David Y P Tng
UFBA - Federal University of Bahia, IBIO Institute of Biology, Department Member
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Geography, Biogeography, Plant Ecology, Forest Ecology, Fire Ecology, Bryology, and 19 moreDisturbance Ecology, Plant Taxonomy, Tasmania, Rain Forest Ecology, Sarawak, Tropical biology, Eucalypt biology, Tropical Forest Ecology, Plant sciences, Climate Change, Ecophysiology, Eucalypts, CO2 Effects on Plant Composition, Bryophytes, Epiphytes, Habitat Partitioning, Cool Temperate Rain Forest, Wood Anatomy, and Wood Science edit
Seasonally dry tropical forests are among the least studied of tropical forests. However, in recent years these forests have become recognized as an endangered global biome of great economic and cultural importance. Despite this... more
Seasonally dry tropical forests are among the least studied of tropical forests. However, in recent years these forests have become recognized as an endangered global biome of great economic and cultural importance. Despite this recognition, their status, range, and ecological value in Australia is still poorly appreciated, possibly because they are perceived to be species-poor derivatives of rainforests, and it has proved difficult to define and map their geographic extents.
In Australia, seasonally dry tropical forests grow in Western Australia, Northern Territory, Queensland and New South Wales, and they are often associated with unusual landforms like karsts, sandstone ravines and tablelands. These forests often exhibit dry-season deciduousness and unlike savanna, seasonally dry tropical forests harbor few grasses and they are fire sensitive.
Curious lifeforms such as bottle-shaped trees, prickly plants, and thicket-forming vines are also conspicuous in some areas.
Misleading local terms used to describe these forests, such as “Brush”, “Scrub” and “Vine thickets”, and confusingly “Dry rainforest” impedes development of national and global perspectives on the ecology and conservation status of these unique plant communities. Moving beyond local terms and seeing these forests as part of a global seasonally dry tropical forest biome will promote greater public awareness of their conservation value.
In Australia, around 75% of the original extent of these forests has been cleared. Although now largely protected, these forests still face various threats that often work synergistically, such as climate change, fire damage, mining, livestock damage and weed infestation. Ecological and biogeographical studies are therefore urgently needed to understand the resilience of seasonally dry tropical forests to multiple threats and to inform their conservation.
In Australia, seasonally dry tropical forests grow in Western Australia, Northern Territory, Queensland and New South Wales, and they are often associated with unusual landforms like karsts, sandstone ravines and tablelands. These forests often exhibit dry-season deciduousness and unlike savanna, seasonally dry tropical forests harbor few grasses and they are fire sensitive.
Curious lifeforms such as bottle-shaped trees, prickly plants, and thicket-forming vines are also conspicuous in some areas.
Misleading local terms used to describe these forests, such as “Brush”, “Scrub” and “Vine thickets”, and confusingly “Dry rainforest” impedes development of national and global perspectives on the ecology and conservation status of these unique plant communities. Moving beyond local terms and seeing these forests as part of a global seasonally dry tropical forest biome will promote greater public awareness of their conservation value.
In Australia, around 75% of the original extent of these forests has been cleared. Although now largely protected, these forests still face various threats that often work synergistically, such as climate change, fire damage, mining, livestock damage and weed infestation. Ecological and biogeographical studies are therefore urgently needed to understand the resilience of seasonally dry tropical forests to multiple threats and to inform their conservation.
Research Interests:
Environmental weeds typically invade open, disturbed areas or vegetation edges, and can have devastating ecological and economic consequences. The National Weeds List in Australia informs the public and land managers on weeds prioritized... more
Environmental weeds typically invade open, disturbed areas or vegetation edges, and can have devastating ecological and economic consequences. The National Weeds List in Australia informs the public and land managers on weeds prioritized for management, but shade-tolerant weeds that can invade forest ecosystems are inadequately listed. Such weeds are now globally recognized for their ability to impact native vegetation. The Cherry Guava (Psidium cattleianum) from Brazil, a shrub of the Myrtle family (Myrtaceae), is an exceptional example.
1. Cherry Guava was probably introduced to Australia for its edible fruits. The earliest record (1940s) was in Koah, Far North Queensland. Currently, Cherry Guava infestations are found in three World Heritage Areas in Australia: the Wet Tropics in Queensland; Gondwanan Rainforests of Queensland/New South Wales, and Lord Howe Island. It is listed as a noxious weed only in NSW. There are no Australian regulations restricting import or sale.
2. The Global Invasive Species Database lists Cherry Guava among the World’s 100 Worst Weeds – it tolerates shade; grows and matures rapidly; produces a heavy fruit set and seedling bank; is spread by native and feral animals; coppices extensively; and forms multi-stemmed thickets. It can displace native vegetation. Infestations in Australia appear free of natural enemies and resistant to Myrtle Rust which affects co-occurring native members of the Myrtaceae. In Hawaii, Seychelles and Mascarene Islands, natural forested ecosystems are severely impacted after introductions in the early- to mid-1800s.
