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1
Shaughnessy, Peter D., und Margaret Christian. „Seals (Pinnipedia) at Norfolk Island, south-west Pacific“. Australian Mammalogy 38, Nr. 2 (2016): 234. http://dx.doi.org/10.1071/am15035.
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Five seals were observed at Norfolk Island (29°S, 168°E) between 2000 and 2013. Two have been identified as Arctocephalus forsteri on the basis of photographs, a juvenile or weaned pup that weighed 9.5 kg and a subadult male. The nearest known aggregation of these fur seals is at Three Kings Islands (34°S, 172°E), 700 km to the south-east. Because New Zealand fur seals are increasing in abundance in New Zealand and Australia, sightings of vagrant fur seals at Norfolk Island are likely to increase.
2
Millar, AJK, und GT Kraft. „Catalogue of marine benthic green algae (Chlorophyta) of New South Wales, including Lord Howe Island, south-western Pacific“. Australian Systematic Botany 7, Nr. 5 (1994): 419. http://dx.doi.org/10.1071/sb9940419.
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The marine benthic green macroalgae of the New South Wales mainland and of Lord Howe Island are listed, each with bibliographic, distributional and specimen-voucher details. Included are 113 species in 9 orders, 14 families and 38 genera, of which 12 species are based on New South Wales types. With respect to biodiversity, New South Wales is as rich in numbers of genera and species as southern Australia. Eight genera (Pedobesia, Boodlea, Neomeris, Trichosolen, Ventvicaria, Caulerpella, Pseudochlorodesmis, Sporocladopsis) and 41 species are new records for the State, and 14 species are newly recorded for the Australian continent. The largest genus represented is Cladophora; 22 species are recorded, 13 from Lord Howe Island alone, and 7 are new to Australia (C. cymopoliae, C. colabense, C. dotyana, C. nigrescens, C. ohkuboana, C. patentirainea, C. ryukyuensis). Examination of type and recently collected material of Caulerpa annulata (from Port Arthur, Tasmania) shows it to be synonymous with the earlier Caulerpa hodgkinsoniae (from Ballina, New South Wales).
3
Shaughnessy, P. D., S. D. Goldsworthy und A. I. Mackay. „The long-nosed fur seal (Arctocephalus forsteri) in South Australia in 2013–14: abundance, status and trends“. Australian Journal of Zoology 63, Nr. 2 (2015): 101. http://dx.doi.org/10.1071/zo14103.
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The long-nosed (or New Zealand) fur seal (Arctocephalus forsteri) breeds in southern Australia and New Zealand. Most of the Australian population is in South Australia, between Kangaroo Island and Eyre Peninsula. Fur seal populations in southern Australia were heavily exploited by colonial sealers between 1801 and 1830, resulting in major reductions. Numbers remained low for 150 years, then slowly built up and new colonies established across their presumed former range. Here we present estimates of pup abundance at South Australia colonies, mostly during the 2013–14 breeding season. Long-nosed fur seals bred from Baudin Rocks in the south-east to Fenelon Island in the north-west. In total, 29 breeding colonies produced 20 431 pups, 3.6 times greater than the 1989–90 estimate; the increase is attributed to recovery from 19th century overharvesting. The 2013–14 pup estimate leads to an estimate of abundance of long-nosed fur seals in South Australia of 97 200. Most pups were on Kangaroo Island (49.6%) and the Neptune Islands (38.6%). New breeding colonies were identified on Williams Island and at two small sites on Kangaroo Island. The increasing trend in South Australia is likely to continue over the coming decade, primarily by expansion in colonies on Kangaroo Island and by establishment of new colonies.
4
Millar, AJK, und GT Kraft. „Catalogue of marine brown algae (Phaeophyta) of New South Wales, including Lord Howe Island, south-western Pacific“. Australian Systematic Botany 7, Nr. 1 (1994): 1. http://dx.doi.org/10.1071/sb9940001.
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This catalogue lists 139 species (in 12 orders, 26 families and 63 genera) of brown algae from New South Wales and Lord Howe Island. More than half (71) are endemic to Australia, with the remainder being very widely distributed (e.g. Europe, the Americas and Asia); 28 species have New South Wales type localities (14 from the mainland and 14 from Lord Howe Island). As a result of extensive searching of archival records, the exact locality of many 'Nov. Holl.' types is deduced to be the Sydney region of New South Wales. Four genera (Austronereia, Nemacystis, Nereia and Tomaculopsis) and 10 species are newly recorded, six species being new to the Australian continent. The largest genus represented is Sargassum, for which 37 species have been recorded, including 10 based on local types. Eleven of these Sargassum records are eliminated, the remaining 26 are in urgent need of regional monographic treatment. Eclipsed only by the Fucales (39 species in 9 genera), the order Dictyotales with 36 species in 13 genera, is the dominant group in terms of cover and possibly biomass along the mainland and at Lord Howe Island from low intertidal habitats to to depths of at least 35 m. In many areas of the seabed, brown algae and the cmstose corallines seem to be especially resilient to grazing by the sea-urchin Centrostephanis rodgersii which is presently besieging this coast.
5
Kraft, Gerald T. „Marine and estuarine benthic green algae (Chlorophyta) of Lord Howe Island, south-western Pacific“. Australian Systematic Botany 13, Nr. 4 (2000): 509. http://dx.doi.org/10.1071/sb99015.
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A taxonomic survey of marine and estuarine benthic green algae has been conducted at Lord Howe Island, the site of the world’s southernmost (at 31.5˚S) consolidated coral reef. Thirty-two genera and 71 species are described from habitats ranging from upper intertidal to 20–30-m depths. Sixteen of the species are based on Lord Howe types, and 11 are described as new. Twelve species are currently known only from the Island. Particularly well represented in the flora are the genera Enteromorpha (six species, one variety), Chaetomorpha (four species), Cladophora (13 species),Codium (five species), Caulerpa (seven species, two varieties) and Bryopsis (three species). The island is further distinctive in having two representatives of some relatively obscure genera (Cladophoropsis, Rhipiliopsis, Pseudochlorodesmis) and in being the highest-latitude collecting locality for several species. Affinities of the Lord Howe flora are primarily tropical Indo-Pacific, with very few elements otherwise restricted to southern Australia and New Zealand.
6
Millar, AJK, und GT Kraft. „Catalogue of marine and freshwater red algae (Rhodophyta) of New South Wales, including Lord Howe Island, south-western Pacific“. Australian Systematic Botany 6, Nr. 1 (1993): 1. http://dx.doi.org/10.1071/sb9930001.
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All published, and many unpublished, records of marine and freshwater red algae from the New South Wales mainland and Lord Howe Island are brought together for the first time. Of the 381 species listed (in 14 orders, 41 families and 174 genera), some 22% have New South Wales type localities (58 from the mainland and 24 from Lord Howe Island) and the remainder are either typically southern Australian, Queensland, or much more widely distributed. Twenty-five percent (100) of the species and 20% (35) of the genera are newly recorded for the New South Wales coast, one genus (Callithamniella) is new to the Pacific Ocean, and two (Ditria and Titanophora) are newly recorded for Australia. The new combination Gloiocladia minutula is also proposed. All nomenclature is updated and relevant synonyms and misapplied names are included.
7
Brunner, S., P. D. Shaughnessy und M. M. Bryden. „Geographic variation in skull characters of fur seals and sea lions (family Otariidae)“. Australian Journal of Zoology 50, Nr. 4 (2002): 415. http://dx.doi.org/10.1071/zo01056.
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Geographic variation was observed in skulls of several otariid species, with a general change in size corresponding with a change in latitude and primary productivity. The largest specimens were from cool temperate localities, conforming mostly to Rensch's rule. Skulls of Australian sea lions from Western Australia were generally smaller in condylobasal length, but were more robust than those from South Australia. The subantarctic fur seal did not conform to Bergmann's rule: skulls from Amsterdam Island (37�55´S) were largest, those from Gough Island (40�20´S) intermediate and those from Marion Island (46�55´S) the smallest. For both sexes, skulls of southern sea lions from the Falkland Islands were smaller than their equivalents from mainland South America. Similarly, skulls of South African fur seals from south-east South Africa appeared smaller than those from the west coast of South Africa and Namibia; skulls from Namibia grouped separately from those of south-east and west coast, South Africa. We postulate that the Otariidae are in the process of species divergence, much of which may be driven by local factors, particularly latitude and resources.
8
Zed, T., J. G. Conran und A. Lewis. „Vegetation Patterns in Relation to Bird Nesting Preferences on West Island, South Australia“. Transactions of the Royal Society of South Australia 130, Nr. 2 (Januar 2006): 211–26. http://dx.doi.org/10.1080/3721426.2006.10887060.
