To: Director Conservation Incentives and Design Section Department of Sustainability, Environment, Water, Population and Communities GPO Box 787, Canberra ACT 2601 Fax: 02 6274 1332 wildlife.corridors@environment.gov.au Date: 3 April 2012 Re: Draft National Wildlife Corridors Plan The Wet Tropics Management Authority commends the National Wildlife Corridors Plan Advisory Group for recognising the national importance of ecological and evolutionary connectivity across the Australian landscape. The Wet Tropics has a long and vital history of community conservation and scientific research to enhance habitat and ecosystem connectivity across the region. These efforts have been complementary to the listing of the Wet Tropics of Queensland World Heritage Area and the establishment of many national parks and nature refuges in the bioregion. The Australian and Queensland governments have consistently supported the management of these protected areas. They have also supported planning and community conservation works to prevent or offset further ecological fragmentation from infrastructure and other development. The Authority has several concerns with the draft National Wildlife Corridors Plan. These concerns are summarised briefly below and addressed in more detail later in the submission. The most serious concern is that the Wet Tropics region, including the World Heritage Area, has been excluded from the nominated priority corridors. The Wet Tropics World Heritage Area has been internationally recognised for its rich biodiversity and evolutionary significance. Its biodiversity has been identified as particularly at risk from the impacts of climate change. The Wet Tropics bioregion fits all the criteria for evolutionary connectivity across multiple ecological communities, as specified in the draft plan and supporting documents. The concept for landscape connectivity in the Wet Tropics is well developed and backed by a strong body of scientific research, including benefits for climate change adaptation. The Wet Tropics community has welldeveloped capacity, expertise and experience in landscape conservation and rehabilitation. Whilst the Authority supports the concept of national corridors in principle, it questions the cost-effectiveness and achievability of the nominated corridors. The draft National Wildlife Corridor Plan lacks detail about the proposed corridors – how the concepts would be implemented, how much they would cost and what are the measures for successful completion. The Authority believes that more efficient, practical and feasible outcomes can be achieved through smaller, but often equally significant, corridor concepts such as that proposed for the Wet Tropics. Such regional connectivity may later link to form broader national corridors. The Authority questions the process and criteria by which the priority corridors were identified and the lack of consultation before publication of the draft. The draft plan claims that these corridors are the only existing concepts which have been developed, but there seems to have been little chance for others to present existing proposals or concepts to the Australian Government. The Authority is concerned that these priority corridors, as listed, will be used to direct funding to certain areas and away from other important areas like the Wet Tropics. The draft plan mentions a desire to fund the National Wildlife Corridors through the Biodiversity Fund, but there is little information about how the Biodiversity Fund criteria might allow for this in future and how it would affect other bids to the Fund. Having much experience in fostering community conservation, the Authority questions the practicality and benefit of any further legislation for connectivity and would argue that the use of further incentives would be more productive in promoting landholder participation and community involvement in creating connectivity. A copy of the Authority’s Biodiversity Fund bid is attached. The bid was made in collaboration with the Queensland Office of Climate Change, Terrain Natural Resource Management, Far North Queensland Regional Organisation of Councils, Queensland Parks and Wildlife Service, and numerous community and conservation groups involved in forest restoration. The bid does not cover all the connectivity requirements and priorities in the Wet Tropics, but reflects the criteria of the Biodiversity Fund and the capacity of the community to achieve outcomes over the next five years. For instance, the bid focuses largely on on-ground conservation works and does not include other options such as land acquisition and potentially large works on individual private lands where no agreements have been reached. A detailed submission is attached which emphasises the importance of connectivity in the Wet Tropics and the case for its inclusion in a national wildlife corridor plan. I trust that these comments are useful and would welcome the opportunity to discuss them during the consultation process. Yours sincerely Andrew Maclean Executive Director Why the Wet Tropics meets the criteria for a national corridor The values of the Wet Tropics The Wet Tropics is renowned for scenic panoramas of its rainforest canopy from mountain lookouts, rivers that carve through rugged gorges and cascade into freshwater swimming holes, giant trees and ferns from ancient eras and curiosities from the animal kingdom. It has Australia’s greatest diversity of animals and plants within an area of just 0.26% of the continent. Many plant and animal species in the Wet Tropics are found nowhere else in the world. The diverse range of vegetation communities are habitat to numerous rare and threatened species. The Wet Topics has the oldest continuously surviving tropical rainforests on earth. They are a living museum of how land plants have evolved since the break up of Gondwana 40 million years ago, from ancient ferns, conifers and cycads to the more highly evolved flowering plants. The Wet Tropics is also a living record of the evolutionary history of animals – being home to some species that have changed little since ancient times such as the musky rat-kangaroo and the chowchilla. The richness of Wet Tropics biodiversity is well illustrated in the table below. Wildlife Butterflies Reptiles Birds Freshwater fish Mammals Frogs Ferns Orchids Cycads Percent of Australia’s species 60 20 40 42 35 29 40 30 21 The criteria for national corridors The draft National