Habitat and Prey Resource Overlap Between the Iriomote Cat

Total Page:16

File Type:pdf, Size:1020Kb

Habitat and Prey Resource Overlap Between the Iriomote Cat Mammal Study 28: 47–56 (2003) © the Mammalogical Society of Japan Habitat and prey resource overlap between the Iriomote cat Prionailurus iriomotensis and introduced feral cat Felis catus based on assessment of scat content and distribution Shinichi Watanabe*, Nozomi Nakanishi and Masako Izawa Faculty of Science, University of the Ryukyus, Nishihara, Okinawa 903-0213, Japan Abstract. The Iriomote cat Prionailurus iriomotensis occurs only on Iriomote Island in the Ryukyu Archipelago of southern Japan. The population is estimated at 100 individuals and is on the decline. We examined resource overlap for prey and habitat between this species and introduced cats Felis catus by scat census and analysis of scat contents. The distribution of scats was completely different between the two species. The distribution of scats from Iriomote cats was associated with environmental factors such as vegetation types and terrain conditions, while the distribution of scats from feral cats mainly depended on locations of garbage dumps. Although the feral cat heavily utilized human rubbish, it also preyed upon thirteen species of native animals, ten of which were also used by Iriomote cats. From 1997 to 2001, the number of observed scats from Iriomote cats declined significantly, while feral cat scat became more common. Feral cats on Iriomote Island still depend on humans, but the expansion of their distribution into habitats of Iriomote cats may increase the competition for prey and habitat resources in the future. Key words: Felis catus, habitat use, interspecific competition, introduced species, Prionailurus iriomotensis. Introduced species often greatly affect local fauna and status or even extinction (Kitching and Jones 1981; King flora through predation, resource competition and 1984). In Okinawa and the Amami Islands of southern hybridization with native species (Elton 1958; Diamond Japan, mongooses introduced to control a venomous and Case 1986; Ecological Society of Japan 2002). Iso- snake (Habu Trimeresurus flavoviridis) and rats have lated fauna and flora with a small number of species are become established in vacant niches. As a result, many particularly vulnerable to invasive introduced species rare or endemic species of amphibians, reptiles, terres- (Elton 1958; Diamond and Case 1986; Frankel and Soulé trial birds, and mammals have been preyed upon and 1981). In recent history, 75% of extinctions of birds and threatened (Abe et al. 1991, 1998; Ogura et al. 2002; mammals have occurred on isolated islands, and 43% of Kawauchi and Sasaki 2002; Ministry of the Environment these were caused by introduced predators (Frankel and 2002a, b, c). Soulé 1981). Species are more susceptible in islands Introduced species often compete for prey and habitat because of restricted habitats and lack of experience with resources against native species, but the impacts of com- new predators, and are often at a competitive disadvan- petition are notably stronger on closely related species tage against aggressive invasive species (Frankel and (Diamond and Case 1986; Ecological Society of Japan Soulé 1981). Well-documented examples occurred in 2002). The Iriomote cat Prionailurus iriomotensis is a Australia and New Zealand, where unique fauna in iso- small felid and inhabits only Iriomote Island of the lated habitats were affected by introduced carnivores like Ryukyu Archipelago. This species is listed as endan- dingos Canis lupus dingo, feral cats Felis catus, and red gered because of its restricted habitat and small popula- foxes Vulpes vulpes. Predation on native marsupials and tion size, (IUCN 2000) estimated at approximately 100 terrestrial birds pushed many populations to threatened individuals (JWRC 1994). The population has declined *To whom correspondence should be addressed. E-mail: [email protected] 48 Mammal Study 28 (2003) Fig. 1. Location of the census route to collect scats on Iriomote Island in the Ryukyu Archipelago of southern Japan. A census route along a paved road six kilometers long and five meters wide was divided into 24 sections (a–x) at 250 m intervals. during the last decade due to habitat loss from develop- Study area ment and mortality from traffic accidents (Izawa and Doi 1991). While P. iriomotensis is the only native member The study was conducted on Iriomote Island (284 km2, of the order Carnivora on Iriomote Island, the introduced 24°20’N, 123°49’E) located in the southern Ryukyu feral cat F. catus distribution has been expanding away Archipelago, Japan. The climate is warm-temperate to from human settlements, often following new road subtropical with average monthly temperatures ranging construction. from 17°C in January to 29°C in July, and average Among carnivores, scat provides information about annual precipitation of approximately 2,300 mm at the individuals at specific sites (Macdonald 1980). The Iriomote Meteorological Station. Most of the island is Iriomote cat leaves scat on exposed surfaces such as dominated by highly folded mountains (the