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E. Davis. Jr., William. „Heard Island: Southern Ocean Sentinel“. Pacific Conservation Biology 13, Nr. 2 (2007): 145. http://dx.doi.org/10.1071/pc070145.
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Heard Island is one of the most remote places on earth. It is of volcanic origin (and currently volcanically active) on the submarine Kerguelen Plateau in the Southern Ocean, roughly 4 000 km south-west of Australia, 1 500 km from Antarctica, 3 750 km from Africa, and 7 500 km from India. The island is 367 km2 in area at latitude 53�S, south of the Antarctic Polar Front (Antarctic Convergence), is 70% covered with glaciers, and has a geologic, biologic and human history of substantial interest. Because of its remoteness, relative recent discovery (1853), and infrequent human visitation, it is pristine with no human-introduced plants or mammals.
10
Antos, Mark, und William Steele. „A likely breeding record of Brown Quail Synoicus ypsilophorus at St Peter Island, Nuyts Archipelago, South Australia“. Australian Field Ornithology 38 (2021): 107–12. http://dx.doi.org/10.20938/afo38107112.
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This note reports observations of birds and other vertebrates during a short stay at St Peter Island, Nuyts Archipelago, South Australia, during November 2019. Of most interest was a sighting of juvenile Brown Quail Synoicus ypsilophorus, outside the generally reported range of this species and representing the first breeding record of which we are aware for this species at St Peter Island. This is one of a series of relatively recent sightings in the west of South Australia, which indicates an ongoing range expansion for this species. Further fauna surveys on the Nuyts Archipelago, with documentation of observations, are encouraged.
11
COLLOFF, MATTHEW J. „New species of Crotonia (Acari: Oribatida: Crotoniidae) from Lord Howe and Norfolk Islands: further evidence of long-distance dispersal events in the biogeography of a genus of Gondwanan relict oribatid mites“. Zootaxa 2650, Nr. 1 (19.10.2010): 1. http://dx.doi.org/10.11646/zootaxa.2650.1.1.
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Three new species of oribatid mite belonging to the genus Crotonia are described: one from Lord Howe Island (C. gorgonia sp. nov.) and two (C. norfolkensis sp. nov. and C. utricularia sp. nov.) from Norfolk Island, South-west Pacific. Crotonia gorgonia sp. nov. belongs to the Capistrata species group which reaches its highest diversity in Australia but is absent from New Zealand. Crotonia norfolkensis sp. nov. is a member of the Cophinaria group, recorded from Australia, New Zealand and New Caledonia, but with closest morphological similarity to C. brachyrostrum (Hammer, 1966) from New Zealand. Crotonia utricularia sp. nov. belongs to the Unguifera group, which reaches its highest diversity in New Zealand, is absent from Australia, and is present on Vanuatu and the Marquesas. The distribution of members of the species-groups of Crotonia in the south-western Pacific indicates that the species from Lord Howe Island has affinities with species from Australia, while the species from Norfolk Island are both most similar to species from New Zealand, and represents further evidence of the capacity of Crotonia spp. for long-distance dispersal to oceanic islands.
12
PALE, Sophia E. „CHINA, AUSTRALIA AND OCEANIA: WHO IS FOR AND WHO IS AGAINST WHOM“. Southeast Asia: Actual Problems of Development, Nr. 2(55) (2022): 64–73. http://dx.doi.org/10.31696/2072-8271-2022-2-2-55-064-073.
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In 2022, the world has globally divided itself into two parts by the redistribution of resources, and each participant is important in this confrontation. Currently, China, the main rival of the West, is fighting for the loyalty of 12 independent small developing island countries of Oceania in the South Pacific Ocean, which have the right to vote in the UN and are historically included in the sphere of defense and geopolitical influence of the United States and its loyal allies – Australia and New Zealand. Now Beijing is making every effort to take control over the island neighbors. This article also analyzes the attitude of the Pacific Island Countries to this issue.
13
Shaughnessy, Peter D., Catherine M. Kemper, David Stemmer und Jane McKenzie. „Records of vagrant fur seals (family Otariidae) in South Australia“. Australian Mammalogy 36, Nr. 2 (2014): 154. http://dx.doi.org/10.1071/am13038.
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Two fur seal species breed on the southern coast of Australia: the Australian fur seal (Arctocephalus pusillus doriferus) and the New Zealand fur seal (A. forsteri). Two other species are vagrants: the subantarctic fur seal (A. tropicalis) and the Antarctic fur seal (A. gazella). We document records of vagrant fur seals in South Australia from 1982 to 2012 based primarily on records from the South Australian Museum. There were 86 subantarctic fur seals: 49 specimens and 37 sightings. Most (77%) were recorded from July to October and 83% of all records were juveniles. All but two specimens were collected between July and November. Sightings were prevalent during the same period, but there were also nine sightings during summer (December–February), several of healthy-looking adults. Notable concentrations were near Victor Harbor, on Kangaroo Island and Eyre Peninsula. Likely sources of subantarctic fur seals seen in South Australia are Macquarie and Amsterdam Islands in the South Indian Ocean, ~2700 km south-east and 5200 km west of SA, respectively. There were two sightings of Antarctic fur seals, both of adults, on Kangaroo Island at New Zealand fur seal breeding colonies. Records of this species for continental Australia and nearby islands are infrequent.
14
GILL, ANTHONY C., JOHN J. POGONOSKI, GLENN I. MOORE und JEFFREY W. JOHNSON. „Review of Australian species of Plectranthias Bleeker and Selenanthias Tanaka (Teleostei: Serranidae: Anthiadinae), with descriptions of four new species“. Zootaxa 4918, Nr. 1 (26.01.2021): 1–116. http://dx.doi.org/10.11646/zootaxa.4918.1.1.
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Australian species of the anthiadine genera Plectranthias and Selenanthias are reviewed. Twenty-two species of Plectranthias and two species of Selenanthias are recorded from Australian waters: Plectranthias sp. 1 from a seamount north of Middleton Reef and Norfolk Ridge, Tasman Sea; P. alleni Randall from off southwest Western Australia; P. azumanus (Jordan & Richardson) from off southwest Western Australia; P. bennetti Allen & Walsh from Holmes Reef, Coral Sea; P. cruentus Gill & Roberts from Lord Howe Island, and possibly off Stradbroke Island, Queensland; P. ferrugineus n. sp. from the North West Shelf and Arafura Sea; P. fourmanoiri Randall from Christmas Island and Holmes Reef, Coral Sea; P. grahami n. sp. from off central New South Wales, Tasman Sea; P. inermis Randall from Christmas Island; P. japonicus (Steindachner) from the Arafura Sea and North West Shelf; P. kamii Randall from the Coral Sea, Lord Howe Island and Christmas Island; P. lasti Randall & Hoese from the North West Shelf and off Marion Reef, Queensland; P. longimanus (Weber) from the Timor Sea, Great Barrier Reef, Coral Sea and southern Queensland; P. maculicauda (Regan) from southeastern Australia; P. mcgroutheri n. sp. from the North West Shelf; P. megalophthalmus Fourmanoir & Randall from northeast of the Whitsunday Islands, Queensland; P. melanesius Randall from southeastern Queensland and a seamount north of Middleton Reef; P. moretonensis n. sp. from off Stradbroke Island, Queensland; P. nanus Randall from the Cocos (Keeling) Islands, Christmas Island, Great Barrier Reef and Coral Sea; P. retrofasciatus Fourmanoir & Randall from the Great Barrier Reef; P. robertsi Randall & Hoese from off Queensland, Coral Sea; P. winniensis (Tyler) from the Great Barrier Reef and Coral Sea; Selenanthias analis Tanaka from the North West Shelf and Arafura Sea; and S. barroi (Fourmanoir) from west of Lihou Reef, Coral Sea. Five of the species represent new records for Australia: P. azumanus, P. kamii, P. megalophthalmus, P. melanesius and S. barroi. Previous records of P. megalophthalmus from the North West Shelf are based on misidentified specimens of P. lasti. Records of P. wheeleri from the North West Shelf are based on specimens here identified as P. mcgroutheri n. sp. A record of P. yamakawai Yoshino from Christmas Island is based on a misidentified specimen of P. kamii. Plectranthias retrofasciatus was previously recorded from the Great Barrier Reef as P. pallidus Randall & Hoese, here shown to be a junior synonym of P. retrofasciatus. Video-based records of P. kelloggi from the Great Barrier Reef appear to be based on P. retrofasciatus. Identification keys, diagnoses, character summaries, photographs and Australian distribution information are presented for all species. Full descriptions are provided for the new species and for those newly recorded from Australia.
15
Lim, An Suk, und Hae Jin Jeong. „Primary production by phytoplankton in the territorial seas of the Republic of Korea“. Algae 37, Nr. 4 (15.12.2022): 265–79. http://dx.doi.org/10.4490/algae.2022.37.11.28.
