Research Article |
Corresponding author: Marcela Osorio-Beristain ( mosorio@uaem.mx ) Academic editor: Luis Fabio Silveira
© 2018 Marcela Osorio-Beristain, Angeles Rodríguez, Cristina Martínez-Garza, Raúl Ernesto Alcalá.
This is an open access article distributed under the terms of the Creative Commons Attribution License (CC BY 4.0), which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Citation:
Osorio-Beristain M, Rodríguez A, Martínez-Garza C, Alcalá RE (2018) Relating flight initiation distance in birds to tropical dry forest restoration. Zoologia 35: 1-7. https://doi.org/10.3897/zoologia.35.e12642
|
Flight initiation distance (FID), defined as the distance at which an individual flees from an approaching predator, might depend on how the individual perceives the risk of being predated. Using a standardized walking approach method on focal bird individuals, we investigated whether different levels of vegetation cover (habitat) influence the perception of predation risk. To do this, we worked in an area of tropical dry forest in central Mexico that is currently part of a restoration ecology experiment. We hypothesized that restoration decreases individual’s predation risk perception by increasing the complexity of the vegetation cover. The escape responses of three tropical birds with different diets and foraging strategies were also contrasted. There was no effect of habitat on FID, suggesting that birds in both habitats perceived predation risk in a similar manner. There was, however, a difference in FID among species: the Golden-cheeked Woodpecker tolerated closer human presence before flight than the Inca Dove and Streak-backed Oriole. This difference is likely due to the use of an alternative avoidance strategy of this species, which uses trunks for hiding. To decrease birds’ perceived predation risk, restoration intervention plans should include a mosaic of larger excluded plots located near relatively well-conserved sites to increase the area covered by vegetation.
Escape from predators, foraging strategies, habitat quality, predation risk, tropical birds
Predation risk is one of the main selective forces shaping animal behavior (
Fleeing is a main predator avoidance strategy. However, it involves large potential costs due to the energetic cost of flight itself and the many costs associated with abandoning fundamental activities such as courtship‚ breeding‚ and foraging (
Flight initiation distance (FID), or the distance at which potential prey initiates flight when approached by a predator (
The study of escape behavior has an important potential role in evaluating habitat quality within the framework of restoration ecology. Restoration ecology not only aims for the recovery of biodiversity per se, but more broadly aims to re-establish natural processes reduced or eliminated by human-induced disturbance. Several studies have shown that after eliminating anthropogenic disturbance in an area, the structural complexity of vegetation (i.e. density, biomass, vertical strata, percent cover) increases by natural succession, from secondary vegetation to mature forest (
Animals respond to approaching humans similarly to terrestrial predators (
The Sierra de Huautla Biosphere Reserve is a federally protected area (ca. 59 030 ha) located in the southern part of the state of Morelos, Mexico. It borders the states of Guerrero and Puebla (18°20’10”, 18°34’20” N and 98°51’20”, 98°08’15” W). The topography is variable and elevation ranges from 900 to 1,300 m. The mean annual temperature is 24.5 °C and the average total rainfall is 850 mm, with peak rainfall occurring between June and October. Climate is classified as tropical subhumid with summer rains (CONAGUA, Gerencia Regional Balsas). The original vegetation is tropical dry forest (
A large portion of tropical dry forest near the town of El Limón de Cuauchichinola (ca. 300 inhabitants, 1220 m asl) was deforested in the early 1990s, used for maize cultivation for six years, and subsequently abandoned. Despite abandonment, the area is still degraded, since the secondary forest has been used mainly to sustain cattle ranching (~ 7 head/ha,
All observations were conducted on medium-sized species (
In 2006, 14 experimental plots (50 × 50 m) with similar vegetation and history of use were located and marked (details in
Eight experimental plots were enclosed with electric fences to avoid the intrusion of small and large domestic animals, and the remaining plots were marked but remained open to domestic animals. By the sixth year after exclusion, marked differences in the vegetation matrix were detected. For example, herbaceous vegetation (Poaceae and Asteraceae) cover was 20 times greater in the excluded than in non-excluded plots (
The observer walked slowly in the plot searching for a focal individual. Once a bird was identified, the distance between the observer and the individual was recorded as escape behavior is influenced by the intruder’s starting distance (
Direct starting distance calculated using the Pythagorean Theorem was used as a measurement of FID, since escape behavior is often influenced by the height at which the bird was perched at in the tree (
An analysis of covariance (ANCOVA) with independent slopes was performed to evaluate the effect of habitat, species, and intruder starting distance on FID. The effect of habitat was included as a nominal variable with two levels (restored and perturbed plots) with fixed effects. Species identity was included as a three-level nominal variable with fixed effects, and intruder’s starting distance was included as the covariate (
The ANCOVA utilized to evaluate the effect of habitat, identity of birds on FID explained 22 % of the total variance. According to the effect tests of the analysis of covariance, the species identity and starting distance (the covariate) showed a marginal and a highly significant effect, respectively, on the variation in FID (Table
ANCOVA results for species identity, habitat, the covariate and the interaction terms on FID.
