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Lifespan, longevity, and ageing

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

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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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Conservation

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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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Description

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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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Habitat

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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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Range

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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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Status

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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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Threats

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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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Black-faced spoonbill

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Wintering in Aogu Wetland, Taiwan

The black-faced spoonbill (Platalea minor) is a species of wading bird in the ibis and spoonbill family Threskiornithidae, found in eastern Asia. This species has the most restricted distribution of the six spoonbill species, and it is the only one regarded as endangered. Spoonbills are large water birds with dorso-ventrally flattened, spatulate bills.[2] These birds use a tactile method of feeding, wading in the water and sweeping their beaks from side-to-side to detect prey.[3] Confined to the coastal areas of eastern Asia, it seems that it was once common throughout its area of distribution. It currently breeds only on a few small rocky islands off the west coast of North Korea, with four wintering sites at Macau, Hong Kong, Taiwan and Vietnam, as well as other places where they have been observed in migration. Wintering also occurs in Jeju, South Korea, Kyushu and Okinawa, Japan, and the Red River delta in Vietnam. More recently, sightings of black-faced spoonbill birds were noted in Thailand, the Philippines, and additional sites in China.[1]

The black-faced spoonbill was internationally classified as an endangered species by the IUCN in 2000. Nearly driven to global extirpation in the 1980s, conservation efforts amongst various Asian countries in recent years has helped in bringing its population back onto a steadily increasing trend.[4] The black-faced spoonbill population in the 2012 census was recorded at 2,693 birds, with an estimation of 1,600 mature birds. Breeding colonies occur between March and August, on small islands. In the 2022 global census, the black-faced spoonbill population was recorded at 6,162 individuals.[4]

Black-faced spoonbills are known to be crepuscular eaters, using intertidal mudflats.[1] Conservation efforts on protecting breeding sites and wintering sites have been made since, and surveys were taken in order to determine the opinions and awareness of the local residents, residing close to the black-faced spoonbill's natural habitats. One survey taken by Jin et al. 2008, inquired upon the 'Willingness-To-Pay" factor in the locals, as well as understanding effects on mandatory surcharges compared to voluntary payments.[3]

Taxonomy

A study of mitochondrial DNA of the spoonbills found that the black-faced and royal spoonbills were each other's closest relatives.[5] Out of the six Platalea species within the family Threskiornithidae, the black-faced spoonbill is the rarest.[5]

Breeding

Black-faced spoonbills reached a serious low in population in the 1990s, but by 2003 their numbers increased to at least 1,069 counted individuals.[5] While it is known that their breeding area covers northeastern China and several islands between North and South Korea,[6] human-assisted breeding efforts have not been overly successful due to the difficulty in sexing the black-faced spoonbills, yet using the polymerase chain reaction technique on DNA samples has allowed researchers to use another method to correctly sex adult Platalea minor specimens.[5]

After migrating to their wintering locations, black-faced spoonbills return with yellow breeding plumage, which extends from the back of their heads to their breasts.[6] While this plumage only develops during the third or fourth year of life when the black-billed spoonbill is sexually mature, only about half of black-faced spoonbills with this plumage breed each breeding season, which contributes to the very slow pace at which the population numbers are increasing.

Distribution

The global population of this species, is likely based on the winter population count which was carried out in 1988–1990 in all known sites. This count estimated about only 288 individuals. As of 2006, following sustained conservation efforts, the estimated global population had increased to 1,679;[7] the 2008 census resulted in an estimated total count of 2,065 individuals [1]; and a 2010 census reported 2,346 [2]. The known localised population of North Korea is not known to exceed 30 birds. However, there is believed to be another, so far undiscovered colony which provides regional population stability and it is assumed to be probably located in north-east China; for example, on the islands of Liaoning (near the Korean nesting zone).

As black-faced spoonbills are migratory birds, their conservation is based on the protection of their breeding, "stop-over" and wintering grounds, making conservation efforts complex. However, spoonbills are able to adapt to disturbances of large-scale. The exact distribution of the species remains unclear, although some attempts at modelling population developments under climate change impacts have been made.[8]

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 aquaculture 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.

With the construction of a Shinkansen bridge in the Yatsushiro Sea between 2004 and 2009 next to a very important migration site for the black-faced spoonbills, many feared that it would cause their numbers to decrease. Thankfully, because of carefully planned out measures implemented in order to counter act the construction of the bridge, the population actually managed to increase during the time of construction.[9]

Human disturbances can also be much more direct. Many humans disturb mating patterns unknowingly by taking photographs of birds during their mating time, leading to a decrease in offspring. According to a research done in the Xing-Ren Tuo region of China in 1999, shellfish collectors, photographers, powerboats, and gull egg collectors are the major sources of disturbance causing the black-faced spoonbill to leave their nests.[10]

Conservation

The bird is a protected species in China as part of the China Red Data Book; its stopover site at Jiuduansha off Shanghai is a national nature preserve.[11] In Hong Kong, it is a protected species under Wild Animals Protection Ordinance Cap 200. 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.

