Post-fledging dispersal and habitat use of a reintroduced population of the Crested Ibis (Nipponia nippon)
© Huo et al.; licensee BioMed Central Ltd 2014
Received: 31 July 2014
Accepted: 9 August 2014
Published: 3 November 2014
Knowledge of dispersal movement of birds and their habitat preference during the post-fledging period is fundamental to the understanding of their ecological and evolutionary processes. The Crested Ibis is now being reintroduced to protected sites within its historical range, with the goal of establishing a self-sustaining population that may eventually qualify the species for delisting.
We carried out an ecological study of post-fledging dispersal and habitat use of a reintroduced population of the Crested Ibis (Nipponia nippon) from 2008 to 2012 in Ningshan County, China, by using banding and radio-telemetry methods.
In about two weeks (an average of 14.3 days) after fledging, the activities of the fledglings were concentrated in a range of about 100 m around their natal sites, such as the oak-pine forest patches at the edge of open habitats. During this period, fledglings were still partially dependent upon parental care and fed typically on a daily basis. Siblings increasingly became independent by mid-August and then gradually moved away from their natal sites to post-fledging dispersal locations. During the period of the post-fledging dispersal process, most juveniles moving southwest were concentrated at the mean direction (μ = 254.6°, š = 70.5°) with a mean dispersal distance of 5.1 km. It took an average of 56.4 days to disperse from the natal territory to the first wintering area. Also, forging habitats for juvenile ibis varied with time and local conditions. For example, paddy fields were used most frequently among all habitat types, while shallow rivers just from August to October. Masson pine (Pinus massoniana) was often regarded as the roosting tree species preferred by the Crested Ibis, with the highest utilization rate among all the roosting habitat types. The juveniles of the wild population dispersed four times as far as that of the reintroduced population, but the overall pattern of post-fledging dispersal is similar for the reintroduced and wild populations.
Our results are very useful for us to predict the distance and direction of dispersal under various landscape conditions in other released sites. The project is a good example for reintroducing endangered species to their former ranges, and will be valuable for the protection of reintroduced populations of this critically and other endangered species.
KeywordsCrested Ibis Ningshan County Post-fledging dispersal Habitat use Reintroduced population
Dispersal is one of the most important life-history traits for animals. The study of dispersal has received increasing attention from animal ecologists during the past two decades (Clobert et al. , Barbraud et al. ). Knowledge of dispersal movements is fundamental to our understanding of many ecological and evolutionary processes, as well as for the design of successful conservation strategies (Paradis et al. ). It is often defined as the permanent movement an animal makes from its natal site to the place where it reproduces or would have reproduced if it had survived and found a mate (Howard ). Greenwood and Harvey () suggested distinguishing between “natal dispersal” and “breeding dispersal”, the latter referring to the movements undertaken by adults between breeding sites. Post-fledging dispersal refers to the movements of the young after they become independent of their parents and leave their natal territory to move to wintering areas (Bull et al. ). In the avian life-cycle this stage is poorly understood, but limited studies have documented post-fledging periods lasting up to two months (Morton ; Baker ). For migratory birds, some investigators have assumed that once the young disappear from their natal site they begin a slow movement to the south (Bent ; Pulich ). The young of resident species have been shown to stay in the general vicinity of where they were hatched, but will move into different habitats (Nolan ; Rappole and Ballard ; Bocetti ).
The Crested Ibis (Nipponia nippon) was once one of East Asia’s most widespread and well-known birds, but deforestation and destruction of habitat has led to successive extinctions of Russian, Korean and Japanese populations in the 20th century (Yamshina ; Archibald et al. ; Yusuda ). The Chinese population was presumed extinct for two decades preceding the 1981 discovery of seven birds in Yangxian County, Shaanxi Province (Liu ). During the past 30 years, a great deal of conservation effort, both in-situ and ex-situ, has been undertaken by researchers and the local government. The wild population in China has increased to approximately 800 and more than 700 captive-bred individuals now reside in eight protection centers located in China, Japan and Korea. This rare species is now being reintroduced to protected sites within its historical range, with the goal of establishing stable, secure populations that may eventually qualify the species for delisting (Yu et al. ).
