K’gari

Country
Australia
Inscribed in
1992
Criteria
(vii)
(viii)
(ix)
The conservation outlook for this site has been assessed as "good with some concerns" in the latest assessment cycle. Explore the Conservation Outlook Assessment for the site below. You have the option to access the summary, or the detailed assessment.

Fraser Island lies just off the east coast of Australia. At 122 km long, it is the largest sand island in the world. Majestic remnants of tall rainforest growing on sand and half the world’s perched freshwater dune lakes are found inland from the beach. The combination of shifting sand-dunes, tropical rainforests and lakes makes it an exceptional site. © UNESCO

Stephan Ridgway CC BY 2.0

Summary

2025 Conservation Outlook

Finalised on
11 Oct 2025
Good with some concerns
K’gari (Fraser Island) has been viewed as a model in participatory conservation management between many different stakeholders and several excellent management plans for a variety of issues have been put in place. The state of the site's World Heritage values remains relatively good and significant human and financial resources are being directed to the management of the threats to these values. However, pressures from tourism and recreational use, as well as climate change, are impacting on values and will require continued monitoring and increased management efforts to ensure preservation of the site's values in the long-term. The K'gari (Fraser Island) World Heritage site includes land and sea that is the traditional country of the Butchulla First Nations people. The Butchulla people are recognised by the High Court of Australian as holding Native Title rights to K'gari. The Island is now officially known as K'gari, the traditional Butchulla name for the Island. The Traditional Ecological Knowledge held by the Butchulla people incorporates knowledge of cultural heritage values, natural heritage values, and overall needs for the culturally appropriate management of K'gari. Incorporating Butchulla people's Traditional Ecological Knowledge into the management of the World Heritage site is critical to protect the island's natural and cultural values. The Queensland Department of the Environment, Tourism, Science and Innovation is collaborating with the Butchulla people to ensure that management of the site incorporates Traditional Ecological Knowledge and practices.

Current state and trend of VALUES

Low Concern
Since inscription in 1992 the state of World Heritage values remains relatively good and significant human and financial resources are being directed to the management of the threats to these values. However the extent of many of the threats is increasing, with many being exacerbated by climate change. This can be expected to flow through to impact on values in the future unless these threats can be more effectively addressed. Increased incorporation of cultural heritage values (not covered in this assessment) is being addressed in current planning and management.

Overall THREATS

High Threat
Increased visitation, biosecurity concerns and impacts of climate change are the major threats to the property. Increased tourism is acting as a driver for several other threats, which include pollution, erosion and siltation, disturbance, and the introduction of invasive species. Management capacity is relatively high but significant negative effects on the site's values and integrity are probable without proportional management intervention. Climate change seems to be irreversibly changing some of the physical properties of the site and is already a threat to several site values. These threats are likely to gain in importance in the future, with increases in risks such as localised species loss, sea level rise, loss of habitat (such as patterned fens), increased dune erosion, increased number of droughts and dramatic climate rainfall/storm events and wild fires and impacts to biosecurity.

Overall PROTECTION and MANAGEMENT

Mostly Effective
Protection and management is mostly effective. The Queensland Department of the Environment, Tourism, Science and Innovation, Queensland Parks and Wildlife Service and Partnerships (QPWS&P) provides strategic oversight and undertakes day to day management activities through a collaborative arrangement with the Butchulla Aboriginal Land and Sea Ranger Program. However, high levels of visitation and pressures from recreational use and impacts related to climate change, sea level rise, biosecurity and surrounding land use activities will require enhanced and systematic monitoring and increased management focus on World Heritage values to ensure conservation of the site’s values in the long-term. Climate adaptation planning is underway, supported by the Butchulla Aboriginal Corporation RNTBC (BAC), the Australian and Queensland governments but it is too early to assess the effectiveness of implementation of these plans.

Full assessment

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Description of values

Largest sand island in the world with spectacular beaches, cliffs and blowouts

Criterion
(vii)
K'gari (Fraser Island) is the largest sand island in the world, containing a diverse range of features that are of exceptional natural beauty. The area has over 250 km of clear sandy beaches with long, uninterrupted sweeps of ocean beach, including more than 40 km of strikingly coloured sand cliffs as well as spectacular blowouts (World Heritage Committee, 2012).

Tall rainforest growing on high coastal sand dunes

Criterion
(vii)
The development of rainforest vegetation communities, with trees up to 50 metres tall on tall coastal dunes, is a phenomenon believed to be unique in the world (World Heritage Committee, 2012).

Largest unconfined aquifer and perched freshwater dune lakes

Criterion
(vii)
The world’s largest unconfined aquifer on a sand island and half of the world’s perched freshwater dune lakes occur on the island, producing a spectacular and varied landscape. K’gari also has a variety of freshwater dune lakes which are exceptional in terms of number, diversity and age. The dynamic interrelationship between the coastal dune sand mass, aquifer hydrology and the freshwater dune lakes provides a sequence of lake formation both spatially and temporally (World Heritage Committee, 2012).

Most complete age sequence of coastal dune systems

Criterion
(viii)
Immense sand dunes, which are part of the longest and most complete age sequence of coastal dune systems in the world and still evolving (World Heritage Committee, 2012).

Unique process of soil formation with deepest podzols in the world

Criterion
(viii)
Unique process of soil formation due to the successive overlaying of dune systems, meaning soil profiles range from rudimentary profiles less than 0.5 metres thick to giant forms more than 25 metres thick, deeper than any podzols anywhere else in the world (World Heritage Committee, 2012).

Unique flora and fauna demonstrating ongoing succession, speciation and radiation

Criterion
(ix)
Unique relict and disjunct populations of ancient angiosperm heathland and closed forest plant communities and associated vertebrate and invertebrate fauna with specialised adaptations to low fertility, fire, waterlogging and aridity, demonstrating ongoing speciation and radiation. The low shrubby heaths (‘wallum’) are of considerable evolutionary and ecological significance. The island has the only examples of sub-tropical patterned fens (along with those at Cooloola) known in the world. These fens support an unusual number of rare and threatened invertebrate and vertebrate species (World Heritage Committee, 2012). The area provides most of the world's known habitat for 'acid' frogs, threatened species which have adapted to the highly specialised acidic environment associated with wet heathlands and sedgelands in this siliceous sand environment. Vegetation associations and succession represented on Fraser Island display an unusual level of complexity, with major changes in floristic and structural composition occurring over very short distances. There is clear zonation and succession of plant communities according to salinity, water table, age and nutrient status of dune sands. The chronosequence of podzol development has a direct influence on plant succession, with the older dune systems causing retrogressive succession (World Heritage Committee, 2012).
Dingoes
Butchulla people and dingoes (wongari) have a long history of close cultural and spiritual association on K’gari (Fraser Island). As such, the Butchulla have cultural obligations to ensure their welfare. Dingo management on K’gari (Fraser Island) is a collaborative partnership between Queensland Parks and Wildlife Service and Partnerships and the Butchulla Aboriginal Corporation (IUCN Consultation, 2020a).
Although some degree of hybridisation between dingoes and domestic dogs is suspected to have historically occurred on the island (Clutton‐Brock et al., 1994; Woodall et al., 1996; Behrendorff, 2016), K’gari represents an opportunity to maintain a self-sustaining population of wild genetically pure dingoes (UNESCO, 2001).
Marine biodiversity
The World Heritage site extends seaward 500 m from the high-water mark. A substantial amount of internationally important marine biodiversity including resident and migratory shorebirds, waterfowl and seabirds, fish, crustaceans, oysters, sea turtles, sea snakes, dugongs, cetaceans and seagrass meadows occur within the property, which lies adjacent to the Great Sandy Marine Park and includes the Great Sandy Strait Ramsar site  (State Party of Australia, 1991; State Party of Australia, 2003).

Assessment information

High Threat
Increased tourism is acting as a driver for several threats to the property, including pollution, erosion and siltation, disturbance, and the introduction of invasive species. The 2020 bushfire that impacted over half of the island, and the projections of significantly greater likelihood of severe fire as a result of climate change show that wildfire will be an increasing and significant threat to values. Management capacity is high, but significant negative effects on the site's values and integrity is probable unless proportional management intervention is increased. There is a need for up to date consistently collected data on the number of visitor arrivals on K'gari (Fraser Island) as this data is critical for effective decision-making and management outcomes.
Invasive Non-Native/ Alien Species
(Invasive species and pathogens)
Invasive/problematic species
Xiphophorus maculatus
Gambusia holbrooki
Acridotheres tristis
Pheidole megacephala
Other invasive species names
Bitou bush (Chrysanthemoides monilifera); Easter cassia (Senna pendula); Singapore daisy (Sphagneticola trilobata); pandanus leafhopper (Jamella australiae); cane toad (Rhinella marina); myrtle rust (Uredo Rangelii), Feral cat (Felis catus), Indian Myna
High Threat
Inside site
, Scattered(5-15%)
Outside site
Over 200 invasive species are present in the World Heritage area (DES, 2019). These include weeds such as bitou bush, Easter cassia, groundsel, invasive grass species, Abrus, Singapore daisy and asparagus fern; pests such as the Jamella pandanus leafhopper; feral animals including cane toads, cats, horses and coastal brown ants; and pathogens such as myrtle rust. Management is good and some species like horses and foxes have not been detected in repeat and ongoing monitoring in excess of 5 years and are considered eradicated.