During the winter months, over half of the black-faced spoonbill population migrates to the Chiku Wetland in southwestern Taiwan. The birds are incapable of catching large fish; therefore many of them rely on the largescale mullets to feed off of in the winter months spent in the wetlands.[12] These mullets however have recently become endangered due to the increase of spoonbill population who spend the winter months there (minimum of 191 birds in 1991/1992 up to a minimum of 840 in 2004/2005). Conservation of the largescale mullet is imperative in order to continue to sustain the endangered black-faced spoonbills.[12]

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. Disease has the ability to devastate the black-face spoonbills as well. In the winter of 2002/2003, 73 of the population died due to avian botulism. It may be necessary to establish additional protective areas or reserves in order to not let the population of birds to succumb to disease.[13]

The black-faced spoonbill is legally recognized as natural monument #205 and a first-class endangered species in South Korea

References

  1. ^ a b c BirdLife International (2017). "Platalea minor". IUCN Red List of Threatened Species. 2017: e.T22697568A119347801. doi:10.2305/IUCN.UK.2017-3.RLTS.T22697568A119347801.en. Retrieved 19 November 2021.
  2. ^ Swennen, C.; Yu, Y. (2005). "Food and Feeding Behavior of the Black-faced Spoonbill". Waterbirds. 28 (1): 19–27. doi:10.1675/1524-4695(2005)028[0019:fafbot]2.0.co;2. JSTOR 1522310. S2CID 84120382.
  3. ^ a b Jin, Jianjun; Wang, Zhishi; Liu, Xuemin (2008). "Valuing black-faced spoonbill conservation in Macao: A policy and contingent valuation study". Ecological Economics. 68 (1–2): 328–335. doi:10.1016/j.ecolecon.2008.03.014.
  4. ^ a b "Black-faced Spoonbill population hits record high of 6,000". The Hong Kong Bird Watching Society. The Hong Kong Bird Watching Society, 2022.
  5. ^ a b c d 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. doi:10.11646/zootaxa.2603.1.2.
  6. ^ a b Black-faced Spoonbill Conservation Association. (2001).Black-faced Spoonbill. Retrieved from http://www.bfsa.org.tw/en/ep02.htm
  7. ^ Yu, Yat-tung & Wong, Chi-chun (January 2006). The International Black-faced Spoonbill Census: 6-8 January 2006 (PDF) (Report). The Hong Kong Bird Watching Society Limited. Retrieved 22 February 2021.
  8. ^ Hu, Junhua; Hu, Huijian; Jiang, Zhigang (2010). "The impacts of climate change on the wintering distribution of an endangered migratory bird". Oecologia. 164 (2): 555–565 hidotdgfhf. Bibcode:2010Oecol.164..555H. doi:10.1007/s00442-010-1732-z. PMID 20677016. S2CID 19346000.
  9. ^ Takano, Shigeki; Henmi, Yasuhisa (2012). "The influence of constructing a Shinkansen bridge on Black-Faced Spoonbills Platalea minor Wintering in Kyushu, Japan". Ornithological Science. 11 (1): 21–28. doi:10.2326/osj.11.21. S2CID 86666935.
  10. ^ Wei Guo-An; Lei Fu-Min; Yin Zuo-Hua; Ding Chang-Qing & Ding Wen-Ning (2005). "Nesting and Disturbance of the Black-faced Spoonbill in Liaoning Province, China". Waterbirds. 28 (4): 420–425. doi:10.1675/1524-4695(2005)28[420:nadotb]2.0.co;2. JSTOR 4132622. S2CID 86311011.
  11. ^ "Birds Archived 9 January 2015 at the Wayback Machine". The Shanghai Jiuduansha Wetland Nature Reserve (Shanghai), 2014.
  12. ^ a b Yih-Tsong Ueng; Jen-Jiun Perng; Jiang-Ping Wang; Jug-Hsuan Weng & Ping-Chun Lucy Hou (2007). "Diet of the Black-faced Spoonbill Wintering at Chiku Wetland in Southwestern Taiwan". Waterbirds. 30 (1): 86–91. doi:10.1675/1524-4695(2007)030[0086:dotbsw]2.0.co;2. JSTOR 4132567. S2CID 85780556.
  13. ^ Ueng, Yih-Tsong; Wang, Jiang-Ping; Hou, Ping-Chun Lucy (2007). "Predicting Population Trends of the Black-faced Spoonbill (Platalea minor)". The Wilson Journal of Ornithology. 119 (2): 246–252. doi:10.1676/05-112.1. S2CID 85115854.

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Black-faced spoonbill: Brief Summary

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Wintering in Aogu Wetland, Taiwan

The black-faced spoonbill (Platalea minor) is a species of wading bird in the ibis and spoonbill family Threskiornithidae, found in eastern Asia. This species has the most restricted distribution of the six spoonbill species, and it is the only one regarded as endangered. Spoonbills are large water birds with dorso-ventrally flattened, spatulate bills. These birds use a tactile method of feeding, wading in the water and sweeping their beaks from side-to-side to detect prey. Confined to the coastal areas of eastern Asia, it seems that it was once common throughout its area of distribution. It currently breeds only on a few small rocky islands off the west coast of North Korea, with four wintering sites at Macau, Hong Kong, Taiwan and Vietnam, as well as other places where they have been observed in migration. Wintering also occurs in Jeju, South Korea, Kyushu and Okinawa, Japan, and the Red River delta in Vietnam. More recently, sightings of black-faced spoonbill birds were noted in Thailand, the Philippines, and additional sites in China.

The black-faced spoonbill was internationally classified as an endangered species by the IUCN in 2000. Nearly driven to global extirpation in the 1980s, conservation efforts amongst various Asian countries in recent years has helped in bringing its population back onto a steadily increasing trend. The black-faced spoonbill population in the 2012 census was recorded at 2,693 birds, with an estimation of 1,600 mature birds. Breeding colonies occur between March and August, on small islands. In the 2022 global census, the black-faced spoonbill population was recorded at 6,162 individuals.

Black-faced spoonbills are known to be crepuscular eaters, using intertidal mudflats. Conservation efforts on protecting breeding sites and wintering sites have been made since, and surveys were taken in order to determine the opinions and awareness of the local residents, residing close to the black-faced spoonbill's natural habitats. One survey taken by Jin et al. 2008, inquired upon the 'Willingness-To-Pay" factor in the locals, as well as understanding effects on mandatory surcharges compared to voluntary payments.

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