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BOSQUE 32(1): 39-45, 2011Seed <strong>dispersal</strong> <strong>by</strong> <strong>birds</strong> <strong>in</strong> <strong>the</strong> forest <strong>of</strong> ChiloéTable 1. The two tree species studied <strong>in</strong> <strong>the</strong> temperate ra<strong>in</strong>forest<strong>of</strong> sou<strong>the</strong>rn Chile. Their taxonomic assignment, life form, foresthabitat, flower<strong>in</strong>g period, fruit<strong>in</strong>g period and fruit and <strong>seed</strong> characteristicsare <strong>in</strong>dicated.Dos especies de árboles estudiados en el bosque del sur deChile. Se <strong>in</strong>dica su filiación taxonómica, forma de vida, hábitat del bosque,periodo de floración, período de fructificación y características delos frutos y semillas.CharacteristicsLumaapiculataAextoxiconpunctatumFamily Myrtaceae AextoxicaceaeLife form Tree TreeForest habitat Edge InteriorFlower<strong>in</strong>g period Autumn SummerFruit<strong>in</strong>g period W<strong>in</strong>ter AutumnFruit type Berry DrupeFruit color Black BlackFruit mass (mg) 300 300Seed mass (mg) 10 260Seed per fruit 4-7 1Ancud (Quempillén). This patch was located at less than50 m from <strong>the</strong> coastl<strong>in</strong>e, adjacent to highway Ruta 5 andclose to <strong>the</strong> Nor<strong>the</strong>rn <strong>of</strong> Puente Pudeto (41° 53’ S; 73° 50’W). This A. punctatum fragment has an estimated area <strong>of</strong>18 ha, and is <strong>the</strong> only patch > 10 ha <strong>in</strong> <strong>the</strong> study area. Theedges <strong>of</strong> <strong>the</strong> patch have recently been colonized <strong>by</strong> exoticshrubs, particularly Ulex europaeus L. (Papilionaceae) andCytisus scoparius L. (Papilionaceae).Identification and abundance <strong>of</strong> <strong>birds</strong>. Potentially frugivorous<strong>birds</strong> were recorded and identified <strong>by</strong> direct observationwith b<strong>in</strong>oculars along a 2 km long transect, runn<strong>in</strong>gthrough <strong>the</strong> riparian vegetation <strong>of</strong> Biological Station “SendaDarw<strong>in</strong>”, which presented L. apiculata adult established<strong>in</strong>side <strong>the</strong> remnant forest <strong>of</strong> A. punctatum (“olivillo”). Over10 days, transects were repeated between April and May.Transects were performed <strong>by</strong> walk<strong>in</strong>g very slowly andstopp<strong>in</strong>g irregularly <strong>in</strong> order to observe and identify <strong>the</strong>potentially frugivorous <strong>birds</strong>. Each transect was performedover a period <strong>of</strong> at least three hours, approximately.We considered a bird species as potentially frugivoreswhen its mouth gape was at least as large as <strong>the</strong> meanfruit diameter <strong>of</strong> L. apiculata and A. punctatum (Armestoet al. 1987). In this study, <strong>the</strong>re were no narrow mou<strong>the</strong>d<strong>birds</strong> consum<strong>in</strong>g fruits, although <strong>the</strong>y may eventually be<strong>seed</strong> dispersers (see Armesto et al. 1987, Correa et al.1990, Rozzi et al. 1996, and Díaz 2005 for more detailson frugivorous bird species). There are o<strong>the</strong>r potentiallyfrugivorous vertebrates identified <strong>in</strong> secondary forests <strong>of</strong>Chiloé, for example <strong>the</strong> marsupial Dromiciops gliroides(Microbio<strong>the</strong>ria: Microbio<strong>the</strong>riidae) (Amico et al. 2009),which will not be studied <strong>in</strong> this opportunity.Quantitative <strong>component</strong> <strong>of</strong> disperser <strong>effectiveness</strong>. Fruitconsumption <strong>by</strong> <strong>birds</strong> was observed dur<strong>in</strong>g visits to 10isolated trees <strong>of</strong> L. apiculata with abundant fruit crops <strong>in</strong>an area <strong>of</strong> 2 km 2 <strong>in</strong> “Senda Darw<strong>in</strong>”. The order <strong>of</strong> <strong>the</strong> fieldobservations <strong>of</strong> <strong>the</strong> trees was always <strong>the</strong> same. Consumptionon L. apiculata was recorded over 13 consecutive days <strong>in</strong>May and <strong>the</strong> observations were performed between 08:00and 16:00 h, with a total <strong>of</strong> 24 hours.To record fruit consumption on 14 A. punctatum trees,over 10 days between April and May, direct observationswere performed. Dur<strong>in</strong>g this period, A. punctatum treespresent <strong>the</strong>ir maximum crop <strong>of</strong> ripe fruits. Complet<strong>in</strong>g atotal <strong>of</strong> 20 hours on A. punctatum, observations were madeon clear days between 08:00 and 10:00 h, when <strong>birds</strong> have<strong>the</strong>ir highest activity levels <strong>in</strong> Chiloé (Sabag 1993).In both tree species, we recorded <strong>the</strong> number <strong>of</strong> <strong>birds</strong>visit<strong>in</strong>g each L. apiculata and A. punctatum trees per hour,and <strong>the</strong> number <strong>of</strong> fruits <strong>in</strong>gested per hour. To estimatehow <strong>seed</strong>s are dispersed per hour, <strong>the</strong> number <strong>of</strong> <strong>birds</strong>visit<strong>in</strong>g per hour was multiplied <strong>by</strong> <strong>the</strong> number <strong>of</strong> fruits<strong>in</strong>gested per visit. To obta<strong>in</strong> <strong>the</strong> number <strong>of</strong> L. apiculata<strong>seed</strong>s dispersed per hour it was considered that each fruitconta<strong>in</strong>ed four <strong>seed</strong>s (table 1). The A. punctatum fruitsconta<strong>in</strong> one <strong>seed</strong>.We assumed that <strong>the</strong> frugivorous <strong>birds</strong> are legitimate<strong>seed</strong> dispersers dur<strong>in</strong>g austral w<strong>in</strong>ter because <strong>the</strong>re is<strong>in</strong>direct evidence to <strong>in</strong>dicate this (Correa et al. 1990,Hernández 1995, Willson et al. 1996c, Figueroa andCastro 2002). Specifically, studies <strong>in</strong> L. apiculata havedemonstrated that <strong>seed</strong>s are not digested <strong>by</strong> frugivorous<strong>birds</strong>, and its <strong>seed</strong>s require that <strong>the</strong> fruit pulp be digestedpreviously <strong>in</strong> order to germ<strong>in</strong>ate (Figueroa and Castro2001). Evidence also shows that A. punctatum <strong>seed</strong>s arenot digested and germ<strong>in</strong>ation is not ceased <strong>by</strong> frugivorous<strong>birds</strong>: <strong>seed</strong>s obta<strong>in</strong>ed from fruits germ<strong>in</strong>ated to <strong>the</strong> sameextent as those <strong>seed</strong>s <strong>in</strong>gested <strong>by</strong> <strong>birds</strong> 1 .RESULTSIdentification and abundance <strong>of</strong> <strong>birds</strong>. Four bird specieswere recorded as potential L. apiculata fruit consumers(table 2). Turdus falcklandii was significantly <strong>the</strong> mostabundant (118 <strong>in</strong>dividuals), followed <strong>by</strong> Phytotoma raraMol<strong>in</strong>a (Phytotomidae), Colaptes pitius Mol<strong>in</strong>a (Picidae)and Curaeus curaeus Mol<strong>in</strong>a with 26, 5, and 2 <strong>in</strong>dividuals,respectively (χ 2 = 99.1; P < 0.001). The frugivores found<strong>in</strong> <strong>the</strong> “olivillo” forest patch were T. falcklandii (1,760<strong>in</strong>dividuals) and C. araucana (300 <strong>in</strong>dividuals) (table 2).Here, T. falcklandii was significantly more abundant thanC. araucana (χ 2 = 590.1; P < 0.001).Quantitative <strong>component</strong> <strong>of</strong> disperser <strong>effectiveness</strong>. Turdusfalcklandii was <strong>the</strong> ma<strong>in</strong> potential frugivore visit<strong>in</strong>gL. apiculata trees, constitut<strong>in</strong>g 72 % <strong>of</strong> <strong>the</strong> feed<strong>in</strong>g visitsrecorded (n = 53) at a rate <strong>of</strong> 2.2 feed<strong>in</strong>g visits per hour1M Salvande: data not published.41

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