However, work on cane toads and ants has been less successful but ongoing (IUCN Consultation, 2017; 2024). Myrtle rust, an exotic airborne pathogen, was first detected on K’gari in 2013 across a range of Myrtaceae species and based on the most recent monitoring in August 2020, has now become well established, impacting on vegetation regeneration following wildfire, particularly for Melaleuca quinquenervia (IUCN Consultation, 2020b). Research is underway to establish impact levels, at both a species and plant community level, to assist in the development of species conservation and management plans. The Queensland Department of Agriculture and Fisheries is working in collaboration with the Department of Environment, Tourism, Science and Innovation and the Butchulla Land and Sea Rangers to enhance biosecurity and awareness of Myrtle Rust on the island (IUCN Consultation, 2020a).

The extensive wildfire on the island in late 2020 impacted 46% of the K’gari section of Great Sandy National Park with the most extensively impacted (82%) regional ecosystem being RE 12.2.9 (Banksia aemula low open woodland) (Meiklejohn et al, 2023). The fire sensitive foredune communities (RE 12.2.14) that were significantly impacted by the fire are likely to be less resilient to invasion by Chrysanthemoides monilifera subspecies rotundata (bitou bush) and the risk of new invasions is high due to the large number of vehicles and widespread camping in the coastal zone (Meiklejohn et al, 2023). Ongoing monitoring has not detected any new infestations.
Logging, Harvesting & Controlling Trees
(Illegal firewood collection by tourists)
Very Low Threat
Inside site
, Localised(<5%)
Illegal firewood collection by tourists presented a problem. However, a range of park management tools have been employed and this practice has been largely eliminated (IUCN Consultation, 2020a, 2024).
While firewood collection itself is a low threat to the World Heritage values, the 2020 bushfire which had a serious impact on the island started from an illegal campfire (see fire hazard threat).
Fire & Fire Management
(Fire hazards)
Very High Threat
Inside site
, Throughout(>50%)
Long-term traditional fire management practices maintained K’gari (Fraser Island) floristic diversity and complexity. Historical European fire management may have increased the risk of damaging bushfire on the island.

Cultural burning (cool, patchwork burns) coupled with planned burning aligned with the Bioregional Planned Burn Guidelines (DES 2022), across broad landscape scale provides opportunity to reduce the risk of damaging bushfires on the island under likely future climate change scenarios and maintain biodiversity on K’gari (Fraser Island). Cultural burns will help reinforce Butchulla identity and cultural knowledge relating to K’gari (Fraser Island). Butchulla Land and Sea Rangers and scientists are working with Queensland Parks and Wildlife and Partnerships (QPWS&P) staff to develop fire management strategies and policies that take account of cultural burn requirements (IUCN Consultation, 2020a). Data show fire regimes can alter vegetation community dynamics through changes in fire frequency and intensity (Stewart et al., 2020). The window of opportunity for planned burns is reducing as a result of climate change. Changes in plant communities may be driven by future climate change and accelerated by the increase in fires (Stewart and Moss, 2015). It is felt that modern regimes driven by climate change will result in a decrease in native biodiversity with a possible increase in pyrogenic invasive plant species (Stewart et al., 2017).
In late 2020, extensive wildfire impacted on nearly half of the island and in excess of 80% of some vegetation communities (Meiklejohn et al., 2023). While the majority of vegetation communities are fire adapted, widespread and intense fires such as this may negatively impact communities and associated natural and cultural values. Some fire sensitive communities were significantly impacted (55% of the foredune complex, which includes highly fire sensitive Casuarina equisetifolia (coastal she-oak) and 69% of the beach ridge communities were burnt, in some places at high to severe intensity) with likely impacts on resilience and recovery (Meiklejohn et al., 2023). Others such as the rainforests, mangroves and saltmarshes were little impacted. An assessment of recovery of the vegetation by Qld Herbarium found that robust recovery was occurring across all the nine REs sampled with the exception of the foredune complex (Neldner et al. 2021). A report on post-fire monitoring of wetlands, threatened species and threatened ecological communities (Collett et al., 2023) that assesses 100 wetland sites found a broad distribution of both native and introduced species but also a " concerning number of instances of potential localised extinctions where wallum frog and fish species had been recorded historically, but not after the 2019-2020 fires" (Collett et al., 2023). Native wallum fish species were more abundant in unburnt sites while introduced fish species were more abundant in fire-affected sites (Collett et al., 2023).

The ecological assessment of the northern lakes’ precinct in June 2022 (to evaluate impacts of the Duling fire and recovery) found window lakes showed very minor fire impacts and were in good condition. Most other wetland types, other than in popular visitor sites, were also mostly in good condition. Exceptions were some peat-based wetlands that had burnt under dry conditions either in the Duling fire and/or previous fire(s). very minor fire impacts on window lakes. Previously unrecorded populations of fish species were found at several wetlands including the Endangered honey blue eye and ornate rainbowfish. Some previously recorded populations of these two spp were also reconfirmed. Of concern was the absence of these species from two previously known locations – one in the northern lakes’ precinct and on the south of the precinct. Fire seems unlikely to be the causal factor, with lake drying suspected to be the cause. Five native frog spp were recorded in the wetland in the northern lakes precinct with threatened and near threatened frogs being observed at many sites (Melzer et al. 2024).

The likelihood of climate change induced increases in extreme and widespread wildfires, in the absence of a managed fire regime, means that the threat level for fire hazards is increasing.
Recreational Activities
(Disturbance caused by tourists)
High Threat
Inside site
, Scattered(5-15%)
The large numbers of 4WD vehicles driving along the beaches and beach camping disturb the littoral fauna, changes sand deposition and can disrupt the sense of wilderness, 'exceptional natural beauty' and 'uninterrupted sweeps of ocean beach' in some areas. Increased visitation also disturbs the native fauna and flora, especially by trampling vegetation around lakes. Schlacher et al. (2008) showed that macrobenthic invertebrate populations are reduced on off-road vehicle-impacted beaches and the death of such species can impact on sandy-beach food chains thus influencing the abundance of birds, crabs and fish that rely on them for food. Vehicle related impacts are concentrated around visitor sites and travel routes and are unlikely to be negatively altering on-going geomorphological processes at the landscape level (IUCN Consultation, 2017). The impact of beach camping and unrestricted camping in dunes (especially without toilet facilities) has been shown to degrade the coastal dunes (Hockings and Twyford 1997) and in a preliminary study conducted in 2015 (Carter et al., 2015) that suggested nutrient levels in the watertable were enriched in camping zones.
Overall visitor use of the island has showed a steady growth over the past 5 years, and especially in the beginning of 2022 when COVID related travel restrictions for domestic tourists were removed (Earthcheck, 2024). There is a lack of quantitative data on environmental and social impacts (especially cumulative impacts) of current levels of visitation on the values of the island but concern is being expressed, based on perceptions and more anecdotal data by stakeholder groups (Earthcheck, 2024).
Water-borne & other effluent Pollution
(Pollution caused by visitation and residents)
Low Threat
Inside site
, Scattered(5-15%)
Tourist numbers may have doubled since inscription in 1992; and tourism, along with climate change, is considered as a major driver for many of the current threats facing the World Heritage site today. Earlier water quality monitoring by University of Queensland and the Queensland Government of several lakes (ranging from low to high visitation) concluded that water quality was good and unchanged from monitoring conducted in 1988 (Arthington et al., 1989; Moss, 2009; DSITIA, 2012). However, at beach camping zones nutrient levels at the water table interface and beach flows show enrichment with faecal coliforms and faecal sterols resulting in negative environmental impacts of these zones (Carter et al., 2015). Regular and more frequent monitoring and research on water quality in the lakes is beneficial and has been incorporated into the draft QPWS&P Values Based Management thematic strategy (DES, 2019). In 2019, the Butchulla Land and Sea Rangers commenced a Water Quality Monitoring program. The Queensland Department of the Environment, Tourism, Science and Innovation are working with Fraser Coast Regional Council to improve management of waste transfer stations and historical sites which may contain asbestos. Fraser Coast Regional Council recently developed the Fraser Coast Waste Strategy 2019-2029, with plans to upgrade transfer stations at Eurong, Happy Valley and Orchid Beach by 2024 (IUCN Consultation, 2020a). In 2024, a major investigation led by Burnett Mary Regional Group with the Butchulla Aboriginal Corporation, CSIRO, Department of Environment, Science and Innovation and University of Adelaide, commenced to investigate K’gari’s groundwater resources (IUCN consultation, 2024).
Changes in Temperature Regimes, Changes in Precipitation & Hydrological Regime
(Increased temperature, more variable precipitation, extreme weather events)
Very High Threat
Inside site
, Throughout(>50%)
Outside site
Overall, climate change impacts including higher temperatures, rising sea levels, and more frequent and extreme weather events pose a very high potential threat to species composition, coastal processes, fire regimes and hydrological processes (Gontz et al., 2015; Wardell-Johnson et al., 2015). Increase in fire frequency, intensity and sequence is expected due to climate change drivers (Stewart and Moss, 2015). Fire regimes may also increase myrtle rust susceptibility. Myrtacea may be vulnerable when they sprout new growth after fire; Coutinhou (1998) notes that eucalyptus rust can be fatal when it infects coppice growth of highly susceptible species. Predictions include increasing numbers of lower rainfall days/drought followed by heavy rainfall events which may further disrupt species distribution and abundance. Changing conditions will also increase biosecurity risk with the movement and prevalence of pest species including wind-borne myrtle rust and new weed species (IUCN Consultation, 2020b). A recent report by CSIRO, Managers of World Heritage Properties in Australia, and Indigenous Reference Group (2022) has assessed the likely impacts and vulnerabilites of Australia's World Heritage properties to climate change. For K'gari (Fraser Island), the report concludes that "The relationship between the coastal dune sand mass, hydrology, soil formation and the structure of plant communities and wetlands on K’gari are strongly interconnected. Sea level rise, changes to ocean transport processes, changes in fire regimes and increased storm intensity and wave strength and direction pose important and irreversible threats to the physical properties underpinning K’gari’s Outstanding Universal Values." Ex Tropical Cyclone Alfred impacted Southeast Queensland with severe weather and flooding between 4 March and 31 March 2025.