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The primary production (PP) by phytoplankton in marine ecosystems is essential for carbon cycling and fueling food webs. Hence, estimating the PP in the territorial sea of each country is a necessary step to achieving carbon neutrality. To estimate the PP in the territorial sea of the Republic of Korea from 2005 to 2021, we analyzed various physiochemical parameters, such as sea surface temperature (SST), Secchi depth, and concentrations of chlorophyll-a and nutrients in the seas of five regions, including the East Sea, West Sea, western South Sea, eastern South Sea, and the waters off Jeju Island. During the 17-year study period, the SST tended to increase, while the nutrient concentrations declined, except in the Jeju area. Overall, the PP did not show a specific temporal trend, but daily PP in the western South Sea was the highest among the five regions. Moreover, the maximum PP in the Korean territorial waters (76,450 km2 ) was estimated at 11,227 Gg C y-1, which accounts for 0.03% of the global PP. The results may give insights into a better understanding of the PP, further resource utilization, and environmental sustainability in the studied region.
16
Delroy, LB, J. Earl, I. Radbone, AC Robinson und M. Hewett. „The Breeding and Reestablishment of the Brush-Tailed Bettong, Bettongia-Penicillata, in South-Australia“. Wildlife Research 13, Nr. 3 (1986): 387. http://dx.doi.org/10.1071/wr9860387.
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The brush-tailed bettong formerly ranged over much of southern Australia, but is now extinct except in the south-west of Western Australia and northern Queensland. A small colony was obtained from the Perth Zoo in 1975 and these were bred successfully at the Para Wirra Recreation Park near Adelaide and provided stock for a re-establishment program in South Australia. Details of the breeding program are given. Bettongs were kept in small colonies, usually one male and two or three females; the young were removed when they reached 550 g, or, with very intensive breeding, at a lower weight. The animals were fed principally on commercial kangaroo pellets with a range of supplements. Usually two offspring per year were produced although up to three were produced with intensive breeding. Females commenced breeding when approximately 4 months old. Techniques for re-establishment were tested on small islands. One island, Island A in Venus Bay, provided apparently ideal habitat and the captive-bred stock released there established quickly. Bettongs bred in the wild on two small and two large islands. However, the introduction to St Francis I., their last stronghold before extinction in South Australia, was least successful. Possible reasons for this are discussed.
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Heenan, Peter B., Ian R. H. Telford und Jeremy J. Bruhl. „Three new species of Gingidia (Apiaceae: Apioideae) from Australia and New Zealand segregated from G. montana“. Australian Systematic Botany 26, Nr. 3 (2013): 196. http://dx.doi.org/10.1071/sb13007.
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Three new species of Gingidia (Apiaceae: Apioideae) segregated from the G. montana (J.R.Forst. & G.Forst.) J.W.Dawson complex are named, with G. montana now regarded as a New Zealand endemic. The new Australian endemic, G. rupicola I.Telford & J.J.Bruhl, is restricted to the eastern escarpment of the New England Tableland, New South Wales. With few populations and limited numbers of plants, the conservation assessment of G. rupicola is Endangered. G. haematitica Heenan is described as a new species from North-West Nelson, South Island, New Zealand, where it is restricted to base-rich substrates in the Burnett Range. Because of its restricted distribution and the continued mining for dolomite at the site of the largest population, G. haematitica is considered to have a conservation assessment of Nationally Critical. The second New Zealand endemic, G. amphistoma Heenan, is known from alpine habitats in the Southern Alps, South Island. Distributions of the three new species are mapped, habitats noted, and a table compares attributes of these species and G. montana.
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Beveridge, I., T. H. Cribb und S. C. Cutmore. „Larval trypanorhynch cestodes in teleost fish from Moreton Bay, Queensland“. Marine and Freshwater Research 68, Nr. 11 (2017): 2123. http://dx.doi.org/10.1071/mf17010.
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During a helminthological examination of teleost fish of Moreton Bay (Qld, Australia), 976 fish from 13 orders, 57 families and 133 species were examined and nine species of trypanorhynch metacestodes were identified. Callitetrarhynchus gracilis (Rudolphi, 1819) was the most frequently encountered species, found in 16 species of fish, with Callitetrarhynchus speciosus (Linton, 1897), Pterobothrium pearsoni (Southwell, 1929), Otobothrium alexanderi Palm, 2004, Otobothrium mugilis Hiscock, 1954, Otobothrium parvum Beveridge & Justine, 2007, Proemotobothrium southwelli Beveridge & Campbell, 2001, Pseudotobothrium dipsacum (Linton, 1897) and Heteronybelinia cf. heteromorphi Palm, 1999 occurring in fewer host species and at lower prevalences. Comparisons are made with studies elsewhere in the world and specifically within the South-west Pacific. Of the best studied regions in the South-west Pacific (Heron Island, Lizard Island, New Caledonia and now Moreton Bay), the fauna from Moreton Bay was found to be the most distinctive, with fauna from the three reef locations sharing 35–48% of species between sites and just 12–24% with Moreton Bay. The fauna of trypanorhynch cestodes from Lizard Island and New Caledonia was found to be the most similar.
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Specht, RL, und A. Specht. „Species Richness of Sclerophyll (Heathy) Plant Communities in Australia ̵2 the Influence of Overstorey Cover“. Australian Journal of Botany 37, Nr. 4 (1989): 337. http://dx.doi.org/10.1071/bt9890337.
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The species richness (number of vascular-plant species per unit area) of sclerophyll (heathy) plant communities is examined from south-east Queensland to south-west Western Australia. The species richness of communities of heathy open forest, heathy open scrub, dry heathland and wet heathland is consist- ently similar throughout southern Australia and decreases from dry heathland (on laterite, coastal and inland localities) to heathy open forest, heathy open scrub and wet heathland. Investigation of related microcommunities at Cooloola, Stradbroke Island, Ku-ring-gai Chase and Wilsons Promontory indicates that species richness decreases linearly as overstorey cover increases. In post-fire succession on Stradbroke Island heathy woodland and Dark Island heathland, species richness declines linearly as overstorey cover increases during the regeneration of the community. The appli- cation of limiting fertiliser to Stradbroke Island heathy woodland and Dark Island heathland increases the rate of development of overstorey cover, with a simultaneous decrease in species richness. Species richness of the understorey strata of plant communities appears to be inversely related to the rate of development of foliage projective cover in the overstorey. If an environmental or biotic factor inhibits or retards the development of overstorey cover, the understorey increases in species richness. Conversely, if any environmental or biotic factor accelerates the development of overstorey cover, the understorey species show a reduction in species richness.
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Bhardwaj, Jessica, Yuriy Kuleshov, Zhi-Weng Chua, Andrew B. Watkins, Suelynn Choy und Qian (Chayn) Sun. „Evaluating Satellite Soil Moisture Datasets for Drought Monitoring in Australia and the South-West Pacific“. Remote Sensing 14, Nr. 16 (16.08.2022): 3971. http://dx.doi.org/10.3390/rs14163971.
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Soil moisture (SM) is critical in monitoring the time-lagged impacts of agrometeorological drought. In Australia and several south-west Pacific Small Island Developing States (SIDS), there are a limited number of in situ SM stations that can adequately assess soil-water availability in a near-real-time context. Satellite SM datasets provide a viable alternative for SM monitoring and agrometeorological drought provision in these regions. In this study, we investigated the performance of Soil Moisture Active Passive (SMAP), Soil Moisture and Ocean Salinity (SMOS), Soil Moisture Operational Products System (SMOPS), SM from the Advanced Microwave Scanning Radiometer 2 (AMSR-2) and SM from the Advanced Scatterometer (ASCAT) over Australia and south-west Pacific SIDS. Products were first evaluated in Australia, given the presence of several in-situ SM monitoring stations and a state-of-the-art hydrological model—the Australian Water Resources Assessment Landscape modelling system (AWRA-L). We further investigated the accuracy of SM satellite datasets in Australia and the south-west Pacific through Triple Collocation analysis with two other SM reference datasets—ERA5 reanalysis SM data and model data from the Global Land Data Assimilation System (GLDAS) dataset. All datasets have differing observation periods ranging from 1911-now, with a common period of observations between 2015–2021. Results demonstrated that ASCAT and SMOS were consistently superior in their performance. Analysis in the six south-west Pacific SIDS indicated reduced performance for all products, with ASCAT and SMOS still performing better than others for most SIDS with median R values ranging between 0.3–0.9. We conducted a case study of the 2015 El Niño and Positive Indian Ocean Dipole-induced drought in Papua New Guinea. It was shown that ASCAT is a valuable dataset indicative of agrometeorological drought for the nation, highlighting the value of using satellite SM products to provide early warning of drought in data-sparse regions in the south-west Pacific.
