Academic literature on the topic 'Wildlife conservation Victoria French Island'

Koala (Phascolarctos cinereus) populations in southern Australia have a history of bottlenecks – earlier this century the species became extinct in South Australia, and almost so in Victoria. Subsequently large numbers of animals from island populations (founded from very few animals) have been translocated back to mainland sites and to other islands in the region. As part of a larger study of the genetic structure of koala populations in southern Australia, we have undertaken a survey of mitochondrial DNA restriction fragment length polymorphism (mtDNA-RFLP) variability. Genomic DNA from 91 koalas from five populations was examined using 23 restriction enzymes, and mtDNA fragments were detected using a domestic cat full-length mtDNA clone. Only one of the enzymes, TaqI, revealed polymorphism – a relatively low amount of variation compared with other mammals, although low mtDNA-RFLP variation has also been reported in Queensland koalas. French Island and populations established predominantly from French Island immigrant koalas, either directly or via other island populations, were indistinguishable by haplotype frequencies. The mtDNA data are thus consistent with the interpretation that the koala translocation programme has homogenized gene frequencies amongst those populations involved. South Gippsland is not recorded as having received translocated koalas directly, and has significantly different mtDNA-RFLP haplotype frequencies from all other populations examined. The fact that this distinction was not previously observed in nuclear gene frequencies may reflect predominantly male-mediated dispersal in koalas.

It is important to have knowledge of basic population parameters to understand how these vary geographically and temporally and how they contribute to population dynamics. This paper investigates three of these parameters in Victorian koala populations: sexual maturity, aspects of the breeding season, and the continuity of individuals’ breeding. The investigation was carried out in koalas of known-age in two free-living (Redbill Creek on French Island and Brisbane Ranges) and one semi-captive (the Koala Conservation Centre on Phillip Island) population as well as koalas of unknown age in four Victorian populations of overabundant koalas: Mt Eccles and Framlingham in south-west Victoria, French Island in Western Port and Snake Island in south Gippsland. At sexual maturity, female koalas had a mean age (±95% confidence interval) of 24.4 months (23.5–25.3 months), a mean head length of 125 mm (124–127 mm) and a mean body mass of 6.6 kg (6.3–6.8 kg). Only 7.4% of independent females (of unknown age) were carrying young when they weighed less than 6 kg. The breeding season was more restricted in the south-west populations. At Framlingham and Mt Eccles 85% and 91% of births, respectively, occurred between December and March. At Snake and French Islands only 46% and 53% of births, respectively, were recorded in the same period. In the Chlamydia-free population (Red Bill Creek) none of the koalas that were monitored stopped breeding and then resumed breeding in a subsequent season whereas many females from Chlamydia-infected populations (Brisbane Ranges and the Koala Conservation Centre) did so. This variation in reproductive patterns is likely to make an important contribution to the variation in the demography observed in different koala populations.

With the rising popularity of social media, conservation organisations and zoos need to understand its impact on public perceptions of the animals they house and their role in conservation. In addition, many zoos offer close-encounter experiences, and visitors frequently share images from these experiences online. This study measured the effects that viewing such encounter images had on public perceptions of both the zoo and the animals they saw. One of sixteen images was randomly presented to participants in two samples: one of Zoo Community followers and members of Zoos Victoria (n = 963), and a representative sample of the Australian public (n = 1619). Each image featured one of four animals (Eclectus parrot, Kangaroo Island kangaroo, Monteith’s leaf insect, Centralian carpet python) and one of four human positions (human and animal touching, human and animal ~30 cm apart, human and animal ~1 m apart, animal alone). Results indicated that viewing different animals and the different human positions within these human–animal encounter images can affect public perceptions of zoo animals. In particular, the closer the proximity of a human to an animal in an image, the more likely respondents were to think that the animal was not displaying a natural behaviour and the more likely it was for General Public respondents to think that the animal would make a good pet. These findings can be used by zoos, wildlife tourism, and media organisations to ensure that they are sending clear, positive, and intended messages about zoo facilities and animals, as well as providing insights into animal encounter images in wider settings.