highest point on bare lands, rocks, and roads (Sakaguchi et al. 1986). = 469 m, Mt. Komi) and covered with subtropical ever- Sakaguchi et al. (1986) frequently observed scats from green broad-leaved forests dominated by Castanopsis Iriomote cats along streams, along the edges of forests sieboldii and Quercus miyagii. Flatlands occur only and grasslands. Scats were not present in the interior along the coast, where human activities, cultivated fields of cultivated fields, grasslands, or barren ground. Similar and villages are concentrated. About 2,000 people live patterns of habitat use were observed in radio-tracking on the island, mostly inhabiting twelve villages along the surveys (Watanabe 2001; Watanabe et al. 2001). Saka- coast. guchi et al. (1986) also suggested that the distribution The study site is in the eastern part of the island near of scat from Iriomote cats reflects both habitat use and two small villages (Fig. 1) with populations of 70 people specific preferences for latrine sites. In the current in Komi and 24 people in Mihara in January 2002. A study, we used scat locations to evaluate habitat use by paved road, 5 m wide and 50 km long was constructed in both Iriomote cats and feral cats. We also assessed prey 1976. We established a 6 km census route on the road preferences through fecal analysis of both species. divided into 24 sections (a–x) at 250 m intervals (Fig. 1). The route crosses three streams, and traverses subtropi- Watanabe et al., Resource overlap of native and feral cats 49 cal evergreen forests, rice fields, cultivated fields, man- containing a prey type/total number of analyzed scats) groves, and swampy forests. The two villages are along was calculated for each prey type and for each taxon sections h–j (Komi) and adjacent to sections w–x (mammals, birds, reptiles, amphibians, fishes, insects, (Mihara). Two garbage dumps are located 250 m away crustaceans, and others). from section i in a cane field and 50 m away from section u in a forest. Analysis of scat distribution According to the statistical reports of Taketomi Town Habitat utilization of P. iriomotensis is reported to be Office, while the population on Iriomote Island grew affected by environmental factors including terrain and from 1,892 people in 1995 to at least 1,976 people in vegetation (Watanabe 2001; Watanabe et al. 2001). In 2000, visitor numbers increased from 201,967 people in this study, we analyzed the relationships between scat 1995 to 285,080 people in 2000. locations for the two cat species and the surrounding environment by using a geographic information system Methods (GIS). Deflection of scat distribution was tested for each Scat census species by one-sample Kolmogorov-Smirnov tests. Scat Scats were collected by one or two observers walking distribution was compared between species by two- along both sides of the route at the end of each month sample Kolmogorov-Smirnov tests. from November 1997 to October 2001. Locations, cir- Multiple regression models were developed according cumstances, and conditions of scat were recorded during to quantification theory type I (Hayashi 1952) for the dis- these censuses. tribution of scat of the two species. The total number of scats collected in each section was the dependent Scat identification variable and six environmental factors were independent It was necessary to distinguish between the scats of variables. Three variables related to terrain: (1) mean the two cat species at the point of collection. Scat of P. elevation, (2) mean slope in each section, and (3) dis- iriomotensis can be easily distinguished by the specific tance from streams to the center of each section, were odors secreted from anal glands (Imaizumi et al. 1977; derived from digital elevation models (Digital Map 50 m Sakaguchi et al. 1986). Fecal odors withstand weather- mesh, Elevation published by Geographical Survey ing and degradation for longer periods than the interval Institute, Japan). Vegetation type (4) in each section between our censuses. Therefore, scats having the was categorized as forest, rice field and swamp, and specific odor of P. iriomotensis could be positively cultivated and bare land according to digital vegetation identified based on the odor. However, scat with no data, from the Natural Environment Information GIS characteristic odors could not be designated as F. catus (Environment Agency 1999). Variables related to human scat without further evidence. Since mammals ingest activities such as (5) distance from garbage dumps, and their own hair during grooming and pass it in their scat (6) distance from residential areas to the center of (Imaizumi et al. 1977), we characterized cat hairs in scat each section were calculated using GIS software, IDRISI at the time of collection and during lab analysis. version 32.2 (Clark Labs, The Idrisi Project). Multiple Although some feral cats have similar collar patterned regression analysis was performed using a macro in fur to that of Iriomote cats, hairs in scat were clearly Microsoft Excel. identified by hair-length, solidity, and color pattern when All independent variables were categorized, and each viewed under a stereomicroscope.