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Wibowo, Kunto, und Hiroyuki Motomura. „Distributional range extension of a rare scorpionfish, Hipposcorpaena filamentosa (Actinopterygii, Scorpaeniformes, Scorpaenidae)“. Acta Ichthyologica et Piscatoria 51, Nr. 1 (31.03.2021): 23–28. http://dx.doi.org/10.3897/aiep.51.63344.
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The distributional range of Hipposcorpaena filamentosa Fowler, 1938, previously recorded only from the Philippines, Indonesia, and Papua New Guinea is extended to include South Africa and Australia, on the basis of two specimens (17.2–29.5 mm standard length) which are described in detail. In addition, the first underwater photograph of H. filamentosa, taken at Kashiwa-jima Island, Kochi, Japan, is included. The species is apparently widely distributed in the Indo-West Pacific.
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Haryono, Timbul. „IN SEARCH OF POLYNESIAN ORIGINS: WITH SPECIAL REFERENCE TO LAPITA CULTURE“. Berkala Arkeologi 7, Nr. 2 (26.09.1986): 55–75. http://dx.doi.org/10.30883/jba.v7i2.460.
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The islands of Polynesia make up the largest group among the islands in the Pacific ocean. This group, in fact, consist of many islands forming a triangle. The main groups in the west are the Tongan, and Samoan and Ellice groups. The Cook, Society and Tuamotus lie in the east, with Easter Island as a far-off isolate, while the Hawaiian Islands and New Zealand are separated to the north and south respectively of the main west-east belt. The location of these islands between Asia in the west, Australia in the south and South America continent in the east is of considerable significance to the peopling and cultural development of the region. Many scholars have therefore been led to postulate the route of human movement into these scattered islands. Archaeological and anthropological researches have been carried out within the area to determine where the Polynesians originally come from. Various hypotheses have been proposed thereafter.
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COLLOFF, MATTHEW J. „A new genus of oribatid mite, Spineremaeus gen. nov. and three new species of Scapheremaeus (Acari: Oribatida: Cymbaeremaeidae) from Norfolk Island,South-west Pacific, and their biogeographical affinities“. Zootaxa 2828, Nr. 1 (21.04.2011): 19. http://dx.doi.org/10.11646/zootaxa.2828.1.2.
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A new genus of oribatid mite, Spineremaeus is erected and its type species, S. smithi sp. nov., is described from Norfolk Island, as well as three new species belonging to the genus Scapheremaeus. Spineremaeus is morphologically closest to the Emarginatus species-group of Scapheremaeus, found in Australia, Java and New Zealand. Scapheremaeus pinguis sp. nov. is closest morphologically to S. emarginatus from New Zealand. Scapheremaeus pacificus sp. nov. and S. tumidus sp. nov., members of the Carinatus species-group, are closest morphologically to each other and to S. insularis, also from New Zealand. Thus all four cymbaeremaeid species from Norfolk Island show strongest biogeographical affinities with the oribatid fauna of New Zealand rather than Australia.
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Sarmili, Lili. „OPENING STRUCTURE OF THE BONE BASIN ON SOUTH SULAWESI IN RELATION TO PROCESS OF SEDIMENTATION“. BULLETIN OF THE MARINE GEOLOGY 30, Nr. 2 (15.02.2016): 97. http://dx.doi.org/10.32693/bomg.30.2.2015.79.
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Sulawesi Island is situated on the three major plates, namely the Indo-Australian plate together with Continent Australia (Australian Craton) plate moves towards the North - Northeast and crust Pacific - Philippines moves towards the West - Northwest, causing the collision with the Eurasian plate (Sunda Land) which more passive or stable. The Bone basin is located between South Sulawesi and Southeast Sulawesi arms. This basin is formed by several fault system, such as, Walanae, Palukoro, West and East Bone faults and others. Several active faults are likely to be extended each other into the openings structure and characterized by the accumulation of young sediment in the Bone basin. Keywords: Sulawesi, collision Bone basin, faults, sedimentation Pulau Sulawesi merupakan tempat pertemuan antara tiga lempeng besar, yaitu lempeng Indo-Australia bersama-sama dengan lempeng Benua Australia (Australian Craton) bergerak ke arah Utara - Timurlaut dan Kerak Pasifik - Filipina bergerak ke arah Barat - Baratlaut sehingga terjadi tumbukan dengan lempeng Eurasia (Daratan Sunda) lebih bersifat pasif atau diam. Secara geologi Cekungan Bone terletak diantara Lengan Sulawesi Selatan dan Lengan Sulawesi Tenggara. Cekungan ini terbentuk oleh beberapa sistem sesar yaitu sesar Walanae, Palukoro, Timur dan Barat Bone dan lainnya. Beberapa sesar aktif tersebut kemungkinannya saling tarik menarik menjadi struktur bukaan dan ditandai dengan adanya akumulasi sedimentasi muda di cekungan Bone. Kata kunci: Sulawesi, tumbukan, Cekungan Bone, Sesar, Sedimentasi
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Shaughnessy, Peter D., und Simon D. Goldsworthy. „Dispersion of long-nosed fur seals (Arctocephalus forsteri) determined by tagging“. Australian Journal of Zoology 67, Nr. 3 (2019): 173. http://dx.doi.org/10.1071/zo20032.
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Long-nosed fur seals (Arctocephalus forsteri) were tagged as pups in colonies on Kangaroo Island, South Australia in eight consecutive pupping seasons from 1988–89 to 1995–96. Thirty-nine tagged animals were sighted on the southern Australian coast, being 0.89% of those tagged. They were aged from 9 months to 14 years 6 months, with half in their second and third years. Most records (88%) were of animals that moved eastwards. The most distant records were from Sydney in the east (1700 km), south of Tasmania in the south (1240 km) and Head of Bight in the west (700 km). One animal was seen twice, both times on the north coast of Kangaroo Island, once underwater and two years later ashore. Satellite telemetry studies of juvenile A. forsteri from Kangaroo Island showed that they typically forage in pelagic waters ~1000 km further south in association with the subtropical front. The study reported here shows that some animals tagged as pups disperse widely as juveniles around the southern Australian coast. The possibility of genetic interchange between breeding colonies is suggested by sightings of three tagged females aged 4 years and older at non-natal colonies.
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Aldrich, Robert. „The Decolonisation of the Pacific Islands“. Itinerario 24, Nr. 3-4 (November 2000): 173–91. http://dx.doi.org/10.1017/s0165115300014558.
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At the end of the Second World War, the islands of Polynesia, Melanesia and Micronesia were all under foreign control. The Netherlands retained West New Guinea even while control of the rest of the Dutch East Indies slipped away, while on the other side of the South Pacific, Chile held Easter Island. Pitcairn, the Gilbert and Ellice Islands, Fiji and the Solomon Islands comprised Britain's Oceanic empire, in addition to informal overlordship of Tonga. France claimed New Caledonia, the French Establishments in Oceania (soon renamed French Polynesia) and Wallis and Futuna. The New Hebrides remained an Anglo-French condominium; Britain, Australia and New Zealand jointly administered Nauru. The United States' territories included older possessions – the Hawaiian islands, American Samoa and Guam – and the former Japanese colonies of the Northern Marianas, Mar-shall Islands and Caroline Islands administered as a United Nations trust territory. Australia controlled Papua and New Guinea (PNG), as well as islands in the Torres Strait and Norfolk Island; New Zealand had Western Samoa, the Cook Islands, Niue and Tokelau. No island group in Oceania, other than New Zealand, was independent.
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Bougher, N. L., und J. A. Friend. „Fungi consumed by translocated Gilbert's potoroos (Potorous gilbertii) at two sites with contrasting vegetation, south coastal Western Australia“. Australian Mammalogy 31, Nr. 2 (2009): 97. http://dx.doi.org/10.1071/am09012.
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Gilbert’s potoroo (Potorous gilbertii) was previously widespread in south-west Australia but is now restricted to one location – a granitic area of shrubby heath at Two Peoples Bay Nature Reserve on the south coast of Western Australia. To alleviate the threat of extinction a program is under way to establish potoroos in other locations. At Two Peoples Bay Gilbert’s potoroos feed almost exclusively on truffle fungi. However, it was not known whether potoroos translocated to any new areas would be able to rapidly access and consume fungi after translocation, or whether truffles could be a sustainable food supporting breeding populations of potoroos in translocation sites. Furthermore, it was not known whether translocation of potoroos would be successful only in areas with vegetation similar to their refuge at Two Peoples Bay. The current study addressed these questions by analysing the diet of potoroos translocated into two contrasting areas – one on Bald Island with similar topography and vegetation to that of Two Peoples Bay, and the other a 14-ha enclosure on the mainland dominated by Eucalyptus–Allocasuarina woodland. The diet of potoroos was characterised by microscopic examination of scats from individuals trapped after their translocation to these areas. At Bald Island a diverse range of fungi was consumed immediately after translocation. Four potoroos released onto the island only 4–8 days previously consumed 23 species of fungi. Consumption was sustained over time. Three potoroos released onto Bald Island 1–2 years previously and one island-born individual consumed 27 species of fungi during a two-day sampling period. Nine of the 27 fungi species were the same as those that had been consumed by the potoroos within days after their release onto the island. This indicates that production of fungi and their consumption by potoroos on the island was sustained at least 1–2 years after translocation. Potoroos bred on Bald Island during this period. During the same period, two potoroos that were moved from captivity to the mainland site (Ryedene) were consuming six species of truffles within 29 days after release, and 14 species within three months. Such data indicate that a wider selection of vegetation types and areas than just those similar to where potoroos occur at Two Peoples Bay may be able to sustain potoroos and should be investigated for future translocations.