Abstract ContextFeral domestic cats (Felis catus) have contributed to substantial loss of Australian wildlife, particularly small- and medium-sized terrestrial mammals. However, mitigating cat impacts remains challenging. Understanding the factors that facilitate coexistence between native prey and their alien predators could aid better pest management and conservation actions. AimsWe estimated feral cat density, examined the impact of habitat cover on long-nosed potoroos (Potorous tridactylus tridactylus), and assessed the spatial and temporal interactions between cats and potoroos in the ‘Bluegums’ area of French Island, south-eastern Australia. Materials and methodsWe operated 31 camera stations across Bluegums for 99 consecutive nights in each of winter 2018 and summer 2018/19. We used a spatially explicit capture–recapture model to estimate cat density, and two-species single-season occupancy models to assess spatial co-occurrence of cats and potoroos. We assessed the influence of vegetation cover and cat activity on potoroo activity by using a dynamic occupancy model. We also used image timestamps to describe and compare the temporal activities of the two species. Key resultsBluegums had a density of 0.77 cats per km2 across both seasons, although this is a conservative estimate because of the presence of unidentified cats. Cats and long-nosed potoroos were detected at 94% and 77% of camera stations, respectively. Long-nosed potoroo detectability was higher in denser vegetation and this pattern was stronger at sites with high cat activity. Cats and potoroos overlapped in their temporal activity, but their peak activity times differed. Conclusions Feral cat density at Bluegums, French Island, is higher than has been reported for mainland Australian sites, but generally lower than in other islands. Long-nosed potoroos were positively associated with cats, potentially indicating cats tracking potoroos as prey or other prey species that co-occur with potoroos. Temporal activity of each species differed, and potoroos sought more complex habitat, highlighting possible mechanisms potoroos may use to reduce their predation risk when co-occurring with cats. ImplicationsOur study highlighted how predator and prey spatial and temporal interactions, and habitat cover and complexity (ecological refuges), may influence the ability for native prey to coexist with invasive predators. We encourage more consideration and investigation of these factors, with the aim of facilitating more native species to persist with invasive predators or be reintroduced outside of predator-free sanctuaries, exclosures and island safe havens.

Abstract Background The island of Crete is a biodiversity hotspot having 223 endemic vascular taxa (species and subspecies) as a result of its long isolation and the wide range of habitats it includes. We explore trends and patterns in the electronic trade of these unique genetic resources and in their involvement in wildlife tourism, the ways these two activities are performed and the associated potential threats on the plants’ wild populations, and we also identify priority taxa requiring special attention. The main part of the study was conducted in 2016–2017 using English as a search language; an additional search was conducted in 2019 using German and French. Results We found e-commerce for 28 (13%) endemic taxa. These are traded by 65 nurseries from 14 countries, the UK primarily. Among the traded plants, 16 face extinction risk and/or are under protection status. Prices vary largely for the same taxon and form of sale. Lamiaceae is the family with the highest number of e-traded taxa, Tulipa bakeri is the most traded species, and the living plant is the commonest form of sale. Thirty-seven endemic taxa are advertised in the websites of travel agencies involved in wildlife tourism. Tulipa doerfleri is the most frequently encountered taxon in these websites, whereas Lamiaceae, Liliaceae and Orchidaceae are similarly represented. The additional search showed a very rapid increase in the e-trade of the Cretan endemis. Conclusion The two examined markets are similar in that geophytes play a prominent role and Lamiaceae rank first among the represented plant families, but differ in several aspects: only 22.6% of the taxa detected are common in both, obedience to rules exhibited by travel agencies is not usually the case with nurseries, and potential threats to wild populations are estimated as considerably higher for the traded plants. Sixteen endemic taxa of Crete were identified as requiring special attention.

Abstract A description is provided for Leptogium cochleatum. Some information on its associated organisms and substrata, habitat, dispersal and transmission, and conservation status is given, along with details of its geographical distribution (Africa (Ethiopia, Kenya, Lesotho, Madagascar, Sao Tome and Principe, South Africa, Tanzania), North America (Canada (Nova Scotia), Mexico, USA (Alabama, Arizona, Colorado, Florida, Georgia, Maine, Maryland, Massachusetts, Michigan, Minnesota, New Hampshire, New Jersey, North Carolina, Virginia)), Central America (Belize, Costa Rica, El Salvador, Guatemala, Nicaragua), South America (Argentina, Bolivia, Brazil (Bahia, Mato Grosso, Pará, Rio de Janeiro, Rio Grande do Sul, Santa Catarina, São Paulo), Colombia, Ecuador, French Guina, Peru, Surinam, Venezuela), Asia (China (Beijing, Yunnan), India (Andaman & Nicobar Islands, Karnataka, Maharashtra, Nagaland, Sikkim, Tamil Nadu, Tripura, Uttarakhand, West Bengal), Indonesia, Japan, Malaysia, North Korea, Papua New Guinea, Philippines, Russia (Primorsky Krai), Singapore, South Korea, Taiwan, Thailand, Vietnam), Atlantic Ocean (Bermuda, Cape Verde, Portugal (Azores, Madeira), Spain (Canary Islands), St Helena), Australasia (Australia (New South Wales, Queensland, Victoria), New Zealand, Norfolk Island), Caribbean (Cuba, Guadeloupe), Europe (Austria, Croatia, France, Greece, Ireland, Italy, Norway, Poland, Portugal, Romania, Russia (Krasnodar Krai), Spain, Sweden, Switzerland, UK, former Yugoslavia), Indian Ocean (Mauritius), Pacific Ocean (New Caledonia, USA (Hawaii), Vanuatu)). This species is used in the British Isles as an indicator when making ecological assesments.

