Key Biodiversity Area Special Series                                  


Key Biodiversity Areas identification in Japan Hotspot


Yoji Natori 1, Mari Kohri 2, Seiji Hayama 3 & Naamal De Silva 4


1,2 Conservation International Japan, Shinjuku i-Land Tower 39F, 6-5-1 Nishi-Shinjuku, Shinjuku-ku, Tokyo 163-1339, Japan

3 Wild Bird Society of Japan, 3-9-23 Nishi-gotanda, Shinagawa-ku, Tokyo 141-0031, Japan

4 Conservation International, 2011 Crystal Drive, Suite 500, Arlington, VA 22202, USA

Email: 1 (corresponding author), 2, 3,4




Date of publication (online): 06 August 2012

Date of publication (print): 06 August 2012

ISSN 0974-7907 (online) | 0974-7893 (print)


Manuscript details:

Ms # o2999

Received 08 November 2011

Final revised received 26 December 2011

Finally accepted 04 June 2012


Citation: Natori Y., M. Kohri, S. Hayama & N. De Silva (2012). Key Biodiversity Areas identification in Japan Hotspot. Journal of Threatened Taxa 4(8): 2797–2805.


Copyright: © Yoji Natori, Mari Kohri, Seiji Hayama & Naamal De Silva 2012. Creative Commons Attribution 3.0 UnportedLicense. JoTT allows unrestricted use of this article in any medium for non-profit purposes, reproduction and distribution by providing adequate credit to the authors and the source of publication.


Author Details and Contributions:

Yoji Natori is the Ecosystem Policy Manager at Conservation International Japan. His current responsibilities include national and international biodiversity policy, management of a forest restoration project, and mainstreaming of biodiversity into society including the outreach of KBA. He led the study and preparation of the manuscript.

Mari Kohri is currently a researcher at Tokyo Metropolitan University and the principal investigator of a Grant-in-Aid project, “Developing a mapping method for selecting biodiversity conservation priority area and for invasive species measures in the oceanic islands” from Japanese Ministry of Education, Culture, Sports, Science & Technology. She supported the process as a consultant to CI, and collected distribution information of KBA trigger species to produce draft KBA mapping.

Seiji Hayama is the Head of Nature Conservation Office, Wild Bird Society of Japan. He is involved in conservation, monitoring and research in IBA sites. He also conducts lobbying activities. He provided information on IBAs to facilitate the KBA identification process.

Naamal De Silva is the Director of Conservation Priorities and Outreach at Conservation International. With background in identifying globally significant sites for biodiversity conservation, her current role includes developing CI’s institutional framework for identifying geographic priorities and helping to link science staff in CI headquarters with technical staff in the field. She advised the study by providing her experiences in the similar exercises in other countries.

All the authors participated in a workshop on conservation priority sites in Tokyo in September 2010.


Acknowledgements:  This project benefited from expert information provided by Dr. Masafumi Matsui, Dr. Kazumi Hosoya, Dr. Nobuo Ishii, Dr. Takuma Hashimoto, Mr. Hiromune Mitsuhashi, Mr. Mitsuhiko Toda, Mr. Hitoshi Imai, Dr. Sachiko Yasui-Kamijo, Dr. Yuya Watari, Dr. Ken Sugimura, and Dr. Kazuto Kawakami, and Mr. Takehiko Sato. Ms Satoko Shirai provided valuable assistance. Conservation International would like to give special thanks to the Biodiversity Center of Japan, Ministry of the Environment for allowing use of the data from the National Survey on the Natural Environment.  The project (non-bird taxa) was made possible by a financial support from Keidanren Nature Conservation Fund to Conservation International during 2009-2011.




Abstract: Priority sites within Japan Hotspot were identified using Key Biodiversity Area (KBA) criteria, based on vulnerability and irreplaceability. The identification process considered 217 trigger species from mammals, birds, reptiles, amphibians, freshwater and brackish water fishes and odonates, and focused on identifying gaps in Japan’s protected-area system. We identified 228 sites as KBAs and 50 rivers as candidate KBAs. Collectively, KBAs occupy 18% of the land, about half is not protected. Sites selected include natural and semi-natural environments, and appropriate form of protection is site-dependent. Twenty percent of Japanese terrestrial area is already protected, although to varying degrees, but additional 8% should also receive protection or proper management to strengthen the conservation of biodiversity in Japan.