Workshops undertaken between 9 December 2024 and February 2025 with the K’gari World Heritage Advisory Committee, provided up-to-date information regarding the impacts on the OUV. Initial natural and cultural values assessments, in coordination with Butchulla Peoples representatives and QPWS technical advisors, indicate limited impacts relative to other SEQ protected area managed sand islands. Management capability was impeded by impacts on communications infrastructure during the event requiring implementation of contingency communication measures. These impacts have been resolved. Visitor management infrastructure impacts were largely focused on beach camping access (due to high eroded dune faces) and road washouts and closures due to isolated tree fall. Immediate recovery action has resolved the majority of impacted sites, with some longer-term road recovery works in planning.
Impacts to the natural values, including those pertaining to the OUV, were primarily focused on the coastline, with significant beach erosion, accumulation of ocean current born flood and tidal debris from off island locations, and loss of near shore vegetation at some locations. Inland impacts include isolated tree fall and siltation of some drainage lines. Natural and Cultural values recovery to date has included clean-up of the majority of flood debris, closure of camping areas in the vicinity of significant erosion and/or vegetation loss to enable natural recovery, and siltation clearing of road related drainage and siltation capture infrastructure. While initial values assessment, including health checks (condition assessments) indicates no significant event related impacts outside of natural cyclical ecological processes, with the ability of natural regeneration QPWS has designed and is implementing a more comprehensive natural values assessment programme. The comprehensive assessment report is envisaged to be complete within the first quarter of 2025/26 and will inform any necessary ongoing recovery actions relating to biosecurity, fire, and visitor management actions (IUCN Consultation, 2025).
Earth & Sediment Management
(Siltation)
Low Threat
Inside site
, Localised(<5%)
The large number of 4WD vehicles (including tour buses) used by visitors, commercial tourists and residents and coastal urban development compact the soil and provoke erosion and siltation, filling pristine dune lakes with sediment (GHD, 2002; Waldron, 2023, 2021). The impacts of recreational use and vehicular access have been under active management to ensure resource conservation (State Party of Australia, 2003). Several road sections have been realigned and site access redesigned to minimise sedimentation issues (IUCN Consultation, 2017). Sea level rise of approximately 100mm since the early 1900s may also affect erosion rates (CSIRO, undated) and recent global predictions of up to 1 m of sea-level change by 2100 would result in significant disruption of both coastal dunes and the key beach transportation network on the island. Current observations of road degradation show that a more sustainable transport system should be implemented to mitigate further erosion from vehicular and weather impacts (Waldron, 2023, 2021).

Recreational Activities
(Overtourism)
Very High Threat
Inside site
, Throughout(>50%)
The increased number of visitors to K’gari has resulted in a range of continuing pressures that are contributing to visitor management issues on the island. The impacts are placing immediate pressure on infrastructure at key sites, particularly at peak periods, and are contributing to the congestion of daily vehicle movements directly related to traffic from barge arrivals and tidal patterns (Earthcheck, 2022). A report by Earthcheck has also determined that pressure is being placed on “bucket list” sites, such as Eli Creek and Lake McKenzie, and creating associated visitor behavioural issues, including activities that extend visitor zones. These are exacerbated by higher levels of free and independent travellers and by visitors who have not previously visited the island, particularly since the COVID-19 pandemic. Current estimates place visitation somewhere between 450,00 and 500,000 per year. While there is capacity for the island to absorb this level of tourism visitation, the true number could be as high as 800,000 to one million visitors per year according to K'gari's World Heritage Advisory Committee (K'gari (Fraser Island) World Heritage Advisory Committee, 2023). Visitation is expected to increase in the next decade, particularly due to the Olympics in Brisbane in 2032. National park reports also state that 337,000 camper nights and almost 67,000 vehicle access permits were purchased for K'gari in 2023. While overtourism may be considered 'data deficient' if no accurate means of reporting is available, there is sufficient evidence to argue that K'gari's values are at risk and will require effective management approaches to mitigate.
Very High Threat
Climate change projections indicate irreversible change of some of the physical properties of the site. Climate change has already been demonstrated as a threat to several of the values of the property, and will gain in importance in the future, with potential impacts on species composition, coastal processes, fire regimes and hydrological processes. Regional flooding in southeast Queensland and northern New South Wales in 2022 led to a significant increase in marine debris along the K'gari (Fraser Island) east coast. The Queensland Department of Environment, Science and Innovation is collaborating with the Australian Government and the Butchulla Aboriginal Corporation to progress climate adaptation planning. Increased visitation may increase the probability that other invasive species will be introduced. High rates of human visitation and the possibility that domestic dogs (although domestic animals are prohibited on K'gari) continue to be brought by visitors to the island also raises the prospect of disease introduction.
Invasive Non-Native/ Alien Species
(Invasive species)
Invasive/problematic species
Anoplolepis gracilipes
Abrus precatorius
Oreochromis mossambicus
Very High Threat
Inside site
, Extent of threat not known
Outside site
Increased visitation may increase the probability that other invasive species will be introduced (State Party of Australia, 2003). The Fraser Coast Regional Council (FCRC) has released a Fraser Coast Biosecurity Plan (2019-2022). Biosecurity management initiatives are underway through a partnership between the Butchulla Aboriginal Corporation, the Queensland Department of Agriculture and Forestry and the Queensland Department of the Environment, Science and Innovation. The biosecurity management initiatives are intended to reduce the likelihood of additional invasive species being introduced (IUCN Consultation, 2020a). However, the lack of preventative requirements for appropriate hygiene standards and the presence of potentially serious invasive species such as yellow crazy ant (Anoplolepis gracilipes) on the adjacent mainland can present significant concern. A project (August 2020), supported by the Australian Government through the University of Melbourne's Centre of Excellence for Biosecurity Risk Analysis and Chief Environmental Biosecurity Office, has developed tools and strategies to minimise the risks of new priority pests, weeds and pathogens (IUCN Consultation, 2020b). The methodology will be used by the Queensland University of Technology to undertake a complete risk assessment as part of the K’gari Biosecurity Strategy development (2024-25) being delivered by the Butchulla Aboriginal Corporation (IUCN consultation, 2024). Fraser Coast Regional Council has declared two additional weed species that have been listed under Local Law #3. These include crab’s eye creeper (Abrus precatorius subsp. africanus) – which has established in Happy Valley. Queensland's Department of the Environment, Science and Innovation has confirmed a tilapia population has been discovered in a lagoon at K'gari's Kingfisher Bay Resort. It remains unclear how the fish made it to the island. The Department of Agriculture and Fisheries (DAF) has been in contact with Queensland Parks and Wildlife Service staff and the leaseholder to provide support and discuss management options for K'gari (Marie, 2024).
Unknown Threats
(Disease introduction, low genetic diversity and the prospect for population decline)
Data Deficient
Inside site
, Throughout(>50%)
Current pilot study estimates for the K'gari dingo population suggest that numbers lie between 73 (lower end of Conroy (2016b) range) and 257 (upper end of the range of Allen et al. (2015)) total individuals (see also Appleby and Jones, 2011), coupled with the geographic isolation the population is subject to, the population may be at risk of decline and possibly extinction at some point in the future. Conroy (2016a) reported relatively low genetic diversity, as to be expected for an island population, compared to mainland dingoes. High rates of human visitation and the possibility that domestic dogs (although domestic animals are prohibited on K'gari) continue to be brought by visitors to the island also raises the prospect of disease introduction. Thus, there are additional reasons for concern. Regular population monitoring, including abundance, survival and genetic studies, along with disease screening ongoing, are required to ensure population survivability.