The first reintroduction was at Zhaigou village, Ningshan County in China’s Shaanxi Province. From May 2007 to October 2011, 56 captive-bred individuals (29 males and 27 females) were released into the wild (Li et al. ). From these birds, 14 breeding pairs have, so far, produced 46 fledglings. With a 62.5% survival rate for released birds, this first reintroduction program in China has had a promising start (Li et al. ). Post-fledging dispersal is the original stage for juveniles, laying the foundations for the entire dispersal process, which to a certain extent, also determines the following series of the dispersal process. Therefore, the study of post-fledging dispersal can contribute to the study of the entire dispersal process, necessary to mark out successfully the strategies to protect the reintroduced populations. Also, the study of habitat utilization of the Crested Ibis helps us to understand the use of spatial resources and the effect of their variety on the movements of the birds. Post-fledging dispersal patterns and habitat utilization during the breeding period by the Crested Ibis in the wild have been studied recently (Yu et al. ; Liu et al. ), but dispersal behavior and habitat relationships in the reintroduced population remain unclear. Therefore, we designed the current study in order to explore the population dynamics and the habitat utilization of a reintroduced population of the Crested Ibis, attempting to provide theoretical and practical bases for reintroduction and conservation.
The Crested Ibis establishes a small breeding territory of no more than 50 m in diameter (Shi and Cao ). The species is not highly territorial. To establish a new population, it is essential for released birds not only to survive successfully during the establishment phase of pairing and breeding, but also to disperse successfully into wintering areas. The onset of juvenile dispersal is usually more or less arbitrarily defined on the basis of some estimation of the typical size of the territory of adults (Ferrer ; Walls and Kenward ). Juvenile dispersal is characterized by an initial wandering and exploratory phase that contrasts with the restricted pre-dispersal movements. Such contrast is likely to be identifiable as a period of increased variability in the distance to the nest and hence could be used to identify the onset of juvenile dispersal. Thus, Soutullo et al. () used a criterion of distance to determine the onset of dispersal. We monitored movements of the Crested Ibis following release using banding and radio-telemetry. Specifically, we sought 1) to document distance and direction of post-fledging dispersal, 2) to determine changes in habitat use between natal and dispersal sites, 3) to compare dispersal patterns between released and wild population in Yangxian County studied by Yu et al. () and 4) to propose management suggestions for conservation and future release.
From 2008 to 2012, we conducted fieldwork in Ningshan County (33°07′–33°50′N, 108°02′–108°56′E), located on the south slope of the Qinling mountains in central China’s Shaanxi Province. The study area lies in a warm, temperate zone and is moderately humid. The annual temperature averages 12.5°C, with a minimum in January (−12.8°C) and a maximum in July (36°C). The frost-free period is 215 days. The annual precipitation is 899 mm with July through September being the wettest time of the year (Ningshan County meteorological station).
The elevation of the study area ranges from 700 to 1100 m. This area is often developed for rice paddies interspersed with dry farmlands in the valley and for forest stands on hillsides. The study area includes all areas used by both young and adult birds for dispersal. A large number of shallow rivers and streams roll southward through this area into the Hanjiang River, one of the longest tributaries of the Yangtze River. Almost all nesting areas were in pine and oak forests characterized by trees with diameter at breast height (DBH) ranging from 5 to 40 cm and canopy height between 10 and 25 m, planted on slopes near local farmer settlements. These patches are primarily deciduous, broadleaf forests where the dominant tree species include Quercus variabilis, Pinus tabulaeformis, P. massoniana, and Platycladus orientalis. Forest patches provide 80% of the coverage used by ibis for nesting.
In the study area, the Crested Ibis forages in paddy fields, shallow rivers, arid wastelands, grasslands and streams. The birds roost in P. massoniana and other tree species. During the daytime, in between foraging grounds, the ibis temporarily rests on rock outcrops, poles and at the edges of fields.
