The Eastern Otway Ranges, Victoria is an area recognised for its significant
flora and fauna communities. An area of about 7000 ha, the Anglesea heathlands
has been listed on the register of the National Estate. Although symptoms of
the plant pathogen Phytophthora cinnamomi have been
recorded in the area since the 1970s, the extent of infestation and its
effects have not been documented. The aims of this study were to assess the
distribution of infestation, identify the relationship of plant infection to
site variables and to identify evidence of spread of the pathogen. The
presence of P. cinnamomi was assessed at 50 study sites
by a visual evaluation of the vegetation, using species such as
Xanthorrhoea australis (Austral grass tree) and
Isopogon ceratophyllus (horny cone bush) as indicator
species. Soil and plant tissues were assayed for the presence of the pathogen
by cotyledon baiting and immunoassay methods.
Phytophthora cinnamomi was isolated at 76% of the
study sites from the floristic communities identified: heathy open forest;
heathy woodland I and II; Bald Hills heathland; riparian open forest. There
were significantly more diseased sites at lower altitudes. The pathogen is
widely spread and causing disease throughout the area, but at present often
only in small patches. There is an urgent need for disease management to
protect the significant communities. These findings suggest that management
actions such as mapping current infestations, closing tracks and implementing
vehicle wash-down points are required.
The confirmed vector of Ross River virus, Ochlerotatus camptorhynchus (Thomson), is the dominant mosquito species inhabiting saline marshes in coastal Victoria. This paper re-examines previously published data on Oc. camptorhynchus , plus additional data collected since that time, and provides greater spatial and temporal definition of Oc. camptorhynchus numbers at seven sites across the Gippsland Lakes system of eastern Victoria. A total of 357 672 Oc. camptorhynchus was captured from 1188 trap-nights across the seven trap sites during trapping seasons from 1990 to 2001. The dominance of Oc. camptorhynchus across the seven sites averaged 75%, with significant differences in mean abundance of Oc. camptorhynchus found between all trap sites. Significant differences in monthly abundance of Oc. camptorhynchus were observed for Wellington Shire. Increase in populations of Oc. camptorhynchus was associated with increases in rainfall at all trap sites, higher minimum temperatures at two of the seven trap sites, and wind speed at one trap site. Prioritisation of mosquito control may be applied based on spatial and temporal factors according to the findings of this study.
This study investigated the distribution, habitat and population dynamics of
the swamp antechinus (Antechinus minimus maritimus) in
the eastern Otway Ranges. The species has a restricted, disjunct distribution
and has been recorded at 25 sites between 1969 and 1999. All sites were
located within 7 km of the coast, occurred at altitudes up to 80 m above sea
level and within 10 m of a gully. Analysis of landscape site variables
identified sun index as being significant in determination of the probability
of occurrence of A. minimus. The presence of
A. minimus is negatively associated with sun index,
occuring at sites that have a southerly aspect and gentle slope.
A. minimus was located in a range of structural
vegetation including Open Forest, Low Woodland, Shrubland and Hummock
Grassland and a number of floristic groups, some characterised by high
frequencies of sclerophyll shrubs, others by high frequencies of
Pteridium esculentum, hummock grasses and herbaceous
species. A. minimus occurs in fragmented, small
populations with maximum population densities of 1.1–18
ha–1. Populations at inland sites became extinct
after the 1983 wildfire which burnt 41 000 ha. These sites have not been
recolonised since, while on the coast the species did not re-establish until
1993–97. One population that is restricted to a narrow coastal strip of
habitat is characterised by high levels of transient animals. The species is
subject to extinction in the region due to habitat fragmentation, coastal
developments and fire. Management actions to secure the present populations
and ensure long-term survival of the species in the area are required and
include implementation of appropriate fire regimes, prevention of habitat
fragmentation, revegetation of habitat, and establishment of corridor habitat.
The pathogen Phytophthora cinnamomi causes extensive ‘dieback’ of Australian native vegetation. This study investigated the distribution of infection in an area of significant sclerophyll vegetation in Australia. It aimed to determine the relationship of infection to site variables and to develop a predictive model of infection. Site variables recorded at 50 study sites included aspect, slope, altitude, proximity to road and road characteristics, soil profile characteristics and vegetation attributes. Soil and plant tissues were assayed for the presence of the pathogen. A geographical information systyem (GIS) was employed to provide accurate estimations of spatial variables and develop a predictive model for the distribution of P. cinnamomi. The pathogen was isolated from 76% of the study sites. Of the 17 site variables initially investigated during the study a logistic regression model identified only two, elevation and sun‐index, as significant in determining the probability of infection. The presence of P. cinnamomi infection was negatively associated with elevation and positively associated with sun‐index. The model predicted that up to 74% of the study area (11 875 ha) had a high probability of being affected by P. cinnamomi. However, the present areas of infection were small, providing an opportunity for management to minimize spread into highly susceptible uninvaded areas.
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