Wildlife Corridor Plan lists the aims of the plan (section 1.3), a range of guiding principles for wildlife corridor design and implementation (section 1.4) and foundation stones (section 1.8), before going on to list a range of existing and prospective national corridors. There do not seem to be any specific criteria in the draft plan for selecting the corridors mentioned. However, in one of the supporting documents provided, Whitten et al (2011) lists a set of operational criteria to define these National Wildlife Corridor initiatives. The Authority believes that the Wet Tropics corridor proposals fit these criteria admirably. The operational definition (Whitten et al 2011) is quoted below. Operational definition ‘Corridor’ and ‘connectivity conservation’ are used in multiple ways across multiple scales. In this report the term ‘corridor’ or ‘large-scale corridor’ is being used as defined for evolutionary connectivity (Worboys et al 2010). Evolutionary connectivity requires habitat and connectivity on a scale sufficient to permit gene exchange and range expansion, and inclusive of scales necessary to support trophic relationships, disturbance processes and hydro-ecological flows. Our resultant working definition of Australian wildlife corridor initiatives is: 1. Scale: sufficient to deliver evolutionary connectivity across multiple ecological communities, and in most cases, consideration of opportunities to manage climate connectivity 2. Scope – jurisdictional and tenure: typically achieving evolutionary connectivity will involve multiple jurisdictions at the local, natural resource management region, state and occasionally national or continental level 3. Scope – partnerships: effective connectivity management will require collaborations across multiple forms of tenure including public, private, Indigenous and other tenure arrangements. Effective collaborations are likely to involve organisations that can best engage and leverage values across these tenures including governments, regional NRM groups, non-government organisations (NGOs), businesses and others (such as statutory authorities) 4. Institutional development: our emphasis will be on those corridor initiatives that have been formally identified and which are moving towards a formalised structure (though not necessarily with formalised governance or widespread implementation). Whitten et al (2011) also quotes Worboys et al (2010) to show the relationship between type of connectivity and the scale of the corridor. The Authority notes that Worboys & Pulsford (2011), which contains a similar set of national corridors, did include a Queensland eastern ranges corridor with the Wet Tropics at the northern end. The Queensland section of the eastern ranges corridor also appears in another supporting document commissioned by SEWPaC (Parris et al 2011) which contains an overview of key socio-economic factors, principles and guidelines in wildlife corridor planning and implementation. However, the eastern ranges corridor was not in included in the draft National Wildlife Corridors Plan. Why the Wet Tropics fits the criteria for a national corridor The Authority argues that the Wet Tropics community already has a thriving culture of rehabilitation and conservation for connectivity across the region and that the current programs and future proposals for connectivity across the bioregion fit all the operational criteria. The Wet Tropics has a strong scientific basis for establishing evolutionary connectivity and the community has a shared vision for future conservation and connectivity throughout the region. Criterion 1. Scale: sufficient to deliver evolutionary connectivity across multiple ecological communities and, in most cases, consideration of opportunities to manage climate connectivity. Evolutionary connectivity across multiple ecological communities The Wet Tropics of Queensland World Heritage Area demonstrates the evolution of rainforest plants and animals and contains numerous endemic and rare species which have survived over the ages (as described in the criteria for World Heritage listing). For instance, the Area contains 676 terrestrial vertebrate species, 83 of which are found no where else in the world, and 396 plant species are listed as rare or threatened under the Queensland Nature Conservation Act 1992 (WTMA 2009). Connectivity across the Wet Tropics bioregion is vital to ensure evolutionary connectivity of many species which have survived over millennia because there has always been a range of suitable habitats, including the cool wet refugia of the montane rainforests. There is ample scientific evidence to show that connectivity across the Wet Tropics is not only important across numerous ecological communities, but will be vital for managing the impacts of climate change on evolutionary connectivity, both within the bioregion and beyond. When complete, the Wet Tropics corridors will connect coastal ecological communities such as mangroves, littoral forests, open woodlands and lowland rainforest to the montane rainforests of the nearby ranges and the upland rainforests, wet sclerophyll and savannah ecosystems to the west and north to Cape York. The corridors will allow wildlife movements and gene flows across significant altitudinal and climatic gradients and increase the potential for adaptation to the impacts of climate change. Impacts of climate change The Wet Tropics of Queensland World Heritage Area is particularly vulnerable to the impacts of climate change. Climate change (temperature increases between 1.4ºC by 2030 and 4.2ºC by 2070 under high emission scenarios) will have severe and interacting effects on the values of the Area. We can anticipate changes in the abundance and distribution of flora and fauna. Interactions between organisms, such as predator-prey relationships and insect pollination, are likely to be disrupted, creating consequent changes in ecosystem composition, structure and function (WTMA 2008). While some animals and plants in the cool, wet mountain tops may have little room for adaptation, the dramatic vertical gradients and numerous refugial areas and climatic variation within the Wet Tropics make connectivity across the landscape a most important factor in allowing animals and plants to more easily adapt to climate change and associated threats such as changes in fire regimes and water flows. The Wet Tropics bioregion contains a wide range of differentiated ecological communities and niches where species can adapt to climate change. Some of the major impacts of climate change in the Wet Tropics are described below (from WTMA 2008): 1. 