3. Cherry Guava spread is ongoing, but given the recent Australian history and localized infestations, eradication may be possible with incisive intervention. Government listings and restricting import and sale are first steps. Options to eliminate infestations could combine ecotourism, volunteers and biological control agents.
1. Cherry Guava was probably introduced to Australia for its edible fruits. The earliest record (1940s) was in Koah, Far North Queensland. Currently, Cherry Guava infestations are found in three World Heritage Areas in Australia: the Wet Tropics in Queensland; Gondwanan Rainforests of Queensland/New South Wales, and Lord Howe Island. It is listed as a noxious weed only in NSW. There are no Australian regulations restricting import or sale.
2. The Global Invasive Species Database lists Cherry Guava among the World’s 100 Worst Weeds – it tolerates shade; grows and matures rapidly; produces a heavy fruit set and seedling bank; is spread by native and feral animals; coppices extensively; and forms multi-stemmed thickets. It can displace native vegetation. Infestations in Australia appear free of natural enemies and resistant to Myrtle Rust which affects co-occurring native members of the Myrtaceae. In Hawaii, Seychelles and Mascarene Islands, natural forested ecosystems are severely impacted after introductions in the early- to mid-1800s.
3. Cherry Guava spread is ongoing, but given the recent Australian history and localized infestations, eradication may be possible with incisive intervention. Government listings and restricting import and sale are first steps. Options to eliminate infestations could combine ecotourism, volunteers and biological control agents.
Research Interests:
The need to maintain a mosaic of rainforest and eucalypt forest in the Australian Wet Tropics World Heritage Area poses a perplexing conundrum for land managers. Rose Gum (Eucalyptus grandis) dominated giant eucalypt forests at the... more
The need to maintain a mosaic of rainforest and eucalypt forest in the Australian Wet Tropics World Heritage Area poses a perplexing conundrum for land managers. Rose Gum (Eucalyptus grandis) dominated giant eucalypt forests at the margins of World Heritage tropical rainforests are habitats for threatened marsupials like the Yellow-Bellied Glider. Rainforest developing in the understoreys of these forests is believed to threaten the dominant overstorey eucalypts and associated fauna. Land managers prescribe frequent low-intensity fires to try to stop rainforest species from establishing in Rose Gum forests understory. However, these practices are not consistent with the ecology of Rose Gum forest:
1. Rose Gums are obligate seeders and need rare, large, high-intensity landscape fires for successful regeneratation. Low-intensity fires do not stimulate Rose Gum regeneration because they do not release seeds stored in the canopy or create conditions suitable for initial growth. Repeated fires may kill young Rose Gum trees that do not have fully developed bark and these fires can reduce the protective capacity of the bark of mature trees.
2. Under current climatic conditions, rainforest expansion averages 0.6m/decade, and is occuring across all landscape conditions likely due to a global driver like increased atmospheric CO2. Using low-intensity fire to control this process is difficult because rainforest will only burn under exceptional conditions. Also, many rainforest species recover from a single fire. Natural and rare high-intensity fires will likely enable Rose Gum regeneration throughout the landscape.
The landscape ecology and plant functional biology of Rose Gum forest suggest that they are ecologically like secondary rainforest. Abstaining from prescribed burning and letting Rose Gum forests regenerate naturally from rare large fire events best approximates their regeneration
ecology.
1. Rose Gums are obligate seeders and need rare, large, high-intensity landscape fires for successful regeneratation. Low-intensity fires do not stimulate Rose Gum regeneration because they do not release seeds stored in the canopy or create conditions suitable for initial growth. Repeated fires may kill young Rose Gum trees that do not have fully developed bark and these fires can reduce the protective capacity of the bark of mature trees.
2. Under current climatic conditions, rainforest expansion averages 0.6m/decade, and is occuring across all landscape conditions likely due to a global driver like increased atmospheric CO2. Using low-intensity fire to control this process is difficult because rainforest will only burn under exceptional conditions. Also, many rainforest species recover from a single fire. Natural and rare high-intensity fires will likely enable Rose Gum regeneration throughout the landscape.
The landscape ecology and plant functional biology of Rose Gum forest suggest that they are ecologically like secondary rainforest. Abstaining from prescribed burning and letting Rose Gum forests regenerate naturally from rare large fire events best approximates their regeneration
ecology.
Research Interests:
Australian tall eucalypt forests have been the subject of awe and admiration since early colonial days. In the Wet Tropics of North Queensland, such forest occurs in transitional or ecotonal patches between rainforests and open woodland... more
Australian tall eucalypt forests have been the subject of awe and admiration since early colonial days. In the Wet Tropics of North Queensland, such forest occurs in transitional or ecotonal patches between rainforests and open woodland savannas. Rainforest species are commonly interpreted to be encroaching into the understorey of these tall eucalypt forests, namely those with statuesque Rose Gum (Eucalyptus grandis) dominants. This has led to concerns for the long term persistence of E. grandis forests, and ongoing debates over their need for active fire management. In this essay, I highlight the enigmatic ecology of these ecotonal forest habitats, and make the case that the management of these habitats should be grounded in ecological principles within a broader perspective of patterns in global vegetation change.