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Tidemann, CR. „Morphological Variation in Australian and Island Populations of Goulds Wattled Bat, Chalinolobus-Gouldii (Gray) (Chiroptera, Vespertilionidae)“. Australian Journal of Zoology 34, Nr. 4 (1986): 503. http://dx.doi.org/10.1071/zo9860503.
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Univariate and bivariate analyses were used to demonstrate that C. gouldii increases in size from north to south and, to a lesser extent, from west to east. There is little difference between the sexes in most dimensions. Although significant differences exist between animals from localities widely separated geographically, multivariate analyses suggest that C. gouldii once occurred over most of mainland Australia, Tasmania, Norfolk I. and New Caledonia. The species appears to have become extinct or very rare in recent times on Norfolk I.; the possibility of re-introduction is discussed.
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Pichon, A., L. Arvanitakis, O. Roux, A. A. Kirk, C. Alauzet, D. Bordat und L. Legal. „Genetic differentiation among various populations of the diamondback moth, Plutella xylostella Lepidoptera Yponomeutidae“. Bulletin of Entomological Research 96, Nr. 2 (April 2006): 137–44. http://dx.doi.org/10.1079/ber2005409.
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AbstractGenetic variation among 14 populations of Plutella xylostella (Linnaeus) from USA (Geneva, New York), Brazil (Brasilia), Japan (Okayama), The Philippines (Caragan de Oyo), Uzbekistan (Tashkent), France (Montpellier), Benin (Cotonou), South Africa (Johannesburg), Réunion Island (Montvert), and five localities in Australia (Adelaide, Brisbane, Mareeba, Melbourne, Sydney) were assessed by analysis of allozyme frequencies at seven polymorphic loci. Most of the populations were not in Hardy–Weinberg equilibrium and had a deficit in heterozygotes. The global differentiation among populations was estimated by the fixation index (Fst) at 0.103 for the 14 populations and at 0.047 when populations from Australia and Japan, which differed most and had a strong genetic structure, were excluded from the analysis. By contrast, the populations from Benin (West Africa) and Brazil (South America) were very similar to each other. Genetic differentiation among the populations was not correlated with geographical distance.
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Mackenzie, Lydia, Henk Heijnis, Patricia Gadd, Patrick Moss und James Shulmeister. „Geochemical investigation of the South Wellesley Island wetlands: Insight into wetland development during the Holocene in tropical northern Australia“. Holocene 27, Nr. 4 (28.09.2016): 566–78. http://dx.doi.org/10.1177/0959683616670219.
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The South Wellesley Islands in the Gulf of Carpentaria, northern Australia, were the recent focus of a palynological investigation which found vegetation change during the Holocene was driven by coastal progradation and regional climate. Here, we present new elemental data from x-ray fluorescence core scanning which provides non-destructive, continuous and high resolution analysis from three wetlands across Bentinck Island, the largest of the South Wellesley Islands. Elemental data and grain size analyses are combined with lead-210 (210Pb) and accelerator mass spectrometry (AMS) carbon-14 (14C) dates. An open coastal environment was present 1250 cal. a BP on the south east coast of Bentinck Island, with sediment supply incorporating fluvial deposition and detrital input of titanium and iron from eroding lateritic bedrock. Prograding shorelines, dune development and river diversion formed a series of swales parallel to the coast by ~800 cal. a BP, forming the Marralda wetlands. Wetlands developed at sites on the north and west coasts ~500 and ~450 cal. a BP, respectively. Geochemical and grain size analyses indicate that wetlands formed as accreting tidal mudflats or within inter-dune swales that intercepted groundwater draining to the coastal margins. The timing of wetland initiation indicates localised late-Holocene sea level regression, stabilisation and coastal plain development in the Gulf of Carpentaria. Elemental data provide new records of wetland development across Bentinck Island, highlighting the value of a multi-proxy approach to understanding environmental change during the Holocene in tropical northern Australia.
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Shepherd, SA. „Studies on southern Australian Abalone (Genus Haliotis). VIII. Growth of juvenile H. laevigata“. Marine and Freshwater Research 39, Nr. 2 (1988): 177. http://dx.doi.org/10.1071/mf9880177.
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The growth of juvenile H. laevigata was studied by analysis of sequences of length-frequency distributions obtained in below- and above-boulder habitats at West Island, South Australia. The mean growth rate overall is 1.69 mm month-1 and is linear with length for the first 5 years, but thereafter declines with increasing length. The mean growth rate of four groups of marked H. laevigata aged 1 and 3 years is 1.6-2.1 mm month-1, and thus supports the estimation of growth rate from analysis of length-frequency distributions.
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Copley, P. B., und P. J. Alexander. „Overview of The Status of Rock-wallabies in South Australia.“ Australian Mammalogy 19, Nr. 2 (1996): 153. http://dx.doi.org/10.1071/am97153.
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The status of Yellow-footed Rock-wallabies (Petrogale xanthopus) and Black-footed Rock-wallabies (P. lateralis) in South Australia was assessed by comparing recent survey and census data with previously collated information about the distribution and relative abundance of each taxon. Petrogale xanthopus has maintained most of its known geographic range within the state; however, its relative abundance has declined significantly and 35 (or 15%) of a total of 229 recorded colonies have become extinct since European settlement. Eight of these colony extinctions have occurred over the past 25 years; three of them since 1981. As this species is continuing to decline it should be regarded as threatened within the state. Petrogale lateralis has at least two sub-species which occur in South Australia. Petrogale lateralis pearsoni is endemic to the state and occurs on offshore islands. Since 1960 its natural occurrence of about 3-500 individuals on North Pearson Island has been expanded to four other islands through translocations and the total population is now about 700-1100 animals. This subspecies, while not occurring in large numbers, is nonetheless relatively secure due to the additional populations established and the fact that these are on islands isolated from most mainland threats. The mainland subspecies, Petrogale lateralis MacDonnell Ranges race, by comparison has suffered a drastic reduction in both geographic range and abundance to the point where it is South Australia’s most critically endangered vertebrate taxon. It has declined from being a very common species in the state’s far north- west to only two known, widely separated, colonies which total less than 100 animals between them. Management and research recommendations are provided.
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„Spongospora subterranea f.sp. subterranea. [Distribution map].“ Distribution Maps of Plant Diseases, Nr. 5) (01.08.1987). http://dx.doi.org/10.1079/dmpd/20046500034.
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Abstract A new distribution map is provided for Spongospora subterranea (Wallr.) Lagerh. f.sp. subterranea. Hosts: potato (Solanum tuberosum). Information is given on the geographical distribution in Africa, Algeria, Egypt, Kenya, Madagascar, Mauritius, Mozambique, South Africa, Tanzania, Zimbabwe, Asia, China, India, Maharashtra, Himalayas, Madras, Japan, Lebanon, Nepal, Philippines, Sri Lanka, Taiwan, Kazakhstan, Kirgizia, Australasia & Oceania, Australia, New South Wales, South Australia, Western Australia, Victoria, Queensland, Tasmania, Hawaii, New Zealand, Europe, Austria, Belgium, Bulgaria, Cyprus, Czechoslovakia, Denmark, Faroe Islands, Finland, France, Germany, Greece, Iceland, Irish Republic, Italy, Sardinia, Netherlands, Norway, Poland, Portugal, Romania, Sweden, Switzerland, UK, USSR, Yugoslavia, North America, Canada, Alberta, British Columbia, Graham Island, Lulu Island, New Brunswick, Newfoundland, Nova Scotia, Ontario, Prince Edward Island, Quebec, Mexico, USA, Maine, Pennsylvania, Minnesota, Wyoming, Washington, Alabama, Florida, Missouri, Oklahoma, South Carolina, Central America & West Indies, Costa Rica, Panama, South America, Bolivia, Brazil, Chile, Colombia, Ecuador, Falkland Islands, Peru, Uruguay, Venezuela.