Keywords: conservation priority, Aichi Target, red list, GIS, IBA, Key Biodiversity Area, KBA, vulnerability, irreplaceability





The Key Biodiversity Area series documents the application of the concept and showcases the results from various parts of the world.  The series is edited under the auspices of the IUCN World Commission on Protected Areas/Species Survival Commission Joint Task Force on ‘Biodiversity and Protected Areas’, with the editors supported by BirdLife International, Conservation International, IUCN, National Fish & Wildlife Foundation, NatureServe, Parks Canada, and PlantlifeInternational.




For images, tables -- click here





The Japanese archipelago stretches 3,000km from the sub-tropics in the south to the sub-Arctic in the north. Although the four main islands—Hokkaido, Honshu, Shikoku and Kyushu—account for much of Japan’s land area (approximately 375,000km2), collections of smaller islands support relatively high levels of biodiversity. As a heavily populated, industrialized nation, there are few unmodified areas, but high biodiversity is still seen. Owing to this, the archipelago has been identified as one of the world’s 35 Biodiversity Hotspots (Mittermeier et al. 2004; Williams et al. 2011) with nearly 2,000 endemic vascular plants (Kato & Ebihara, 2011; Mittermeier et al. 2004). Besides the more natural landscapes, human-influenced habitats often made up of paddy-fields and secondary forests also play an important role in supporting the biodiversity of Japan (Natori et al. 2011; Washitani, 2001).

There is a wide range of protected area categories in the Japanese nature conservation system. The major ones include national parks, quasi-national parks, and prefectural natural areas under the Natural Parks Law; wildlife protection areas under the Wildlife Protection and Hunting Law; wilderness areas and nature conservation areas under the Nature Conservation Law; and forest reserves and forest ecosystem conservation areas under the Forestry Law. Except for the areas designated under Natural Parks Law and Nature Conservation Law, designations are mutually complementary and several designations can commonly overlap. Combining all these areas, the existing protected areas cover 20% of Japan’s land surface. Additionally, the Endangered Species Law provides for the protection of designated species, and some associated habitat areas have been designated for protection. The Law for Protection of Cultural Properties, which was established much earlier than the Endangered Species Law, also protects species and sites of scientific importance (called “natural monuments”), some of which are threatened.

The selection of these existing protected areas is however not based on systematic biodiversity assessments. Therefore, important sites for biodiversity need to be identified systematically so that all such sites are known and preferably become protected. Key Biodiversity Areas (KBAs) are globally important sites for biodiversity conservation, identified based on two criteria: vulnerability and irreplaceability (Langhammer et al. 2007). It is a species-based site-selection methodology, but with the aim of site conservation. The most significant sites for bird conservation have been identified using these criteria, and there are 167 Important Bird Areas (IBAs) in Japan (Wild Bird Society of Japan, 2010). The KBA identification process adds to IBAs by bringing other taxa into consideration.

The major questions we addressed were, “Where are gaps in Japanese protected-area system that deserve protection or proper management? And what particularly significant biodiversity occurs in existing protected areas?” Our focus was less on the assessment of the performance of the existing protected areas, but more on identifying the parts of the land that still need to be protected, i.e., highlighting existing gaps.





The standard global set of criteria of vulnerability and irreplaceability (Langhammer et al. 2007) was used in selecting trigger species (Table 1). The KBA selection process took into account all terrestrial vertebrate taxa (mammals, birds, reptiles, amphibians and fresh- and brackish-water fish) and odonates (Table 2). For the taxa of which the IUCN Red List is incomplete or outdated, the more recent and comprehensive compilation of Japan’s Red Lists were used (see below for a further discussion). When finalizing the lists of trigger species (especially when adding species that are not IUCN threatened species), we consulted with a few experts regarding the appropriateness.

The study built on the earlier work of IBA identification (Wild Bird Society of Japan, 2010), and we adopted all IBAs as KBAs. Fish and odonates were included in the analysis to give emphasis to freshwater systems, which are under-represented in the national protected-area network.



We used the IUCN threatened species list (IUCN, 2010) to define the vulnerability of trigger species of mammals and amphibians. We considered the information on threatened status of these two taxa to be up to date, because the global assessments have only recently been completed. Since IBAs were treated as KBAs automatically, bird trigger species used for IBA identification were also KBA trigger species. For other taxa, the IUCN list is incomplete and/or in need of updating. Thus, we supplemented the IUCN list with the Japan’s national red lists (Ministry of the Environment, 2006, 2007). In doing so, we only considered those species endemic to Japan since these assessments represent the global status of such species (as recommended by Eken et al. (2004) p. 1114). Where the IUCN category differed from the national one, the national category was given precedence since we considered that Japan’s national lists were more up to date and carried higher accountability for species endemic to Japan.