2. 3. 4. 5. There will be severe adverse impacts on wildlife and their habitats as well as on ecosystems and the goods and services they provide society. There will be changes in species’ ranges, both latitudinal and altitudinal (Hilbert et al 2001 and Williams et al 2003), and changes in species’ abundance (including local extinctions (Krokenberger 2002). In general, all native species will be more vulnerable, even those able to tolerate climatic changes per se, as they will all have to deal with a variety of new competitors, predators, diseases and introduced species for which they may have no natural defence. It is predicted that existing ecosystems will undergo major changes. Some are likely to disappear entirely; some totally new or novel ecosystems may appear; and others will experience dramatic changes in species composition and geographic extent. While rainfall totals may not vary by much under climate change, there could be significant changes to the variability and seasonality of rainfall. Climate change will adversely affect a range of environmental goods and services provided by the Area. For instance, a rise in cloud levels would cause a significant decline in catchment water yield sourced from cloud stripping, an important source during the dry season. The figures below show the dramatic impacts of temperature increases on climate and vertebrate distribution in the Wet Tropics. Areas in the Wet Tropics with mean annual temperatures less than 22.0ºC (black) in today’s climate (left) and after 2.0ºC warming (right), Rainforest CRC 2003. The decline in distribution of species richness of regionally endemic terrestrial vertebrates with increasing temperature (the darker the shade of grey the greater the species richness), Williams et al 2003. The benefits of ecological corridors for resilience to climate change The Wet Tropics forests have been fragmented by agricultural and urban development, leaving many coastal and upland sections of the World Heritage Area separated from the main body. There are also some very narrow sections in the main body of the Area where connectivity is limited and there is a large gap to the Paluma Range section in the south. Most of these ecological disconnections are relatively recent and can be repaired relatively cheaply and easily by establishing corridors on private and public lands. The attached Biodiversity Fund bid provides examples of the high priority corridors to reconnect the World Heritage Area and create resilience to the impacts of climate change. There has already been at least 20 years of community tree planting and conservation on private lands to help achieve these connections. There is ample evidence that corridors such as Donaghy’s Corridor can achieve ecological connectivity and gene flows between rainforest sections (Paetkau et al 2009, Tucker & Simmons 2009). In the Wet Tropics, a range of short corridors can achieve connectivity across a significant altitudinal gradient and a wide range of ecological communities and climates. Improved connectivity in the Wet Tropics will allow wildlife greater access to refugia. In evolutionary terms, refugia are parts of the landscape in which certain types or suites of organisms are able to persist during periods in which most of their original geographic range becomes uninhabitable because of climatic change. The resulting refugia contain high frequencies of endemic species because the species in them tend to respond to the contraction of range by evolving differences from their original, widespread stock. Refugia, therefore, are important as they represent those areas where favourable habitat will persist or develop as the climate changes (WTMA 2008). Criterion 2. Scope: jurisdictional and tenure: typically achieving evolutionary connectivity will involve multiple jurisdictions at the local, natural resource management region, state and occasionally national or continental level For many years now the Wet Tropics community has shared a vision and a coordinated approach to connectivity across the region. The Wet Tropics Management Authority has worked closely with state government agencies (particularly the Queensland Parks and Wildlife Service), Terrain Natural Resource Management, the Far North Queensland Regional Organisation of Councils (FNQROC), community conservation groups, nurseries, private landholders and Traditional Owners to promote ecological connectivity across the broader landscape. The Wet Tropics Conservation Strategy (WTMA 2004) lists a broad range of corridor priorities across the bioregion and emphasises the many different benefits of each corridor, including ecological connectivity, climate change adaptation, and wildlife movement for threatened species such the cassowary and mahogany glider. These priorities are largely reflected in the Terrain NRM Regional Plan (FNQ NRM Ltd & Rainforest CRC 2004) and the Far North Queensland Regional Plan 2009–2031. They are now being expressed at a more detailed scale in council planning schemes under the Queensland Sustainable Planning Act 2009. The FNQROC has developed an Integrated Biodiversity Assessment and Planning Framework (Sydes, in prep) which includes detailed mapping of biodiversity assets and identifies key areas required for connectivity using methods similar to those detailed in Beier et al (2011). The Authority is currently working with FNQROC, QPWS, Terrain NRM and the Great Barrier Reef Marine Park Authority to update connectivity mapping in the Wet Tropics for a range of criteria including biodiversity significance, climate change, water quality and wetlands, reef health, fire management, and individual threatened species such as cassowaries, tree-kangaroos and mahogany gliders. The mapping is based on a plethora of scientific data on biodiversity hotspots, species distributions, significant threats, community capacity, Aboriginal cultural importance and costeffectiveness. The various jurisdictions in the Wet Tropics region have long worked together to promote connectivity at a local and regional scale. They have been supported by numerous community groups and private landholders who have actively promoted connectivity and developed extensive experience and expertise in tree planting and conservation techniques (see community