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Overview

Distribution

Range Description

Gorsachius goisagi breeds in Japan. There has been one report of breeding from Taiwan (China), and recent work has discovered a breeding site at Jeju Island, South Korea (Oh et al. 2010). It has also been recorded in spring and summer in Russia (Primorye and Sakhalin), and is a passage migrant in coastal mainland China and Hong Kong (China), and also in Taiwan. The main wintering area appears to be in the Philippines, but it has also been recorded as a non-breeding visitor to Indonesia, and as a vagrant to Brunei and Palau. Improved awareness of the identification criteria for immatures of this species has led to a marked increase in records from the Philippines (D. Allen in litt. 2012). It was apparently locally common in Japan until the 1970s, but by the 1980s and 1990s had disappeared from many of its former breeding sites. There have apparently been just two records from mainland China since the early 1960s, one of two sightings at Wuyuan in Jiangxi Province in April 2006 and a taxidermy specimen noted in Haiyan county in Zhejiang province in February 2010 and apparently purchased in Haining city in April 1998 (He Fenqi in litt. 2007, 2012). The relative paucity of recent records suggested that the population numbered fewer than 1,000 mature individuals, but recent work in Japan and increasing numbers of records from the Philippines imply that this may have been overly pessimistic. Hence, the true figure may lie within the band 1,000-2,499 individuals. However, this may still be an underestimate (K. Kawakami in litt. 2012).

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Range

S Japan; winters se China to Ryukyu Islands and Indonesia.

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Ecology

Habitat

Habitat and Ecology

Habitat and Ecology
It breeds in heavily forested areas, including coniferous, broadleaved and degraded forest, on hills and the lower slopes of mountains (up to 1,500 m), where there are watercourses and damp areas. It winters in dark, deeply shaded forest near water up to 2,400 m. It forages mainly in forest, but will use swamps, rice-fields and farmland and is mainly crepuscular. Breeding has been recorded from April to July (Kawana 2006). Earthworms are probably the principal food source, but land snails, cicadas, crabs, and ground and scarabid beetles are all present in its diet (Kawakami et al. 2005, K. Kawakami in litt. 2007, Oh et al. 2010).


Systems
  • Terrestrial
  • Freshwater
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Molecular Biology and Genetics

Molecular Biology

Statistics of barcoding coverage: Gorsachius goisagi

Barcode of Life Data Systems (BOLDS) Stats
Public Records: 0
Specimens with Barcodes: 6
Species With Barcodes: 1
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Source: Barcode of Life Data Systems (BOLD)

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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
2012

Assessor/s
BirdLife International

Reviewer/s
Butchart, S. & Symes, A.

Contributor/s
Allen, D., He, F., Kawakami, K. & Kominami, Y.

Justification
This species has a very small, declining population, and therefore qualifies as Endangered. Declines are primarily a result of deforestation in its breeding and wintering ranges.

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Population

Population
Recent work in Japan suggests the previous assertion that the global population comprises fewer than 1,000 individuals may have been overly pessimistic (although Brazil 2009 estimated fewer than 100 breeding pairs, fewer than 50 individuals on migration and fewer than 50 wintering individuals in Japan). Hence, the true figure probably lies within the band 1,000-2,499 individuals. This equates to 667-1,666 mature individuals, rounded here to 600-1,700 mature individuals.

Population Trend
Decreasing
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Threats

Major Threats
The main threat is deforestation for timber and agriculture in both its breeding and non-breeding ranges. The development of dense scrub undergrowth in forest and on abandoned farmland (following a change in traditional agricultural practices) is believed to reduce the suitability of these habitats for feeding. It has probably been hunted in many parts of its range and suffers from human disturbance (Anon. 2009). It declined rapidly on Miyake-jima in the Izu Islands, where it was formerly abundant, following the introduction of Siberian weasel Mustela sibirica in the early 1970s. Today nest predation by corvids is an increasing threat as crow populations increase in urban and suburban areas.

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Management

Conservation Actions

Conservation Actions
Conservation Actions Underway
It is legally protected in Japan and Hong Kong. Birds may occur in protected areas in Japan and it has been recorded in Quezon National Park, Philippines. Environmental Impact Assessments are conducted prior to major developments in Japan, and if this species is identified using a site mitigation measures are taken (K. Kawakami in litt. 2007).

Conservation Actions Proposed
Survey its breeding range in Japan and its wintering range in the Philippines. Establish a monitoring programme of its breeding and wintering populations. Study its home-range requirements using radio-telemetry. Protect and manage forests in its breeding and wintering grounds. Ensure official protection throughout its range and strengthen and enforce legislation to prevent the sale of this (and other threatened) species. Establish public-awareness programmes concerned with its conservation. Control and monitor invasive species where appropriate within its range.

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Wikipedia

Japanese Night Heron

The Japanese night heron (Gorsachius goisagi) is a species of night heron found in East Asia. It breeds in Japan, and winters in the Philippines and Indonesia. It is also seen in the spring and summer in Korea and the Russian Far East.

The Japanese night heron prefers dense, damp forest, in both its breeding and winter ranges. Common until the 1970s, this species is threatened by deforestation in its summer and winter ranges. Other documented threats include the introduction of the Siberian Weasel (Mustela sibirica) in its breeding range. The current population is estimated at less than 1,000 mature individuals.

See also[edit]

References[edit]

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