Introduction
Ornithological studies in the Neotropical region have increased considerably in recent years (Xiao et al. 2017), but the basic aspects of the biology of many bird species remain limited. Among them are reproductive aspects, mainly lack of knowledge about nests and eggs (Heming et al. 2013, Jahn et al. 2017). Not all studies of avian breeding biology have given to these aspects the attention of practical and theoretical importance they deserve, such as incubation and nestling period (Skutch 1945).
The Gray-fronted Dove Leptotila rufaxilla ranges widely in South America with six recognized subspecies (Baptista et al. 2020). In Brazil, this species is widely distributed, and four subspecies are recognized (Piacentini et al. 2015). In southwestern Amazon (State of Acre), southeastern Colombia, eastern Ecuador, south Venezuela and north Brazil represent the limit of the distribution of L. r. dubusi (Baptista et al. 2020). In Acre L. rufaxilla inhabits the interior of the forest and is common to occur in open areas with plantations, where occurs in sympatry with its congener L. verreauxi (Guilherme 2016). Few data are available on the reproductive biology of L. rufaxilla, with some observations in northern Brazil (Oniki & Willis 1983), French Guiana (Tostain 1989), Surinam (Ingels 1981), Trinidad (Snow & Snow 1964) and Argentina (Bodrati & Salvador 2013, de la Peña 2019). Here we present new information on the breeding biology, such as nestling growth, of L. rufaxilla from a lowland forest in southwestern Brazilian Amazon.
Material and methods
We conducted fieldwork at the Zoobotanical Park (ZP) (09°57’08.9”S, 67°52’22.5”W) of the Federal University of Acre (UFAC), in Rio Branco, Brazilian state of Acre. The ZP is a forest fragment with an area of ca.100 ha surrounded by an urban matrix, and it is one of the largest urban forest fragments of the Rio Branco (Meneses-Filho et al. 1995, Souza et al. 2020). The vegetation is composed of successional forests of varying ages dominated by the cycle of mass mortality and succession of the bamboo Guadua weberbaueri, and dense understory with many vine tangles (Meneses-Filho et al. 1995, Silveira 1999). The region’s climate is humid tropical, with a dry season (May-October) and a rainy season (November-April) (Duarte 2006). The avian assemblage of the ZP is composed by 150 birds species distributed over 36 families, and some species are migratory and others have restricted geographical distribution (Guilherme 2001).
We found the nests during non-systematic observations made between 2012 and 2014. We monitored all nests found, irrespective of stage, until they became inactive. We measured eggs and nestlings using an analogue calliper (0.05 mm precision) and millimeter ruler, respectively. We weighed eggs and nestlings using a Pesola® scale with a capacity of 100 g and accurate to the nearest 1 g. We collected nests after they became inactive and deposited them in the collection of the UFAC ornithology laboratory. We described the nests according to the standardized scheme proposed by Simon and Pacheco (2005).
We calculated the incubation period from the date the last egg was laid until the last chick hatched. Post-hatching, we measured the mass of nestlings every two days to minimize our impact on nests. We considered the nestling development period based on the hatching of the first nestling (day 0, see Oniki & Willis 2001) and the abandonment of the nest by the second chick. We estimated growth following Ricklefs (1967) using the equation:
W(t) = A / (1+e[- K(t - ti)]
Where W(t) is the mass of the nestling at age t, A is the asymptote of the growth curve, K is the constant growth rate and ti is the inflection point of the growth curve. We run the equation in the R software version 3.5.1 (R Core Team 2018). We applied the Mayfield (1961) method to calculate reproductive success rates and determined apparent success as the ratio between the number of successful nests and the total number found (Jehle et al. 2004).
We searched for records of active L. rufaxilla nests, including those with nestlings on the Brazilian Wikiaves site (http://www.wikiaves.com.br/) and eBird site (http://www.ebird.org), up to 29 June 2020. We verified the date, location, the author, and the content of each photograph (nests with eggs or nestlings). For the purposes of the study, we considered all the photographs from all localities, except those of a given nest taken on the same or subsequent days. We compiled a list of the number of records per month over the course of the year, including active nests and nests with nestlings, to determine the period of the species’ breeding season. Citizen science plays an especially important role in the compilation of data on the natural history of bird species (Tewksbury et al. 2014, Turnhout et al. 2016).