capacity below). The Wet Tropics World Heritage Area forms the core of conservation efforts to promote broader landscape connectivity across the region. The Queensland Government has recently transferred the tenure of over 300,000ha of state lands in and around the Area to National Park and other conservation tenures under the Nature Conservation Act 1992. The government has also worked with the community to create 8,250ha of Nature Refuges in the bioregion, the majority of which are adjacent to protected areas or help to form wildlife corridors. These Nature Refuges include some private lands bought by non-government organisations as conservation reserves with assistance from National Reserve System funding. For instance, Bush Heritage now manages Yourka Reserve (43,000ha) and the Australian Wildlife Conservancy manages Brooklyn Reserve (59,058ha) and the Taravale and Mount Zero Reserves (60,308ha). The Queensland Government has bought Wairuna Station (75,454ha) to manage for conservation purposes. These properties all provide ecological linkages along the western edges of the Wet Tropics rainforests and wet sclerophyll forests, as well as linkages to the drier savannahs to the west. There are also numerous private landholders working with the community to promote conservation and connectivity on their lands (see below). Criterion 3. Scope: partnerships: effective connectivity management will require collaborations across multiple forms of tenure including public, private, Indigenous and other tenure arrangements. Effective collaborations are likely to involve organisations that can best engage and leverage values across these tenures including governments, regional NRM groups, non-government organisations (NGOs), businesses and others (such as statutory authorities) The Wet Tropics is a region that can demonstrate effective partnerships across multiple tenures. In many ways, the community has provided the inspiration and motivation for over thirty years of conservation and connectivity work, including the initial campaign to have the World Heritage Area listed. This community culture of conservation is demonstrated by the numerous community groups who for many years have fostered tree planting, wildlife corridors, nurseries and conservation. These include Trees for the Evelyn and Atherton Tablelands (TREAT), Community for Coastal and Cassowary Conservation (C4), Daintree Cassowary Conservation Group, Rainforest Rescue, Kuranda EnviroCare, Kuranda Conservation, Tree Kangaroo and Mammal Group, Mahogany Glider Recovery team, Cassowary Recovery Team, Cairns and Far Northern Environment Centre, Mulgrave River, Russell River and Johnstone River Landcare Groups, Barron River Catchment Management Association, Mitchell River Watershed Management Group, Terrain NRM workgroups, Conservation Volunteers Australia, council nurseries and tree planting teams, and QPWS rehabilitation teams. These groups work together with large numbers of private landholders who are promoting conservation, connectivity and sustainable agriculture on their lands. Regional bodies such as the Wet Tropics Management Authority, Terrain Natural Resource Management, the Far North Queensland Regional Organisation of Councils and the Queensland Parks and Wildlife Service work together with the community to offer a strategic regional overview and priorities for connectivity in the region. Criterion 4. Institutional development: our emphasis will be on those corridor initiatives that have been formally identified and which are moving towards a formalised structure (though not necessarily with formalised governance or widespread implementation). The Wet Tropics Management Authority, together with numerous other regional organisations and the Queensland Office for Climate Change, applied for funding from the Biodiversity Fund 2011-2012 to promote connectivity across the Wet Tropics bioregion, in particular to connect separate sections of the World Heritage Area and to promote adaptation to the impacts of climate change (see attached map and submission). The submission was possible in such a short time because of the large amount of existing knowledge and planning and the well-established relationships between government and community groups across the region. The Biodiversity Fund submission catered for existing capacity to do the hard onground work of tree planting, weed control and other rehabilitation. The bid is practical and achievable and many corridors are already underway. The submission also reflects a sense of urgency to achieve connectivity in some areas in the near future before urban and rural development made it more difficult and more expensive. The on-ground connectivity works are being undertaken in conjunction with a range of other strategies for to conserve and acquire lands for connectivity. Other more costly connectivity proposals were not included in the bid and some private lands, where the only current means available to create connectivity was acquisition, were also excluded. The FNQ Regional Plan 2009–2031 regulates sustainable growth in the region and specifies areas of biodiversity significance and corridors of regional importance. Councils are currently developing their planning schemes to give effect to the regional plan and many are including designated corridors as habitat investment areas. As already mentioned, the Wet Tropics Conservation Strategy (WTMA 2004) and the Terrain NRM Regional Plan (FNQ NRM Ltd & Rainforest CRC 2004) list regional connectivity priorities which have strong scientific rationales and community capacity. These priorities have formed the basis for numerous conservation and tree planting projects over the past ten years, often with funding assistance from a succession of Australian Government funding programs. Socioeconomic benefits and other goals in the draft National Wildlife Corridor Plan The goals of the draft National Wildlife Corridor Plan also include other important reasons for promoting corridors that are not directly covered by the above criteria. Many of these are also mentioned in a supporting document to the plan – ‘An overview of key socio-economic factors, principles and guidelines in wildlife ‘corridor’ planning and implementation (Parris et al, 2011). Parris et al (2011) details numerous potential benefits for social capital by creating connectivity. The document states that, while targeted investment may have some direct economic benefits, ‘more significant benefits are likely to come through the engagement processes used in the planning, implementation and management of corridor projects which generate substantial social capital’, and ‘enhanced social capital generates flow-on economic benefits as networks and strong patterns of communication and information sharing have been shown to facilitate relatively low cost transfer of economic innovation.’ As well as direct benefits, creating connectivity can have ‘a range of non-use benefits (sense of place, cultural heritage, and spiritual values) which contribute to a wider cultural richness and human well-being’ (Parris et al, 2011). Some of the socioeconomic and organisational factors in creating connectivity have already been discussed above. A few more indirect benefits for the Wet Tropics are discussed below. Protecting natural stores of carbon in native ecosystems to minimise greenhouse gas emissions. In addition to improving the resilience of Wet Tropics ecosystems and providing significant biodiversity habitat, the Authority’s Biodiversity Fund bid calculated the annual CO2 sequestration of 363ha of proposed corridors to sequester 3519.28 tonnes of carbon per year. Upland areas more suitable for climate change refugia generally had higher value than lowland forests. At a rate of $23 per tonne, this equates to 3519.28 x $23 = $80.943.44 per year. The bid also stated that: ‘While many landholders within the proposed corridors are already willing participants, the carbon revenue generated by the project would be a significant incentive for further landholders to participate and a fitting contribution to reward the time and effort landholders put in over the years to maintain conservation works on their properties. The use of carbon credits will also offer ongoing legal protection for the biodiversity conservation and restoration on private lands. There is a high opportunity cost for land in the Wet Tropics. The average unimproved value of rural land within the Cairns Regional Council area is $11,138 per hectare – amongst the highest in Queensland based on data from the Queensland Valuation Administration System (QVAS).’ Helping to manage and protect Australia’s iconic landscapes and Indigenous and non-Indigenous culture and heritage The Australian Government is currently considering an application for National Heritage listing of the Wet Tropics World Heritage Area for its cultural values. The Area is home to 18 different Aboriginal tribal groups and much of the Area has formally recognised Native Title rights or areas under claim. Traditional Owners have been supportive of the proposals to rehabilitate habitat and connectivity across the Wet Tropics and have often been employed to do on-ground works through QPWS, Terrain NRM and Conservation Volunteers Australia work crews. Native Title agreements in the Wet Tropics have been finalised with Djabugay people, Mandingalbay Yidinji people, Eastern Kuku Yalanji people people, NgadjonJii people, Girramay people, Combined Dulabed and Malanburra Yidinji people, Muluridji people, Djiru people, Wanyurr Majay people, Jirrbal people, Bar-Barrum people and Combined Gunggandji people. These agreements include various arrangements for tenure and land management and often include arrangements for Aboriginal people to work with government to manage lands for conservation. There are also several large properties adjacent to and within the Area such as Badjuballa and Mungalla Stations that are managed by Indigenous Corporations. Increasing community knowledge and understanding of wildlife corridors and connectivity conservation In partnership with community and conservation groups, the Authority, Terrain NRM, FNQROC and QPWS have all invested in public education about the benefits of connectivity for landholders, the community, wildlife and ecosystems. Numerous community groups (see criterion 3 above) work tirelessly to educate landholders and the community about the benefits of tree planting and ecological connectivity. They lead by example and are the primary force that motivates people to get involved in on the ground activities and to participate on their own lands. These groups have also developed local expertise and participated in much of the research on the effectiveness of corridors and tree planting and conservation techniques. Researchers have actively worked with communities to develop adaptive community-based biodiversity conservation such as the Mission Beach Habitat Network Action Plan (Hill et al, 2010). This process focused on a particular species – the cassowary – as a basis for community planning (Hill & Robinson et al 2011). There are numerous cases in the Wet Tropics where cassowaries, tree-kangaroos, bettongs and mahogany gliders have been the focal point for connectivity conservation for small groups of the community. In many cases, where corridors rely on participation of neighbouring landholders, individual landholders are influenced by the enthusiasm of their neighbours and by watching the results achieved by those in their social circles and local region. Such cooperation can take years to grow and nurture, but is very effective. A Wet Tropics Management Authority poster A strong scientific rationale for connectivity There has been significant research in the Wet Tropics bioregion into the impacts of fragmentation and how best to rehabilitate rainforest communities. There has also been significant monitoring of the effectiveness of corridors and tree planting methods. A few examples are provided below to demonstrate the strong scientific rationale behind efforts to improve Wet Tropics connectivity and resilience. In the Wet Tropics there is a range of scientific evidence to show the benefits of connectivity to improve biodiversity and reduce the impacts of climate change and associated threats such as invasive species and changed fire regimes. The Authority believes there is a strong argument for connectivity in areas such as the Wet Tropics, while the evidence for national corridors remains less convincing. Whitten et al (2011) states that: ‘Australian science is an early leader in the study of landscape-scale fragmentation and the need for various forms of connectivity conservation but ecological understanding of patterns and processes at the scale of the Great Eastern Ranges or Gondwana Link is poorly understood. We are unaware of any ecological modelling or comprehensive spatial