The status of frogs in the Watagan Mountains area the Central Coast of New South Wales

1993 ◽  
pp. 257-264 ◽  
Author(s):  
M. J. Mahony
1962 ◽  
Vol 61 (4) ◽  
pp. 295-300 ◽  
Author(s):  
J. N. Hobbs ◽  
M. Kaveney

1997 ◽  
Vol 3 (1) ◽  
pp. 13 ◽  
Author(s):  
D. Lunney ◽  
A. L. Curtin ◽  
D. Fisher ◽  
D. Ayers ◽  
C. R. Dickman

The aims of this study were to identify common ecological patterns among threatened fauna in New South Wales, and to identify priority areas for research and management by determining which regions and habitats contain high numbers of threatened fauna. Threatened and non-threatened fauna were taken from the listings of Lunney et al. (1996, 1997). Species were categorized into weight classes, diet groups, habitats and regions and by level of knowledge available about them. All regions and habitats of the State contain threatened species. The northeastern region of New South Wales contains the greatest number of threatened species but the western region has suffered the most extinctions, especially of mammals. Species that historically inhabited a greater number of regions are less likely to be currently threatened or to be extinct than those with restricted distributions, and large species are more likely to be threatened than smaller species. The best predictors of a threatened mammals species were seeds and vegetation in the diet, heavier body weight, and ground-dwelling, burrowing, and rock pile/cave-dwelling habits. The Critical Weight Range (35?5 500g), although strongly associated with extinction of non-volant mammals, was not the most important predictor. Lord Howe Island held the highest proportion of threatened and extinct birds. Factors showing the strongest associations for threatened birds were carnivory, large size, and distribution in the southeastern region. The most poorly-known region for birds was the north-east, and the least known habitat was shrubland (including mallee, heath and chenopod shrubland). The status of reptiles was poorly known in all regions, especially the western region. Frogs were also poorly known in all regions. Frogs were most at risk if they were large, inhabited closed forest or occurred in the central or northeastern region. The study further revealed little association between particular ecological attributes and conservation status. This indicates that there are complex and pervasive threats affecting the status of New South Wales fauna. Research and management priority status could be argued for all regions and most habitats in the State, but the western or northeastern regions may face the most problems depending on the criteria used (e.g., past extinctions, number vs proportion of threatened species). Further, the conservation status of birds, reptiles and frogs is in particular need of attention from researchers.


1995 ◽  
Vol 22 (5) ◽  
pp. 601 ◽  
Author(s):  
D Priddel ◽  
N Carlile ◽  
C Davey ◽  
P Fullagar

Gould's petrel, Pterodroma leucoptera leucoptera, breeds only on Cabbage Tree Island, New South Wales. Annual surveys to estimate the size of the breeding population and the reproductive output were conducted between 1989 and 1992. Annual estimates of the total number of pairs breeding in the two gullies containing the main population were between 122 +/- 20 (s.e.) and 202 +/- 26. Breeding success was less than 20% between 1989 and 1991, but rose to 24.7% in 1992. This marginal improvement may be the result of management action undertaken to reduce mortality of breeding adults and fledglings. The total population is estimated to have declined from 2004 (95% confidence limits: 1464,3185) in 1970 to 1479 (1250,1815) in 1992, a decline of 26% in 22 years. The reasons for this decline are unclear.


1972 ◽  
Vol 20 (4) ◽  
pp. 391 ◽  
Author(s):  
RT Williams ◽  
I Parer

Epizootics of myxomatosis which occurred each year from 1968 until 1971 in a rabbit population inhabiting a 700-acre study site at Urana, N.S.W., were studied. Transmission was rapid in 1968 and 1969, Anopheles annulipes being the vector, and the peak of these epizootics occurred in early November. Transmission in 1970 was primarily by the flea Spilopsyllus cuniculi, and was slower, but the midpoint of the epizootic still occurred in early November. In 1971 the epizootic peaked in late December, transmission was rapid, and the vector was unknown. Each year, about 75% of the susceptible animals older than 3 months of age at the time of the epizootic contracted myxomatosis; of these, 60% recovered, and of the recoveries, 20% died between the time of recovery (early December) and 1 January. Fewer animals (16-55 %) under 3 months of age were seen with myxomatosis; of these, about 50% were seen to recover, and a large proportion (from 25 to 45%) of animals seen to recover died before 1 January each year. The great majority of animals not seen to contract myxomatosis probably died from other causes without being exposed to the disease. These data indicate that myxomatosis killed very few animals directly during these epizootics, and that other factors were responsible for the majority of deaths which occurred during the epizootic period. In 1968, 1969, and 1970, reactivation of latent virus in animals which had previously recovered from myxomatosis was probably the source of the virus which initiated the epizootics.


1981 ◽  
Vol 32 (3) ◽  
pp. 439 ◽  
Author(s):  
R Brown

Saccocirrids (archiannelids) were collected from coarse-grained sediments in turbulent water from the central New South Wales coast. Saccocirrus jouinae, sp. nov., and S. tridentiger, sp, nov., are described, and S. krusadensis Alikunhi, 1948 newly recorded in Australia. In these species gonads occur only on the left side of the body and cilia are found on the ventral surface. Of the 17 species attributed to the Saccocirridae, seven species are known to have unilateral gonads and ventral ciliation. They occur only in the Indo-Pacific region. Species with gonads on both sides of the body have not been described with cilia on the ventral surface. Their distribution is world-wide.


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