Results
We found five nests in ZP (one in February 2012, two in January 2013, one in August, and one in September 2014), which all were active. All nests were constructed in open areas or at the edge of forest on different substrates. Two nests were built in forks of Theobroma grandiflorum (Fig. 1a, b) and three nests in tangled vegetation at the edge of forest, which we did not identify the support plants. On average, nests were placed 1.90 m above ground (range 1.50-2.50 m). We found all nests with eggs. Most nests were built of dry leaves, pliable blades of dry grass, plants tendril and many sticks conformed to the simple / platform type sited in the fork of thin branches or over the accumulation of dry leaves among the vegetation at the forest edge (Figs. 1c, d, e). Mean measurements of nests were height of the external wall = 10 cm (n = 1), diameter 13.5 ± 2.1 cm (12-15 cm; n = 2), depth = 3 ± 1.4 cm (2-4 cm; n = 2) and mass = 44.61 g (n = 1).
The clutch size was two eggs in all nests. Eggs were predominantly white and elliptic shape (Fig. 2a). Mean eggs (n = 9) mass was 6.1 ± 1.1 g (5-7 g) and size 28.4 × 20.2 ± 1.3-0.4 mm (27-31 × 20-21 mm). In nest 5, female laid eggs in consecutive days. Of all the nests monitored, eggs of nests 2 and 3 were failed to hatch by predation (e.g., Fig. 2b).
We recorded the longest incubation period of 15 days based in one nest. Daily nest survival rate showed there is 60% chance that a nest survives from one day to the next. Daily survival rate during the incubation period was 90%. Mayfield success during the incubation period was 20%, assuming duration of 15 days. Apparent success was 56% in the incubation period.
We monitored the development of five nestlings (two in March 2012, two in September, and one in October 2014) after approximately one and four days from nests 1, 4 and 5 (Fig. 3). Nestlings hatch with dark pink skin, white plumes all over the body and eyes closed (Fig. 2c). After four or five days, the eyes are slightly open, the skin darkens, and the feathers of the remiges start to develop (Fig. 2d). Minimum hatch weight was 10 ± 2 g (n = 3) (8-12 g), and nestling weight reached a mean 13-29 g after only 4 days, 40 g on day 6 (Fig. 2e) and 62 g on day 14 (Fig. 2f, g), the heaviest recorded of any nestling (Fig. 3, Nest 1). All nestlings from nests 4 and 5 were infected with maggots (Diptera) under skin on the head. Chicks fledged after day 14. One chick from nest 4 fledged with ten days. We ringed three chicks in the nest (codes L-84948, H-84945 and M-29021). The longest nestling period was 14 days and chicks fledged at a mean mass of 56 ± 6 g (50-62 g, n = 3) (Figs. 2g, 3). The constant growth rate (K) of the nestlings was 0.40 ± 0.05 (0.28-0.47) with a growth asymptote of 60.7 ± 18.9 g (53.89-71.31 g) (Fig. 4). Daily survival, Mayfield success and apparent success were 100% for nestling period, assuming chicks remained in the nest for 14 days.
We found active nests in January (2), February (1), August (1) and September (1) (Fig. 5) in ZP. From Brazilian Wikiaves and eBird sites we obtained records of 28 active nests of L. rufaxilla (20 of which contained eggs and eight with nestlings) from ten of the 26 Brazilian states and from French Guiana, Peru and Bolivia between 2005 and 2019. Photographs of active nests were found from all the months of the year except July and August (Fig. 5), although most records were obtained between September-December and February-March (82.1%, n = 23) (Fig. 5). Most the records (n = 14) were obtained in Brazil’s North and Southeast region, with five from the Northeast, four from Midwest and one from South regions. We obtained two records of nest with eggs and nestlings in French Guiana, one with eggs in both Peru and Bolivia.