Recommended publications
  • The Stoloniferous Octocoral, Hanabira Yukibana, Gen. Nov., Sp
    Contributions to Zoology 88 (2019) 54-77 CTOZ brill.com/ctoz The stoloniferous octocoral, Hanabira yukibana, gen. nov., sp. nov., of the southern Ryukyus has morphological and symbiont variation Yee Wah Lau Molecular Invertebrate Systematics and Ecology Laboratory, Graduate School of Engineering and Science, University of the Ryukyus, 1 Senbaru, Nishihara, Okinawa 903-0123, Japan [email protected] Frank R. Stokvis Naturalis Biodiversity Center, P.O. Box 9517, 2300 RA, Leiden, The Netherlands Yukimitsu Imahara Wakayama Laboratory, Biological Institute on Kuroshio, 300-11 Kire, Wakayama-shi, Wakayama 640-0351, Japan James D. Reimer Molecular Invertebrate Systematics and Ecology Laboratory, Graduate School of Engineering and Science, University of the Ryukyus, 1 Senbaru, Nishihara, Okinawa 903-0123, Japan Tropical Biosphere Research Center, University of the Ryukyus, 1 Senbaru, Nishihara, Okinawa 903-0123, Japan Abstract Stoloniferan octocorals (Cnidaria: Anthozoa: Octocorallia: Alcyonacea) are a relatively unexplored fauna in the Ryukyus (southern Japan), known to be a tropical marine region of high biodiversity and endemism of species. Specimens of stoloniferous octocorals were collected during fieldwork along the coasts of two islands (Okinawa and Iriomote) in the Okinawa Prefecture. Despite their phenotypic polyp variation, this study shows their morphological and molecular uniqueness, leading to the description of a new genus with a single species: Hanabira yukibana, gen. nov., sp. nov. They are placed within the Clavulariidae and form a sister clade basally to the genus Knopia Alderslade & McFadden, 2007 and species of Clavularia Blainville, 1830. The polyps of this new species show morphological variation in both shape and sclerite density, but there is conformity in the typical overall petal shaped tentacles, which have fused pinnules (pseudopinnules).
    [Show full text]
  • Effects of Constructing a New Airport on Ishigaki Island
    Island Sustainability II 181 Effects of constructing a new airport on Ishigaki Island Y. Maeno1, H. Gotoh1, M. Takezawa1 & T. Satoh2 1Nihon University, Japan 2Nihon Harbor Consultants Ltd., Japan Abstract Okinawa Prefecture marked the 40th anniversary of its reversion to Japanese sovereignty from US control in 2012. Such isolated islands are almost under the environment separated by the mainland and the sea, so that they have the economic differences from the mainland and some policies for being active isolated islands are taken. It is necessary to promote economical measures in order to increase the prosperity of isolated islands through initiatives involving tourism, fisheries, manufacturing, etc. In this study, Ishigaki Island was considered as an example of such an isolated island. Ishigaki Island is located to the west of the main islands of Okinawa and the second-largest island of the Yaeyama Island group. Ishigaki Island falls under the jurisdiction of Okinawa Prefecture, Japan’s southernmost prefecture, which is situated approximately half-way between Kyushu and Taiwan. Both islands belong to the Ryukyu Archipelago, which consists of more than 100 islands extending over an area of 1,000 km from Kyushu (the southwesternmost of Japan’s four main islands) to Taiwan in the south. Located between China and mainland Japan, Ishigaki Island has been culturally influenced by both countries. Much of the island and the surrounding ocean are protected as part of Iriomote-Ishigaki National Park. Ishigaki Airport, built in 1943, is the largest airport in the Yaeyama Island group. The runway and air security facilities were improved in accordance with passenger demand for larger aircraft, and the airport became a tentative jet airport in May 1979.
