Frugivoria Por Aves Em Bordas De Fragmentos Florestais, Uberlândia-Mg

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Frugivoria Por Aves Em Bordas De Fragmentos Florestais, Uberlândia-Mg 1 FRUGIVORIA POR AVES EM BORDAS DE FRAGMENTOS FLORESTAIS, UBERLÂNDIA-MG. SUÉLEN AMÂNCIO 1,2 e CELINE DE MELO 1 RESUMO. O objetivo do trabalho foi verificar quais são as principais aves que visitam plantas zoocóricas em bordas de ambientes florestais e classificar o frugívoro em dispersor ou predador para avaliar seu potencial de dispersão. O trabalho foi realizado em bordas de ambientes florestais do Parque do Sabiá e Estação Ecológica do Panga entre agosto/2006 a abril/ 2007. A fenologia foi realizada quinzenalmente para as espécies de plantas com frutos. As observações das aves visitantes foram realizadas nos períodos da manhã e tarde para aquelas espécies de plantas que apresentavam no mínimo cinco indivíduos com frutos maduros. Miconia albicans frutificou entre out/2006-jan/2007, foram observados apenas registros ocasionais de Turdus leucomelas e Thraupis sayaca. Tococa formicaria frutificou entre ago-dez/2006, porém não foi registrada visita com consumo de frutos por aves. Miconia chamissois frutificou entre jul-set/ 2006 e foi visitada por 21 espécies de aves (N=118 visitas) em 33,5 horas. Thraupis sayaca (17,8%) foi a espécie que mais visitou Miconia chamissois seguida por Pitangus sulphuratus (15,25%). Os maiores potenciais de dispersão foram encontrados para Colaptes melanochloros (0,21), Turdus amaurochalinus (0,21) e Turdus rufiventris (0,19). Miconia theaezans frutificou entre os meses de fev-mar/2007 e foi visitada por 20 espécies de aves (N=256 visitas) em 26 horas. Pitangus sulphuratus (27,63%) foi a espécie que mais visitou Miconia theaezans, seguida por Thraupis sayaca (12,45%) e Turdus amaurochalinus (7,78%). Os maiores potenciais de dispersão em Miconia theaezans foram encontrados para Turdus leucomelas (0,25), Icterus cayanensis (0,21) e Antilophia galeata (0,21). Em áreas perturbadas, verifica-se a predominância de aves generalistas (57%), como o verificado para Miconia chamissois e Miconia theaezans. As espécies de plantas estudadas são consideradas pioneiras e não são seletivas para seus dispersores, pois possuem frutos com sementes pequenas, coloração atrativa e cascas delgadas. No entanto, a segregação na oferta de frutos, sua disponibilidade durante todo o ano e a morfologia pouco seletiva, as tornam importante fonte de recurso para manutenção da avifauna local. Palavras-chave: frugivoria, bordas de ambientes florestais, avifauna. 1 Instituto de Biologia da Universidade Federal de Uberlândia, Rua Ceará S/N, Bloco 2D, Campus Umuarama, 38400-902, Uberlândia-MG, [email protected]. 2 Bolsista do CNPq, projeto nº B-023/2006. 2 ABSTRACT. The goal of this study was to identify the most important bird visitors of animal-dispersed plants in forest environment edges, classify the frugivorous species as dispersers or predators and evaluate their dispersion potential. This work was carried out at edges of forest environments located in the Parque do Sabiá and the Estação Ecológica do Panga (Uberlândia, Minas Gerais, Brazil) between August of 2006 and April of 2007. The phenological study of the fruit-bearing plants was conducted fortnightly. The observation of the visiting birds was performed in the morning and afternoon periods for those plant species which presented at least five individuals with ripe fruits. Miconia albicans bore fruits between October of 2006 and January of 2007 and only occasional visits by Turdus leucomelas and Thraupis sayaca were registered. Tococa formicaria presented fruits between August and December of 2006 but no visits with fruit consumption by birds were recorded (3 hours). Miconia chamissois had fruits between July and September of 2006 and was visited by 21 bird species (N=118 visits) in 33.5 hours. Thraupis sayaca (17.8%) was the most common visitor of Miconia chamissois, followed by Pitangus sulphuratus (15.25%). The highest dispersion potentials were found for Colaptes melanochloros (0.21), Turdus amaurochalinus (0.21) and Turdus rufiventris (0.19). Miconia theaezans bore fruits between February and March of 2007 and was visited by 20 bird species (N=256 visits) in 26 hours. Pitangus sulphuratus (27.63%) was the most common visitor of Miconia theaezans, followed by Thraupis sayaca (12.45%) and Turdus amaurochalinus (7,78%). The highest dispersion potentials for Miconia theaezans were found for Turdus leucomelas (0.25), Icterus cayanensis (0.21) and Antilophia galeata (0.21). In areas altered by man, there is a predominance of generalist birds (57%), as observed for Miconia chamissois and Miconia theaezans. The studied plants are considered precursor species and are not selective towards their dispersers because they bear small-seeded, attractive-colored, thin-peeled fruits. Nevertheless, the seasonal segregation of the fruit offer, its presence throughout the year and the little selective morphology make them an important resource for the maintenance of the local bird fauna. Keywords: frugivory, forest environment edges, bird fauna. 