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Frugivory and potential of birds as dispersers of Siparuna guianensis/Frugivoria e potencial de aves como dispersores de Siparuna guianensis.

1. Introduction

Seed dispersal is a process that exerts control over the density and distribution of plants in a range of environments (Fuentes, 2000), influencing colonization and maintenance of species diversity (Wang and Smith, 2002). In tropical environments up to 90% of plant species have fruit dispersed by animals (Howe and Smallwood, 1982),

Birds are important seed dispersal agents, mainly in understory (Gentry, 1982), where they have an important role in forest regeneration (Jordano et al., 2006). In the tropics, birds are among the main dispersers of tree pioneers species, being important in the early establishment of communities (Duncan and Chapman, 1999). Moreover, they contribute to the deposition of seeds in disturbed habitats (Wunderle, 1997) and initiation of secondary succession (Charles-Dominique, 1986).

Frugivorous birds are adapted to track, select, feed and digest fruit (Corlett, 2011). Among the neotropical frugivorous Passeriformes, Pipridae and Contigidae are the most specialized (Fleming and Kress, 2011). However, species of these families are rare in most parts of the Brazilian Cerrado (Bagno and Marinho-Filho, 2001; Marcal-Junior et al., 2009), where the seed dispersal is done mainly by generalists and opportunist species (Gottsberger and Silberbauer-Gottsberger, 2006).

Several factors determine the efficiency of a bird species as a seed disperser, like gape width (Wheelwright, 1985), visit frequency (Vazquez et al., 2005), time that the bird remained on the fruit-bearing plant (Pratt and Stiles, 1983), fruit handling behavior (Levey, 1988), gut transit time (Herrera, 1984) and post foraging movement (Westcott and Graham, 2000; Jordano et al., 2006). Due to these factors, different species of frugivorous birds have different efficiency in seed dispersal and environmental regeneration (Schupp, 1993).

This work aims to evaluate the potential of birds as dispersers of Siparuna guianensis in a semi deciduous forest fragment in central Brazil.

2. Material and Methods

2.1. Study area

The study was conducted in a 37 ha semi deciduous forest fragment (18[degrees] 57' 03" S; 48[degrees] 12' 22" W) in the municipality of Uberlandia, in central Brazil. The forest has around 96 tree species and a canopy of 15 to 20 m (Araujo and Haridasan, 1997). The climate in the region is classified as Aw according to Koppen, with rainy summer and dry winter (Rosa et al., 1991).

2.2. Study specie

Siparuna guianensis Aublet (Siparunaceae) is a woody species that occurs on the edge and in the interior of Cerradao, mainly in the understory (Oliveira and Felfili, 2005). This specie has a fruit with sweet aril that is very attractive to birds, which are its main seed dispersers (Valentini et al., 2010a). This specie is important because of its medicinal components used to treat stomach disorders, malaria, fevers and colic (Valentini et al., 2010b).

2.3. Phenology

A monthly phenological monitoring for S. guianensis was made between February 2011 and January 2012, covering the rainy and dry season. In a 400 m transect with 4 m width, 2 m on each side (Arantes, 2002; Melo et al., 2003), 10 individuals of S. guianensis bearing fruit were tagged and monitored. For each individual the fruit phenophase was registered, being noted the presence / absence of green and ripe fruit. A fruit was considered ripe when the ariled seed was exposed.

2.4. Frugivory and seed dispersal

Observations by plant-focal method were conducted in seven individuals of S. guianensis during April 2011. The observation sections occurred early in the morning (06:30h-10:30h) and afternoons (15:30h-17:30h), using a 8x40mm binoculars. The observers remained 10 m distant from the focal tree so as to not disturb bird visits.