    [Show full text]
  • Analysis of Drifting Polystyrene Degradation Surround Japan
    Open Access Austin Journal of Environmental Toxicology Research Article Analysis of Drifting Polystyrene Degradation Surround Japan Amamiya K1, Koizumi K2, Yamada K1, Hiaki T1, Kusui T4 and Saido K1,3* Abstract 1College of Industrial Technology, Nihon University, Due to accidental or intentional littering, plastics make their way into Japan rivers and ultimately into oceans. No studies have been conducted on plastic 2College of Science & Technology, Nihon University, decomposition at low temperatures in the ocean owing to the misconception that Japan plastic hardly decomposes, if at all. To clarify if drifting plastics do indeed break 3Albatross Alliance, Japan down or not. Not only does this happen through micro/nano-scale fragmentation, 4Toyama Prefecture University, Japan but also potentially noxious chemicals are generated. To examine the level of *Corresponding author: Katsuhiko Saido, College of chemical contamination of ocean bodies due to debris/waste Polystyrene (PS), Industrial Technology, Nihon University, Chiba, Japan 2,000 sand and water samples surrounding Japan were analyzed by GC/MS since 2,000 to 2015. All samples containing styrene oligomer (SOs) which Received: January 09, 2020; Accepted: February 06, consist of ethynylbenzene (Styrene Monomer, SM), 2,4-diphenyl-1-butene 2020; Published: February 13, 2020 (Styrene Dimer, SD) and 2,4-6-triphenyl-1-hexene (Styrene Trimer, ST). The composition ratios were SM1: SD1: ST 7 to10. Mega/Macro debris PS not only fragmented to generate micro/nano PS-particles (micro/nano plastic) but also chemically degraded to basic structure unite chemicals SOs. One Sentence Summary: PS in the ocean breaks into its oligomer at ambient temperatures throughout the year, posing a serious threat to marine ecosystems.
    [Show full text]
  • Do Zoos Work at Raising Awareness? Quantifying the Impact of Informal Education on Adults Visiting Japanese Zoos
    ________________________________________________________ Do zoos work at raising awareness? Quantifying the impact of informal education on adults visiting Japanese zoos ___________________________________________________________________ AYAKO UOZUMI “A thesis submitted in partial fulfilment of the requirement for the degree of Master of Science and the Diploma of Imperial College London.” September 2010 1 DECLARATION OF OWN WORK I declare that this thesis (insert full title) …………………………………………………………………………………………… …………………………………………………………………………………………… …………………………………………………………………………………………… …………………………………………………………………………………………… is entirely my own work and that where material could be construed as the work of others, it is fully cited and referenced, and/or with appropriate acknowledgement given. Signature …………………………………………………….. Name of student …………………………………………….. (please print) Name of Supervisor …………………………………………. 2 1 INTRODUCTION....................................................................................................................................... 8 1.1 AIMS AND OBJECTIVES..........................................................................................................................................10 1.2 OVERVIEW OF THESIS STRUCTURE ....................................................................................................................10 2 BACKGROUND........................................................................................................................................11 2.1 A BRIEF HISTORY OF
    [Show full text]
  • PICA Project Report (Action A2.2 & 2.3)
    PICA Project Report (Action A2.2 & 2.3) Investigation of Pallas’s cat activity patterns and temporal interactions with sympatric species Authors: Katarzyna Ruta, Gustaf Samelius, David Barclay, Emma Nygren PICA - “Conservation of the Pallas’s cat through capacity building, research, and global planning” 1. Introduction: 1.1 Activity patterns of wild felids: Activity patterns form a part of species’ adaptation to their environment (Beltran & Delibes, 1994) and are therefore a fundamental aspect of animal behaviour (Nielsen, 1983; Weller & Bennett, 2001). Felids are generally considered to be crepuscular and nocturnal in their activity (Kitchener, 1991), although they are well adapted to function in a wide range of light conditions (Sunquist & Sunquist, 2002). Numerous abiotic pressures and biotic interactions are known to shape the temporal behaviour of (cat-like) carnivores (Marinho et al., 2018), including changes in temperature (Beltran & Delibes, 1994; Podolski et al., 2013), light (Huck et al., 2017; Heurich et al., 2014) and season (Podolski et al., 2013; Manfredi et al., 2011), sex and reproductive status of the animal (Kolbe & Squires, 2007; Schmidt, 1999; Schmidt et al., 2009), predation risk (Caro, 2005; Farías et al., 2012) and human disturbance (Wolf & Ale, 2009; Ale & Brown, 2009). Owing to the dietary constraints of carnivores whose preys have their own well-defined circadian rhythms (Halle, 2000; Zielinski, 2000), the availability and vulnerability of prey is, however, considered as one of the main influences on predator temporal activity (Zielinski, 1988; Lodé, 1995). According to Optimal Foraging Theory, predators are expected to synchronize their daily activity with the activity of their most profitable prey, increasing the probability of encounters while reducing energy expenditure (MacArthur & Pianka, 1966; Monterroso et al., 2013; Emmons, 1987).