Involvement of stakeholders and rightsholders, including indigenous peoples and local communities, in decision-making processes
Highly Effective
In 2014, the Federal Court of Australia made a consent determination recognizing the Butchulla people's native title rights in relation to Fraser Island (National Native Title Tribunal, 2014). The establishment of the Butchulla Aboriginal Corporation RNTBC (BAC) has provided the basis for co-stewardship arrangements to be established between Butchulla and Queensland Parks, Wildlife and Partnerships managers of the site. A second consent determination made December 2019 recognized the Butchulla people's native title rights in relation to the mainland, Great Sandy Strait and to high water on Fraser Island (National Native Title Tribunal, 2019). This has resulted in the formation of a second group, the Butchulla Native Title Aboriginal Corporation RNTBC (BNTAC). An Administrative Working Group meets regularly to enable Parks Managers and the BAC to liaise for decision-making purposes. Negotiations are underway between the State Government and BAC in relation to strengthening and supporting co-stewardship arrangements into the future. The Queensland Department of the Environment, Tourism, Science and Innovation support a Butchulla Land and Sea Ranger team that works alongside national parks managers.
Legal framework
Highly Effective
99% of the island is included in the Great Sandy National Park and protected under the Nature Conservation Act 1992 (Qld). The marine zone (500m) surrounding the island lies within the Great Sandy Marine Park and is subject to the Marine Parks Act 2004 (Qld). There is also specific legislation for World Heritage sites (Environment Protection and Biodiversity Conservation Act 1999 (Cth)). Legislation is rigorously enforced (World Heritage Committee, 2012). Other relevant legislation includes Recreation Areas Management Act 2006 (Qld); Planning Act 2016 (Qld); Environmental Protection Act 1994 (Qld); Fisheries Act 1994 (Qld); Aboriginal Cultural Heritage Act 2003 (Qld), Queensland Heritage Act 1992 and the Fraser Coast Regional Council Local Government Planning Scheme (IUCN Consultation, 2017). Whilst the majority of the Fraser Island World Heritage Area is within a protected area tenure, there are also around 500 private freehold properties. However, all development, regardless of land tenure, is subject to the Australian Government Environment Protection and Biodiversity Conservation Act 1999 as well as numerous State legislative controls, which are considered highly effective in maintaining World Heritage values.
Governance arrangements
Mostly Effective
Governance arrangements are clear and well documented. There are existing protocols for co-ordination between the Commonwealth Government (as signatory to the World Heritage Convention) and the Queensland State Government which has ownership of the National Park and governance responsibilities across the whole island and adjacent marine areas. The entire World Heritage site is within State territorial responsibilities. In 2014, the Federal Court of Australia made a consent determination recognizing the Butchulla people's native title rights in relation to Fraser Island (National Native Title Tribunal, 2014). The establishment of the Butchulla Aboriginal Corporation RNTBC (BAC) has provided the basis for co-stewardship arrangements to be established between Butchulla and Queensland Parks, Wildlife and Partnerships managers of the site. A second consent determination made December 2019 recognized the Butchulla people's native title rights in relation to the mainland, Great Sandy Strait and to high water on K'gari (Fraser Island) (National Native Title Tribunal, 2019). This has resulted in the formation of a second group, the Butchulla Native Title Aboriginal Corporation RNTBC (BNTAC). An Administrative Working Group meets regularly to enable Parks Managers and the BAC to liaise for decision-making purposes. In December 2021, the Queensland Government appointed the new K’gari (Fraser Island) World Heritage Advisory Committee with a membership of 15 members (5 Butchulla, 5 scientific/technical and 5 community members, in addition to an independent Chair) for a term of 3 years (State Party of Australia, 2023). The committees, supported by a secretariat through the Queensland Department of the Environment, Tourism, Science and Innovation and funding from the Australian Government, provide advice directly to both State and Federal ministers via a Communique which is published on the Department's website.
Integration into local, regional and national planning systems (including sea/landscape connectivity)
Mostly Effective
Management of the World Heritage site is guided by the Great Sandy Region Management Plan 1994 (currently under revision). The revised management plan is being developed under the Values-Based Management Framework (VBMF) that includes management effectiveness and evaluation (MEE) in line with IUCN MEE standards (Queensland Government 2023). Queensland Parks and Wildlife Service and Partnerships continues to work towards linking park key values and World Heritage values for the purposes of effective management, monitoring and reporting (IUCN Consultation, 2020a). The Butchulla Aboriginal Corporation (BAC) has developed a Strategic Business Plan 2020-30 to guide the organisation clarifying its vision, purpose and strategic priorities. The Butchulla Native Title Aboriginal Corporation has also developed a Strategic Plan 2023-28 for their organisation.
Boundaries
Highly Effective
Existing boundaries are operationally sufficient (World Heritage Committee, 2012) however the Queensland Government is considering proposals to include significant additional areas of the Great Sandy Region in an expanded World Heritage site (subject to a consent framework to be developed with Indigenous Traditional Owners) (IUCN Consultation, 2017).
Overlapping international designations
Mostly Effective
The World Heritage site partially overlaps with the Ramsar site Great Sandy Strait along the western shore of K'Gari, and the Great Sandy Biosphere Reserve.
The Ramsar site is managed by the Wetlands Team in the Queensland Department of the Environment, Tourism, Science and Innovation, who regularly communicates with focal points of the World Heritage site (State Party of Australia, 2023).
The World Heritage site management falls under the Great Sandy National Park Management Plan. Communication between the Great Sandy Biosphere Reserve and the World Heritage site focal point is occasional (State Party of Australia, 2023).
At an Australian Biosphere Conference with the theme “We are all connected” in 2019 the K'gari (Fraser Island) World Heritage Property was a feature of the conference which included key-note speaker from UNESCO’s Division of Ecological and Earth Sciences “Man and the Biosphere" (State Party of Australia, 2023).
Inter-governmental agreements are also in place for the parts of the Ramsar Wetland within the World Heritage area with China, Japan and the Republic of Korea (State Party of Australia, 2023).
Implementation of World Heritage Committee decisions and recommendations
Data Deficient
N/A
Climate action
Mostly Effective
The K'gari World Heritage Area Advisory Committee welcomed the development of the K’gari Climate Adaptation Plan (CAP) for K’gari and a Butchulla Climate Change Response Plan has also been developed. The plan was developed using an adapted methodology, based on the Australian Government’s Climate change toolkit for World Heritage property managers. The Butchulla-led project was delivered by Indigenous groups, government agencies and the NESP Climate Systems Hub.
Management plan and overall management system
Mostly Effective
The Queensland Parks and Wildlife Service and Partnerships is regarded as developing "best practice" for many aspects of protected areas management. However, there is no individual management plan for Fraser Island World Heritage Area. It falls under the Great Sandy National Park Management Plan which covers the Great Sandy Region National Park, of which the Island is a section, along with adjacent marine areas and some lands outside the protected area. There is an urgent need for a specific World Heritage focussed plan that addresses Outstanding Universal Value (OUV) and is focussed solely on the World Heritage site. Fortunately, a strategic plan for the World Heritage site is currently in development in partnership with the Butchulla people through the Butchulla Aboriginal Corporation (BAC) and the Butchulla Native Title Aboriginal Corporation, however it remains unknown when the plan will be available and implemented. Additional specific Island plans include Fraser Island Dingo Conservation and Risk Management Strategy and associated Implementation Plan (2013), a Landscape Weed Management Plan (Harvey, 2011) K’gari VBMF thematic Pest Strategy and Fire Management Strategy and a Disaster Management Plan (Sub-Plan to the Fraser Coast, Fraser Coast Regional Council, 2023), Climate adaptation planning (IUCN Consultation, 2020a), as well as Monitoring and Assessment Thematic Strategy and Cultural Heritage Thematic Strategy are underway (IUCN Consultation, 2020b). In addition, a VBMF Plan is in development for the K'gari (Fraser Island) section of the Great Sandy (IUCN Consultation, 2020b), including identification of significant OUV and Ramsar attributes, with a draft expected to be available by the end of 2025.
Law enforcement
Mostly Effective
There is an active compliance program operating on the island with a priority focus on visitor behaviour (commercial tour operators and recreational visitors) and dingo management through the FIDCRMS Implementation Plan (IUCN Consultation, 2020b). Additional Compliance and Education rangers were established in 2023, for implementation of Nature Conservation Act 1992, Recreational Area Management Act 2006 and Marine Parks Act 2004, and associated regulations.
Sustainable finance
Mostly Effective
Organisational changes within the Queensland Government make direct comparisons of funding over time difficult. The Queensland Department of the Environment, Tourism, Science and Innovation provides funding for day-to-day management of the National Park. The Australian Government provides $145,000 annually to support the Advisory Committee structure and fund secretariat services. It is estimated that the Australian Government contributes about 2% of funding, including for an Executive Officer, support for a World Heritage Advisory Committee and a 2019 Australian Heritage Grant to the Fraser Coast Council for waste management on the island (State Party of Australia, 2023). This is reflective of the low level of Australian Government financial support for some World Heritage properties relative to others in Australia. The advisory committee has recommended a user pays (visitor levy) system to be implemented to fund protection of OUV and Traditional Owner needs on the island. The Queensland Government has considered the option, and relevant legislative changes required for levy collection will need to be addressed (IUCN Consultation, 2020a; 2025).
Staff capacity, training and development
Mostly Effective
