1 ANNEX 1 PROJECT SYNOPSIS COLLABORATIVE SEED COLLECTION / RESEARCH PARTNERSHIP Project Partners Department of Infrastructure, Planning & Environment Northern Territory Government Australia And Royal Botanic Gardens, Kew Millennium Seed Bank Project Wakehurst Place Ardingly, West Sussex United Kingdom PROJECT MANAGER: PROJECT SUPERVISION: MSBP INTERNATIONAL CO-ORDINATOR: 2 David Albrecht & John Nightingale Tony Bowland Michiel Van Slageren 1. PROJECT SYNOPSIS The Project synopsis provides background information related to the development of an international plant conservation partnership between the Department of Infrastructure, Planning & Environment (“NT Government”), and the Royal Botanic Gardens Kew Millennium Seed Bank Project (“MSBP”). It outlines the Project purpose and outputs, summarises the major activities, and highlights the specific benefit-sharing and capacity building components. The Project synopsis also defines the context of the Project in relation to global, national and state legislation/strategies, and considers collection priorities to pursue these mandates. Finally it summarises the roles and responsibilities of the Partners and describes the required inputs needed for the effective implementation and delivery of the Project. The Project synopsis forms Annex 1 of the Access and Benefit-Sharing Agreement between the Northern Territory Government of Australia (represented by the Minister for Parks and Wildlife) and the Board of Trustees of the Royal Botanic Gardens, Kew, United Kingdom (“RBG, Kew”). 1.1 BACKGROUND Department of Infrastructure, Planning and Environment (NT Government) is a Northern Territory Government Department with primary responsibility for the conservation of the Northern Territory’s wildlife. NT Government is presently involved in a number of specific conservation projects that align directly with the aims of the MSBP, making it the logical partner for the MSBP. Current NT Government projects include: On-going collection and housing of Northern Territory plant specimens in the Northern Territory Herbarium located at the Alice Springs Desert Park (ASDP) and in Palmerston near Darwin. Data entry and maintenance of the Herbarium database. Stored information relates to specimen location, habitat, abundance, habit, and reproductive state. The process of identifying target species for conservation work is facilitated by access to the specimen data; Development and maintenance of a vascular plant checklist for the Northern Territory that provides up-to-date information on species localities and their taxonomic and conservation status; Operation of ASDP which displays a range of broad arid Northern Territory habitat types and the George Brown Darwin Botanic Gardens (GBDBG) which displays significant habitat types of the Top End and is developing the International Cycad Garden. Staff at these institutions have been involved in various research projects (including student honours programmes), some of which have involved seed longevity and germination work. Seed collection, storage and administration is integral to the running of both parks and as such, staff are well versed in general seed storage procedure; Establishment of a species fire response database as part of the broader Commonwealth and Territory funded Desert Knowledge Australia programme (http://www.desertknowledge.com.au/); 3 Establishment of a species’ ecological traits database that includes information relating to plant growth form, life history, dispersal mode, phenology, and stress responses. Information relating to seed biology gained from the proposed project would feed directly into this database; Development of an interactive taxonomic key for the MacDonnell Ranges Bioregion representing the first stage of a revision of the entire arid Northern Territory flora. Herbarium specimens and live material from the ASDP nursery and plantings are used for the purposes of recording plant attributes for the key; Development of the Flora of the Darwin Region which is an identification guide to the Flora of the NW Top End. Herbarium specimens and live material from the GBDBG plantings are used for the purposes of recording plant attributes for the flora; Development of Bioregional Conservation Strategies that aim to ensure that the species, ecosystems and ecological processes in the Northern Territory areas are adequately conserved; Development of new Northern Territory-wide conservation master plan that seeks to take account of on- and off- park conservation priorities including those identified by indigenous people of being of cultural/economic importance; Single-species studies on various rare or threatened plants; and Development of National recovery plans and Northern Territory wide management plans for threatened plant species. The Millennium Seed Bank Project is a 10-year global plant conservation initiative managed by the Seed Conservation Department at the Royal Botanic Gardens, Kew, in the United Kingdom. Bilateral research, training, and capacity building relationships are supported at an international level in order to advance the conservation of wild plant species. The MSBP aims to collect and undertake longterm seed storage from 10% of the world’s seed bearing flora (primarily in arid and semi-arid regions) by 2010. In Australia there are already MSBP partnerships successfully operating within Western Australia, South Australia, New South Wales and Queensland. Discussions on similar partnerships are in progress between Kew and plant conservation groups/agencies in Victoria and Tasmania. It therefore seems timely to develop this Partnership between Kew and the NT Government addressing plant conservation through an expanded seed collecting program and developing improved long-term seed management and storage protocols for the Northern Territory’s threatened and priority plant species. A six-year collaborative program to strengthen and expand the existing ex situ seed conservation and research program in the Northern Territory has been developed (the “Project”). The Project will have a duration of six (6) years commencing from the date of signing of the Access and Benefit-Sharing Agreement. The project will be based in Alice Springs at the State Herbarium (“NT”)/ASDP precinct for the following reasons: basic facilities and equipment are available; staff has a strong interest in seed biology research, seed curation and storage, and ease of access to the NT arid and semi-arid flora. Field work in the Top-end will operate out of the State Herbarium in Darwin (“DNA”) and make use of the facilities offered there. 