Abstract A description is provided for Arcyria cinerea, one of the most consistently abundant and widespread myxomycete species associated with lianas, aerial woody remnants, leaves and inflorescences in tropical and mangrove forests. Some information on its associated organisms and substrata, interaction and habitats, infraspecific variation, dispersal and transmission, and conservation status is given, along with details of its geographical distribution (AFRICA: Algeria, Angola, Burundi, Cameroon, Democratic Republic of the Congo, Egypt, Equatorial Guinea, Gambia, Kenya, Liberia, Madagascar, Malawi, Mayotte, Morocco, Mozambique, Nigeria, Rwanda, Sierra Leone, Somalia, South Africa, Tanzania, Tunisia, Uganda, Western Sahara, Zambia, Zimbabwe; NORTH AMERICA: Canada (Alberta, British Columbia, Manitoba, New Brunswick, Ontario, Quebec, Saskatchewan), Mexico, USA (Alaska, Arizona, Arkansas, California, Colorado, Connecticut, Delaware, Florida, Georgia, Idaho, Illinois, Indiana, Iowa, Kansas, Kentucky, Louisiana, Maine, Maryland, Massachusetts, Michigan, Minnesota, Mississippi, Missouri, Montana, Nebraska, New Hampshire, New Jersey, New Mexico, New York, North Carolina, North Dakota, Ohio, Oklahoma, Oregon, Pennsylvania, Rhode Island, South Carolina, Tennessee, Texas, Vermont, Virginia, West Virginia); CENTRAL AMERICA: Belize, Costa Rica, El Salvador, Guatemala, Honduras, Nicaragua, Panama; SOUTH AMERICA: Argentina, Bolivia, Brazil (Alagoas, Amazonas, Bahia, Ceara, Mato Grosso, Minas Gerais, Paraiba, Parana, Pernambuco, Rio Grande do Norte, Rio Grande do Sul, Rondonia, Roraima, Santa Catarina, Sao Paulo, Sergipe), Chile, Colombia, Ecuador (including Galapagos), French Guiana, Guyana, Paraguay, Peru, Surinam, Venezuela; ANTARCTICA: Antarctica; ASIA: China (Anhui, Guangdong, Guangxi, Heilongjiang, Hong Kong, Jiangsu, Kwangtung, Yunnan), Christmas Island, Georgia, India (Assam, Chandigarh, Himachal Pradesh, Jammu & Kashmir, Karnataka, Madhya Pradesh, Maharashtra, Orissa, Uttarakhand, Uttar Pradesh, West Bengal), Indonesia, Iran, Japan, Kazakhstan (Aktobe, Atyrau, Pavlodar, West Kazakhstan), Laos, Nepal, Papua-New Guinea, Philippines, Russia (Altai Krai, Altai Republic, Chukotka Autonomous Okrug, Irkutsk Oblast, Khabarovsk Krai, Khanty-Mansi Autonomous Okrug, Krasnoyarsk Krai, Magadan Oblast, Primorsky Krai, Republic of Buryatia, Sakhalin Oblast, Tyumen Oblast, Yamalo-Nenets Autonomous Okrug), Singapore, Sri Lanka, Taiwan, Thailand, Turkey, Uzbekistan, Vietnam. Atlantic OCEAN: Ascension Island, Spain (Canary Islands); AUSTRALASIA: Australia (New South Wales, Northern Territory, Queensland, Tasmania, Victoria, Western Australia), New Zealand, Raoul Island; CARIBBEAN: American Virgin Islands, Antigua and Barbuda, Bahamas, Cuba, Dominica, Dominican Republic, Grenada, Guadeloupe, Haiti, Jamaica, Martinique, Puerto Rico, Trinidad & Tobago; EUROPE: Andorra, Austria, Belgium, Czech Republic, Denmark, Estonia, Finland, France, Germany, Greece, Iceland, Ireland, Italy, Lithuania, Luxembourg, Moldova, Netherlands, Norway, Poland, Portugal, Romania, Russia (Astrakhan Oblast, Chelyabinsk Oblast, Kalinigrad Oblast, Komi Republic, Krasnodar Krai, Kursk Oblast, Leningrad Oblast, Moscow Oblast, Murmansk Oblast, Orenburg Oblast, Perm Krai, Republic of Bashkortostan, Republic of Karelia, Rostov Oblast, Smolensk Oblast, Tver Oblast, Voronezh Oblast, Volgograd Oblast, Vologda Oblast), Slovakia, Slovenia, Spain, Sweden, Switzerland, Ukraine, UK; Indian OCEAN: Mauritius, Reunion, Seychelles; Pacific OCEAN: French Polynesia, New Caledonia, USA (Hawaii)).