Source | DF | Sum of Squares | F | p |
Species (S) | 2 | 2.99 | 2.51 | > 0.05 |
Habitat (H) | 1 | 0.36 | 0.61 | > 0.05 |
Covariate (C) | 1 | 6.75 | 11.31 | < 0.005 |
S×C | 2 | 0.72 | 0.61 | > 0.050 |
H×C | 1 | 0.31 | 0.52 | > 0.050 |
Due to the fact that, in this ANCOVA, the effect of habitat and both interaction terms were non-significant, a model that included only the effect of species identity, the starting distance, and their interaction was also tested. The effect test of this ANCOVA showed statistical significance only for the effect of species identity and the covariate were statistically significant (Table
ANCOVA results for species identity, the covariate and the interaction term on FID.
Source | DF | Sum of Squares | F | p |
Species (S) | 2 | 3.66 | 3.08 | < 0.05 |
Covariate (C) | 1 | 6.38 | 10.75 | < 0.005 |
S×C | 2 | 0.77 | 0.65 | > 0.05 |
The significant effect of starting distance (the covariate) indicates that birds in our study, were on alert to potential predators. This is consistent with the hypothesis that animals should not pay the attentional cost for continued monitoring of an approaching predator and should flush at a greater distance as starting distance increases (
We propose three possible non-exclusive explanations for the lack of differences in FID between habitats. First, while restoration actions clearly increased cover of both herbaceous (
Second, it is also possible that the lack of effect of habitat could result from the geographic scale at which restored plots are present within the landscape. The 50 × 50 m plots could represent very small vegetated patches in comparison with the overall landscape (~50 ha), which is mainly composed of open areas and a broken canopy of trees. Birds may have been unable to perceive the decreased risk at this scale, and the landscape’s fragmented physiognomy may have even produced edge effects with higher predation risk. Small patches were perceived as risky sites by birds (
Third, the study site is within an ecologically fragmented matrix, surrounded by secondary forest, maize cultivation plots, open areas with limited vegetation and eroded soil. Individuals could have been sensitized by frequent proximity to humans or cows (i.e. perceive greater risk from repeated exposure to the predator type‚ see
The decreased FID in the Golden-cheeked Woodpecker compared to the other two species was contrary to our prediction. This was also contrary to the general expectation that FID increases with body size (see
Interestingly, the Inca Dove, a species that occurs in urbanized sites, was less tolerant to human approach than Golden-cheeked Woodpeckers. The Inca Dove is a ground forager with low aspect ratio. Individuals find small seeds by picking at the soil surface in open sites. While foraging, individuals maintain their heads down and have limited predator detection capacity. Birds with a lower aspect ratio have longer FID as they have limited potential to escape from predation (
Animals’ behavior and decisions can be useful indicators to evaluate the success of habitat management actions for birds in different context as restoration ecology, urban parks and protected areas. In this study, we found that for medium sized bird species, small (ca. 2500 m2) and isolated restored plots may not decrease perceived predation risk. Therefore, to decrease birds’ perceived predation risk, restoration plans should include a mosaic of larger excluded plots located near relatively well-conserved sites to increase the area covered by vegetation. Wildlife managers should use FID in zones that are far removed from human impact on wild species to avoid possible sensitization or habituation effects. So, in conjunction with restoration plans it is important to identify buffer zones in order to avoid disturbance induced by human activity.
This study was funded by the Programa para el Desarrollo Profesional Docente en Educación Superior UAEMOR-CA 56. MOB was supported by an Individual Project from the Universidad Autónoma del Estado de Morelos and CMG by the Consejo Nacional de Ciencia y Tecnología Project #80027. The Centro de Investigación en Biodiversidad y Conservación supported researchers at the El Limón Biological Station. MOB is grateful to ECOLAB from University Paul Sabatier for its support during her sabbatiacal stay. Gregory Charre made useful comments on the manuscript and Lynna Kiere reviewed the English. We are grateful to Juan Camacho for his participation in the fieldwork and to Gerardo Pacheco from El Limón, Luz María Ayestarán, and Alondra Nicolás for their contributions to the maintenance of the experimental pots. This research was carried out in accordance with Mexican laws and ethical guidelines.