    [Show full text]
  • Volume 2. Animals
    AC20 Doc. 8.5 Annex (English only/Seulement en anglais/Únicamente en inglés) REVIEW OF SIGNIFICANT TRADE ANALYSIS OF TRADE TRENDS WITH NOTES ON THE CONSERVATION STATUS OF SELECTED SPECIES Volume 2. Animals Prepared for the CITES Animals Committee, CITES Secretariat by the United Nations Environment Programme World Conservation Monitoring Centre JANUARY 2004 AC20 Doc. 8.5 – p. 3 Prepared and produced by: UNEP World Conservation Monitoring Centre, Cambridge, UK UNEP WORLD CONSERVATION MONITORING CENTRE (UNEP-WCMC) www.unep-wcmc.org The UNEP World Conservation Monitoring Centre is the biodiversity assessment and policy implementation arm of the United Nations Environment Programme, the world’s foremost intergovernmental environmental organisation. UNEP-WCMC aims to help decision-makers recognise the value of biodiversity to people everywhere, and to apply this knowledge to all that they do. The Centre’s challenge is to transform complex data into policy-relevant information, to build tools and systems for analysis and integration, and to support the needs of nations and the international community as they engage in joint programmes of action. UNEP-WCMC provides objective, scientifically rigorous products and services that include ecosystem assessments, support for implementation of environmental agreements, regional and global biodiversity information, research on threats and impacts, and development of future scenarios for the living world. Prepared for: The CITES Secretariat, Geneva A contribution to UNEP - The United Nations Environment Programme Printed by: UNEP World Conservation Monitoring Centre 219 Huntingdon Road, Cambridge CB3 0DL, UK © Copyright: UNEP World Conservation Monitoring Centre/CITES Secretariat The contents of this report do not necessarily reflect the views or policies of UNEP or contributory organisations.
    [Show full text]
  • Gliding Ability of the Siberian Flying Squirrel Pteromys Volans Orii
    Mammal Study 32: 151–154 (2007) © the Mammalogical Society of Japan Gliding ability of the Siberian flying squirrel Pteromys volans orii Yushin Asari1,2, Hisashi Yanagawa2,* and Tatsuo Oshida2 1 The United Graduate School of Agricultural Science, Iwate University, Morioka 020-8550, Japan 2 Laboratory of Wildlife Ecology, Obihiro University of Agriculture and Veterinary Medicine, Obihiro 080-8555, Japan Abstract. Forest fragmentation is a threat to flying squirrel population due to dependence on gliding locomotion in forests. Therefore, it is essential to understand their gliding ability. The gliding locomotion of Pteromys volans orii, were observed from July 2003 to June 2005, in Obihiro, Hokkaido, Japan. The horizontal distance and glide ratio obtained from 31 glides were employed as indicators to know their gliding ability. The gliding ability was not affected by weight and sex in the Siberian flying squirrel. Mean horizontal distance and glide ratio were 18.90 m and 1.70 with great variation. Although maximum values were 49.40 m (horizontal distance) and 3.31 (glide ratio), most of the horizontal distance and glide ratio were in the ‘10–20 m’ and ‘1.0–1.5’, respectively. Therefore, to retain the flying squirrel populations, forest gaps should not exceed the distance traversable with a glide ratio of 1.0 (distance between forests/tree height at the forest edg). Key words: gliding ability, gliding ratio, horizontal distance, Pteromys volans orii. The Siberian flying squirrel, Pteromys volans, ranges The key purposes of gliding may be to avoid predators over northern parts of the Eurasia, and from Korea to or to minimize the energy costs of moving (Goldingay Hokkaido, Japan.