analysis at this ‘mega’ corridor scale (p vi)’. Impacts of fragmentation There have been numerous Wet Tropics studies on the fragmentary impacts of roads, powerlines and other linear infrastructure on rainforest ecosystems (for instance, Goosem 2001 and 2007, Pohlman et al 2007). There have been numerous overpasses and underpasses designed, built and monitored (for instance, Goosem 2001). The impacts of roads as barriers to stream connectivity have also been investigated and various solutions designed (see Lawson et al 2010). Impacts of climate change Wet Tropics biodiversity has been shown to be extremely vulnerable to climate change. Numerous rare and endemic vertebrate species, particularly those in the cooler upland regions ,will be under threat from changes to climate and habitat (see Hilbert et al 2001, Krockenberger 2002, Rainforest CRC 2003, Shoo et al 2006, Williams et al 2003, Williams 2006, Williams et al 2008, and WTMA 2008). Improved ecological connectivity has been proposed as an important way of assisting wildlife to deal with climate change impacts (Shoo et al 2011, WTMA 2008) Restoration techniques The long history of restoration activities in the Wet Tropics (Catterall and Harrison 2006) has provided the community with great expertise in tree planting methods and the benefits of planting certain combinations of tree species for the maximum restoration and natural recruitment (Florentine & Westbrooke 2004). These species vary according to specific habitats and are listed in detail in Repairing the Rainforest (Goosem and Tucker 1995). As part of a current Caring for Our Country project, Dr Luke Shoo is currently researching the most suitable areas for climate refuges for temperature-sensitive species including Herbert River and Daintree River ringtail possums, golden bowerbirds, rainforest skinks, and Lumholtz’s tree-kangaroos. Dr Susan Lawrence (James Cook University) has begun work to study accelerating species richness gains and carbon sequestration in secondary regrowth at sites on the tablelands. Monitoring and evaluation Monitoring and evaluation of restoration projects has looked at the long term success (or otherwise) of community plantings, the biodiversity benefits and the need for long term funding and planning (Catterall et al 2004b, Catterall and Harrison 2006, Harrison et al 2004, Kanowski 2010, Pert et al 2010). Researchers have also developed toolkits to help the community monitor restoration projects (Freebody 2007, Kanowski et al 2010). Researchers have also focused on the use of corridors by various animals (Jansen 1997 and 2005, Kanowski et al 2006, Caterall 2004a) and the benefits for genetic transfer between previously separated sites (Paetkau et al 2009, Tucker and Simmons 2009). Planning and mapping The Wet Tropics Conservation Strategy (WTMA 2004) and Sustaining the Wet Tropics (FNQ NRM Ltd & Rainforest CRC 2004) give a broad overview of connectivity priorities in the region and are currently being updated. There have been more specific studies that focus on particular regions and issues such as the Cairns to Cardwell cassowary corridors (Biotropica Australia 2005). A report card on regional biodiversity values and trends recommends prioritising investment to enhance vegetation and biodiversity management outside the Wet Tropics World Heritage Area and adjacent to the World Heritage Area (Pert et al 2010). The Far North Queensland Regional Plan 2009–2031 has also included broad biodiversity corridors which are being used to designate more detailed corridors in council planning schemes using multi-criteria mapping of biodiversity connectivity and habitat investment linkages (Sydes, in prep). Achievability and cost-effectiveness Whilst the Authority supports the general concept of national corridors, it questions the cost-effectiveness and achievability of such large corridors. The draft plan needs to provide more detail about the designated national corridors, how they would be implemented and how much they would cost. The Authority considers that smaller connectivity projects such as the Wet Tropics are more achievable and provide better value for money. The best way to create national corridors is to focus first on their significant components. Even regional connectivity proposals like the Wet Tropics would require large commitments of funds and community effort to be realistically achieved over the next ten or twenty years. Any large scale corridor project will involve progressively linking local and regional scale protection and rehabilitation measures. The Authority suggests that the initial focus for connectivity should be in richly biodiverse area such as the Wet Tropics where the need for connectivity is based on a solid scientific basis, a healthy community capacity and readily achievable outcomes. Once important regional connectivity is achieved, then the links to neighbouring bioregions can be considered. For instance, the Wet Tropics would form a vital component of a national Eastern Ranges Corridor and has strong links to the rainforests and savannah lands of Cape York and the savannahs and river systems of the Einasleigh. However, these ecological links are not as strong as those within the bioregion where there is ample evidence of the need for wildlife movement for increased ecological resilience. Public consultation The Authority questions the process and criteria by which the priority corridors were identified and the lack of consultation or investigation before publication of the draft. The draft plan claims that these corridors are the only existing concepts which have been developed, but there seems to have been little chance for others to present existing proposals or concepts the Australian Government. The Wet Tropics Management Authority, Terrain NRM and some other regional organisations were invited to a meeting on very short notice just prior to release of the draft plan, but opportunities to contribute to the draft plan seem largely limited to the networks represented on the advisory committee. The Authority looks forward to an improved process of engagement in advance of preparation of the final plan so that it can attract widespread support and confidence among regional communities. Given the focus on national connectivity across jurisdictions and tenures, there does not seem to have been much consultation with state governments or local governments. This would also be necessary for setting priorities