Overview

Brief Summary

Biology

The breeding season begins in early May and nests are constructed upon cliffs; the clutch size is usually three eggs. Breeding success is relatively low but fledging generally occurs at around five weeks old (4). By mid-August, the young are independent and the annual migration to the wintering grounds can begin. These birds are relatively gregarious, roosting together in flocks usually during daylight hours (4). Foraging may also occur in groups, and flocks of around 25 birds have been seen feeding on the mud flats, their bills just skimming the surface of the water for food (4). A variety of tidal species are taken, from small fish to crabs and shrimp; foraging appears to take place in the dark or is dependent on the tide (4).
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Comprehensive Description

Description

The black-faced spoonbill is a relatively small wading bird with, as its name would suggest, an elongated, spoon-shaped bill. The plumage is white in colour, and the face and bill are black (2). During the breeding season, mature adults develop longer crest feathers at the back of the neck, and these and the breast area become a golden yellow (5). Adult black-faced spoonbills have red eyes and yellow patches on their cheeks (6). Male black-faced spoonbills can be distinguished from females by their longer bills; while the bills of immature birds are a pinkish-grey rather than black (5).
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Distribution

Range Description

Platalea minor breeds on islets off the west coast of North Korea and South Korea, and Liaoning province in mainland China. Birds have been reported in the Tumen estuary of Russia, and breeding was recorded in South Primorye for the first time in 200613. The three major wintering sites are the Tsengwen estuary of Taiwan, the Deep Bay area of Hong Kong (China), and the Chinese mainland and Hainan Island. It also winters in Cheju, South Korea, Kyushu and Okinawa, Japan, and Red River delta, Vietnam2, and there are recent records from Thailand, the Philippines, Macau (China) and inland China10. The key known stopover sites used during migration are Yueqing Bay, Wenzhou Bay and Sanmen Bay9. A recent study infers an historical population of c.10,300 individuals4, which fell to an estimated low of 288 individuals in 1988 but it appears to have recovered subsequently to a total of 1,679 individuals counted during the 2006 International Black-faced Spoonbill Census12. Recent censuses show that this total appears to have increased year on year at most important wintering sites, but there has been no increase in Vietnam's Red River Delta, where conditions in the Xuan Thuy National Park have been deteriorating3,12. It also remains unclear whether census increases represent increased survey effort, displacement of birds from other unknown wintering sites or genuine population increases.
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Range

Found along the east Asian coast, these birds are known to breed on islands off the coast of North and South Korea and in Liaoning Province, China. Following the breeding season, the population migrates to wintering grounds at three major sites: Tsengwen Estuary, Taiwan, Inner Deep Bay, Hong Kong, and the Red River Delta, Vietnam (2).
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Ecology

Habitat

Habitat and Ecology

Habitat and Ecology
It breeds in mixed colonies on small islands from March to August8. Breeding success is low. It is mainly a crepuscular feeder utilising intertidal mudflats7; resting, sleeping and digesting occur at a variety of sites (trees, man-made structure, shallow water) within 2-3 km of feeding areas6. Spoonbills employ tactile feeding using lateral sweeps of the bill to locate fish and shrimp prey5. Satellite tracking has shown that birds wintering in Hong Kong and Taiwan migrate along the coast of eastern China to northern Jiangsu, then over the Yellow Sea to the Korean peninsula. Wintering birds form large aggregations and it has been recorded amongst flocks of Eurasian Spoonbills Platalea leucorodia10. It matures at 5 years of age and birds of at least 9.5 years old have been recorded in the wild11.

Systems
  • Freshwater
  • Marine
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Habitat

Inhabits intertidal habitats along the coast; nesting occurs on cliffs close to tidal flats, whilst winter grounds are situated on estuary wetlands, mudflats and mangroves (4).
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Life History and Behavior

Life Expectancy

Lifespan, longevity, and ageing

Maximum longevity: 15 years (captivity) Observations: One specimen lived for 15 years in captivity (Brouwer et al. 1994).
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Molecular Biology and Genetics

Molecular Biology

Statistics of barcoding coverage: Platalea minor

Barcode of Life Data Systems (BOLDS) Stats
Public Records: 0
Species: 2
Species With Barcodes: 1

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Conservation

Conservation Status

IUCN Red List Assessment


Red List Category
EN
Endangered

Red List Criteria
C2a(i)

Version
3.1

Year Assessed
2008

Assessor/s
BirdLife International

Reviewer/s
Butchart, S., Bird, J., Chan, S.

Contributor/s
Coulter, M.

Justification
This spoonbill is listed as Endangered because it has a very small population, split into several small subpopulations, that is believed to be undergoing a continuing decline owing to loss of habitat to industrial development, land reclamation, and pollution. A lack of baseline data makes identifying a population trend problematic, but if the apparent recent increases are confirmed as genuine, the species may warrant downlisting in the future.

History
  • 2006
    Endangered
  • 2004
    Endangered
  • 2000
    Endangered
  • 1996
    Critically Endangered
  • 1994
    Critically Endangered
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Status

Classified as Endangered (EN) on the IUCN Red List 2007 (1), and listed on Appendix I of the Convention on Migratory Species (CMS or Bonn Convention) (3).
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Population

Population
Yu and Wong (2006).