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„Xiphinema rivesi. [Distribution map].“ Distribution Maps of Plant Diseases, October (18.11.2021). http://dx.doi.org/10.1079/dmpd/20210455197.
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Abstract A new distribution map is provided for Xiphinema rivesi Dalmasso. Enoplea: Dorylaimida: Longidoridae. Hosts: polyphagous. Information is given on the geographical distribution in Africa (Egypt), Asia (Iran, Pakistan), Europe (France, Germany, Italy, Portugal, Slovenia, Spain, Canary Islands), North America (Canada, Ontario, Quebec, Prince Edward Island, Guadeloupe, United States, Arkansas, California, Colorado, Georgia, Idaho, Illinois, Iowa, Kansas, Maryland, Michigan, Montana, Nebraska, New Jersey, New York, Oregon, Pennsylvania, Rhode Island, South Carolina, Tennessee, Vermont, Virginia, Washington, West Virginia), Oceania (Australia, Victoria, Western Australia, Samoa, Tonga), South America (Argentina, Chile, Peru).
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„Puccinia polysora. [Distribution map].“ Distribution Maps of Plant Diseases, Nr. 6) (01.08.1992). http://dx.doi.org/10.1079/dmpd/20046500237.
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Abstract A new distribution map is provided for Puccinia polysora Underw. Hosts: Maize (Zea mays). Information is given on the geographical distribution in Africa, Agalega Island, Benin, Cameroon, Chad, Congo, Ethiopia, Equatorial Guinea, French Equitorial Africa, French West Africa, Gabon, Ghana, Guinea, Ivory Coast, Kenya, Liberia, Madagascar, Malawi, Mauritius, Mozambique, Niger, Nigeria, Reunion, Rodriguez Island, Senegal, Sierra Leone, Somalia, South Africa, Sudan, Tanzania, Togo, Uganda, Zaire, Zambia, Zimbabwe, Asia, Brunei, China, Hainan Island, Christmas Island, India, West Bengal & Sikkim, Karnataka, Indonesia, Celebes, Java, West Irian, Japan, Kampuchea, Malaysia, Peninsular Malaysia, Sabah, Sarawak, Philippines, Taiwan, Thailand, Vietnam, Australasia & Oceania, Australia, Queensland, Cocos Island, Fiji, New Caledonia, Papua New Guinea, Solomon Islands, Tonga Vanuatu, Western Samoa, North America, Mexico, USA, Alabama, Arkansas, Florida, Georgia, Hawaii, Illinois, Indiana, Iowa, Kansas, Louisiana, Massachussetts, Maryland, Missouri, Mississippi, New Jersey, North Carolina, Ohio, Oklahoma, South Carolina, Texas, Virginia, Wisconsin, Central America & West Indies, Belize, Canal Zone, Costa Rica, Cuba, Dominican Republic, El Salvador, Grenada, Guatemala, Honduras, Jamaica, Martinique, Nicaragua, Panama, Puerto Rico, St Lucia, St Vincent, Trinidad & Tobago, South America, Bolivia, Brazil, Rio de Janeiro, Pennsylvania, Rio Grande do Sul, Colombia, Guyana, Peru, Venezuela.
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„Elsinoe veneta. [Distribution map].“ Distribution Maps of Plant Diseases, Nr. 2) (01.08.1993). http://dx.doi.org/10.1079/dmpd/20046500503.
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Abstract A new distribution map is provided for Elsinoe veneta (Burkh.) A. E. Jenk. Hosts: Rubus spp. Information is given on the geographical distribution in Africa, South Africa, Zimbabwe, Australasia, Australia, New South Wales, South Australia, Tasmania, Victoria, New Zealand, Europe, Bulgaria, Denmark, France, Germany, Greece, Latvia, Netherlands, Norway, Poland, Romania, Russia, Leningrad region, Byelorussia, Bryansk, UK, England, Scotland, North America, Canada, British Columbia, Manitoba, New Brunswick, Nova Scotia, Ontario, Prince Edward Island, Quebec, Saskatchewan, USA, Central America & West Indies, El Salvador, South America, Argentina, Brazil, Chile.
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„Alternaria passiflorae. [Distribution map].“ Distribution Maps of Plant Diseases, No.October (01.08.2014). http://dx.doi.org/10.1079/dmpd/20143369342.
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Abstract A new distribution map is provided for Alternaria passiflorae Simmonds. Dothideomycetes: Pleosporales: Pleosporaceae. Host: passionflower (Passiflora sp.). Information is given on the geographical distribution in Asia (Bhutan, China, Guangdong, India, Kerala, Sikkim, West Bengal), Africa (Kenya, Malawi, Mauritius, South Africa, Tanzania, Uganda, Zambia, Zimbabwe), North America (Canada, British Columbia, Florida, Hawaii), South America (Brazil, Sao Paulo, Colombia, Venezuela), Oceania (Australia, Queensland, Western Australia, Fiji, New Caledonia, New Zealand, Niue, Norfolk Island, Papua New Guinea, Tonga).
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„Diplocarpon mespili. [Distribution map].“ Distribution Maps of Plant Diseases, Nr. 3) (01.08.1992). http://dx.doi.org/10.1079/dmpd/20046500327.
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Abstract A new distribution map is provided for Diplocarpon mespili (Sorauer) B. Sutton. Hosts: Rosaceae. Information is given on the geographical distribution in Africa, Ethiopia, Kenya, Madagascar, Malawi, Morocco, Mozambique, South Africa, Zimbabwe, Asia, Afghanistan, India, Kashmir, Iran, Israel, Japan, Turkey, USSR, Alma-Ata, Armenia, Kirgiz, Tashkent, Yemen, Australasia & Oceania, Australia, New South Wales, Queensland, Victoria, Western Australia, Tasmania, New Zealand, Europe, Austria, Bulgaria, Channel Island, Jersey, Denmark, France, Germany, Greece, Hungary, Italy, Netherlands, Norway, Poland, Romania, Spain, Switzerland, UK, USSR, Caucasus, Lithuania, Moldavia, Ukraine, Kraznodar, Yugoslavia, North America, Canada, British Columbia, Manitoba, Nova Scotia, Ontario, Prince Edward Island, Quebec, Saskatchewan, Mexico, USA, Central America & West Indies, Central America, Panama, South America, Argentina, Brazil, Sao Paulo, Minas Gerais, Rio Grande do Sul, Chile, Colombia, Uruguay.
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„Corticium rolfsii. [Distribution map].“ Distribution Maps of Plant Diseases, Nr. 4) (01.08.1992). http://dx.doi.org/10.1079/dmpd/20046500311.
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Abstract A new distribution map is provided for Corticium rolfsii Curzi. Hosts: Various. Information is given on the geographical distribution in Africa, Angola, Benin, Botswana, Burkina Faso, Burundi, Cameroon, Cape Verde, Central African Republic, Congo, Egypt, Equatorial Guinea, Ethiopia, French West Africa, Gabon, Gambia, Ghana, Guinea, Ivory Coast, Kenya, Lesotho, Liberia, Madagascar, Malawi, Mali, Mauritania, Mauritius, Morocco, Mozambique, Niger, Nigeria, Rodriguez, Rwanda, Senegal, Sechelles, Sierra Leone, Somalia, South Africa, Sudan, Tanzania, Togo, Uganda, Zaire, Zambia, Zimbabwe, Asia, Andaman Islands, Bangladesh, Brunei, Burma, China, Sichuan, Yunnan, Hong Kong, India, Assam, Mahharashtra, Nagaland, Indonesia, Java, Sumatra, Irian Jaya, Iran, Iraq, Israel, Japan, Kampuchea, Korea, Laos, Lebanon, Malaysia, Peninsular, Sabah, Sarawak, Nepal, Okinawa, Pakistan, Philippines, Saudi Arabia, Syria, Taiwan, Thailand, Turkey, Vietnam, USSR, Caucasus, Georgia, Krasnodar, Australasia & Oceania, Australia, New South Wales, Queensland, Tasmania, Western Australia, Northern Territory, Vict, South Australia, Fiji, French Polynesia, Guam, Hawaii, New Caledonia, New Zealand, Norfolk Island, Papua New Guinea, Solomon Island, Tonga, Vanuatu, Europe, Channel Island, Guernsey, Jersey, Cyprus, Denmark, Germany, Greece, Italy, Netherlands, Portugal, Sardinia, Spain, UK, England, USSR, Moldavia, Yugoslavia, North America, Bermuda, Mexico, USA, Central America & West Indies, Antigua, Antilles, Barbados, Belize, Costa Rica, Cuba, Dominica, Dominican Republic, El Salvador, Guadeloupe, Guatemala, Haiti, Honduras, Jamaica, Martinique, Montserrat, Nicaragua, Panama, Puerto Rico, St Kitts, St Lucia, St Vincent, Trinidad & Tobago, South America, Argentina, Brazil, Sao Paulo, Minas Gerais, Chile, Colombia, French Guiana, Guyana, Peru, Surinam, Uruguay, Venezuela.