Staff capacity needs consistent assessment to respond to management demands of with increasing visitation. In 2023 K’gari staff restructure created additional focused management units, with additional positions. Queensland Parks and Wildlife Service and Partnerships staff have multiple training and development opportunities and continue to receive essential training in core skills requirements, including the use of firearms, fire and pest management, workplace health and safety, first aid, infrastructure management, communications, compliance and legislation (IUCN Consultation, 2017). Cultural heritage training is delivered to all QPWS&P staff who work on K’gari (Fraser Island) National Park by the Butchulla Aboriginal Corporation (IUCN Consultation, 2020a). Butchulla peoples are also employed as rangers and administrators. The property managers are also partnering with the Butchulla people at the community level and increasing the capacity of the Butchulla Land & Sea Rangers to manage the property through enhanced training programs (State Party of Australia, 2023).
Education and interpretation programmes
Mostly Effective
Visitors are able to access information on K'gari through a variety of media: web sites, social media, brochures, videos, maps, signage, ranger briefings and an app. A more coherent approach to interpretation with a focus on the islands history, access and values is required (Wardell-Johnson et al, 2015). Queensland Parks and Wildlife Service and Partnerships is developing new interpretive materials which can be downloaded from the Queensland Department of the Environment, Tourism, Science and Innovation’s website – the 12-page ‘Be dingo-safe!’ brochure being notable as well as the ‘Be dingo-safe! quick tips’ sheets, which are available in multiple languages. A K’gari (Fraser Island) app was developed by the University of the Sunshine Coast (USC) in partnership with the Butchulla Aboriginal Corporation (BAC) and launched in 2018. The app is a free guide for anyone planning a trip to the island and provides important information on what visitors need to know, including information on getting to the island and what to do when on the island. Since 2018, the BAC has been working with QPWS&P on Central Station Master Planning. The plans to upgrade the Central Station precinct and interpretative displays will enable the project’s partners to share Butchulla culture and lore. The project will also enable the Butchulla story and association with the World Heritage site to be delivered on Country. However, only minor upgrading and building stabilisation works have been implemented so far pending project management agreement (IUCN consultation, 2024). There is a need for an increase in visitor briefings on dingo-safety with a focus on current risks and risk areas on-island (Archer-Lean et al., 2017) with marked increases since Department enhanced wongari (dingo) management programme implementation since 2023. The K’gari World Heritage Discovery Centre in Kingfisher Bay was opened on 1 March 2021 by Cllr George Seymour, Mayor of Fraser Coast Regional Council. The Centre is based on four key themes:
⦁ Exceptional natural beauty (World Heritage List criterion vii)
⦁ Significant ongoing geological processes (World Heritage List criterion viii)
⦁ Significant ongoing biological processes (World Heritage List criterion ix)
⦁ Conservation of the island.
Tourism and visitation management
Some Concern
Visitor management covers: (i) pre-visit information; (ii) off-site orientation; (iii) on-site orientation; (iv) site interpretation; and (v) post-visit reinforcement (State Party of Australia, 2003). QPWS&P aims to manage K'gari (Fraser Island) at the Exceptional Level of Service for visitor management due to the significant number of visitors to this major tourism destination. Exceptional is the highest Levels of Service (LoS) benchmark used to set the desired management standards across all Queensland National Parks. The Sustainable Visitor Management and Capacity study released in 2023 indicates a strongly seasonal but steadily growing visitation level. Significant concerns exist in relation to visitor interaction with dingoes, impacts of camping on the coastal zone, illegal campfires (e.g. the starting source of the 2022 wildfire) and use impacts and development demands on the iconic key visitation sites on the island with effects on water quality and pollution. The Olympic Games scheduled to be held in Brisbane in 2032 will likely increase visitation to the island significantly and adequate preparation to manage this likely temporary but significant increase will be needed. There is a lack of monitoring and data on visitor patterns, quality of visitor experiences and environmental and social impacts.
Sustainable use
Data Deficient
The site is managed primarily under Queensland’s Nature Conservation Act 1992. Sustainable uses of the Island and adjacent waters include commercial tourism and recreation, recreational and commercial fishing (Queensland Fisheries Act 1994), community lifestyles, natural resource management and cultural heritage protection. The Queensland Parks and Wildlife Service and Partnerships, within the Department of the Environment, Tourism, Science and Innovation, implements the Values-Based Management Framework (VBMF) (Queensland Government, 2023) which is a IUCN compatible methodology for park management planning across all national parks in Queensland. The Department recently released a Sustainable Visitor Capacity and Management Study (2023) and report recommendations are being implemented through operational action plans and VBMF planning.
Monitoring
Some Concern
Key value health checks (part of a state-wide system instituted by QPWS&P) (Melzer et.al. 2019) are undertaken as a routine part of VBMF park management and to support revision of the Management Plan. WetCAT (DES 2022) monitoring has been undertaken in at least 22 wetlands (Melzer et al. 2024). The QPWS Monitoring and Research Strategy includes water monitoring recommendations and a collation of baseline data exists for any future monitoring to assess changes (IUCN Consultation, 2020b). A positive development is the Queensland Government funding of Butchulla Land and Sea Rangers, through the Queensland Indigenous Land and Sea Ranger Program. These rangers have started monitoring myrtle rust and water quality. The Butchulla Land and Sea Rangers’ work will be invaluable in supporting improved monitoring regimes (IUCN Consultation, 2020a). While the health check system used by QPWS&P provides good overall surveillance monitoring, more detailed monitoring of some species and attributes is lacking. Social monitoring including basic visitation data is lacking.
Research
Some Concern
Biennial Fraser Island Conferences were initiated by the community group, the Fraser Island Defenders Office (FIDO) in 2004. USC hosted a K’gari research symposium at the Fraser Coast campus in 2019 with the support of the BAC. The conferences enable networking of stakeholders and the dissemination of recent and relevant research. The K’gari Towards 2050 Research Symposium was hosted by the University of the Sunshine Coast in partnership with Butchulla Aboriginal Corporation (BAC) on 26 November 2021. In 2023, FIDO and the University of the Sunshine Coast combined their efforts to host the K'gari Land and Sea Country: djaa-ngarawinj Conference from 9-10 December 2023, with the support of the BAC and the Butchulla Native Title Aboriginal Corporation (BNTAC). The K’gari (Fraser Island) Research Archive is held by the University of the Sunshine Coast and brings together various collections of resources which contribute to research into K’gari (Fraser Island). The Archive is founded on a collection of material donated by John Sinclair AO, which underpinned his research in lobbying for environmental protection and World Heritage listing of the Island (https://libguides.usc.edu.au/fiacollection). The University of Queensland has long term flora and fauna monitoring projects and the University of Southern Queensland are collaboratively facilitating research into dingo genetics. The QPWS&P Monitoring and Assessment Strategy outlines previous research and identifies other research required for particular key values. QPWS&P Rangers and others have used QPWS&P data in peer reviewed publications (IUCN Consultation, 2020b).
There has been a considerable amount of research relating to the property published over the last four years (IUCN consultation, 2024). This is also likely to increase with a major, 7-year, research partnership announced between the ARC Centre of Excellence for Indigenous and Environmental Histories and Futures (CIEHF) and Butchulla Aboriginal Corporation. The CIEHF aim to generate a new direction in knowledge creation based on Aboriginal and Torres Strait Islander led approaches to managing Land and Sea Country. While there has been focussed research on some species with flow on to management action (dingoes, ground parrots, pest species, fire related plant ecosystems, glossy black cockatoos, black-breasted button quail), broader application of research to management is limited. Mechanisms for prioritising research needs and means to measure and record outputs of research relevant to management is required to be incorporated in the K'gari Monitoring and Research Strategy.
Effectiveness of management system and governance in addressing threats outside the site
Serious Concern
Threats originating outside the site include climate change, significant growth in human population, biosecurity concerns, an expansion of residential development and an increase in tourism and support industries in the Great Sandy Region. These issues are being addressed in management plans but very limited biosecurity control procedures (limited washdown system mechanisms, limited surveillance of threats in adjacent areas) are of concern.
Effectiveness of management system and governance in addressing threats inside the site
Some Concern
Increasing impacts from climate change, wildfire, invasive species and visitation-related pressures all indicate the challenge that these threats represent for management and governance. Increased management capacity and new approaches to management of these pressures will be required to effectively respond to the site-based consequences of drivers that are largely out of the control of site managers. The new QPWS&P VBMF is expected to evaluate management effectiveness on a regular basis (IUCN Consultation, 2017).
Protection and management is mostly effective. The Queensland Department of the Environment, Tourism, Science and Innovation, Queensland Parks and Wildlife Service and Partnerships (QPWS&P) provides strategic oversight and undertakes day to day management activities through a collaborative arrangement with the Butchulla Aboriginal Land and Sea Ranger Program. However, high levels of visitation and pressures from recreational use and impacts related to climate change, sea level rise, biosecurity and surrounding land use activities will require enhanced and systematic monitoring and increased management focus on World Heritage values to ensure conservation of the site’s values in the long-term. Climate adaptation planning is underway, supported by the Butchulla Aboriginal Corporation RNTBC (BAC), the Australian and Queensland governments but it is too early to assess the effectiveness of implementation of these plans.