    [Show full text]
  • Developmental Processes of Mangrove Habitat Related To
    季 刊 地 理 学 Vol. 47 (1995) pp. 1-12 Quarterly Journal of Geography Developmental Processes of Mangrove Habitat Related to Relative Sea-level Changes at the Mouth of the Urauchi River, Iriomote Island, Southwestern Japan Kiyoshi FUJIMOTO* and Yasuhiro OIINUKI** Abstract In order to clarify geomorphologically the developmental processes of the mangrove habitats of Iriomote Island, topographic and surface geological surveys were performed along four lines in and around the mangrove habitat at the mouth of the Urauchi River in northwestern Iriomote Island. As a result, it was learned that the mangrove habitat of Iriomote Island has migrated in response to relative sea level changes. It is especially worth noting that the mangrove habitat abruptly moved seaward by a relative sea level fall that occurred about 1,000 yrs BP. During the rising sea-level phase between 2, 000 yrs BP and 1, 000 yrs BP, the mangrove forests of the island retreated, landward, which indicates that they are possibly more sensitive to sea-level changes than mangrove forests of tropical areas such as Micronesia and the Philippines, where landward movement of mangroves during this period has not recognized. On the other hand, at the Rhizophora stylosa habitat situated in the inner mangrove forest, it was found that the mangroves have maintained their habitat and position by accumulating mangrove peat against relative sea level rise after 260 yrs BP. Keywords Mangrove habitat, Relative sea level changes, Radiocarbon dating, FeSZ contents analysis, Aerial photograph, Iriomote Island habitat has little sediment supply and no geomor- L Introduction phological barrier against coastal processes.
    [Show full text]
  • Présentation Powerpoint
    The Use of ALOS AVNIR-2 and GIS tools for mapping tropical Mangroves in Iriomote Island 西表島- South Japan Plan I. Iriomote Island II. Mangroves III. Problems and Objective IV. Materials and Methods V. Nakama’s river Mangrove map VI. Conclusion I. Iriomote Island • The second largest in Okinawa. • Area = 289 km², Population < 2,000 • Visitors > 150,000 • Tropical rainforest climate. • Typhoon season (June to September). • 80% is a protected state land. • 90% dense jungle and mangrove swamps. • 34.3% forms the Iriomote National Park. • Mt. Komi (古見岳 Komidake) 470 m, is the highest point. • The Iriomote Cat (Prionailurus iriomotensis) 西表山猫. II. Mangroves – The primary coastal ecosystem in the tropical and subtropical region of the world (Mahfud, 1999). – They thrive in salty environments because they are able to obtain fresh water from saltwater. – They trap and cycle various organic materials, chemical elements, and important nutrients. They provide attachment surfaces for various marine organisms. – They provide protected nursery areas and shelters for fishes, crustaceans, and shellfish. Bruguiera gymnorrhiza Bruguiera Rhizophora stylosa Sonneratia alba Kandelia candel III. Problematic and Objective - Recognize and detect changes of Mangrove ecosystems in Iriomote Island. - High accuracy maps using remote sensing and GIS tools: ALOS AVNIR, PRISM, PALSAR - Apply this methodology on South of Sulawesi in Indonesia. Pangkep Sulawasi Makassar Makassar IV. Materials and Methods 1. ALOS AVNIR-2 – Advanced Visible and Near Infrared Radiometer type
    [Show full text]
  • Coral Reefs of Japan
    Yaeyama Archipelago 6-1-7 (Map 6-1-7) Province: Okinawa Prefecture Location: ca. 430 km southwest off Okinawa Island, including Ishigaki, Iriomote, 6-1-7-③ Kohama, Taketomi, Yonaguni and Hateruma Island, and Kuroshima (Is.). Features: Sekisei Lagoon, the only barrier reef in Japan lies between the southwestern coast of Ishigaki Island and the southeastern coast of Taketomi Island Air temperature: 24.0˚C (annual average, at Ishigaki Is.) Seawater temperature: 25.2˚C (annual average, at east off Ishigaki Is.) Precipitation: 2,061.1 mm (annual average, at Ishigaki Is.) Total area of coral communities: 19,231.5 ha Total length of reef edge: 268.4 km Protected areas: Iriomote Yonaguni Is. National Park: at 37 % of the Iriomote Is. and part of Sekisei Lagoon; Marine park zones: 4 zones in Sekisei 平久保 Lagoon; Nature Conservation Areas: Sakiyama Bay (whole area is designated as marine special zones as well); Hirakubo Protected Water Surface: Kabira and Nagura Bay in Ishigaki Is. 