Population Trend
Decreasing
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Threats

Threats

Major Threats
Recent speculation suggests that pollution from pesticides is most congruent with demographic history, in terms of scale and timing of declines and subsequent recovery, as an explantation of past population reduction4. However, habitat destruction is probably the biggest threat currently. The main wintering grounds are threatened by industrial development, particularly a key site in Taiwan and also in China, and reclamation, especially in South Korea, Japan and China. Economic development in China has converted many coastal wetlands into aquaculture ponds and industrial estates. Pollution remains a major threat to birds wintering in Hong Kong. An outbreak of botulism at one of the major wintering sites killed 73 birds representing 7% of the world population from December 2002 to February 20031,2. Increasing levels of disturbance by fishers and tourists and also hunting are threats in China and Vietnam8. Fishers in China collect waterbird eggs at nesting sites.
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Threats

Habitat destruction in the form of the alteration and drainage of wetlands for aquaculture and industrial development is probably the biggest threat to the survival of the black-faced spoonbill (4). The small number of wintering sites means that the species is very vulnerable to any chance event that may occur, particularly to the potentially catastrophic effects of pollution (4).
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Management

Conservation Actions

Conservation Actions
Conservation Actions Underway
It is legally protected in China (including Hong Kong), Taiwan, North Korea, South Korea and Japan. Breeding sites in North Korea, at Taegam-do, Unmu-do, Sonchonrap-do and Tok-do, are designated as seabird sanctuaries and sites in China have been declared as non-hunting areas. Protected wintering sites include Mai Po and Inner Deep Bay (Hong Kong), Xuan Thuy and Tien Hai (Vietnam), and Manko (Japan). An action plan was published in 1995 and workshops involving all major range countries were held in 1996 and 1997. Education material, satellite tracking and field survey results and management recommendation have been produced. Annual censuses have been conducted in recent years.

Conservation Actions Proposed
Survey coastal wetlands in China for additional wintering sites. Ensure full protection of the wintering site at Tainan (Taiwan), new breeding sites in China, important wetland sites along the western and southern coast of South Korea, and wintering sites at Hakata Bay and Ariake Bay, Japan. Develop management plans and education programmes for all sites. As pollution has been heavily implicated in the major population reduction that this species suffered, environmental monitoring is recommended as a proactive step to prevent future pollution or disease outbreaks4. Continue annual population censuses.

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Conservation

The black-faced spoonbill is protected in China, Taiwan, North Korea, South Korea and Japan, and a number of both breeding and wintering sites are protected as sanctuaries (2). An Action Plan for the species was produced in 1995, following an international workshop; the Wild Bird Society of Japan acts as the secretariat of the Black-faced Spoonbill Conservation Network (4). Educational and research programmes have been undertaken in a number of countries, and an international census has been established and run by Hong Kong Bird Watching Society (5).
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Wikipedia

Black-faced Spoonbill

The Black-faced Spoonbill (Platalea minor) has the most restricted distribution of all spoonbills, and it is the only one regarded as endangered. Confined to the coastal areas of eastern Asia, it seems that it was once common throughout its area of distribution. It has a niche existence on only a few small rocky islands off the west coast of North Korea, with three wintering sites at Hong Kong, Taiwan and Vietnam, as well as other places where they have been observed in migration.

Contents

Taxonomy

A study of mitochondrial DNA of the spoonbills found that the Black-faced and Royal Spoonbills were each others' closest relatives.[1]

Distribution

The global population of this species, based on the winter population count carried out in 1988-1990 in all known sites, was estimated at 288 individuals. As of 2006, thanks to conservation efforts over the years, the estimated global population had increased to 1,679 [1]; the 2008 census resulted in an estimated total count of 2,065 individuals [2]; and a 2010 census reported 2,346 [3]. The niche population of North Korea does not exceed 30 birds, which implies that there must be another colony which has not been discovered yet, and which is perhaps located in northeast China; for example, on the islands of Liaoning (near the Korean nesting zone).

Threats

It is thought that the principal cause of the decline of this species is the destruction of its habitat, more particularly the "valorization" of intertidal mudholes for agriculture, and more recently aquiculture and industrialization. The Korean War (1950–1953) must also have had a negative impact on the species, because the birds ceased nesting in South Korea at that time. In Japan, where it was once common for them to winter, they became extremely rare at this same time, and in later years there has never been a winter in which more than 5 birds were observed.

Conservation

In Hong Kong, it is a protected species under Wild Animals Protection Ordinance Cap 170. In Mai Po Marshes, a quarter of the world's population of Black-faced Spoonbill can be found during migration.

The species is reasonably well protected in North Korea, where their nesting islands off the coast were declared a Zone of Protection with restricted access. There remain nevertheless several threats, mainly in the wintering zones. The need for land to assign to industry is great in the wintering sites in Taiwan, whereas those in Vietnam are being converted for shrimp breeding, though they are within a reserve subject to the Ramsar Convention. In Hong Kong, disturbances by fishermen and shell gatherers often prevent the birds from feeding at low tide. In addition, with the continued expansion of human populations in the Far East, pollution will probably become an important problem.

The Black-faced Spoonbill is legally recognized as natural monument #205 in South Korea.

References

  1. ^ Chesser, R.Terry; Yeung, Carol K.L.; Yao, Cheng-Te; Tians, Xiu-Hua; Li Shou-Hsien (2010). "Molecular phylogeny of the spoonbills (Aves: Threskiornithidae) based on mitochondrial DNA". Zootaxa (2603): 53–60. ISSN 1175-5326. 
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