Largest sand island in the world with spectacular beaches, cliffs and blowouts

Low Concern
Trend
Stable
The World Heritage site is still the largest sand island in the world and has spectacular beaches, cliffs and blowouts. Colonisation of sand blows is largely a natural process fundamental to on-going geological processes (IUCN Consultation, 2017). A possible threat in this area is the potential for accelerated coastal erosion on the east coast under rising sea-levels and disruption of dunes in the western part of the island as a result of increased intensity of fires. No obvious changes have occurred yet; however, ongoing monitoring is required (IUCN Consultation, 2020a).

Tall rainforest growing on high coastal sand dunes

Low Concern
Trend
Stable
Rainforest on K’gari includes Araucarian vine forest on parabolic high dunes and notophyll vine forest on parabolic high dunes – both of which are Of Concern Regional Ecosystems. Recent research has evaluated the long-term succession of wet-sclerophyll forest (Syncarpia hillii–Lophostemon confertus) within the FIWHA (Krishnan et al., 2019). The wet-sclerophyll species Syncarpia hillii is endemic to K'gari and the nearby Cooloola sandmass. Approximately 10,000 hectares remain with an 'of concern' biodiversity status (Queensland Government, 2019). Increased efforts to actively manage and conserve the wet-sclerophyll forest may be required to prevent a transition to rainforest (Krishnan et al., 2019). Conversely, intense wildfires burning into rainforest areas is a growing risk. Changes in fire regime under predicted climate change and recent observed fires (climate change and/or fire management related) indicates increase risk of dune destabilisation from this source, because of the destabilisation of vegetation after the fire(s). Similarly, high intensity burns penetrating into rainforest areas may pose threats to the long-term viability of rainforest on K’gari (Fraser Island), although only a small area (<1%) of the rainforest was impacted in the 2020 wildfire event (Meiklejohn et al., 2022). Myrtle rust is established all over the island and has the potential to impact on Myrtaceae species which in turn may affect rainforest dynamics. The 2020 bushfire event resulted in significant impacts on a range of different ecosystems, with widespread epicormic and seedling regeneration (for myrtaceous spp) creating ideal conditions for spread and impact of myrtle rust. Myrtle rust is being monitored by the Queensland Government and the Butchulla Land and Sea Rangers. The rainforests of K’gari (Fraser Island) contain a wide range of plant foods and resources that were fundamental to traditional Butchulla residential occupation of the island (IUCN Consultation, 2020a).

Largest unconfined aquifer and perched freshwater dune lakes

Low Concern
Trend
Stable
A program of groundwater and window lake monitoring recently commenced (2024) to increase knowledge about K’gari’s aquifers (IUCN consultation, 2024). The program is being led by the Burnett Mary Regional Group in partnership with the BAC, DESI, CSIRO and the University of Adelaide (John Tibby). Evidence from previous work suggests that the lakes are being well managed. Most impacts appear to be aesthetic and relate to localised erosion and infilling at key visitor access points (IUCN Consultation, 2017). Further research is required in respect to potential impacts of climate change and increased camping activity. Further research is also required to enhance understanding of the relationship between annual rainfall and groundwater table levels in the dune field (IUCN Consultation, 2020a).

Most complete age sequence of coastal dune systems

Low Concern
Trend
Stable
All major changes in dunes are natural, with only minor changes due to localised erosion. The University of Queensland has recently undertaken research that has demonstrated that the oldest sands on the island exceed 800,000 years (Ellerton et al 2020, 2022; Patton, 2022; Patton et al, 2019, 2022; Rittenour et al., 2024). These sands occur in the lower parts of the cliffs on the eastern side of the island (and may also occur in cliffs on the western side). These sites are sensitive to coastal erosion, especially under rising sea-level scenarios. However, it is likely that other old sands would be exposed if coastal retreat occurred (IUCN Consultation, 2020a). Observations from east coast cliff sections and Ground Penetrating Radar (GPR) studies confirm the presence of the giant podzols. These buried soils are largely robust to changes at the surface but almost impossible to monitor.

Unique process of soil formation with deepest podzols in the world

Low Concern
Trend
Stable
The underlying natural processes of soil formation are continuing at the World Heritage site scale (IUCN Consultation, 2017).

Unique flora and fauna demonstrating ongoing succession, speciation and radiation

Low Concern
Trend
Deteriorating
There is limited information available from monitoring the status of threatened species on the island. Four species of "acid frogs" occur on the island: Near Threatened Cooloola sedgefrog (Litoria cooloolensis), Vulnerable wallum rocket frog (L. freycineti), Vulnerable wallum sedgefrog (L. oblongburensis) and Vulnerable wallum froglet (Crinia tinnula) (Meyer et al., 2006). The Oxleyan pygmy perch (Nannoperca oxleyana) and honey blue eye (Pseudomugil mellis) are both listed as EN. The ornate rainbowfish (Rhadinocentrus ornatus) is also present in the wallum wetlands. A post-fire assessment of these species found that "the abundance of native wallum fish species (N. oxleyana, P. mellis and R. ornatus) varied with fire and the presence of introduced species. These species were more abundant in areas that were not burnt in the 2019-2020 fires when compared with areas that were. In contrast, introduced fish species, including eastern gambusia and platy, were found to be more abundant in fire affected waterbodies. However, at sites where a localised extinction was highly likely (e.g., Deep Lake), connectivity in hydrology seemed to be the most important factor influencing fish population dynamics. The complex interactions between hydrology, fire and species suggest that there are numerous factors that directly and indirectly impact the distribution and abundance of wallum fish species. While wallum frog species generally did not show such pronounced patterns in mean abundance of frequency of occupancy as fish, Wallum froglets were found to increase in abundance with fire severity, suggesting a possible benefit of burning in regard to habitat reinvigoration. As with fish, wetland hydrology also served an important role in wallum frog population dynamics" (Collett et al. 2023)

A camera trap study of the Vulnerable Black-breasted button quail (Turnix melanogaster) with post-fire monitoring of known sites has been undertaken (Webster et al. 2022). The species favours littoral forest vegetation and are found along the east coast of K’gari and the adjacent Cooloola area. Foreshore habitat including the littoral forest from the central to northern section of the island was badly impacted by the 2020 bushfire. The report concludes that "the exact impact that fire has on Black-breasted Button-quail populations is unknown and requires further research."

Overall biosecurity is a major concern, particularly from myrtle rust. There is a need for baseline data to be compiled on main taxa and there are other threats such as Phytophthora which could be devastating if established on the island. The major vegetation ecotones are largely stable; however, intense fires have affected K'gari (Fraser Island) over the last decade. Since inscription, a unique ecosystem for the sub-tropics has been recognised (patterned fens). These fens are largely confined to K'gari (Fraser Island) and the adjacent mainland (Cooloola) with the best examples at Moon Point on K'gari (Fraser Island). Private land holdings close to Moon Point and drainage associated with the road to Moon Point, partly to service these properties, pose threats to this ecosystem (IUCN Consultation, 2020a).
Assessment of the current state and trend of World Heritage values
Deteriorating
Since inscription in 1992 the state of World Heritage values remains relatively good and significant human and financial resources are being directed to the management of the threats to these values. However the extent of many of the threats is increasing, with many being exacerbated by climate change. This can be expected to flow through to impact on values in the future unless these threats can be more effectively addressed. Increased incorporation of cultural heritage values (not covered in this assessment) is being addressed in current planning and management.
Assessment of the current state and trend of other important biodiversity values
Data Deficient
Data Deficient
This review cannot adequately assess the trend of the many biodiversity values on the island because of a lack of relevant monitoring data.

Additional information

Outdoor recreation and tourism
With its clean beaches and pristine lakes the island is an important source of recreation for visitors and the small community living on the island. The scenic benefits for tourism of giant dunes, towering rainforest and coloured cliffs are very high. Despite high visitation, there are still “wilderness” values on the island given lack of facilities, which in turn increases human pollution by hikers and swimmers seeking a “wilderness” experience (Hadwin and Arthington, 2003).
Factors negatively affecting provision of this benefit
Overexploitation
Impact level - Moderate
Trend - Continuing
The intensity of use during peak visitation periods at key sites and travel routes may impact on the quality of the visitor experience. More data needed on visitor impacts and quality of visitor experience.
History and tradition,
Sacred natural sites or landscapes
K’gari (Fraser Island) is of great cultural and spiritual significance and home to some 450-500 recorded Indigenous archaeological sites (DERM, 2012). The Butchulla people are the Indigenous Traditional Owners and have continuing connection to country. The 2014 and 2019 Native Title Determinations have major implications for involvement of Butchulla people. Negotiations are underway to formalise co-stewardship arrangements between the Queensland Government and the Butchulla Aboriginal Corporation in relation to ongoing management of the World Heritage area.

The whole island contains tangible (archaeological) evidence for the past occupation of K’gari by the ancestors of Butchulla Traditional Owners, including camping places (e.g. middens), stone quarries (e.g. headlands), burials (isolated graves and cemeteries), and ceremonial places (McNiven et al., 2002). Tangible evidence of long-term Butchulla use of, and association with, marine resources is amply demonstrated by hundreds of shell middens across K’gari, which contain shell and bones of fish, turtle, and dugong. There are many scarred trees and other physical remains of past human occupation. Patterned fens are particularly significant to Butchulla women.

K’gari (Fraser Island) is also a cultural landscape of both tangible and intangible heritage in the form of story places, resource areas, gendered places and other sites and locales of significance. All such places are of value to Butchulla people as an assertion of ongoing ancestral presence, traditional ownership, and identity. These places are protected under the Aboriginal Cultural Heritage Act 2003 [QLD].
Factors negatively affecting provision of this benefit
Overexploitation
Impact level - Moderate
Trend - Continuing
The current patterns and levels of visitor use may conflict with Indigenous cultural values and aspirations for the future. A number of planning processes involving and led by the Butchulla Aboriginal Corporation are underway and will resolve potential conflicts with visitor management and conservation of cultural heritage values.
Access to drinking water
With the largest aquifer on a sand island in the world and half of the world’s perched dune lakes, the site, even if the water is not used apart from local and tourist use, is an important reservoir of fresh water.
Factors negatively affecting provision of this benefit
Climate change
Impact level - Moderate
Trend - Increasing
Climate change may impact on long-term hydrological processes operating at the World Heritage site scale.
Provision of jobs,
Tourism-related income
The Island is the source of many jobs both directly and indirectly through associated industries (hence the conflict between tourism and nature conservation). In 2002 FIDO commissioned an independent study to assess the regional benefits of tourism. The study showed that the annual value of K’gari (Fraser Island) tourism to the Queensland economy was then estimated to be in the order of $277 million generating up to 2,880 jobs (Kleinhardt, 2002).