Nest site characteristics and fledging details for 25 marked Crested Ibis juveniles at Zhaigou village, Ningshan County in Shaanxi Province
Bands of fledglings
Hatching rate (hatched/clutch)
Fledging rate (fledged/clutch )
Banding and radio-telemetry
The Crested Ibis feeds and roosts largely near human settlements (Li et al. ) and their frequent, hoarse calls, especially those given by males early in the breeding season facilitated our efforts to find all nests and mark all nestlings. Twenty-five nestlings from nineteen nests were banded with numbered and colored bands before they fledged at 24–26 days. Each year the bands were checked and verified at nest sites, foraging grounds and winter-roost sites. A radio transmitter set (RI-2D) between 216.368 and 216.691 MHz was placed on the strongest nestlings (typically the eldest) at each nest 23–25 days after hatching. It was attached on the neck using a harness of elastic nylon string, leaving room for growth of the pectoral muscles. At 15 g, its weight was approximately 1% of the body mass of the fledglings. Battery life was estimated at 18 months. Monitoring was accomplished using programmable receivers (TRX-1000S, Wildlife Materials Inc., Carbondale, IL, USA) and three-element, hand-held antennas. Radio-marked individuals generally dispersed with family groups or other wandering flocks for three months. During the study, we observed the different groups at dark (17:40-18:40) when all members of a wandering flock perched in a night-roosting sites and the individuals observed in a fledgling group between 7:00 and 12:00 hours on a rotational basis at 1–3 day intervals until contact was lost. However, radio-telemetry was only an auxiliary method; all access to juvenile dispersal data has been collected on the spot as a means of radio-telemetry.
Bird visits and surveys
We recorded monthly observations of habitat use by hatch-year birds, starting with fledging and ending seven months after fledging. Status (location, survival condition) and behavior were recorded within natal territories five days per week by approaching on foot until the fledgling was sighted or a change in signal strength was recorded. When a signal from a fledgling was lost, we searched across the entire study area and up to 20–40 km outside of the study area boundary using the radio receiver, a spotting scope (GEOMA65A 20–60×) and binoculars (SICONG 10 × 42). On each tracking day, at least one location per individual was recorded during each of three periods: early morning (06:00–09:00), mid-day (09:01–15:00) and late afternoon (15:01–20:00). We chose these periods in order to capture movements of the radio-marked fledglings between night roosting sites and daytime foraging and resting areas. The distribution points of dispersal of the radio-marked fledglings were obtained by radio receiver and spotting scope, their geographical positions and dispersal directions (1–360°, the azimuth angle of the newborn individuals between the location and the natal site) were pinpointed using global positioning system (GPS) receivers. The dispersal distance, referring to the straight line distance between the natal site and post-fledging area, was calculated on 1:50000 topographic maps.
The magnitude of pre-dispersal movements by newly fledged Crested Ibises varies significantly among individuals. Therefore we defined the onset of post-dispersal as the date upon which a fledgling stopped using the nest tree as a night roost and termination as the date upon which an individual no longer exhibited a linear, directional movement away from the natal home range, but instead concentrated its daily movements around a night-roosting site we referred to as post-dispersal ranges (or first wintering sites).
All post-dispersal direction analyses were conducted using Oriana 4.01 (Kovach Computing Services, Wales, UK). We calculated the mean vector (μ) and the angular deviation (r) for the dispersal direction and used Rayleigh’s z to test for the directional pattern (Zar ). All statistical analyses were conducted using SPSS 16.0 (SPSS Inc., Chicago, USA), presented as mean ± standard deviation (SD) with significance set at p = 0.05. Most data were measured by repeated ANOVA. We computed means for observations in the use of forging and roosting habitats for each month of post-fledging, by first averaging the data from observations of all radio-marked members of a sibling group. Pearson correlation analysis was used to compute correlation between mean distances from natal site to foraging ground that breeding pairs frequently attended during the nestling period and days that natal home ranges were occupied.
We identified post-dispersal habitat types for 11 of our 25 surviving juveniles (two juveniles from two broods in 2008, four juveniles from two broods in 2009 and five juveniles from four broods in 2010). The juveniles used a wide range of different habitat types for foraging and roosting.