Research Interests:
The Daintree has garnered the reputation for being “Where the rainforest meets the reef”. But what is actually so special and unique about the Daintree? While the Australian Wet Tropics is famous for rainforest, in this article in the... more
The Daintree has garnered the reputation for being “Where the rainforest meets the reef”. But what is actually so special and unique about the Daintree? While the Australian Wet Tropics is famous for rainforest, in this article in the Oct-Nov volume (Issue 17) of Protected Magazine, we will examine what is found within the rainforests of the Daintree that makes the place truly extraordinary.
Research Interests:
Tall old-growth forests are of global social-economic, political and ecological significance. These forests contribute significantly to the global carbon budget and are of high conservation value given sustained logging and clearing over... more
Tall old-growth forests are of global social-economic, political and ecological significance. These forests contribute significantly to the global carbon budget and are of high conservation value given sustained logging and clearing over the past two centuries (Tng et al. 2012a). In Australia, these old-growth forests extend from tropical to temperate regions of Australia in areas where rainfall exceeds 1000 mm per year, being characterised by emergent eucalypt trees attaining statures of 30 m to more than 80 m, with canopy and understorey layers consisting of mesophytic broad-leaved trees and treelets, sclerophyllous shrubs and graminoids (Fig. 1). These forests support some of the tallest flowering plants in the world, are important habitats for a unique suite of flora and fauna, and are important forest cover for metropolitan water catchments – values that make giant eucalypt forests a focal point of scientific study and eco-tourism (Tng et al. 2012a).This article is protected by copyright. All rights reserved.
Callitris is Australia’s most successful and drought tolerant conifer genus. Callitris species are distributed across a huge geographical range from rainforest to arid zones, and hence they provide a rare opportunity to view plant growth... more
Callitris is Australia’s most successful and drought tolerant conifer genus. Callitris species are distributed across a huge geographical range from rainforest to arid zones, and hence they provide a rare opportunity to view plant growth trends across the continent. Here, we make a continental-scale examination of how climate influences basal diameter growth in Callitris. We sampled a total of five species but focused effort (23 of 28 samples) on the most widespread species, C. columellaris. Cores from a total of 23 trees were sampled from 15 sites that spanned a gradient in mean annual rainfall from 225 to 2117 mm and mean annual temperature from 11.5 to 28.2°C. Ring production is not annual across much of the distribution of the genus, so 14C-AMS dating was used to establish the frequency of ring production for each core. Ring width, tracheid lumen diameter and number of tracheids per ring were also measured on each core. Ring production was close to annual at mesic sites with reliable alternation of rainfall or temperature regimes but was more erratic elsewhere. For C. columellaris, ring width significantly increased with mean annual rainfall (r 2 = 0.49) as a result of wider and more tracheids per ring. For this species tracheid lumen diameter was correlated with annual rainfall (r 2 = 0.61), with a threefold increase from the driest to the wettest sites, lending support to the hypothesis that conifers growing at drier sites will have narrow lumen diameters to maximise mechanical strength of the xylem.
Research Interests:
The atmospheric pollen loads of Hobart, Tasmania, Australia, were monitored between September 2007 and July 2009. To examine the match of the airborne pollen composition with the flowering duration of their contributing plants, the... more
The atmospheric pollen loads of Hobart, Tasmania, Australia, were monitored between September 2007 and July 2009. To examine the match of the airborne pollen composition with the flowering duration of their contributing plants, the phenology of native and non-native plants in various habitats near the pollen-trapping site was undertaken between August 2008 and July 2009. The pollen load was found to have a strong seasonal component associated with the start of spring in September. This is incongruent with the peak flowering season of the total taxa in October. In most taxa, atmospheric pollen signatures appeared before flowering was observed in the field. The presence of most pollen types in the atmosphere also exceeded the observed flowering duration of potential pollen-source taxa. Reasons for this may be related to the sampling effort of phenological monitoring, pollen blown in from earlier flowering populations outside of the sampling area, the ability of pollen to be reworked, and the large pollen production of some wind-pollinated taxa. In 2007–2008, 15 pollen types dominated the atmosphere, accounting for 90% of the airborne pollen load. The top six pollen types belonged to Betula, Cupressaceae, Myrtaceae, Salix, Poaceae and Ulmus. Comparatively, the annual pollen load of Hobart is lower than in most other Australian cities; however, the pollen signal of Betula is inordinately high. Native plants play a minor role as pollen contributors, despite the proximity of native habitats to the pollen-sampling location. The implications of the aerobiological observations are discussed in relation to public health.