In 2022, the Australian Government commissioned a Deloitte report on The Economic and Social Value of Australia’s World Heritage properties. The report includes data on the value added to the Australian economy by each world heritage property in terms of $ Financial contribution and jobs (FTEs) across the country. The report was finalised in 2023 (and includes a K’gari case study) but is still pending release by the Australian Government.

Factors negatively affecting provision of this benefit
Climate change
Impact level - Moderate
Trend - Increasing
Overexploitation
Impact level - Moderate
Trend - Continuing
K'gari (Fraser Island) provides major local and international benefits for nature conservation, tourism (with its scenery and wilderness values) and recreation. The island has the potential to be a living laboratory to increase scientific knowledge. It is also an important source of income, providing jobs and revenue to people living within and outside the World Heritage site though opportunities to enhance benefits for the Butchulla people require further focus. Its large aquifer and perched dune lakes provide an important fresh water reserve. Many aboriginal artefacts and sites occur on the island, and the Indigenous Traditional Owners are becoming increasingly involved in management of the World Heritage site. The 2014 and 2019 Native Title Determinations have major implications for involvement of Butchulla people in the management of the World Heritage site.
Organization Brief description of Active Projects Website
1 Fraser Island Natural Integrity Alliance Acts as an umbrella organisation for government and non-government organisations to work collaboratively to protect and restore the natural integrity of Fraser Island. Projects have included: weed management, pest management – cane toad and Jamella (Pandanus leafhopper) workshops, restoration of the Eurong nursery, revegetation, education and awareness initiatives – website, signage and quarterly Newsletter.
https://finia.org.au/
2 Fraser Island Defenders Organisation Eurong and Happy Valley Bush Regeneration Project (removal of invasive species around inhabited areas) ) and post-fire Pandanus propagation and revegetation along the east coast of K’gari (and other projects, see website).
www.fido.org.au
3 Sandy Cape Lighthouse Conservation Volunteers Pest management, care and maintenance of Sandy Cape precinct, Marine turtle conservation program (working with DETSI).
4 ECOllaboration Assist in ongoing fire rehabilitation project works along the eastern shores of K’gari including seed collection, nursery work and planting focussing on the restoration of the areas most affected.
https://ecollaboration.org.au/project/voluntourism-kgari-graser-island/

References

References
1
Allen, B., Higginbottom, K., Bracks, J., Davies, N., & Baxter, G. (2015). Balancing dingo conservation with human safety on Fraser Island: the numerical and demographic effects of humane destruction of dingoes. Australasian Journal of Environmental Management, 22(2), pp.197-215.
2
Appleby, R. G., & Jones, D. (2011). Analysis of a Preliminary Dingo Capture-Mark-Recapture Experiment on Fraser Island Conducted by the Queensland Parks and Wildlife Service. Brisbane, Australia: Environmental Futures Centre, Griffith University.
3
Archer-Lean, C., Wardell-Johnson, A., Carter, J., Khattab, U. and Mahony, I. (2017). The Iconic Dingoes of K'gari-Fraser Island-communicating for their future: Report prepared for the Fraser Island Dingo Research Program, Queensland Department of Science, Information Technology, Innovation and the Arts, 2016.
4
Arthington, A. H., & Hadwen, W. L. (2003). The significance and management implications of perched dune lakes as swimming and recreation sites on Fraser Island, Australia. Journal of Tourism Studies, 14(2), 35.
5
Arthington, A. H., Miller, G. J., & Outridge, P. M. (1989). Water quality, phosphorus budgets and management of dune lakes used for recreation in Queensland (Australia). Water Science and Technology, 21(2), pp.111-118.
6
Behrendorff, L., Leung, L.K.P., McKinnon, A., Hanger, J., Belonje, G., Tapply, J., Jones, D. and Allen, B.L. (2016). Insects for breakfast and whales for dinner: the diet and body condition of dingoes on Fraser Island (K’gari). Scientific Reports, 6(1), pp.1-12.
7
Carter, R.W., Tindale, N., Brooks, P. and Sullivan, D. (2015). Impact of camping on ground and beach flow water quality on the eastern beach of K'gari-Fraser Island: a preliminary study. Australasian Journal of Environmental Management, 22(2), pp.216-232.
8
Clutton‐Brock, J., Kitchener, A. C., & Lynch, J. M. (1994). Changes in the skull morphology of the Arctic wolf, Canis lupus arctos, during the twentieth century. Journal of Zoology, 233(1), pp.19-36.
9
Collett S, Carpenter-Bundhoo L, Ford E, Butchulla Aboriginal Corporation, Behrendorff L, Blake J & Kennard M (2023). Post-fire monitoring of wetlands, threatened species and threatened ecological communities on K’gari (Fraser Island) and Great Sandy Strait Ramsar site. Burnett Mary Regional Group, Bargara
10
Conroy, G. (2016a). A baseline genetic analysis of the K’gari-Fraser Island dingo population. Sippy Downs, Queensland: University of the Sunshine Coast.
11
Conroy, G. (2016b). A Pilot Dingo Scat DNA Mark Recapture Program to Estimate Population Size. Sippy Downs, Queensland: University of the Sunshine Coast.
12
Coutinho, T. A., Wingfield, M. J.,  Alfenas, A. C. and Crous, P. W. (1998). Eucalyptus rust: a disease with the potential for serious international implications. Plant Disease, 82, pp.819-25.
13
DERM (Department of Environment and Resource Management) (2012). Australia’s World Heritage Places: Fraser Island Information Sheet. http://www.environment.gov.au/heritage/education/pubs/facts…. Downloaded September 2012.
14
DES. (2019). Values Based Management Framework. [online] Department of Environment and Science, Queensland Government. Available at: https://parks.des.qld.gov.au/management/plans-strategies/va… [Accessed 1 December 2020].
15
Department of Science, Information Technology, Innovation and the Arts [DSITIA] (2012). Land cover change in Queensland 2009–10: a Statewide Landcover and Trees Study (SLATS) report, 2012. Brisbane, Australia: Department Science, Information Technology, Innovation and the Arts.
16
Department of the Environment, Science and Innovation, Queensland (2022). Queensland Parks and Wildlife Service Planned Burn Guidelines: Southeast Queensland bioregion of Queensland. Queensland Parks and Wildlife Service. Department of Environment, Science and Innovation, Queensland Government.
17
Department of the Environment, Science and Innovation, Queensland (2022). WetCAT: A condition assessment tool for measuring event recovery and rehabilitation in palustrine and lacustrine wetlands in Queensland. Version 1.0, June 2022, Queensland Wetlands Program, Queensland Government, Brisbane. https://wetlandinfo.des.qld.gov.au/resources/static/pdf/ass…
18
Earthcheck (2022). K'gari (Fraser Island) Sustainable Visitor Capacity and Management Study. Recommendations November 2022. Earthcheck Pty Ltd. Available at: https://parks.desi.qld.gov.au/__data/assets/pdf_file/0027/3…
19
Earthcheck (2024) K'gari (Fraser Island) Sustainable Visitor Capacity Management Study - Recommendations November 2022. Published by Queensland Parks and Wildlife Service, Department of Environment, Science and Innovation
20
Ellerton, D., Rittenour, T., Shulmeister, J., Gontz, A., Welsh, K.J., and Patton, N. (2020). An 800 kyr record of dune emplacement in relationship to high sea level forcing, Cooloola Sand Mass, Queensland, Australia. Geomorphology, Volume 354, 2020, 106999, ISSN 0169-555X, https://doi.org/10.1016/j.geomorph.2019.106999.
21
Ellerton, D., Rittenour, T.M., Shulmeister, J. et al.  (2022). Fraser Island (K'gari) and initiation of the Great Barrier Reef linked by Middle Pleistocene sea-level change. Nat. Geosci. 15, 1017–1026 (2022). https://doi.org/10.1038/s41561-022-01062-6
22
GHD (Gutteridge, Haskins and Davey) (2002). Fraser Island Sustainable Transport Management Study — Transport Strategies Working Paper — Report 41-10875. Brisbane, Australia: GHD.
23
Gontz, A. M., Moss, P. T., Sloss, C. R., Petherick, L. M., McCallum, A., & Shapland, F. (2015). Understanding past climate variation and environmental change for the future of an iconic landscape–K'gari Fraser Island, Queensland, Australia. Australasian Journal of Environmental Management, 22(2), pp.105-123.
24
Harvey, J.P. (2011). Landscape Weed Management Plan for Fraser Island.Invasive plant species management plan developed for the Fraser Island Natural Integrity Alliance (FINIA). Sippy Downs, Queensland: University of the Sunshine Coast.
 
