Distribution and Conservation Status of the Black-Footed Rock-Wallaby, Petrogale lateralis (MacDonnell Ranges race), in the Northern Territory.

1999 ◽  
Vol 21 (2) ◽  
pp. 213
Author(s):  
D.F. Gibson

The distribution and conservation status of the Black-footed Rock-wallaby Petrogale lateralis (MacDonnell Ranges race), in the Northern Territory were investigated to complement previous surveys in adjoining areas of Western Australia and South Australia. Historical data were collated and compared with recent biological survey results obtained between 1870 and 1999. From a total of 469 records, 400 were collated for the period 1975-1999. The species occurs over ten biogeographic regions, principally within the MacDonnell Ranges bioregion, but with many populations in the Burt Plain and Great Sandy Desert bioregions. It is widely distributed through pastoral, Aboriginal, conservation and urban land and, at present, retains much the same distribution as concluded from early records. Thirteen conservation areas and 30 pastoral leases currently support populations of the species. An unknown number of animals live in and about Alice Springs. Only two National Parks, the West MacDonnells and Finke Gorge, are considered large and diverse enough to ensure the long-term survival of P. lateralis. Measures of abundance are not available but numbers of animals in conservation areas are perceived to have remained stable or to have increased over the past 20 years. Surveys undertaken during the period 1975-1999 indicate that P. lateralis have disappeared from 21 of 400 sites. Petrogale lateralis were present on all major rock types, including many granite outcrops. They were most widespread and apparently abundant on major quartzite ranges such as the MacDonnells where steep cliff faces, gorges, scree slopes and fire shadow areas are common. The wide distribution of P. lateralis in the Northern Territory in comparison to other states may be due to a variety of factors: widespread, relatively contiguous and variable habitat, occupation of country north of the core distribution of Oryctolagus cuniculus and of Vulpes vulpes, the inability of Capra hircus to persist and thus to compete in rocky range habitat, and a government 1080 poisoning programme for Canis lupus dingo on pastoral land. There is however, concern for the survival of some populations on many small ranges and rock outcrops on the fringes of its known distribution where recent observations indicate that numbers of animals are low.

Author(s):  
P. F. Cannon

Abstract A description is provided for Phialophora americana (Herpotrichiellaceae, Chaetothyriales) found on decayed wood. Some information on its morphology, habitats, dispersal and transmission, conservation status and economic impacts is given, along with details of its geographical distribution (Antarctica, China (Changbai Mountains), Iran, Taiwan, Australia (Australian Capital Territory, New South Wales, Northern Territory, Queensland, South Australia, Victoria, Western Australia), Austria, Czech Republic, Estonia, Finland, France, Germany, Netherlands, Norway, Poland, Sweden, UK, Canada (New Brunswick, Northwest Territories), Mexico, USA (Minnesota, New York, Virginia, Wisconsin), Chile, Brazil (Parana, Pernambuco, Sao Paulo) and Uruguay) and associated organisms (man, woody plants and other wood-inhabiting fungi).


2001 ◽  
Vol 23 (2) ◽  
pp. 185 ◽  
Author(s):  
S Murphy

THE bare-rumped sheathtailed bat Saccolaimus saccolaimus is a poorly understood species that has a wide distribution covering parts of India, Sri Lanka, Thailand, Myanmar, Malaya, Indonesia, New Guinea, the Solomon Islands and Northern Australia (Bonaccorso 1998). First collected in Australia by De Vis near Cardwell, the current known distribution in Queensland (Qld) extends from Bowen to Cooktown with one isolated specimen collected near Coen on Cape York Peninsula (Hall 1995; Duncan et al. 1999). It has also been recorded in the Alligator River area in the Northern Territory (McKean et al. 1981). The conservation status of S. saccolaimus in Qld has recently been defined as ?Critically Endangered?, and the species has not been recorded anywhere in Australia for at least 18 years (Duncan et al. 1999; Menkhorst and Knight 2001). The likely reasons for the apparent decline are unclear, but may involve land-clearing and changed fire regimes in the coastal zone where it is thought to occur (Duncan et al. 1999). In contrast, Bonaccorso (1998) considers S. saccolaimus to be secure, albeit also poorly known in Papua New Guinea.