Per cent use of post-fledging dispersal feeding habitats by juvenile Crested Ibises
(Obs = 15)
(Obs = 14)
(Obs = 12)
( na = 7)
( n = 12)
( n =12)
( n = 10)
( n = 10)
( n = 10)
( n = 8)
Per cent use and availability of post-dispersal roosting habitats by juvenile Crested Ibises
(Obs = 18)
(Obs = 10)
(Obs = 11)
( na = 4)
( n = 8)
( n =8)
( n =8)
( n = 8)
( n = 8)
( n = 5)
Other tree species
The Crested Ibis was widespread and locally abundant in Northeast Asia in the late 19th century, when it nested in the Russian Far East, Japan and mainland China. It was also presumed to be a winter visitor to the Korean Peninsula (BirdLife International ). The surviving wild population in Yangxian County and the reintroduced population in Ningshan County are residents that make only relatively short, seasonal movements between nesting and wintering sites (Shi and Cao ; Yu et al. ). However, in the past, the former population of Siberia (eastern Russia), northeast China, and Hokkaido (northern Japan) are known to have migrated south in winter (Yamshina ; Archibald et al. ; Yusuda ). The Crested Ibis perhaps exhibits different patterns of post-fledging movements in their former and present ranges. We have no way of measuring the exact distance they travel to their wintering grounds at the Korean Peninsula, Taiwan or Hainan Island from the former breeding sites in Russia and northeastern China, but estimates suggest that this distance exceeds hundreds of kilometers.
In our study, the dispersal distances of the 25 individuals that completed the entire process of post-fledging dispersal were less than 16 km, suggesting that the post-fledging dispersal distance in the first year was highly correlated with the distance between suitable breeding and wintering habitat areas. In comparison, the natal home ranges of fledglings of the reintroduced population were occupied for significantly shorter periods than that of the wild population (21.1 ± 10.2 days, n = 36; t = 3.047, p = 0.004). Most fledglings moving southwest were concentrated at the mean direction (μ = 254.6°, š = 70.5°, n = 25) while fledglings of wild birds dispersed in a southerly direction (189.2 ± 46.5°, n = 36) with a mean dispersal distance of 20.3 ± 7.0 km (n = 36) (Yu et al. ). The overall pattern of post-fledging dispersal of juveniles is similar for the wild and reintroduced populations, but the fledglings of the wild population dispersed four times as far as the reintroduced individuals. These findings are very useful for us to predict the distance and direction of dispersal under various landscape conditions of other released sites.
The process of avian dispersal begins when an individual fledges from its nest and is then guided by a series of decisions: where to move, what to eat, with whom to pair and ultimately where to attempt breeding. Post-fledging dispersal is one of the most important stages in the life-history of birds. Only upon finding a mate and attempting to breed can the dispersal process be regarded as complete. In our study area, juvenile ibis birds moved an average of 5.1 km away from their natal territory during the first year of their life. It took a minimum of two years for fledglings to become sexually mature. Sexual monomorphism in Crested Ibis fledglings makes gender assignment difficult to distinguish during the post-fledging dispersal period. Our observations of the dispersal of ibis fledglings indicate that they are not moving randomly. Similar to wild fledglings (Yu et al. ) and resident Golden Eagles (Aquila chrysaetos; Soutullo et al. ), the juvenile dispersal of our population reared in captivity is typically characterized by an initial exploratory and nomadic phase followed by repeated returns to the vicinity of the natal area. Siblings of each brood increasingly became independent of their parents at the beginning of August and all fledglings routinely joined ibis flocks that included other non-breeders in post-dispersal areas. Breeding opportunities may be more likely in these dispersal flocks than they would be if these young birds were to remain with the family group. In dispersal flocks, individuals may be capable of competing for new territories, thus becoming active breeders by dominating these new areas (Zack and Stutchbury ). The fall/winter flocking period provides an opportunity to interact with possible mates and appears to be very important for sustaining the surviving population. We observed that, within dispersal flocks, adults frequently forced juveniles to roost on peripheral branches through a ritualistic pecking behavior. New pair formation occurs often following the flocking period in late winter and early spring (Shi and Cao ).