and implementing corridors. Funding for connectivity The Authority is concerned that the current priority corridors, as listed, will be used to direct funding to nominated corridors to the exclusion of other important areas like the Wet Tropics. There would be numerous smaller projects in Australia which are eminently achievable and practical (with community and biodiversity benefits) that may not fit the broader criteria of the nominated national corridors. The Authority suggests that there should be criteria that apply for biodiversity conservation and ecological corridors and that applicants for funding seek to satisfy these criteria. This would be preferable to nominating corridors and thus eliminating all other proposals. Pursuit of connectivity as an end in itself risks diverting investment away from practical and immediate measures aimed at protecting and rehabilitating critically important biodiverse habitats. The draft National Wildlife Corridor Plan mentions a desire to fund the National Corridors through the Biodiversity Fund, but there is little information about how the Biodiversity Fund criteria might allow for this in future and how it would affect other bids to the Fund. Legislation Having much experience in fostering community conservation, the Authority questions the practicality and benefit of any further legislation for connectivity and, instead, would recommend the use of further incentives for landholders and greater community involvement. In the Wet Tropics we have the benefit of the Far North Queensland Regional Plan 2009–2031, prepared under Queensland’s Sustainable Planning Act 2009, which includes broad scale mapping of biodiversity, strategic rehabilitation areas and corridors. However, these areas then need to be mapped at a finer scale when included in mapping local government planning schemes to be more effective. The mapping also requires distinct codes to be applied to regulate development and land use within the corridors. It should be noted that such regulation, while important, only applies when there is a development proposal and does little to promote the community motivation required to develop most landscape connectivity. Such legislation, when developed within the State land use planning framework, can be effective, but would be less effective at a national level without the means to implement at a local scale. The Authority is unsure how the Australian Government would legislate to nominate the parameters of national corridors and to further regulate land use at a local level across such broad areas. The proposal for legislation specific to biodiversity corridors would have to be somehow linked to the Commonwealth’s constitutional powers. These areas of land use regulation have traditionally been regulated by the states and local governments. Rather than being separate legislation, any legislative proposal would best be included as a matter of national environmental significance under the EPBC Act. However, given the resources already required to administer the EPBC Act, this would create a need for additional resources to regulate and administer. The Minister has existing powers under the EPBC Act to establish advisory bodies in relation to wildlife corridors. This may be a preferred option. Investment priorities are more appropriately established in policy and strategy than legislation. The use of instruments such conservation agreements under the EPBC Act may also be used as an incentive to promote corridors. The Australian Government could also provide support for state initiatives such as Nature Refuges where the Queensland Government has not always had sufficient funding to meet demand in the Wet Tropics. References Beier, P., Spencer, W. Baldwin, R.F., and Mcrae, B.H. (2011), Toward Best Practices for Developing Regional Connectivity Maps, Conservation Biology, Volume 25, No. 5, p879– 892, 2011. Biotropica Australia (2005), A framework to establish lowland habitat linkages for the Southern Cassowary (Casuarius casuarius johnsonii) between Cairns and Cardwell. Report commissioned by the Australian Rainforest Foundation, Cairns. Catterall, C. P. & Harrison, D. A. (2006) Rainforest Restoration Activities in Australia's Tropics and Subtropics, Cooperative Research Centre for Tropical Rainforest Ecology and Management, Rainforest CRC, Cairns, Australia. Catterall, C., Westcott, DA, Kanowski, J and Dennis, AJ (2004a), Pp 1-4 in Kanowski, J et al (eds) Animal-plant interactions in rainforest conservation and restoration. Cooperative Research Centre for Tropical Rainforest Ecology and Management. Cairns. 2004 Introduction. Catterall, C. P., Kanowski, J., Wardell-Johnson, G. W., Proctor, H. C., Reis, T., Harrison, D. A. & Tucker, N. I. J. (2004b), Quantifying the Biodiversity Values of Reforestation: Perspectives, Design Issues and Outcomes in Australian Rainforest Landscapes. In Conservation of Australia's Forest Fauna (ed. D. Lunney), pp. 359-393. Sydney: Royal Zoological Society if NSW. Florentine, S. K. & Westbrooke, M. E. (2004), Evaluation of Alternative Approaches to Rainforest Restoration on Abandoned Pasturelands in Tropical North Queensland, Australia. Land Degradation & Development 15, 1-13. FNQ NRM Ltd & Rainforest CRC (2004) Sustaining the Wet Tropics: A Regional Plan for Natural Resource Management 2004–2008. FNQ NRM Ltd, Innisfail (208pp).http://www.terrain.org.au/publications/by-terrain/nrm-plans.html Freebody, K. (2007), Rainforest Revegetation in the Uplands of the Australian Wet Tropics: The Eacham Shire Experience with Planting Models, Outcomes and Monitoring Issues. Ecological Management and Restoration 8, 140-143. Goosem M (2001), Effects of tropical rainforest roads on small mammals: inhibition of crossing movements. Wildlife Research 28: 351-364 Goosem, M. (2007), Fragmentation impacts caused by roads through rainforests. Current Science 93, 1587-1595. Goosem M, Izumi Y and Turton S (2001), Efforts to restore habitat connectivity for an upland tropical rainforest fauna: A trial of underpasses below roads. Ecological Management and Restoration 2: 196-202. Goosem, S. & Tucker N.I.J. (1995), Repairing the Rainforest: Theory and Practice of Rainforest Re-establishment in North Queensland’s Wet Tropics, Wet Tropics Management Authority, Cairns. Harrison, R., Harrison, S. R. & Herbohn, J. L. (2004b), An Evaluation of the Performance of the Community Rainforest Restoration Program in North Queensland, Australia. In Human Dimensions of Family, Farm and Community Forestry International Symposium (ed. D. M. Baumgartner), pp. 207-214. Pullman, WA, USA: Washington State University. Hilbert, D., Ostendorf, B. & Hopkins, M. (2001), Sensitivity of tropical forests to climate change in the humid tropics of north Queensland. AustralEcology 26: 590-603. Hill R, Williams KJ, Pert PL, Robinson CJ, Dale AP, Westcott DA, Grace RA, O'Malley T. (2010), Adaptive community-based biodiversity conservation in Australia's tropical rainforest. Environmental Conservation. 