The Irreplaceability criteria were applied for mammals, birds and amphibians only. We used the range sizes of mammalian and amphibian species from the Global Assessments (IUCN, 2009), and only those with global ranges of smaller than 50,000 km2 were used (i.e., restricted-range sub-criterion). Since population information is not available for these taxa, we applied the irreplaceability criterion to only those species with known occurrence in well-defined localities, such as islands.

For birds, as was the case with vulnerability, the IBA trigger species were also KBA trigger species. IBA defined irreplaceability sub-criteria in restricted range, congregation/aggregation and biome-restriction. Unlike mammals and amphibians, the irreplaceability criterion alone was used to trigger KBAs identification for birds. For the purpose of counting trigger species in this paper, the species included in the vulnerability trigger species were not included in irreplaceability trigger species.

Although irreplaceability has not been defined for other taxa, many species likely to trigger sites under the irreplaceability criteria are in any case likely to also trigger identification of sites under the vulnerability criteria. This is especially the case in an insular nation like Japan.


Data sources

The species presence information was obtained from the “National Survey on the Natural Environment,” conducted by the Japanese Ministry of the Environment (MOE) since 1973 (Biodiversity Center of Japan, 2008). Detailed presence information (in approximately 1km x 1km cells, or the “third mesh” in Japanese standard gridding system) on threatened species was used with permission from the Biodiversity Center of the MOE. Published journal articles supplemented this information, particularly for bats and odonates. The “Important Wetlands 500” sites (Ministry of the Environment, 2001) that had been selected for the presence of the vulnerability trigger species were also included.


KBA Identification and Delineation

We built the identification and delineation process  on the existing IBAs. To incorporate other taxa, protected areas that encompassed the locations of trigger species for non-avian taxa were first adopted as KBAs. Protected areas were not divided when delineating KBAs. We considered the following designations as protected areas for the purposes of KBA identification: national parks, quasi-national parks, prefectural natural parks, wilderness areas, nature conservation areas, wildlife protection areas (both national and prefectural), and forest ecosystem reserves.

If the presence data of the trigger species were located outside IBA or existing protected-area boundaries, vegetation maps (Ministry of the Environment; available online: and municipal boundaries were used to help define KBA boundaries.





We identified 228 KBAs, covering over 68,000km2 (Image 1). Some KBAs extended into marine environment to account for trigger species that are dependent on brackish environment and shorelines. The terrestrial part covers a total of 66,000km2, equaling 17.6% of the land area (Table 3). The islands stand out as particularly important conservation priorities. Western Honshu, Kyushu and Shikoku were low in percent of land in KBAs. Overall, about 30,000km2 of the KBA extent is not protected. In addition, 50 rivers were identified as candidate KBAs for the presence of trigger species of fish and odonates. The specification of their boundaries is left to future work with more information from the sites.

All previously identified IBAs were included. Some IBAs were grouped; e.g. the Izu Islands KBA represents a group of eight IBAs. Many KBAs were delineated by expanding IBAs to include the presence localities of non-bird taxa and to incorporate existing protected-area boundaries. Seventy-seven sites were added in KBA triggered by other taxa (Table 4).

Alliance for Zero Extinction sites (AZEs) are a subset of KBAs that are identified by the presence of highly threatened species (CR or EN in the IUCN Red List) known to occur only in single sites globally. There are six AZEs identified in Japan (AZE, 2010). All of them were also identified as KBAs triggered by species other than those used to identify AZEs. Table 5 lists only five AZEs. The sixth AZE, Yatsugatake, has been identified for a species of conifer (Picea koyamae), which was a taxon not considered here for KBA identification, but the site was identified as KBA based on the presence of other trigger species. Only small fractions of five AZEs, Echigo Plain, Oki Island, Tsushima Islands, Tokunoshima Island, Yambaru, are currently protected. In addition to the existing six AZEs, three KBAs may be considered candidates for new AZEs: Kumejima Island (one  AZE trigger species), Ogasawara Islands (four AZE trigger species) and Yaeyama Islands (three AZE trigger species).

The highest numbers of trigger species found at single KBAs were 24 on Yambaru, followed by 23 on the Yaeyama Islands and 19 on the Amami Islands (Table 6); all of which are in the Nansei Islands. Furenko-Nemuro in Hokkaido was the next richest with 14 trigger species. The majority (194 KBAs, 84%), however, were triggered by five species or fewer.

Seven trigger species triggered 15 or more KBAs: Dymecodon pilirostris, Heteroscelus brevipes, Pipistrellus endoi, Myotis pruinosus, Anas platyrhynchos, Columba janthina and Lestes japonicas. Not surprisingly, however, the majority of trigger species triggered only a few KBAs (Table 6), because many trigger species are endemic to specific islands.