According to the optimal foraging theory, the distribution and temporal use of habitat varies due to habitat quality (Lester et al. ). The period that territories were occupied by the reintroduced population were 14.3 ± 7.0 days (n = 25) and 21.1 ± 10.2 days (n = 36) for the wild population (Yu et al. ), which appears to reflect differences in food availability at different nesting sites. The nestlings of the Crested Ibis fledged approximately from mid-June to mid-July and were prevented from foraging in rice fields due to the inaccessibility of the flourishing rice shoots. Therefore, fledglings and their parents had to move to feed in alternate habitats such as rivers and grasslands during this period. In the following months, they returned to their main foraging sites (paddy fields; Table 2). From our study, we speculate that the proximate cause for dispersal of the Crested Ibis is increasing food availability during the conversion process of habitat, but potential pairs and pairing formation eventually might be found in colonies during the dispersal process and thus achieve population continuity, which is the ultimate factor for the post-dispersal of the birds (the remote cause).
Since 1999, great success for both the wild and captive populations has led some ornithologists to a more positive view regarding long-term reintroduction goals, restoring the species to its former range (Zheng ; Litvinenko ). To date, reintroduction programs have been conducted in 2007 in China (Yu et al. ) and in 2008 in Japan ([Nishimiya and Hayashi]). The eggs failed to hatch on Japan’s Sado Island, but the worldwide program still achieved one of its first goals as new pair formations continued to occur and the number of fledglings produced continued to grow in our study area, Ningshan County (Yu et al. , Li et al. ). Recent investigation of the historical range for this species suggests that regions south of the Qinling mountains should be prioritized for future release efforts. Conservation of migratory endangered species entails preserving adequate breeding, stopover and winter habitats. This may therefore pose greater challenges for managers than resident species do (Serra et al., ). Prior to future release in Siberia and the demilitarized zone (DMZ) at the Imjingak Pavilion in Korea, an extensive investigation should be conducted, because the condition of their former breeding ranges, wintering grounds, and stopover sites remains unknown.
In our study, eight recorded mortalities were split evenly between dependent and independent fledglings. Based on the temporal distribution of dead Crested Ibis birds of the reintroduced population in Ningshan (Li et al. ), the time of death of the juveniles was concentrated in the May-August period, including the period of natal home ranges during post-fledging dispersal. Out of nineteen mortalities incurred among released adults during the 6-year period (three in 2007, three in 2008, four in 2009, three in 2010, two in 2011 and four in 2012), eight of them died from starvation, two were lost due to electrocution by power lines, four died due to predation or injuries attributable to predation (likely due to martens Martes flavigula, a small-size Mustelidae mammal) and one died from unknown causes (Li et al. ). These findings indicate that starvation, especially in winter, can be a significant cause of mortality. We propose therefore the following suggestions to management.
The local government should promote a strategy to harmonize people and nature with a particular focus on sustainable agricultural practice that encourages local farmers to cultivate more rice fields within Crested Ibis release areas. The ibis, its habitat and the local communities will all benefit. Food (mainly loach, Misgurnus anguillicaudatus) should be supplemented to the rice fields where ibis regularly forage, especially during the winter when the temperature is below 0°C. Public education should be implemented to inform local people on the purpose of ibis conservation and on how to get involved. The effects on ibis populations of illegal hunting for frogs, fishes and commercial activities nearby shallow rivers should be made clear and all relevant resource protection laws should be strictly enforced.
The project carried out in Ningshan County, Shaanxi Province is a good example for reintroducing endangered species to their historical ranges. Compared with the wild population in Yangxian County, the juveniles produced from the released population exhibited a similar pattern of post-fledging dispersal. Our results are very useful for us to predict the distance and direction of dispersal under various landscape conditions of other released sites. The food availability during the conversion process of different types of habitat may be the proximate cause for dispersal, and potential pair formations which achieve population continuity are probably the ultimate factor for the post-fledging dispersal. These findings will be valuable for the protection of reintroduced populations of this critically and other endangered species.
We are very grateful to the support and help from the Life Science College of Shaanxi Normal University, and the reintroduction base of Crested Ibis in Ningshan County for providing us the adequate requirements of daily life and related techniques uesd to observation. Special thanks Mr. R.Hammond and R.Hamilton for their careful comments and help in the editing of the manuscript. We also thank Cao Hai-xin for assistance in field observation and Ningshan County meteorological station for providing meteorological information. Financial support was provided by National Nature Science Foundation of China (31172103).
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