4 1.2 PROJECT DESCRIPTION 1.2.1. Project Goal The Goal of the Project is the development of an effective ex situ conservation program for plant biodiversity in the Northern Territory co-ordinated by the Department of Infrastructure, Planning & Environment (“NT Government”). 1.2.2 Project purpose To support plant conservation in the Northern Territory with complementing in situ plant conservation activities by establishing a program of increased seed collection for targeted species, and undertaking research to understand the germination and longterm storage requirements for seed of collected species. 1.2.3. Project outputs The Project purpose will be addressed through the delivery of three Project outputs: 1. The establishment of a verified and well-documented collection of seed of wild native species from the Northern Territory based at the ASDP Seed Bank and, in parallel, at the Kew Seed Bank. These collections will include taxa with a threatened status, data deficient taxa, taxa of least concern both reserved and nonreserved and will include endemic, common species under threat, and economically important plant species to safe guard them against extinction if species disappear in the wild. 2 The development of a research programme that will further our understanding of aspects of the seed biology of various Northern Territory plant species. The lack of detailed species-level biological research currently poses one of the greatest impediments to the proper management of the Northern Territory flora. Research efforts should focus on aspects of seed dormancy, longevity, dispersal, germination, emergence and establishment. Further research is also required into seed storage behaviour. The Project will provide opportunities to establish stronger research collaboration links and partnerships with other Australian institutions, such as Kings Park Botanic Gardens, Perth and a variety of international seed research institutions. 3 The creation of opportunities for staff training and development to strengthen the capacity of NT Government to carry out the Project goal. The Project will provide NT Government with opportunities for training in seed biology techniques. Capacity building will also include the acquisition of new equipment where required. 1.2.4. Project activities These Project outputs will be delivered through the implementation of activities including: 5 a. b. c. Recruitment of a seed curator/biologist by the NT Government; Procurement of relevant equipment for cleaning, testing and storing seed; Collection of vouchered seed accessions based on the tentative species prioritisation outlined in this document. Seeds of priority plant species will be collected in an ecologically sustainable way, consistent with Action 1.9.3 of the National Strategy for the Conservation of Australia’s Biological Diversity; d. Allocation of collected seed and herbarium vouchers to RBG Kew and ASDP seed bank/herbarium; e. Conducting pre-storage seed germination tests on collected accessions to determine viability and facilitate long-term storage; f. Conducting research experiments to determine whether and the type of dormancy mechanisms present in seeds; develop methods to overcome dormancy issues in species identified as being difficult to germinate; develop methods to optimise maintenance of viability after storage; and to assess the effect of seed treatments on germination and seedling vigour in laboratory (and field conditions where practical); g. The implementation of an efficient monitoring program to determine the effect of storage conditions on long-term conservation collections; h. Engage two post graduate students to undertake specific seed biology projects; i. sharing seed viability, germination and verification results carried out on material at both NT Government and the Royal Botanic Gardens Kew; j. The establishment of a network of regional volunteers in the Northern Territory to assist in monitoring fruiting phenology and seed collection; k. Conducting seed techniques training workshops for regional staff and volunteers; l. Continued training of NT Government technical staff in seed conservation techniques through formal courses and research attachments at the Millennium Seed Bank in the United Kingdom; m. Dissemination of data generated during the Project, by attending conferences, by publication of articles in peer reviewed journals and by electronic means. 1.3 BENEFIT-SHARING NT Government and Kew have agreed on the following benefit-sharing activities: 1.3.1 Personnel While the NT Government employs staff with expertise in a range of plant taxonomic and ecological fields, the organisation does not currently employ a qualified seed curator/biologist. It is for this reason that the NT Government is proposing the establishment of a new professional level position (“P”) to be funded by MSBP for a period of six years. The NT Government is currently exploring options to engage a traditional ecologist to address the documentation of traditional knowledge about native plant species, including information relevant to the MSB project. An Aboriginal apprentice would be associated with the seed curator/biologist and traditional ecologist positions. 6 It is envisaged that staff training would constitute a considerable aspect of the seed curator/biologist’s work brief. The NT Government staff (mainly associated with ASDP and the Northern Territory State Herbarium) would provide technical support for this position. Time will be spent in the Herbarium in Darwin to facilitate access to Top End flora and local expertise. Academic training will be undertaken jointly by Universities and the NT Government where Postgraduate research opportunities are to be made available through the appropriate faculty. The Department’s Regional Manager, Dr Tony Bowland would undertake project supervision. 