For each effective visit (visit together with fruit consumption): (1) bird species; (2) number of fruits taken; (3) time that the bird spent on the plant, classified as: "1" - < 1 min, "2"- > 1 min and < 2 min, "3"- > 2 min and < 3 min, "4"- > 3 min < and 4 min, "5"- > 4 min; and (4) handling behavior, classified according to Schupp (1993) as: "swallow"--ingestion of the whole fruit, without damaging the seed; "bite"--taking out part of fruit aril; and "smash"--fruit consumption with seed damage were registered. The avifauna was taxonomically classified according to CBRO--Comite Brasileiro de Registros Ornitlogicos (CBRO, 2011), in relation to the feeding guild (Motta-Junior and Lombardi, 1990; Sick, 1997), to forest dependence ("dependent", "semi-dependent" and "independent"), and in relation to sensibility to habitat disturbance: "low", "medium" and "high" sensibility (Stotz et al., 1996).

The dispersal potential (DP), which measures the efficiency of a species as seed dispersers from the number of fruit taken and time spent on visits, was calculated for each bird species as follows (Equation 1):

DP = f/t .n (1)

being, f the mean number of fruits ingested undamaged per visit; t the mean time that the bird remained on the fruit-bearing plant; n the number of effective visits per hour.

3. Results

The fruiting period of Siparuna guianensis concentrated during the months of February, March and April.

Sixty nine (69) hours of observation were conducted in Siparuna guianensis, registering the consumption of fruit by seven bird species, all Passeriformes of four different families (Table 1). The Thraupidae family was represented by four species. Fifty seven per cent (n = 4) of the bird species registered are dependent of forest environments. In relation to the sensibility to habitat disturbance, no species was considered as highly sensitive, two were considered medium sensitive and all the others were low sensitive. Antilophia galeata was the only frugivorous bird, all the others were classified as omnivores.

A hundred and fifty three (153) effective visits were registered, two hundred and forty two (242) ariled seeds being taken, giving a mean of 1.6 + 1.3 fruit per visit. The peak of visitation was concentrated between 09:00 and 09:30 (Figure 1). Antilophia galeata made 41.83% (n = 64) of the total visits and consumed more than 42% (n = 91) of the fruit. Saltator similis was the second most frequent species (21.26%; n = 27), followed by Lanio penicillatus (20.47%; n = 26) and Dacnis cayana (18.90%; n=24). The most used handling behavior was "swallow" (48.36%) and bite (34.64%).

4. Discussion

Siparuna guianesis offers ripe fruits between December and April, at the end of the rainy season and the beginning of the dry season (Approbato and Godoy, 2006). This strategy allows the plant to attract dispersers, increasing the chance of seed dispersal (Melo et al., 2003). This dependence on dispersal agents is related, in some cases, with the increase of seed survival and establishment of seedlings over great distances from the mother plant (Murali, 1997).

Siparuna guianensis is a species of early secondary succession (Higuchi et al., 2006). Its fruit have small seeds (10 mm) and are produced in large quantities, which can result in a large removal rate and colonization in open areas (Francisco and Galetti, 2002). There is a functional relationship between the fruit size and the body size of frugivores (Kantak, 1979), e.g., small fruit (<10 mm) facilitate the accessibility by birds with different sizes (Melo et al., 2003), increasing fruit consumption. Gomes (2013) found this functional relationship between beak size and fruit size in seasonal forests in Cerrado.

Frugivorous birds are sensitive to habitat disturbance, especially the larger species (Gomes et al., 2004). The loss of some frugivorous species can have a detrimental impact on the composition of plant communities (Silva and Tabarelli, 2000). The low sensitivity to habitat disturbance observed in the fruit consumers of S. guianesis can be due to the conservation status of the habitats in which these species occur. In disturbed habitats there is a domain of less sensitive and generalist species, which are responsible for seed dispersal in these habitats.