Rodriguésia ◽  
2018 ◽  
Vol 69 (2) ◽  
pp. 693-698 ◽  
Author(s):  
Guilherme Alves Elias ◽  
André Luís de Gasper ◽  
Joanna Marie Tucker Lima ◽  
Guilherme Lodetti ◽  
Robson dos Santos

Abstract In this study, we examined the distribution and conservation status of understory palms in the Brazilian state of Santa Catarina using data collected by the Floristic and Forest Inventory of Santa Catarina (IFFSC). Understory palms were systematically sampled within sampling units (SU) distributed over a state-wide 10 × 10 km grid. Among the 206 total SU monitored by IFFSC within Pluvial and Coastal Forest, 86% (n=177 SU) contained understory palms, comprising 1738 individuals from the following species: Bactris setosa, Geonoma elegans, G. gamiova, and G. schottiana. To explore the conservation status of understory palm populations in Santa Catarina, we overlaid a map of federal priority conservation areas on top of IFFSC distribution data for understory palms. Conservation priority levels defined by the Brazilian Environmental Agency (MMA) are rated Extremely High, Very High, High and Insufficiently Known. Ninety-four percent of the SU containing understory palms overlapped priority conservation areas, highlighting the centrality of understory palms in biodiversity conservation. Despite the wide distribution of understory palm communities in Santa Catarina, intense scrutiny of forest remnants is necessary in view of sensitivity to environmental disturbance, so as to guarantee the maintenance of understory palm populations and their ecosystem services.


Oryx ◽  
2015 ◽  
Vol 50 (2) ◽  
pp. 360-363 ◽  
Author(s):  
Ricardo Faustino de Lima ◽  
Eden Maloney ◽  
W. Brian Simison ◽  
Robert Drewes

AbstractThe shrew Crocidura thomensis is a little-known species endemic to São Tomé Island. We review its distribution, ecology and conservation status based on nine published and 23 new records. The species has a wide distribution across São Tomé, preferring rugged forested areas with high rainfall. The location of new records coincides with that of historical records but the proportion of records in plantations has declined, possibly as a result of agricultural intensification, increased use of pesticides, and presence of exotic species. The shrew is restricted to a single island, its extent of occurrence is < 1,000 km2 and its habitat is declining in extent and quality, and thus its categorization as Endangered on the IUCN Red List remains appropriate. It is important to gain a better knowledge of population trends, ecological preferences and sensitivity to potential threats, but the effective protection of São Tomé Obô Natural Park and surrounding forests is the most important measure to ensure the long-term survival of this mammal.


Animals ◽  
2019 ◽  
Vol 9 (10) ◽  
pp. 724
Author(s):  
Noack ◽  
Heyns ◽  
Rodenwoldt ◽  
Edwards

The establishment of enclosed conservation areas are claimed to be the driving force for the long-term survival of wildlife populations. Whilst fencing provides an important tool in conservation, it simultaneously represents a controversial matter as it stops natural migration processes, which could ultimately lead to inbreeding, a decline in genetic diversity and local extinction if not managed correctly. Thus, wildlife residing in enclosed reserves requires effective conservation and management strategies, which are strongly reliant on robust population estimates. Here, we used camera traps combined with the relatively new class of spatially explicit capture-recaptured models (SECR) to produce the first reliable leopard population estimate for an enclosed reserve in Namibia. Leopard density was estimated at 14.51 leopards/100 km2, the highest recorded density in Namibia to date. A combination of high prey abundance, the absence of human persecution and a lack of top-down control are believed to be the main drivers of the recorded high leopard population. Our results add to the growing body of literature which suggests enclosed reserves have the potential to harbour high densities and highlight the importance of such reserves for the survival of threatened species in the future.


