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Coturnix japonica

日本鹌鹑

Source:IUCN

Taxonomy



 

Taxonomy in detail

Scientific name


 
Authority


 
Synonyms


 
Common names


 
Taxonomic sources
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Identification Information
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Taxonomic notes


 

Assessment Information

IUCN Red List Category and Criteria
Near Threatened A2cd+3cd+4cd ver 3.1
Assessment language
English
Year published
2016
Date assessed
2016-10-01 00:00:00 UTC

Assessment Information in detail

Previously published Red List assessments


 
Regional assessments
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Assessor(s)


 
Reviewer(s)


 
Contributor(s)
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Facilitator(s) / Compiler(s)
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Partner(s) / Institution(s)
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Authority / Authorities
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Justification
This species is listed as Near Threatened because it is suspected to be undergoing a moderately rapid population decline, potentially owing to hunting and shifts in agriculture. Research is urgently required to establish population numbers, trends, and to assess and mitigate the threats to the species.

Geographic Range

Native
Extant (resident)
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Extant
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Number of locations
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Geographic Range in detail

FAO Fishing Areas
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Estimated area of occupancy (AOO) (km²)
Continuing decline in area of occupancy (AOO)
Extreme fluctuations in area of occupancy (AOO)
Estimated extent of occurrence (EOO) (km2)
Continuing decline in extent of occurrence (EOO)
Extreme fluctuations in extent of occurrence (EOO)
Continuing decline in number of locations
Extreme fluctuations in the number of locationsN
RANGE DESCRIPTION
Coturnix japonica breeds in eastern Asia, including northern Mongolia, Sakhalin Island and the Baikal and Vitim regions of Russia, north-eastern China, Japan, North Korea and South Korea. Some populations in Japan are resident, but most birds migrate south, wintering in southern China, Laos, Vietnam, Cambodia, Myanmar, Bhutan and north-eastern India (del Hoyo et al. 1994). There are also introduced populations in Italy and Hawaii (USA). No reliable population estimate exists, and although the species was previously considered to be fairly common in China (del Hoyo et al. 1994), declines appear to have occurred in Laos (Duckworth 2009) and Japan (Okuyama 2004, H. Nagata in litt. 2009), and there are fears that the species has undergone a significant decline overall (del Hoyo et al. 1994, Duckworth 2009).

Population

Current population trend
Decreasing
Number of mature individuals
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Population severely fragmented
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Continuing decline of mature individuals
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Population in detail

Extreme fluctuations
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No. of subpopulations
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Continuing decline in subpopulations
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Extreme fluctuations in subpopulations
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All individuals in one subpopulation
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No. of individuals in largest subpopulation
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Description
The global population size has not been quantified, but the species was has been reported to be fairly common (del Hoyo et al. 1994; Fuller et al. 2000). However, owing to recent suspected declines, the species is likely to be less common than previously thought. National population estimates include: c.10,000-100,000 breeding pairs and c.1,000-10,000 individuals on migration in China; c.100-10,000 breeding pairs, c.50-1,000 individuals on migration and <c.50 wintering individuals in Japan and c.10,000-100,000 breeding pairs in Russia (Brazil 2009).

Habitat and Ecology

System
Terrestrial
Number of mature individuals
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Continuing decline in area, extent and/or quality of habitat
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Generation length (years)
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Congregatory
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Movement patterns
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Habitat and Ecology in detail

Habitat and Ecology
Behaviour This species is an annual migrant, although some populations in Japan are resident (del Hoyo et al. 1994). Egg-laying occurs from late April to early August in Russia, and late May to August in Japan. Clutch size is varied, with larger clutches in Russia (nine to ten) than in Japan (five to eight). The female is the sole incubator of the eggs (del Hoyo et al. 1994). Habitat Little is known about the preferred habitat of this species, although it is thought to prefer open habitats such as meadows, steppes, and dry mountain slopes near water. It has also been recorded in grassland and cultivated land (del Hoyo et al. 1994). Diet Its diet is thought to include a wide variety of plant matter, and it will also take terrestrial invertebrates in summer (del Hoyo et al. 1994).

Classification scheme
Habitats Suitability Major importance

Threats

Use trade
Residential & commercial development
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Agriculture & aquaculture
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Energy production & mining
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Transportation & service corridors
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Biological resource use
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Human intrusions & disturbance
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Natural system modifications
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Pollution
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Geological events
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Climate change & severe weather
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Threats in detail

Threats
Specific threats to the species are unknown, although it may be threatened by agricultural change in Asia (Duckworth 2009). Hunting is a threat in Japan (Okuyama 2004), and is likely to be a threat elsewhere in its range.

Classification scheme Threats
title scope timing score severity

Use trade

Use trade

Text summary


Text summary in detail

Conservation Actions Information
Conservation Actions Underway
There are plans to introduce a ban on the hunting of the species in Japan (M. Okuyama in litt. 2010).

Conservation Actions Proposed
Obtain an up-to-date population estimate. Develop a monitoring scheme to establish population trends. Identify and assess the impacts of known and potential threats throughout its range.

About us
本项目由中国科学院A类战略先导专项“地球大数据科学工程”及中国科学院十三五信息化建设专项“科学大数据工程”提供支持,旨在整合物种的评估与保护信息,为生物多样性保护提供数据支持。
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