Abstract A description is provided for Fuligo septica, a myxomycete which occurs on litter, fallen leaves, bark, decorticated branches, rotten stumps, fallen trunks, rotten wood and burnt logs of a very wide range of plants. Some information on its associated organisms and substrata, interactions and habitats, economic impacts, intraspecific variation, dispersal and transmission and conservation status is given, along with details of its geographical distribution (AFRICA: Algeria, Burundi, Democratic Republic of the Congo, Equatorial Guinea, Eritrea, Lesotho, Liberia, Madagascar, Malawi, Mayotte, Morocco, Nigeria, Sierra Leone, South Africa, Tanzania, Tunisia, Uganda, Zimbabwe; NORTH AMERICA: Canada (Alberta, British Columbia, Manitoba, New Brunswick, Newfoundland, Northwest Territories, Nova Scotia, Nunavut, Ontario, Prince Edward Island, Quebec), Mexico, USA (Alabama, Alaska, Arizona, Arkansas, California, Colorado, Connecticut, Delaware, Florida, Georgia, Idaho, Illinois, Indiana, Iowa, Kentucky, Louisiana, Maine, Maryland, Massachusetts, Michigan, Minnesota, Mississippi, Missouri, Montana, Nebraska, Nevada, New Hampshire, New Jersey, New Mexico, New York, North Carolina, North Dakota, Ohio, Oklahoma, Oregon, Pennsylvania, Rhode Island, South Carolina, South Dakota, Tennessee, Texas, Utah, Vermont, Virginia, Washington, West Virginia, Wisconsin, Wyoming), Mexico; CENTRAL AMERICA: Costa Rica, El Salvador, Guatemala, Honduras, Nicaragua, Panama; SOUTH AMERICA: Argentina, Bolivia, Brazil (Bahia, Maranhão, Paraiba, Pernambuco, Roraima, Santa Catarina, São Paulo, Sergipe), Chile, Ecuador (including Galapagos), French Guiana, Guyana, Paraguay, Peru, Uruguay, Venezuela; ASIA: Brunei, China (Fujian, Guizhou, Jiangsu, Zhejiang), Georgia, India (Assam, Chandigarh, Himachal Pradesh, Tamil Nadu, Uttar Pradesh, Uttarakhand), Indonesia, Iran, Japan, Jordan, Kazakhstan (Akmola, Aktobe, Almaty, East Kazakhstan, Karaganda, former Kokshetau, Kostanai, North Kazakhstan, Pavlodar, former Tselinograd, West Kazakhstan), Malaysia, Nepal, North Korea, Pakistan, Papua-New Guinea, Philippines, Russia (Altai Krai, Khanty-Mansi Autonomous Okrug, Krasnoyarsk Krai, Magadan Oblast, Novosibirsk Oblast, Tyumen Oblast), Singapore, South Korea, Turkey, Uzbekistan, Vietnam; ATLANTIC OCEAN: Spain (Canary Islands); AUSTRALASIA: Australia (New South Wales, Queensland, South Australia, Tasmania, Victoria, Western Australia), New Zealand; CARIBBEAN: American Virgin Islands, Antigua and Barbuda, Cuba, Dominica, Dominican Republic, Guadeloupe, Jamaica, Martinique, Puerto Rico, Saint Lucia, Trinidad and Tobago; EUROPE: Andorra, Austria, Belarus, Belgium, Croatia, Czech Republic, Denmark, Estonia, Finland, France, Germany, Greece, Hungary, Ireland, Italy, Latvia, Lithuania, Luxembourg, Moldova, Netherlands, Norway, Poland, Portugal, Romania, Russia (Astrakhan Oblast, Chelyabinsk Oblast, Chuvash Republic, Kaliningrad Oblast, Komi Republic, Krasnodarsk Krai, Kursk Oblast, Leningrad Oblast, Moscow Oblast, Murmansk Oblast, Orenburg Oblast, Pskov Oblast, Republic of Karelia, Stavropol Krai, Tver Oblast, Volgograd Oblast), Serbia, Slovakia, Slovenia, Spain, Sweden, Switzerland, Turkey, Ukraine, UK; INDIAN OCEAN: Christmas Island, Mauritius, Réunion, Seychelles; PACIFIC OCEAN: French Polynesia, Marshall Islands, New Caledonia, Solomon Islands, USA (Hawaii)).

