FACTORS INFLUENCING THE OCCURRENCE OF MAMMALS IN RETAINED LINEAR STRIPS (WILDLIFE CORRIDORS) AND CONTIGUOUS STANDS OF MONTANE ASH FOREST INTHE CENTRAL HIGHLANDS OF VICTORIA, SOUTHEASTERN AUSTRALIA
Db. Lindenmayer et al., FACTORS INFLUENCING THE OCCURRENCE OF MAMMALS IN RETAINED LINEAR STRIPS (WILDLIFE CORRIDORS) AND CONTIGUOUS STANDS OF MONTANE ASH FOREST INTHE CENTRAL HIGHLANDS OF VICTORIA, SOUTHEASTERN AUSTRALIA, Forest ecology and management, 67(1-3), 1994, pp. 113-133
Hairtubing was used to census mammals at 70 sites in 53 year old mount
ain ash (Eucalyptus regnans) and alpine ash (Eucalyptus delegatensis)
forest in the Central Highlands of Victoria, southeastern Australia. A
total of 40 sites was located in linear strips or wildlife corridors
that were retained in timber production areas. The remaining 30 sites
were in stands where the adjacent forest had not been logged. Thirteen
species of mammals were detected in the hairtubing surveys, but only
three were detected frequently enough to allow detailed analysis. The
detectability of these animals and other less commonly recorded specie
s varied according to the placement and the type of hairtubes that wer
e used. Although data on feral predators were very limited, no apparen
t effect of the proximity of hairtubing plots to roads was detected. D
etailed statistical analyses of the data were conducted at two levels:
the site level, and for individual hairtubing plots. Logit regression
models were used to explore the relationships between: (1) the probab
ility of detecting brown antechinus (Antechinus stuartii), bush rat (R
attus fuscipes) and swamp wallaby (Wallabia bicolor) and the measured
dimensions (e.g. width and length), environmental attributes and veget
ation structure of retained linear strips; (2) the probability of occu
rrence of Antechinus stuartii, Wallabia bicolor and R. fuscipes in hai
rtubing plots within areas of contiguous forest and retained linear st
rips and the characteristics of the vegetation structure and plant spe
cies composition in a 10 m area surrounding such plots. For the first
group of models, the variation in topography within retained linear st
rips significantly influenced the proportion of detections of Antechin
us stuartii and R. fuscipes, although there was a different response f
or each species. Other significant explanatory attributes in these mod
els included the number of roads and tracks that disrupted vegetation
cover as well as structural and floristic parameters such as the domin
ant tree species on the site and the basal area of Acacia spp. Analyse
s of the combined data for the two types of sites indicated that Walla
bia bicolor was more likely to be detected in plots within E. regnans
forest and where there was a limited cover of ferns on the forest floo
r. The type of study site (retained strip vs. contiguous forest) was a
significant variable in the models developed for Antechinus stuartii
and R. fuscipes, reflecting a significant influence of the configurati
on of sites on the probability of detection of these animals. Separate
models for the two types of sites were developed both for Antechinus
stuartii and R. fuscipes. The dominant species of tree was a significa
nt factor in several of these models, and there were significantly few
er records of Antechinus stuartii from the ends of strips of E. delega
tensis forest. Most of the other explanatory variables were measures o
f the vegetation cover and plant species composition which are likely
to reflect the importance of the suitability of foraging substrates fo
r Antechinus stuartii and R. fuscipes. For these species, a different
set of variables was found in each of the various models that were dev
eloped. These findings imply a degree of partitioning of the use of th
e forest environment by Antechinus stuartii and R. fuscipes. They also
suggest that patterns of microhabitat use by some species of mammals
may change when areas of montane ash forest are confined to a linear c
onfiguration (i.e. a retained strip).