone between the Atlantic Forest and Cerrado, it is not a surprise that several species have range limits that are close to this region. This feature was shown to be an important factor in the group of PL species analyzed. Species at the edges of their ranges are likely more vulnerable to habitat loss and fragmentation; populations may be at their physiological and ecological limits at their distributional edge; they often present low densities, and thus could be particularly vulnerable to genetic and/or environmental stresses (Gaston, 2003; Sodhi et al., 2004). Of the ecological features, habitat specificity was a frequent trait among the species in the PL group. Habitat loss and fragmentation are strong forces driving to extinction, as have been argued by several authors (e.g. Debinski and Holt, 2000; Laurence, 2008), and species with narrow habitat requirements should be particularly sensitive to habitat loss and fragmentation (Kattan, 1994; Goerk, 1997; Henle et al., 2004). Low tolerance to human-altered habitats decreases the chances of species survival (Stotz et al., 1996), possibly due to variations in resources, such as food availability and nest sites. With regard to the four categories of habitat considered in the present study, species associated to semi-open habitats seemed to be the most affected by landscape modification in the UPR. The semi-open habitat was severely affected by the artificial lake of the Porto Primavera hydroelectric plant, which covered an extensive area of non-forested habitats. This could explain the high rate of semi-open species in the PL group. In addition, of the semi-open habitat PL species, 27% are endemic (all of them to the CSA zoogeographical region), 73% are close (up to 100 km) to edge of their geographic ranges, and 81% appear not to be tolerant to human-altered habitats. Although some species are likely to have been lost in the region, the UPR still supports a rich avifauna, including species of conservation concern at the regional or global levels, such as Harpyhaliaetus coronatus (Vieillot, 1817) (Mikich and Bérnils, 2004; IUCN 2008). Also, Crax fasciolata Spix, 1825, Anhima cornuta (Linnaeus, 1766), Ara ararauna (Linnaeus, 1758), and Ara chloropterus Gray, 1859, considered to be Endangered or Critically Endangered in the State of Paraná (Mikich and Bérnils, 2004) are currently found, in the mentioned State, mostly in the valley of the Paraná River. Data presented here highlights the importance of UPR for the biodiversity of the region. It has been suggested that bird extinctions in the Atlantic Forest could be associated to the loss of floodplains and lowland forests (e.g. Ribon et al., 2003). Indeed, well-preserved extensive river-floodplain environments such as the UPR are becoming scarcer in the Atlantic Forest region, and thus should be target of conservation efforts to prevent further loss of species and ecological processes. Moreover, where major zoogeographic zones meet, as occurs in the UPR where the Atlantic Forest and Central South America zones come into contact, diverse ecological communities can be found, and preserving such areas is a major global priority (Stotz et al., 1996). Acknowledgements - Financial support for this study was provided by CNPq (The National Council for Scientific and Technological Development, Brazil) through the LTER-site 6 program and research/doctorate grants. 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