Abstract A description is provided for Lycogala epidendrum, a wood-inhabiting myxomycete which occurs on dead branches, twigs and wood, rotten logs, stumps and trunks, cut logs and other woody debris. Some information on its associated organisms and substrata, interactions and habitats, economic impacts, intraspecific variation, dispersal and transmission and conservation status is given, along with details of its geographical distribution (Algeria, Angola, Burundi, Cameroon, Congo, Democratic Republic of the Congo, Egypt, Liberia, Malawi, Morocco, Nigeria, Rwanda, Sierra Leone, South Africa, Tanzania, Uganda, Zambia; Canada (Alberta, British Columbia, New Brunswick, Newfoundland, Nova Scotia, Ontario, Prince Edward Island, Quebec, Saskatchewan), Mexico, USA (Alaska, Arizona, California, Connecticut, Florida, Georgia, Illinois, Indiana, Iowa, Kansas, Maine, Maryland, Massachusetts, Michigan, Minnesota, Mississippi, Missouri, Montana, Nebraska, New Hampshire, New Jersey, New York, North Carolina, Ohio, Oregon, Pennsylvania, Rhode Island, South Carolina, Tennessee, Texas, Vermont, Virginia, Washington, West Virginia); Costa Rica, El Salvador, Guatemala, Honduras, Nicaragua, Panama; Argentina, Chile, Colombia, Brazil (Acre, Amazonas, Maranhão, Pará, Paraiba, Pernambuco, Piauí, Rio de Janeiro, Rio Grande do Norte, Rio Grande do Sul, Roraima, Santa Catarina, São Paulo, Sergipe), Ecuador (including Galapagos), French Guiana, Guyana, Paraguay, Peru, Suriname, Uruguay, Venezuela; China (Fujian, Guangxi, Guizhou, Hainan, Jiangxi, Sichuan, Xinjiang, Yunnan, Zhejiang), Georgia, India (Assam, Chandigarh, Himachal Pradesh, Jammu & Kashmir, Karnataka, Maharashtra, Sikkim, Tamil Nadu, West Bengal), Indonesia, Iran, Japan, Kazakhstan (Almaty, East Kazakhstan, Kostanay, North Kazakhstan, former Kokchetau, former Taldy-Kurgan, former Tselinograd), Kyrgyzstan, Malaysia, Mongolia, Nepal, Papua-New Guinea, Philippines, Russia (Altai, Altai Krai, Chukotka Autonomous Okrug, Kamchatka Krai, Khabarovsk Krai, Khanty-Mansi Autonomous Okrug, Krasnoyarsk Krai, Magadan Oblast, Novosibirsk Oblast, Primorsky Krai, Tomsk Oblast, Yamalo-Nenets Autonomous Okrug), Singapore, South Korea, Sri Lanka, Taiwan, Thailand, Turkey, Uzbekistan, Vietnam; Bahamas, Spain (Canary Islands); Australia (New South Wales, Northern Territory, Queensland, South Australia, Tasmania, Victoria, Western Australia), New Zealand; American Virgin Islands, Antigua and Barbuda, Cuba, Dominica, Dominican Republic, Grenada, Guadeloupe, Jamaica, Martinique, Puerto Rico, Saint Lucia, Trinidad and Tobago; Andorra, Austria, Belgium, Bulgaria, Croatia, Czech Republic, Denmark (including Faroe Islands), Estonia, Finland, France, Germany, Greece, Iceland, Ireland, Italy, Kosovo, Latvia, Liechtenstein, Lithuania, Luxembourg, Moldova, Netherlands, Norway, Poland, Portugal, Romania, Russia (Kaliningrad Oblast, Krasnodar Krai, Leningrad Oblast, Moscow Oblast, Rostov Oblast, Vladimir Oblast, Volgograd Oblast), Serbia, Slovakia, Slovenia, Spain, Sweden, Switzerland, Ukraine, UK; Christmas Island, Mauritius, Réunion, Seychelles; Cook Islands, French Polynesia, New Caledonia, USA (Hawaii)).