37 (1):73-82. Hill, R., Robinson, C.J., et al. (2011), Integrated landscape-scale cassowary conservation at Mission Beach. Synthesis of MTSRF Biodiversity Planning Research 2006-2011. Marine and Tropical Sciences Research Facility (MTSRF) Transition Project Final Report. Reef and Rainforest Research Centre Limited, Cairns (44 pp.). Jansen, A. (1997), Terrestrial Invertebrate Community Structure as an Indicator of the Success of a Tropical Rainforest Restoration Project. Restoration Ecology 5, 115-124. Jansen, A. (2005), Avian Use of Restoration Plantings Along a Creek Linking Rainforest Patches on the Atherton Tablelands, North Queensland. Restoration Ecology 13, 275-283. Kanowski, J. J., Reis, T. M., Catterall, C. P. & Piper, S. D. (2006), Factors Affecting the Use of Reforested Sites by Reptiles in Cleared Rainforest Landscapes in Tropical and Subtropical Australia. Restoration Ecology 14, 67-76. Kanowski, J. (2010), What Have We Learnt About Rainforest Restoration in the Past Two Decades? Ecological Management & Restoration 11, 2-3. Kanowski, J., Catterall, C. P., Freebody, K., Freeman, A. N. D. and Harrison, D. A. (2010), Monitoring Revegetation Projects in Rainforest Landscapes. Toolkit Version 3. Reef and Rainforest Research Centre Limited, Cairns (98pp.). Krockenberger, A. (2002), A tropical rainforest possum that can’t take the heat. Conference Abstract in Ecology 2002: Handbook of the 2nd joint meeting of the Ecological Society of Australia Inc., and the New Zealand Ecological Society Inc. Cairns Qld 1-6 December. Ecological Society of Australia Inc., Canberra. Lawson, Tina, Frederieke Kroon, John Russell & Paul Thuesen (2010), Audit and prioritisation of physical barriers to fish passage in the Wet Tropics region, CSIRO Sustainable Ecosystems, Atherton Queensland. Paetkau, D., Va´zquez-Domı´nguez, E., Tucker, N.I.J., and Moritz, C. (2009), Monitoring movement into and through a newly planted rainforest corridor using genetic analysis of natal origin, Ecological Management & Restoration Vol 10 No 3 December 2009. Parris, H., Whitten, S.M., Wyborn, C., Hill, R. and Freudenberger, D. (2011), An overview of key socio-economic factors, principles and guidelines in wildlife “corridor” planning and implementation. A report for the Australian Government Department of Sustainability, Environment, Water, Population and Communities, CSIRO Ecosystem Sciences, June 2011. Pert, P.L., Bruce, C.M., Butler, J.R.A., Metcalfe, D.J., Webster, T. and Goosem, S. (2010), A Prototype Report Card for the Status and Trends of Biodiversity, Soils and Landscapes in the Wet Tropics. Published by the Reef & Rainforest Research Centre Ltd on behalf of the Australian Government’s Marine and Tropical Sciences Research Facility (MTSRF), Cairns (42pp.). Pohlman, Catherine L., Turton, Stephen M., and Goosem, Miriam (2007), Edge effects of linear canopy openings on tropical rain forest understory microclimate. Biotropica, 39 (1). pp. 62-71. Rainforest CRC (2003), Global Warming in the Wet Tropics. Issues in Tropical Forest Landscapes: Issue 2 August 2003. Rainforest CRC, Cairns. Shoo L.P., Williams S.E. & Hero J-M. (2006), Detecting climate change induced range shifts: where and how should we be looking? Austral Ecology 31:22-29. Shoo, L. P., Storlie, C., Vanderwal, J., Little, J. & Williams, S. E. (2011), Targeted Protection and Restoration to Conserve Tropical Biodiversity in a Warming World. Global Change Biology 17, 186-193. Sydes, T. (in prep), Integrated Biodiversity Assessment and Planning Framework, Far North Queensland Regional Organisation of Councils. Tucker, N.I.J. and Simmons T. (2009), Restoring a rainforest habitat linkage in north Queensland: Donaghy’s Corridor, Ecological Management & Restoration Vol 10 No 3 August 2009. Wet Tropics Management Authority (2004), Wet Tropics Conservation Strategy: the conservation, rehabilitation and transmission to future generations of the Wet Tropics World Heritage Area, WTMA, Cairns. http://www.wettropics.gov.au/mwha/mwha_conservation.html Wet Tropics Management Authority (2008), Climate Change in the Wet Tropics: Impacts and Responses – State of the Wet Tropics Report 2007–2008, Cairns, 2008. http://www.wettropics.gov.au/th/th_climate.html Wet Tropics Management Authority (2009), State of the Wet Tropics Report 2008–2009, Cairns 2009. http://www.wettropics.gov.au/res/res_report.html Whitten, S. M., Freudenberger, D., Wyborn, C., Doerr, V. & Doerr, E. (2011), A compendium of existing and planned Australian wildlife corridor projects and initiatives, and case study analysis of operational experience. A report for the Australian Government Department of Sustainability, Environment, Water, Population and Communities, CSIRO Ecosystem Sciences, June 2011. Williams S.E., Bolitho, E. E. & Fox, S. (2003), Climate change in Australian tropical rainforests: an impending environmental catastrophe. Proceedings of the Royal Society Lond. B. 270:1887-1892. Williams S.E. (2006), Vertebrates of the Wet Tropics rainforests of Australia: species distributions and biodiversity, Cooperative Research Centre for Tropical Rainforest Ecology and Management, Cairns, Australia ISBN 0 86443 762 5. http://www.rainforestcrc.jcu.edu.au/publications/vertebrate_distributions.htm Williams, S.E., Isaac, J.L., Shoo, L.P. (2008) The impact of climate change on the biodiversity and ecosystem functions of the Wet Tropics. In Living in a dynamic tropical forest landscape, N. Stork & S. Turton (eds.), Blackwell Publishing. Worboys, G., Francis, W. and Lockwood, M. (eds.) (2010), Connectivity Conservation Management: A Global Guide, Washington DC: Earthscan. Worboys, G.L. & Pulsford, I. (2011), Connectivity Conservation in Australian Landscapes, A report prepared for the Australian Government Department of Sustainability, Environment, Water, Population and Communities on behalf of the 2011 State of the Environment Committee (Draft), in press.