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„Spodoptera litura. [Distribution map].“ Distribution Maps of Plant Pests, Nr. 2nd Revision) (01.08.1993). http://dx.doi.org/10.1079/dmpp/20046600061.
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Abstract A new distribution map is provided for Spodoptera litura (Fabricius). Lepidoptera: Noctuidae. Attacks rice, peanut, cabbage, tobacco, strawberry, sugarbeet. Information is given on the geographical distribution in Asia, Afghanistan, Andaman Islands, Bangladesh, Brunei, Burma, Cambodia, China, Fujian, Guangdong, Guangxi, Guizhou, Hubei, Hunan, Jiangsu, Jilin, Shandong, Zhejiang, Christmas Island, Cocos-Keeling Islands, India, Andhra Pradesh, Assam, Bihar, Gujarat, Haryana, Himachal Pradesh, Jammu & Kashmir, Karnataka, Kerala, Madhya Pradesh, Maharashtra, Orissa, Punjab, Rajasthan, Sikkim, Tamil Nadu, Uttar Pradesh, West Bengal, Indonesia, Java, Kalimantan, Moluccas, Sulawesi, Sumatra, Japan, Korea, Laos, Malaysia, Sabah, Sarawak, West Malaysia, Maldive Islands, Myanmar, Nepal, Nicobar Islands, Ogaswara-shoto, Oman, Pakistan, Philippines, Singapore, Sri Lanka, Taiwan, Thailand, Vietnam, Australasia and Pacific Islands, Australia, Queensland, New South Wales, Western Australia, Caroline Islands, Fiji, Henderson Island, Irian Jaya, Kermadec Islands, Krirbati, Line Islands, Loyalty Islands, Mariana Islands, Marquesas Islands, Marshall Islands, Midway Island, New Caledonia, New Zealand, Niue, Norfolk Island, Papua New Guinea, Phoenix Islands, Pitcairn Island, Rotuma, American Samoa, Society Islands, Solomon Islands, tongo, Tuamotu, Tubuai Islands, Tuvalu, Vanuatu, Wake Island, Wallis Islands.
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„Aulacorthum circumflexum. [Distribution map].“ Distribution Maps of Plant Pests, Nr. 1st Revision) (01.08.1990). http://dx.doi.org/10.1079/dmpp/20046600172.
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Abstract A new distribution map is provided for Aulacorthum circumflexum (Buckton). Hemiptera: Aphidoidea: Aphididae (crescent-marked lily aphid, mottled arum aphid). Attacks a wide range of herbaceous plants, including ornamentals. Information is given on the geographical distribution in Europe, Austria, Belgium, Bulgaria, Czechoslovakia, Finland, France, Germany, Iceland, Ireland, Italy, Netherlands, Norway, Poland, Portugal, Romania, Spain, Sweden, Switzerland, Turkey, United Kingdom, USSR, Latvian SSR, Ukraine, Uzbekistan, Africa, Canary Islands, Gough Island, Morocco, Sao Tomé, South Africa, Tristan da Cunha, Australasia and Pacific islands, Australia, Campbell Island, Crozet Island, Hawaii, Kiribati, New Zealand, Papua New Guinea, Asia, India, Assam, Meghalaya, West Bengal, Indonesia, Java, Sulawesi, Sumatra, Iran, Japan, Malaysia, Sabah, West Malaysia, Philippines, North America, Canada, USA, Central America and Caribbean, Costa Rica, Cuba, Puerto Rico, South America, Argentina, Brazil, Chile, Colombia, Peru, Venezuela.
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„Botrytis allii. [Distribution map].“ Distribution Maps of Plant Diseases, Nr. 4) (01.08.1987). http://dx.doi.org/10.1079/dmpd/20046500169.
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Abstract A new distribution map is provided for Botrytis allii Munn. Hosts: Onion (Allium cepa), leek (Allium porrum), shallot (Allium ascalonicum). Information is given on the geographical distribution in Africa, Canary islands, Egypt, Kenya, Morocco, South Africa, Tanzania, Zambia, Asia, Afghanistan, China, Henan, Cyprus, Iran, Iraq, Israel, Japan, Jordan, Korea, Nepal, Pakistan, Saudi Arabia, Taiwan, Vietnam, Australasia & Oceania, Australia, New South Wales, South Australia, Western Australia, Tasmania, Victoria, New Zealand, Europe, Austria, Belgium, Bulgaria, Denmark, Finland, France, Germany, Italy, Netherlands, Norway, Poland, Romania, UK, USSR, Yugoslavia, North America, Canada, Alberta, British Columbia, Manitoba, Ontario, Prince Edward Island, Quebec, Saskatchewan, Mexico, USA, Central America & West Indies, Costa Rica, Guatemala, Jamaica, Panama, Salavador, South America, Brazil, Chile, Venezuela.
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„Pyrenophora chaetomioides. [Distribution map].“ Distribution Maps of Plant Diseases, Nr. 4) (01.08.1991). http://dx.doi.org/10.1079/dmpd/20046500105.
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Abstract A new distribution map is provided for Pyrenophora chaetomioides Speg. Hosts: Oats (Avena). Information is given on the geographical distribution in Africa, Angola, Egypt, Ethiopia, Kenya, Madagascar, Morocco, South Africa, Asia, Bhutan, Brunei, China, Jiangsu, India, Israel, Japan, Nepal, Pakistan, Taiwan, Turkey, USSR, Latvia, Byelorussia, Russian Far East, Tashkent, Tomsk, Australasia & Oceania, Australia, New South Wales, Queensland, South Australia, Western Australia, New Zealand, Europe, Austria, Belgium, Bulgaria, Cyprus, Denmark, Finland, France, Germany, Irish Republic, Italy, Netherlands, Norway, Romania, Spain, Sweden, UK, Britain and Northern Ireland, North America, Canada, Prince Edward Island, Mexico, USA, Arkansas, Texas, Hawaii, Central America & West Indies, Cuba, Guatemala, Puerto Rico, South America, Argentina, Bolivia, Brazil, Colombia.
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„Phytophthora cinnamomi. [Distribution map].“ Distribution Maps of Plant Diseases, Nr. 6) (01.08.1991). http://dx.doi.org/10.1079/dmpd/20046500302.
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Abstract A new distribution map is provided for Phytophthora cinnamomi Rands. Hosts: Ananas, Cinchona, Cinnamomum, Castanea, Persea, Pinus, Rhododendron and others. Information is given on the geographical distribution in Africa, Burundi, Cameroon, Congo, Gabon, Guinea, Ivory Coast, Kenya, Morocco, South Africa, Uganda, Zambia, Zimbabwe, Asia, China, Jiangsu, India, Madras, Andhra, Pradesh, West Bengal, Indonesia, Java, Sumatra, Israel, Japan, Malaysia, Peninsular, Sabah, Philippines, Taiwan, Turkey, Vietnam, USSR, Georgia, Australasia & Oceania, Australia, New South Wales, Queensland, Victoria, Western Australia, South Australia, Tasmania, Northern Territory, Cook Island, Fiji, Hawaii, New Zealand, Okinawa, Papua New Guinea, Sumatra, Europe, Azores, Belgium, France, Corsica, Germany, Irish Republic, Italy, Netherlands, Portugal, Spain, Switzerland, UK, USSR, Black Sea Region, Yugoslavia, North America, Canada, British Columbia, Mexico, USA, Central America & West Indies, Barbados, Belize, Costa Rica, Cuba, Dominican Republic, Guatemala, Honduras, Jamaica, Panama, Puerto Rico, Salvador, St Lucia, St Vincent, Trinidad, South America, Argentina, Bolivia, Brazil, Sao Paulo, Brasilia, Chile, Colombia, Guyana, Peru, Venezuela.
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Selamat, Muhammad Banda, Mahatma Lanuru und Amir Hamzah Muhiddin. „SPATIAL COMPOSITION OF BENTHIC SUBSTRATE AROUND BONTOSUA ISLAND“. Jurnal Ilmu Kelautan SPERMONDE 4, Nr. 1 (03.04.2018). http://dx.doi.org/10.20956/jiks.v4i1.3801.