Abstract A description is provided for Auricularia auricula-judae, found on dead branches of Sambucus nigra. Some information on its morphology, dispersal and transmission and conservation status is given, along with details of its geographical distribution (Africa (Benin, Côte d'Ivoire, Congo, Democratic Republic of the Congo, Ghana, Ethiopia, Gabon, Kenya, Madagascar, Malawi, Nigeria, Rwanda, São Tomé and Principe, Sierra Leone, South Africa, Tunisia, Uganda, Zambia), Asia (Armenia, Azerbaijan, Bhutan, Cambodia, China, Fujian, Hainan, Hong Kong, Manchuria, Shaanxi, Yunnan, Cyprus, Republic of Georgia, India, Assam, Chhattisgarh, Himachal Pradesh, Jammu and Kashmir, Karnataka, Kerala, Maharashtra, Manipur, Meghalaya, Nagaland, Rajasthan, Sikkim, Uttarakhand, West Bengal, Indonesia, Iran, Israel, Japan, Laos, Lebanon, Malaysia, North Korea, Pakistan, Palestine, Papua New Guinea, Philippines, Russia, Altai Republic, Amur Oblast, Jewish Autonomous Oblast, Khabarovsk Krai, Primorsky Krai, Republic of Sakha, Sakhalin Oblast,, Singapore, Korea Republic, Sri Lanka, Taiwan, Thailand, Turkey, Vietnam), Atlantic Ocean (Portugal, Madeira, Spain, Islas Canarias), Australasia (Australia, New South Wales, Northern Territory, Queensland, Victoria, New Zealand), Caribbean (American Virgin Islands, Cuba, Haiti, Jamaica, Puerto Rico), Central America (Costa Rica, El Salvador, Guatemala, Honduras, Panama), Europe (Andorra, Austria, Belgium, Bosnia and Herzegovina, Bulgaria, Croatia, Czech Republic, Denmark, Estonia, Finland, France, Germany, Greece, Hungary, Irish Republic, Isle of Man, Italy, Jersey, Liechtenstein, Lithuania, Luxembourg, Malta, Moldova, Netherlands, Norway, Poland, Portugal, Romania, Russia, Belgorod Oblast, Karachay-Cherkess Republic, Krasnodar Krai, Kursk Oblast, Leningrad Oblast, Moscow Oblast, Republic of Adygea, Republic of North Ossetia-Alania, Serbia, Slovakia, Slovenia, Spain, Sweden, Switzerland, Ukraine, UK), Indian Ocean (Mauritius), North America (Canada, Alberta, British Columbia, New Brunswick, Nova Scotia, Ontario, Prince Edward Island, Quebec, Mexico, USA, Alabama, Alaska, Arizona, Arkansas, California, Colorado, Connecticut, Florida, Georgia, Idaho, Illinois, Indiana, Iowa, Kansas, Kentucky, Louisiana, Maine, Maryland, Michigan, Minnesota, Mississippi, Missouri, Montana, New Hampshire, New Jersey, New Mexico, New York, North Carolina, Ohio, Oregon, Pennsylvania, South Carolina, Tennessee, Texas, Utah, Vermont, Virginia, Washington, West Virginia, Wisconsin, Wyoming), Pacific Ocean (French Polynesia, Guam, Norfolk Island, USA, Hawaii), South America (Argentina, Bolivia, Brazil, Amazonas, Bahia, Espírito Santo, Mato Grosso, Pará, Paraná, Pernambuco, Rio de Janeiro, Rio Grande do Norte, Rio Grande do Sul, Rondônia, Roraima, Santa Catarina, São Paulo, Chile, Colombia, Ecuador, French Guiana, Guyana, Paraguay, Peru, Suriname, Venezuela)) and host (S. nigra).