Discussion
Despite Leptotila rufaxilla to be commonly found within the forest (Ingels 1982, Schulenberg et al. 2010), in ZP this species appears to nest in open areas with cultivated plants or in forest edge. Overall, the characteristics of the breeding were similar to those recorded for many Neotropical Doves (Skutch 1949, Snow & Snow 1964, Marini et al. 2010, Lima et al. 2019). The shape and dimensions nest of L. r. reichenbachii in Argentina (Bodrati & Salvador 2013) and L. r. rufaxilla in north Brazil (Oniki & Willis 1983) were similar to those found in this work, like “shallow platforms”. This nest type is typical of many Columbidae, e.g., Geotrygon montana (Ingels 1981), L. verreauxi (Lopes et al. 2013) and Paraclaravis mondetoura (Blomberg 2020). The height of the nests above ground was consistent with descriptions for L. rufaxilla in Argentina (Bodrati & Salvador 2013, de la Peña 2019), and in French Guiana, where this species as well build its nests in fruit trees or over the accumulation of dry leaves (Tostain 1989).
Eggs and nestling characteristics, as well as the incubation time and nestling period, were all similar to reported in Suriname (Hellebrekers 1942, Ingels 1981), French Guiana (Tostain 1989), Argentina (Bodrati & Salvador 2013, de la Peña 2019) and for P. mondetoura in southeastern Ecuador (Blomberg 2020). The sexual dimorphism absent in L. rufaxilla did difficult us to identify if parental care was performed by the male or the female in ZP.
However, the alternation on egg incubation and parental care of the chicks was observed in French Guiana (Tostain 1989) as well as for G. montana (Skutch 1949) and P. mondetoura (Blomberg 2020). Regarding the growth rate of nestlings, ours are the first calculations for L. rufaxilla. Our rate was 0.06 lower to the values calculated for four individuals of Columbigallina talpacoti in Suriname, however the growth asymptote was greater (Haverschmidt 1953). Neotropical birds weighing less than 100 g usually have average values of K around 0.38 (Ricklefs 1976). Therefore, L. rufaxilla with mean weight of 130-178 g (Oniki 1978, Silva et al. 1990, Marini et al. 1997, Piratelli et al. 2001) tends to present values of constant growth rate greater than some Passeriformes (Ricklefs 1976, Oniki & Ricklefs 1981).
Predation of L. rufaxilla nests has also been observed in French Guiana (Tostain 1989). This author reported that a Black-faced Hawk Leucopternis melanops attacked a nest with two nestlings. Previous study has shown that adult individuals of L. rufaxilla were preyed upon by Micrastur ruficollis and M. semitorquatus falcons in Guatemala (Thorstrom 2000), and this reveals a susceptibility of L. rufaxilla to predation in the nest, as well as the young, mainly for inhabiting the interior of the forest, such as these falcons. Open nests tend to be more preyed on near to the edge (Marini 2017) or in open areas in relation into the forest (Oniki 1979, Pestana et al. 2020). Certainly, nests characteristics and nesting site where unfavourable to reproductive success complete of L. rufaxilla in ZP. Nesting success of some Neotropical doves are lower than ours results, in example, in Costa Rica ranging from 22 a 33% (Skutch 1985). All nestlings from nests sited in the edge of forest in ZP were probably parasitized by Diptera insects such as observed in Trinidadian birds (Dodge & Aitken 1968). These authors described that L. rufaxilla was parasited by maggots of Philornis angustifrons, and two other species, P. sanguinis and P. downsi for individuals of Leptotila sp. The larvae of these insects also parasitized nestlings of Zenaidura macroura in Louisiana, USA, in which the maggots were scattered over all body surfaces (Glascow & Henson 1957).
Our data, although few, showed that in the ZP active nests begin to appear in the late dry season, that is, August-September, continuing throughout the rainy season (nests in January and February) in Acre (Duarte 2006). That is, that the species begins to reproduce in transition from the dry to the rainy season, extending on through the rainiest months of the year. Photographic records obtained through citizen science showed that this pattern is typical of the rest of Brazil, including the records from French Guiana and Peru. That is, that the species begins to reproduce in transition from the dry to the rainy season (September) in Brazil, extending on through the rainiest months of the year (October-April) (Gan et al. 2004), where most of photographic records were made. When begin reproduction at the end of the dry period, L. rufaxilla with a diet of fruits and seeds (Wilman et al. 2014), is benefited by the increased availability of both these resources (Haugaasen & Peres 2005, 2007) in Amazon that guarantees the feeding of the chicks. Previous studies on breeding records of L. rufaxilla indicate that this species breeds mainly in the rainy season in French Guiana (Tostain 1989), Suriname (Ingels 1981), Brazil (Oniki & Willis 1983), and Argentina (Bodrati & Salvador 2013).