The method used to measure dispersal potential provides a comparative index between the different species of fruit-eating birds, taking into account factors such as consumption rate, time spent and visit rate. In spite of this index not considering pos-feeding factors, such as gut transit effects and place of seed deposition, it can be useful to measure the quantitative component of seed dispersal (Schupp et al., 2010)

Antilophia galeata can be an important seed disperser, having the greatest dispersal potential among the fruit-eating birds of S. guianensis. Silva and Melo (2011) also registered Antilophia galeata eating fruit of S. guianensis. One of the factors that characterize an effective disperser is that the bird remains on the fruit-bearing plant for only the time necessary to eat the fruit, since a longer foraging time increases the chances of the bird dropping the seeds, defecating or regurgitating, below the parental plant crown (Pratt and Stiles, 1983; Motta-Junior and Lombardi, 1990).

Moreover, Antilophia galeata, being a frugivore, spends less time and energy foraging than generalist species (Foster, 1977; Melo and Oliveira, 2009), which makes it a better disperser. However, Antilophia galeata, being a territorialist species, may have a long distance dispersion. The male territories are around 1 ha (Marini and Cavalcanti, 1992), favoring the allelophaty and endogamy (Melo and Oliveira, 2009).

Dacnis cayana and Lanio penicillatus, in spite of being omnivorous, also have a high dispersal potential. Fruit consumption by generalist species is very common in Brazilian Cerrado (Macedo, 2002; Gottsberger and Silberbauer-Gottsberger, 2006; Silva and Melo, 2013), and is important for seed dispersal and regeneration of disturbed environments, since it excludes dependence on specialists frugivorous (Guedes et al., 1997). The generalists species cover a greater area while foraging among plants of the same and different species, carring seeds away from the parental plant and, consequently, allowing the seeds to escape competition and density-dependant mortality (Guedes et al., 1997; Melo and Oliveira, 2009).

Siparuna guianensis fruit were consumed by species of different feeding guilds and habitat use. This can be an important strategy for species that occur in regenerating environments, due to the fact of being less selective in relation to disperser birds, increasing the chances of effective seed dispersal.

http://dx.doi.org/10.1590/1519-6984.11413

Acknowledgements

We are very grateful for CAPES--Brazil and CNPQ Brazil for financial support and Daniella R. F. Teles and Luis Paulo Pires for helpful comments on this manuscript.

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Goncalves, VF (a) *, Silva, AM. (a), Baesse, CQ. (a) and Melo, C. (a)

(a) Instituto de Biologia, Universidade Federal de Uberlandia--UFU, Campus Umuarama, Bloco 2D, sala 28, CEP 38400 902, Uberlandia, MG, Brazil

* e-mail: vanessinha_fg@hotmail.com

Received: July 4, 2013--Accepted: December 12, 2013--Distributed: May 31, 2015 (With 1 figure)

Table 1. Description of bird species that consumed
Siparuna guianensis fruit.

Taxon                   Diet   FD    Sen

Pipridae
Antilophia galeata       F      D     M
Turdidae
Turdus leucomelas        O     SD     L
Thraupidae
Saltator similis         O     SD     L
Lanio penicillatus       O      D     L
Tersina viridis          O      D     L
Dacnis cayana            O     SD     L
Emberezidae
Arremon flavirostris     O      D     M

                        Handling behavior    Visit
Taxon                   (n of fruit eaten)    rate      DP

Pipridae
Antilophia galeata       SW (48), SM (16)     0.78    0.4788
Turdidae
Turdus leucomelas             SW (2)          0.03    0.0145
Thraupidae
Saltator similis             SM (27)          0.39
Lanio penicillatus        SW (6), B (20)      0.22    0.0593
Tersina viridis               B (1)           0.01       -
Dacnis cayana             SW (15), B (9)      0.35    0.1213
Emberezidae
Arremon flavirostris      SW (3), B (7)       0.07    0.0114
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Title Annotation:original Article
Author:Goncalves, V.F.; Silva, A.M.; Baesse, C.Q.; Melo, C.
Publication:Brazilian Journal of Biology
Date:May 1, 2015
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