宇良部岳 Urabutake (Mt.) 野底崎 Nosokozaki 0 2km 伊原間 Ibarama 川平湾 Kabira Bay 6-1-7-① 崎枝湾 浦底湾 Sakieda Bay Urasoko Bay Hatoma Is. 屋良部半島 川平湾保護水面 Yarabu Peninsula Kabirawan Protected Water Surface ▲於茂登岳 Omototake (Mt.) 嘉弥真島 Koyama Is. アヤカ崎 名蔵湾保護水面 Akayazaki Nagurawan Protected Ishigaki Is. Water Surface 名蔵湾 Nagura Bay 竹富島タキドングチ 轟川 浦内川 Taketomijima Takedonguchi MP Todoroki River Urauchi River 宮良川 崎山湾自然環境保護地域 細崎 Miyara River Sakiyamawan 古見岳 Hosozaki 白保 Nature Conservation Area Komitake (Mt.) Shiraho Iriomote Is. 登野城 由布島 Kohama Is. Tonoshiro Yufujima (Is.) 宮良湾 Taketomi Is. Miyara Bay ユイサーグチ Yuisaguchi 仲間川 崎山湾 Nakama River 竹富島シモビシ Sakiyama Bay Taketomi-jima Shimobishi MP ウマノハピー 新城島マイビシ海中公園 Aragusukujima Maibishi MP Umanohapi Reef 6-1-7-② Kuroshima (Is.) 黒島キャングチ海中公園 上地島 Kuroshima Kyanguchi MP Uechi Is.
    [Show full text]
  • Protection and Recovery Program for the Iriomote Cat (Prionailurus Bengalesis Iriomotensis)
    Protection and Recovery Program for the Iriomote Cat (Prionailurus bengalesis iriomotensis) July 17, 1995 Environment Agency Ministry of Agriculture, Forestry and Fisheries I. Objectives of the Program The Iriomote cat (Prionailurus bengalensis iriomotensis) is a feline species found only on Iriomote Island in Okinawa Prefecture. The total population of this species is estimated to be about 100 in this habitat, mainly in the lowland areas of the island. This species was confirmed to represent a new species relatively recently, in 1967*. Subsequent surveys do not suggest precipitous population declines. However, given the restricted range and small population, many factors may affect the steady survival of the current wild population. These factors include the progressive shrinking and fragmentation of the natural habitat in the lowland areas critical to its survival, frequent roadkills, and the risks of introduction and outbreak of contagious disease. The objectives of this program is to ensure the stable survival of the cat in a natural state by monitoring and gathering information on the status of the species; maintaining and improving the environmental conditions necessary for the species; and mitigating and removing factors that pose threats to the species. II. Program areas Mainly on Iriomote Island (Okinawa Prefecture) III. Overview of the Program 1. Understanding the species status and monitoring The following surveys will be undertaken to appropriately and effectively implement the program, based on regular observations of the
    [Show full text]
  • Japanese Horseshoe Crab (Tachypleus Tridentatus)
    Japanese Horseshoe Crab (Tachypleus tridentatus) Table of Contents Geographic Range ........................................................................................................ 1 Occurrence within range states .................................................................................... 1 Transport and introduction ........................................................................................... 2 Population ..................................................................................................................... 4 Population genetics ..................................................................................................... 4 Divergence time estimates ........................................................................................... 4 Point of origin ............................................................................................................... 5 Dispersal patterns ........................................................................................................ 5 Genetic diversity .......................................................................................................... 5 Conservation implications ............................................................................................ 9 Habitat, Biology & Ecology ......................................................................................... 10 Spawning ................................................................................................................... 10 Larval
    [Show full text]