25
Hockings, M. and Twyford, K. (1997) Assessment and management of beach camping impacts within Fraser Island World Heritage Area, South-East Queensland. Australian Journal of Environmental Management 4(1): 26-39.
26
IUCN Consultation (2020a). IUCN World Heritage Confidential Consultation: Respondent 1. Fraser Island, Australia.
27
IUCN Consultation (2020b). IUCN World Heritage Confidential Consultation: Respondent 2. Fraser Island, Australia.
28
IUCN Consultation (2024). IUCN World Heritage Confidential Consultation: K'gari (Fraser Island), Australia.
29
K'gari (Fraser Island) World Heritage Advisory Committee (2023). Communiqué 8 November 2023. Available at: https://parks.des.qld.gov.au/__data/assets/pdf_file/0032/33…
30
Kleinhardt (Kleinhardt –FGT Coorperate Advisors) (2002). Tourism & Recreation Values of the Daintree and Fraser Island. Prepared for the Australian Tropical Research Foundation (AUSTROP). Unpublished report, Cairns. 58 pp.
31
Krishnan, V., Robinson, N., Firn, J., Applegate, G., Herbohn, J., & Schmidt, S. (2019). Without management interventions, endemic wet‐sclerophyll forest is transitioning to rainforest in World Heritage listed K’gari (Fraser Island), Australia. Ecology and evolution, 9(3), pp.1378-1393.
32
Marie, J. (2024). Calls for action after invasive tilapia fish found on K'Gari, off Queensland coast. ABC News. Published online 10 October 2024. Available at: https://www.abc.net.au/news/2024-10-10/pest-fish-threatens-…
33
McNiven, I.J., Thomas, I. and Zoppi, U. (2002). Fraser Island Archaeological Project: Background, aims and preliminary results of excavations at Waddy Point 1 Rockshelter. Queensland Archaeological Research, 13, pp.1-20.
34
Meiklejohn A.R., Melzer, R.I., Hines H.B., Laidlaw M.J., Toyne, M., McPherson K., Behrendorff, L., MacDonald S. (2023) Post-fire Assessment Report – Natural Values: 2020 Duling bushfire, K’gari (Fraser Island), Great Sandy National Park, South East Queensland Bioregion with addendum. Brisbane: Department of Environment and Science, Queensland Government.
35
Melzer R., Meiklejohn A.R., Carpenter-Bundhoo L., Hines H.B., McPherson K., Behrendorff L. and Booth R. (2024) Ecological assessment of northern lakes, post-2020 Duling bushfire, K'gari (Fraser Island), Great Sandy National Park. Brisbane: Department of Environment, Science and Innovation, Queensland Government. https://parks.desi.qld.gov.au/__data/assets/pdf_file/0022/3…
36
Melzer, R., Ezzy, L. and Hines, H., B. (2019) ‘Health checks: A simple tool for assessing the condition of values and effectiveness of reserve management’, Parks, 25(2). Available at: https://doi.org/10.2305/IUCN.CH.2019.PARKS-25-2RM.en.
37
Meyer, E., Hero, J-M., Shoo, L. and Lewis, B. (2006). National recovery plan for the wallum sedgefrog and other wallum-dependent frog species. Report to Department of the Environment and Water Resources, Canberra. [online] Brisbane, Australia: Queensland Parks and Wildlife Service. Available at: https://www.environment.gov.au/biodiversity/threatened/reco… [Accessed 30 November 2020].
38
National Native Title Tribunal (2019). Butchulla People Land and Sea Claim #2. [online] Available at: http://www.nntt.gov.au/searchRegApps/NativeTitleClaims/Page… [Accessed 1 December 2020].
39
National Native Title Tribunal. (2014). Butchulla People #2. [online] Available at: http://www.nntt.gov.au/searchRegApps/NativeTitleRegisters/P… [Accessed 1 December 2020]. 
40
Neldner V.J. and Ngugi M.R. (2021). Vegetation recovery after the 2019 and 2020 bushfires on K’gari (Fraser Island), Great Sandy National Park, Southeast Queensland Bioregion. Brisbane: Queensland Herbarium, Department of the Environment, Science and Innovation, Queensland Government.
41
Patton, N. R., Ellerton, D., & Shulmeister, J. (2019). High-resolution remapping of the coastal dune fields of south east Queensland, Australia: a morphometric approach. Journal of Maps, 15(2), 578–589. https://doi.org/10.1080/17445647.2019.1642246
42
Patton, N.R., (2022). Landscape evolution of the southeast Queensland dune fields. Doctoral dissertation, University of Canterbury, New Zealand.
43
Patton, N.R., Shulmeister, J., Rittenour, T.M., Almond, P., Ellerton, D. and Santini, T. (2022). Using calibrated surface roughness dating to estimate coastal dune ages at K'gari (Fraser Island) and the Cooloola Sand Mass, Australia. Earth Surface Processes and Landforms, 47(10), pp.2455-2470.
44
Queensland Government (2019). Regional ecosystem details for 12.2.4. [online] Available at: <https://apps.des.qld.gov.au/regional-ecosystems/details/?re…;. [Accessed 18 June 2020].
45
Queensland Government (2023) Values-Based Management Framework, Values-Based Management Framework. Available at: https://parks.desi.qld.gov.au/management/plans-strategies/v… (Accessed: 11 April 2025).
46
Rittenour, T.M., Patton, N.R., Ellerton, D., Gontz, A., Hesp, P.A., Santini, T., Miot da Silva, G., Forman, S., Bowyer, H., Kelly, J.T. and McCallum, A. (2024). Chronology and evolution of the world's largest sand island: K'gari (Fraser Island), South East Queensland, Australia. Quaternary Science Reviews. http://doi.org/10.1016/j.quascirev.2024.108529
47
Schlacher, T.A., Richardson, D. and McLean, I. (2008) Impacts of off-road vehicles (ORVs) on Macrobenthic assemblages on sandy beaches. Environmental Management 41, pp.878–892.
48
State Party of Australia (1991). Nomination of Fraser Island and the Great Sandy Region by the Government of Australia for inclusion in the World Heritage List. Canberra, Australia: Department of the Arts, Sport, the Environment, Tourism and Territories on behalf of the Government of Australia. 
49
State Party of Australia (2003). Periodic Report Cycle 1 Section II: Fraser Island (Australia). [online] Paris, France: UNESCO. Available at: http://whc.unesco.org/en/list/630/documents/ [Accessed 30 November 2020].
50
State Party of Australia (2023). Periodic Reporting Cycle 3, Section II: K'gari (Fraser Island), Australia. [online] Available at: https://whc.unesco.org/document/217051 [Accessed on 25 February 2025]
51
Stewart, P. L. C., & Moss, P. T. (2015). Fire patterns of South Eastern Queensland in a global context: A review. In In: Keane, Robert E.; Jolly, Matt; Parsons, Russell; Riley, Karin. Proceedings of the large wildland fires conference; May 19-23, 2014; Missoula, MT. Proc. RMRS-P-73. Fort Collins, CO: US Department of Agriculture, Forest Service, Rocky Mountain Research Station. p. 227-236.
52
Stewart, P.L.C., Moss, P.T. and Farrell, R. (2020). Land Change Analysis of Moon Point Vegetation on Fraser Island, East Coast, Queensland, Australia. International Journal of Ecology and Environmental Sciences, 46(1), pp.25-39.
53
Stewart, P.L.C.F., Moss, P.T., Stewart, D.A. and Farrell, R. (2017). Fire regimes and invasive species: a changing landscape. International Journal of Ecology and Development, 32(1), pp.108-122.
54
UNESCO (2001). Report on the State of Conservation of Fraser Island, Australia. State of Conservation Information System of the World Heritage Centre. [online] Paris, France: UNESCO World Heritage Centre. Available at: <http://whc.unesco.org/en/soc/2493>; [Accessed 30 November 2020].
55
Waldron, R. P. (2023). Impacts of 4WD vehicles on K’gari roads: towards a sustainable transport solution. Doctoral dissertation, University of the Sunshine Coast, Queensland
56
Waldron, R. P., & McCallum, A. B. (2021). A review of road infrastructure development and contemporary degradation on K’gari-Fraser Island. Australasian Journal of Environmental Management, 28(2), 104–125. https://doi.org/10.1080/14486563.2021.1918586
57
Wardell-Johnson, G., Schoeman, D., Schlacher, T., Wardell-Johnson, A., Weston, M.A., Shimizu, Y. and Conroy, G. (2015). Re-framing values for a World Heritage future: what type of icon will K'gari-Fraser Island become?. Australasian Journal of Environmental Management, 22(2), pp.124-148. http://dx.doi.org/10.1080/14486563.2014.985267
58
Webster, P.T., Shimomura, R., Rush, E.R., Leung, L.K.P. and Murray, P.J. (2022). Distribution of Black-breasted Button-quail Turnix melanogaster in the Great Sandy Region, Queensland and associations with vegetation communities. Emu-Austral Ornithology, 122(1), pp.71-76.
59
Webster, P.T., Shimomura, R., Rush, E.R., Leung, L.K.P. and Murray, P.J. (2022). Distribution of Black-breasted Button-quail Turnix melanogaster in the Great Sandy Region, Queensland and associations with vegetation communities. Emu-Austral Ornithology, 122(1), pp.71-76.
60
Woodall, P. F., Pavlov, P., & Twyford, K. L. (1996). Dingoes in Queensland, Australia: skull dimensions and the identity of wild canids. Wildlife Research, 23(5), pp.581-587.
61
World Heritage Committee (2012). Decision: 36 COM 8E Fraser Island Statement of Outstanding Universal Value (Australia). In: Decisions Adopted by the World Heritage Committee at its 36th Session (Saint-Petersburg, 2012). [online] Paris, France: UNESCO World Heritage Centre. Available at: <http://whc.unesco.org/en/list/630/documents/>; [Accessed 30 November 2020].

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