2003 ◽  
Vol 30 (5) ◽  
pp. 513 ◽  
Author(s):  
Theresa J. Nano ◽  
Cate M. Smith ◽  
Elizabeth Jefferys

The diet of the rare central rock-rat, Zyzomys pedunculatus, was assessed by microscopic analysis of 18 faecal pellet samples collected from four different sites in the west MacDonnell Ranges in the Northern Territory. Samples were collected from the four sites in summer (n = 13), one site in winter (n = 3), and two sites in spring (n = 2). Four major food categories were observed in the samples: seed, leaf, stem and insect. Seed was by far the most dominant food in the overall diet of Z. pedunculatus, making up 72% of identifiable particles, leaf was secondary (21%), while stem and insects contributed only 3% and 4% respectively. Although the sample size was small, no major seasonal shift between seed and invertebrate dominance was evident. Seed dominated the diet in both summer and winter, though winter seed consumption was lower (78% v. 58%). The level of seed consumption in the two spring samples was highly divergent (38% v. 93%), stressing the need for more samples to be collected from dry periods. Lowered rates of seed consumption during winter and in one of the spring samples were accompanied by increases in leaf consumption. Insect consumption remained low across all sampled seasons, suggesting that this species is not an omnivore. Rather, the dominance of seed in the diet suggests that Z. pedunculatus is primarily a granivore, a finding that has implications for the conservation status and management of this little-known species.


Author(s):  
D. W. Minter

Abstract A description is provided for Schizothecium vesticola, a dung-inhabiting fungus. Some information on its associated organisms and substrata, dispersal and transmission, habitats and conservation status is given, along with details of its geographical distribution (Africa (Algeria, Morocco)), North America (Canada (Alberta, British Columbia, Manitoba, Nunavut, Prince Edward Island, Quebec, Saskatchewan, Yukon), Mexico, USA (Alaska, Colorado, Idaho, New York, Utah, Washington, Wyoming), South America (Argentina, Brazil, Chile, Falkland Islands/Malvinas), Arctic Ocean (Denmark (Greenland), Norway (Svalbard)), Asia (Iraq, Pakistan, Russia (Sakhalin Oblast)), Atlantic Ocean (Spain (Canary Islands), St Helena), Australasia (Australia (South Australia, Victoria, Western Australia), New Zealand), Europe (Austria, Belgium, Bulgaria, Denmark (including Faroe Islands), Finland, France, Germany, Greece, Hungary, Iceland, Ireland, Italy (including Sicily), Netherlands, Norway, Poland, Romania, Russia (Krasnodar Krai, Moscow Oblast, Yaroslavl Oblast), Spain, Sweden, Ukraine, UK)).


Author(s):  
D. W. Minter

Abstract A description is provided for Podospora excentrica. Some information on its associated organisms and substrata, dispersal and transmission, habitats and conservation status is given, along with details of its geographical distribution (South America (Venezuela), Atlantic Ocean (Portugal (Madeira)), Australasia (Australia (New South Wales, South Australia, Victoria, Western Australia)), New Zealand, Europe (Belgium, Denmark, Germany, Ireland, Italy, Netherlands, Spain, Sweden, UK)).


Author(s):  
D. W. Minter

Abstract A description is provided for Nitschkia broomeana, which are found on cracks in bark. Details are given of its hosts, geographical distribution (Gambia, Ghana, Malawi, Sierra Leone, Zimbabwe, USA (Alabama, Florida, Georgia, Idaho, Louisiana, Nebraska, New Jersey, North Carolina, Ohio, Oklahoma, South Carolina, Tennessee and Virginia), Guatemala, Nicaragua, Panama, Argentina, Brazil, Venezuela, China (Beijing, Fujian, Hebei, Hunan, Jiangsu, Sichuan, Yunnan and Zhejiang), India (Andhra Pradesh, Chhattisgarh, Madhya Pradesh and Maharashtra), Japan, South Korea, Pakistan, Sri Lanka, Taiwan, Australia (South Australia), New Zealand, Czech Republic, France, UK, Italy, and Serbia and Montenegro), transmission, diagnostic features and conservation status.


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