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Coral reefs and seagrass are natural fortress for small islands from waves and ocean currents. The spatial distribution of these benthic substrate should be known and monitored regularly. This study aims were to map existing benthic substrates on the reef flat of Bontosua Island, determine the spatial composition and develop index ratio. Benthic substrates were surveyed using geotagging technique. Their distribution were estimate using Quickbird image that was rectified and classified using ISOcluster method and validate by 240 selected photos. The seagrass were surveyed at 8 stasions to record percent cover and species composition. Depth profiles were track along 10 reef flat line segment. Bontosua Island has an elongated shape from South to Northwest. This study had produced a benthic substrate distribution map with thematic accuracy 76%. Total area able to map were 54.2 hectares. About 43% benthic substrates at Bontosua were mixture of coral rubble, seagrass and algae, 20% was mixture of rubble and algae, 16% dominated by seagrass, 13% mixture of sand and seagrass and 8% substrate were dominated by live coral. There were eight seagrass species found with average percent cover 37.2 ± 12.5 percent. The spatial ratio of live coral, seagrass and mixed substrate for West side reef flat was 2:20:49 and 1:9:9 for East side. This indicate that the distribution of benthic substrates on the West side is much wider than on the East side. This approach potentially applied to study the relationship between benthic substrate composition and the deformation of small islands.
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„Pseudomonas syringae pv. mori. [Distribution map].“ Distribution Maps of Plant Diseases, No.October (01.08.2009). http://dx.doi.org/10.1079/dmpd/20093245828.
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Abstract A new distribution map is provided for Pseudomonas syringae pv. mori (Boyer & Lambert) Young et al., Bacteria. Hosts: mulberry (Morus spp.), hemp (Cannabis sativa) and Lima bean (Phaseolus lunatus). Information is given on the geographical distribution in Europe (Czechoslovakia, France, Mainland France, Germany, Hungary, Italy, Mainland Italy, Romania, Serbia), Asia (China, Anhui, Fujian, Guangdong, Guangxi, Hebei, Hong Kong, Hubei, Jiangsu, Shandong, Sichuan, Zhejiang, Georgia, India, Andhra Pradesh, Karnataka, Kerala, Tamil Nadu, West Bengal, Iran, Japan, Honshu, Korea Democratic People's Republic, Korea Republic, Pakistan, Turkey), Africa (South Africa, Tanzania, Uganda), North America (Canada, Ontario, Prince Edward Island, USA, Connecticut, Massachusetts, Ohio), South America (Brazil, Minas Gerais), Oceania (Australia, New South Wales, Queensland, South Australia, Tasmania, Victoria, Western Australia, New Zealand).
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„Pseudomonas marginalis pv. marginalis. [Distribution map].“ Distribution Maps of Plant Diseases, Nr. 3) (01.08.1993). http://dx.doi.org/10.1079/dmpd/20046500357.
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Abstract A new distribution map is provided for Pseudomonas marginalis pv. marginalis (Brown) Stevens. Hosts: Lettuce (Lactuca sativa) and a wide range of other hosts. Information is given on the geographical distribution in Africa, Egypt, Ethiopia, Kenya, Nigeria, South Africa, Tanzania, Uganda, Asia, India, Japan, Korea, Nepal, Australasia, Australia, Tasmania, Northern Territory, New South Wales, Queensland, Victoria, South Australia, New Zealand, Europe, Austria, Belgium, France, Germany, Italy, Portugal, Spain, UK, Great Britain, Yugoslavia, North America, Bermuda, Canada, Manitoba, Ontario, Nova Scotia, Prince Edward Island, USA, Florida, Kansas, Missouri, New Jersey, New York, Montana, Tennessee, Utah, Central America & West Indies, Barbados, South America, Argentina, Brazil.
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„Helicoverpa assulta. [Distribution map].“ Distribution Maps of Plant Pests, Nr. 1st Revision) (01.08.1994). http://dx.doi.org/10.1079/dmpp/20046600262.
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Abstract A new distribution map is provided for Helicoverpa assulta (Guenée) Lepidoptera: Noctuidae (cape gooseberry budworm, oriental tobacco budworm). Attacks Physalis, tobacco, tomato and other solanaceous plants. Information is given on the geographical distribution in Africa, Aldabra Islands, Angola, Cameroon, Central African Republic, Comoro Islands, Gambia, Ghana, Ivory Coast, Kenya, Liberia, Malawi, Mali, Nigeria, Senegal, Sierra Leone, South Africa, Tanzania, Uganda, Zaire, Zimbabwe, Asia, Bangladesh, Bhutan, Brunei, Burma, China, Beijing, Guangdong, Guangxi, Hebei, Henan, Hubei, Hunan, Jiangxi, Shaanxi, Shanghai, Sichuan, Christmas Island, Cocos-Keeling Islands, India, Andhra Pradesh, Assam, Bihar, Gujarat, Haryana, Himachal Pradesh, Karnataka, Madhya Pradesh, Maharashtra, Meghalaya, Orissa, Tamil Nadu, Uttar Pradesh, Indonesia, Java, Sulawesi, Sumatra, Tanimbar Island, Japan, Korea, Laos, Malaysia, Sabah, Sarawak, West Malaysia, Pakistan, Philippines, Sikkim, Singapore, Sri Lanka, Taiwan, Thailand, Vietnam, Australasia and Pacific islands, Australia, Northern Territory, Queensland, Western Australia, Fiji, Gambier Islands, Mariana Islands, New Britain, New Caledonia, Norfolk Island, Papua New Guinea, American Samoa, Western Samoa, Society Islands, Solomon Islands, Tubuai Islands, Vanuatu, West Irian.
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„Ditylenchus destructor. [Distribution map].“ Distribution Maps of Plant Diseases, Nr. 1) (01.08.2001). http://dx.doi.org/10.1079/dmpd/20066500837.
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Abstract A new distribution map is provided for Ditylenchus destructor Thome Nematoda: Tylenchida: Anguinidae Hosts: Mainly potato (Solanum tuberosum), sweet potato (Ipomoea batatas) and bulbous Iris, but also other ornamental plants. Information is given on the geographical distribution in EUROPE, Albania, Austria, Belarus, Belgium, Bulgaria, Czech Republic, Estonia, Finland, France, Germany, Greece, Hungary, Ireland, Latvia, Lithuania, Luxembourg, Moldova, Netherlands, Norway, Poland, Romania, Central Russia Russia, Northern Russia, Southern Russia, Slovakia, Spain, Sweden, Switzerland, UK, Ukraine, ASIA, Azerbaijan, China, Guangdong, Hainan, Hebei, Henan, Jiangsu, Liaoning, Shandong, Iran, Japan, Honshu, Kazakhstan, Korea Republic, Kyrgyzstan, Pakistan, Saudi Arabia, Tajikistan, Turkey, Uzbekistan, AFRICA, South Africa, NORTH AMERICA, Canada, Prince Edward Island, Mexico, USA, Arkansas, California, Hawaii, Idaho, Indiana, New Jersey, North Carolina, Oregon, South Carolina, Virginia, Washington, West Virginia, Wisconsin, SOUTH AMERICA, Ecuador, Peru, OCEANIA, Australia, New South Wales, South Australia, Tasmania, Victoria, Western Australia, New Zealand.
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„Macrophomina phaseolina. [Distribution map].“ Distribution Maps of Plant Diseases, Nr. 1) (01.08.1985). http://dx.doi.org/10.1079/dmpd/20056500566.
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Abstract A new distribution map is provided for Macrophomina phaseolina (Tassi) Goid. Hosts: Plurivorous. Information is given on the geographical distribution in AFRICA, Botswana, Cameroon, Central African Republic, Egypt, Ethiopia, Gambia, Ghana, Ivory Coast, Kenya, Libya, Malagasy Republic, Malawi, Mauritius, Morocco, Niger, Mozambique, Nigeria, Senegal, Sierra Leone, South Africa, Sudan, Swaziland, Tanzania, Tunisia, Togo, Uganda, Upper Volta, Zaire, Zambia, Zimbabwe, ASIA, Bangladesh, Brunei, Burma, China, Hong Kong, India, Indonesia, Iran, Iraq, Israel, Japan, Korea, Kuwait, Lebanon, Malaysia (Sabah, Sarawak, Malaya, Selangor), Nepal, Oman, Pakistan, Philippines, South Yemen, Sri Lanka, Syria, Taiwan, Thailand, Turkey, Yemen, AUSTRALASIA & OCEANIA, Australia, Fiji, Papua New Guinea, Solomon Islands, New Zealand (Auckland- N. Island; Blenheim, Nelson - South Island), EUROPE, Austria, Cyprus, Denmark, France, Greece, Hungary, Italy, Republic of Ireland, Romania, Spain, Switzerland, United Kingdom, USSR, West Germany, Yugoslavia, NORTH AMERICA, Canada (Ontario), Mexico, USA, CENTRAL AMERICA & WEST INDIES, Bermuda, Jamaica, Dominica, Puerto Rico, Trinidad, Cuba, E1 Salvador, SOUTH AMERICA, Argentina, Brazil, Chile, Colombia, Guyana, Peru, Uruguay, Venezuela.