1997
DOI: 10.1080/00049158.1997.10674709
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The influence of habitat structure on insectivorous bat activity in montane ash forests of the Central Highlands, Victoria

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Cited by 18 publications
(19 citation statements)
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“…The lack of recovery after 36 years in old regrowth coupes is consistent with a number of other studies where low activity persisted for more than 30 years after disturbance (Brown et al 1997;Adams et al 2009;Webala et al 2011), but differs from selective harvesting of wet sclerophyll forest in subtropical Queensland where recovery of bat activity was apparent in a site logged 33 years previously (de Oliveira et al 1999). It is important to note that none of these studies consider activity levels on tracks, riparian zones, or other areas of retention that potentially could ameliorate the effects of clutter from dense regrowth and loss of tree hollows.…”
Section: Recovery Times After Timber Harvestsupporting
confidence: 78%
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“…The lack of recovery after 36 years in old regrowth coupes is consistent with a number of other studies where low activity persisted for more than 30 years after disturbance (Brown et al 1997;Adams et al 2009;Webala et al 2011), but differs from selective harvesting of wet sclerophyll forest in subtropical Queensland where recovery of bat activity was apparent in a site logged 33 years previously (de Oliveira et al 1999). It is important to note that none of these studies consider activity levels on tracks, riparian zones, or other areas of retention that potentially could ameliorate the effects of clutter from dense regrowth and loss of tree hollows.…”
Section: Recovery Times After Timber Harvestsupporting
confidence: 78%
“…This range in age is wide and likely spans considerable variation in above-ground habitat structure due to differences in the amounts of regeneration present; thus, a varied response by bats across studies and geographic locations should be expected. In montane eucalypt forests of south-eastern Australia, bat activity peaked in 165-year-old wildfire regrowth rather than in younger regrowth from clear-felling operations (Brown et al 1997). Unfortunately, the size and shape of clearcuts studied are rarely reported so an evaluation of the effects of cut size and shape on bat activity cannot be made.…”
Section: Clearcut and Deferment Harvestsmentioning
confidence: 99%
“…Smaller canopy gaps could interfere with detection of above-canopy bats and may reduce the activity of bats in the gaps themselves. Like our study, increases in bat activity in older montane ash forests were suggested to be related to larger height differences between primary and secondary canopies and greater crown separation ratios in the primary canopy (Brown et al, 1997; ground-based vertically pointed detectors used). Conversely, a study of bat activity at different heights in mature and young pine plantations found the highest activity levels near the ground (2 m height) in mature plantations, where clutter was less than in young plantations.…”
Section: Effects Of Vegetation Structure On Bat Activitymentioning
confidence: 58%
“…Less horizontal space between boles and vertical space between crowns may have limited the flight activity of bats in the subcanopy and lower canopy of young regrowth, especially those guilds with lower frequency calls. Additionally, while canopy percentage cover did not vary between old and young regrowth, increased tree stem density in young regrowth might have been accompanied by a decrease in the size of gaps between the canopy tree crowns (Brown et al, 1997;Humes et al, 1999), although we did not measure this. All of our bat detectors were pointed towards vegetation gaps.…”
Section: Effects Of Vegetation Structure On Bat Activitymentioning
confidence: 89%
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