3 INTRODUÇÃO As florestas tropicais apresentam altas proporções de espécies vegetais com A dispersão de sementes por sementes dispersas por animais, inclusive o animais pode aumentar o sucesso Cerrado (Manhães, Assis, Castro, 2003; reprodutivo das plantas (Talora & Melo, 2003). Diversos estudos têm Morellato, 2000) e as aves frugívoras relatado a utilização de frutos como apresentam papel relevante nos processos recurso alimentar para as aves, onde altas de dispersão de muitas espécies vegetais taxas de consumo e visitas demonstram a (Figueiredo, Motta-Júnior; Vasconcelos, importância deste recurso para as espécies 1995; Francisco & Galetti, 2002a). Quando frugívoras, assim como para as generalistas atuam como agentes dispersores de (Motta-Junior & Lombardi, 1990; sementes, auxiliam de modo efetivo na Francisco & Galetti, 2001; Francisco & regeneração de florestas, especialmente Galetti, 2002a; Cazetta et al., 2002; devido à sua abundância e freqüência na Marcondes-Machado & Rosa, 2005; ingestão de sementes (Galetti & Stotz, Krügel, Burger, Alves, 2006; Melo, 1996). Assim, ao carregarem as sementes 2003b). das matas para as áreas impactadas, podem A grande oferta de frutos promover a sua reconstituição (Argel-de- aumenta a chance de visitação na planta, Oliveira, Castiglioni, Souza, 1996). atraindo em sua maioria aves generalistas, Um fator determinante na taxa de que se alimentam ocasionalmente deste visitação em plantas zoocóricas é a oferta recurso, o que pode diminuir a taxa de frutos maduros. Muitas espécies de dispersão. Plantas que produzem uma plantas no Cerrado têm mostrado um perfil quantidade menor de frutos, porém mais de assincronia na frutificação, onde ricos em nutrientes, atraem frugívoros algumas frutificam no período chuvoso e específicos, aumentando desta forma, a outras na seca (Snow, 1965; Morellato et chance de dispersão da espécie (Foster, al., 1989; Verdú & García-Fayos, 1994; 1977; Manhães, Assis, Castro, 2003; Melo, Melo, 2003). Quando há uma diminuição 2003). na oferta de frutos por uma espécie, inicia O comportamento dos frugívoros a oferta em outra, este fato desvia o dispersores e o seu papel na manutenção e interesse do frugívoro, mas o mantém fiel regeneração ambiental aumentam o àquele ambiente (Melo, 2003a). interesse na conservação das comunidades de aves como forma de auxílio à tomada de 4 decisão em planos de manejo de áreas (MG). O Parque do Sabiá está localizado degradadas (Francisco & Galetti, 2002b). no perímetro urbano (18º57’S e 48º14’W; No município de Uberlândia 890m), possui remanescentes florestais de (MG), o alto nível de desmamamento das Matas de Galeria, Mesófila e Cerradão, áreas naturais adjacentes à zona urbana é que ocupam área aproximada de 30 ha, um causado principalmente pelo crescimento conjunto hidrográfico composto por três populacional acelerado, industrialização e nascentes que abastecem sete represas e o aumento das fronteiras agrícolas. Brito & originam um grande lago e sete outros Prudente (2005) afirmam que apenas 17% menores, uma praia artificial com 300m de da vegetação nativa do município está extensão, um zoológico com animais em preservada, sobrando assim apenas alguns cativeiro de dezenas de espécies, uma fragmentos isolados. Assim, estudos de estação de piscicultura e área de recreação frugivoria e dispersão de sementes, (Prefeitura Municipal de Uberlândia). A especialmente, daquelas espécies que Estação Ecológica do Panga (19°09’- auxiliam na regeneração ambiental, como 19°11’S e 48°23’-48°24’W; 800m) - está as pioneiras, são essenciais para subsidiar localizada no município de Uberlândia, ações de manejo. MG, pertence a Universidade Federal de O objetivo do trabalho foi Uberlândia e possui uma área total de verificar quais espécies de plantas 409,5ha, sendo a área florestal (Cerradão, zoocóricas oferecem frutos em bordas de Mata Mesófila e Mata de Galeria) entorno ambientes florestais e quais são as de 15ha. Dista do centro da cidade principais aves que as visitam, e assim aproximadamente 30km (Schiavini & classificar o frugívoro, de acordo com seu Araújo, 1989), e faz limite com comportamento, em dispersor ou predador propriedades rurais, cujas áreas são para avaliar seu potencial de dispersão. principalmente destinadas à pastagem. As áreas de estudo estão incluídas MATERIAIS E MÉTODOS no Bioma Cerrado (sensu lato), que é composto por formações florestais, Área de Estudo: savânicas e campestres (Eiten, 1990). O clima da região é Aw, segundo a A coleta de dados foi realizada em classificação de Köppen, possui duas áreas: 1) Parque do Sabiá e 2) Estação sazonalidade
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