The most important gaps in the protected area network were found to be the Nansei Islands, a string of islands extending southwest from southern tip of Kyushu, such as Amami Islands and Yambaru. A more detailed identification of priority sites within this island chain has been performed (WWF Japan, 2009), which should facilitate more focused local conservation actions. Freshwater (and brackish water) systems were also found to be generally under-represented in protected areas; e.g. northern Hokkaido and western Japan. Unprotected KBAs were identified not only in mountainous and other more natural habitats, but also in semi-natural and agricultural areas; e.g. Echigo Plain, Noto Peninsula and Sanuki Plain. Taking into consideration the varying threats to and natural and social conditions of the areas identified as KBAs, the most appropriate form of protection, including the type of protected-area designation, should be determined on site-specific bases.


Caveat and Limitations

This analysis used existing protected-area boundaries where they contained locality records of trigger species and did not refine boundaries further.  KBAs boundaries, if geographically overlapped with existing protected areas, could be delineated larger than they would be in absence of such protected areas. This was done in consideration to management efficiency and with the idea that there is no need to reduce the area of protection if the protection is already committed in the area covering KBAs. The delineation of KBA boundaries outside protected areas were done in ways to minimize adding to KBAs. This means that the priority site for new protection covers 8% of Japan’s land is a stronger message for conservation actions than total area covered by KBAs is 18% of Japan’s land.

We are aware of several limitations of this first analysis of KBA in Japan, and we describe three of them here. First, we recognize that the list of taxa included in the analysis is incomplete. In particular, grassland systems are not well represented, since, for example, plants and butterflies were not included as the trigger species.

This is not to say, however, that important sites for these taxa have not been selected as KBAs. Indeed, KBAs identified here include the top ten sites for plant endemism in Japan (Kato & Ebihara, 2011). This suggests that many key sites meeting the irreplaceability criterion for plants have likely been included in the KBAs identified by this analysis.

Second, the degree of actual protection provided by the existing protected areas to the KBAs identified here should be viewed with caution. We expect that those types of protected-area designation used to define protected areas in this analysis provide some level of deterrent against harmful developments. However, it should be kept in mind that many of them do not provide sufficient enforceable protection. There are zonings within given types of protected area providing different levels of protection. However, this analysis did not distinguish these differences in protection; i.e., in effect, we considered all areas inside the boundaries of existing protected areas to be protected equally. This differs from the treatment of protected-area designation as applied to IBAs by Wild Bird Society of Japan, which considers as protected only those parts of protected areas with the higher protected status. In consideration of actual implementation and enforcement, these differences should be more carefully considered. Such refined analysis is subject of future development, and will result in larger gaps than shown here.

Third, river systems are important and no less than 50 rivers had the presence of trigger species. Currently the entire river stretches are selected as candidate KBAs. Connectivity from upstream to downstream, as well as fragility of the riverine ecosystems to human alteration, poses a challenge in delineating KBAs in rivers. Although precise delineations are yet to be done, the intention is to draw attention to freshwater systems of potential importance to stimulate conservation actions.

The selection of KBA relied on presence-only data. The KBA map only shows the areas known to be important. It does not, by any means, indicate that areas outside these KBAs were excluded because they were assessed and were found to be of low conservation values. Rather, this indicates that they are not included in KBAs because there was insufficient information to justify their inclusion. Most areas simply have not been surveyed. As new information becomes available, additional areas equally important as the KBAs identified here may be found.

Information on important sites, such as KBAs, must be communicated to local authorities. To bridge effectively sites of global conservation importance to on-the-ground conservation actions at local scales, communicating the global importance in local context will become increasingly important.


Future Priorities

Developing capacity in GIS for conservation purposes is important in both selecting the sites at finer scales so that they can be proposed as part of formal protection programs and in providing updated information to enable periodic review of KBAs. For this purpose, the next related development will be to operationalize the Conservation GIS Consortium that will provide the platform for collecting and exchanging biogeographic information in ways that are safe and reliable for both information providers and users.

In 2010, the international community agreed to expand effectively managed protected area network (at least to 17% of the terrestrial area; Aichi Target 11) and to avoid extinction and improve the status of known threatened species (Aichi Target 12) under the Convention on Biological Diversity’s Strategic Plan for Biodiversity 2011-2020 (see Currently, protected areas in Japan collectively cover 20% of land area, but this KBA identification revealed that additional 8% of the land should be protected or properly manged. As additional taxa (e.g., plants and butterflies) are included in the analysis, the number and the area of KBAs will certainly increase. To achieve these global Aichi Targets, this KBA analysis suggests that Japan’s national target should seek securing appropriate management to 28% of the land.





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