1.3.2. Equipment The NT Government is quite well equipped in terms of basic seed research facilities, all of which would be made available for the joint NT Government/Kew project. Facilities include: glass houses; incubation cabinets; ovens; seed processing equipment; field equipment, including a 4WD vehicle; a 'Dry Room' will be constructed during the second year of the project. For its part, the Royal Botanic Gardens Kew will finance the purchase of relevant equipment for the Project: One non-destructive equilibrium relative humidity meter; Two -18C freezers; One zig-zag aspirator seed blower; Two small incubators. This equipment will remain the property of the NT Government at the conclusion of the Project. 1.3.3. Research funding In addition to the funding sought to employ a seed curator/biologist, the NT Government also requests that funds be made available for the acquisition of collecting and laboratory materials and for field allowances. Funding would be required for Postgraduate training. Students registered with Universities will be based at the Herbarium/ASDP precinct. 1.3.4. Collaborative seed science research The activities undertaken as part of the proposed research partnership between Kew Gardens and NT Government would align directly with the two stated themes of the 7 MSBP seed science programme: Seed quality and the environment; and Preservation of seed biodiversity. The overall goal of this proposed research is to progress our understanding of the seed biology of the NT flora such that progress is made towards the removal of barriers to seed use and the maximization of seed storage potential. It is envisaged that this progress will in turn increase the success of plant restoration and recovery programmes in the NT. The work would also have direct implications for the development of vegetation management strategies in the NT, especially in relation to fire use and the amelioration of threatening processes such as weed invasion. Theme 1: Seed quality and the environment Eight different avenues of research would be carried out under the Seed quality and the environment theme. Together these different facets seek to address the main aspects of seed biology in relation to environmental constraints and processes in the NT context. 1.1 Development of effective methods for overcoming seed dormancy (Research Leader: Seed Curator/Biologist) Given that the ultimate goal of seed banking is to provide seeds for plant recruitment in conservation and other plant production pursuits, it is imperative that effective methods for overcoming dormancy in banked and soil-stored seed be developed. Research carried out would seek to develop solutions to germination and dormancy problems in the NT flora. This would involve the use of a factorially designed experimental approach to determine the role of individual germination cues and their interactions. The approach taken would follow standard Kew Gardens’ procedure involving the initial application of dormancy breaking factors that would most likely resemble the environmental conditions that trigger germination in a species’ natural setting. For example, species from fire-prone environments would be subjected to various combinations of heat shock, smoke and scarification treatments by way of mimicking the effects of natural fire events. Alternating diurnal temperature regimes of 25/100C and 35/200C for temperate and tropical species respectively (as per Kew Gardens’ standard procedure) would be applied as part of the initial screening process. Through this process, seeds possessing complicated dormancy (thereby preventing their efficient use) would be isolated, and where appropriate (e.g. threatened species, NT endemics, key representative species etc), would be subjected to a greater range of potential germination cues. Germination success for a representative selection of the NT flora would be also be tested under a variety of diurnal temperature regimes and light and humidity conditions in an effort to ascertain optimum conditions for dormancy breaking. This information will have particular relevance to the consideration of future plant distributions in relation to threatening processes such as weed invasion, inappropriate levels of firing, and climatic change. 1.2 Dormancy type classification of Northern Territory seeds (Research Leader: Seed Curator/Biologist) Baskin and Baskin (2003) identify seed dormancy (in particular physiological dormancy) as a major problem for plant restoration ecology. An understanding of the types of dormancy present across the range of focal species is therefore regarded as an essential component of this proposed seed biology research. Accordingly, results from the germination research undertaken as part of this programme (see section 1.1) would 8 be used in development of a classification of the NT flora on the basis of dormancy type using the existing schemes of Nikolaeva (1969, 1977) and Baskin and Baskin (1998). This would involve the initial division of the NT flora according to whether seeds exhibit exogenous or endogenous dormancy. These groups would then be further divided on the basis of dormancy subtypes (e.g. physiological, morphological, physical etc) and levels within these subtypes. Further dormancy work would enable the identification of species with primary dormancy (dormancy acquired during seed development and maturation) or secondary dormancy capacity (where seeds re-enter dormancy when conditions are unfavourable for germination or survival success), as well as of those exhibiting conditional dormancy (where germination only occurs over a limited range of conditions). 1.3 Viability testing (Research Leader: Seed Curator/Biologist) The development of the most effective methodology for breaking seed dormancy also has direct ramifications for viability testing in that low germination success due to the application of inappropriate cues can lead to an underestimate of the viability of a batch and its subsequent inefficient use. In line with Kew Gardens’s procedure, viability tests using the most effective dormancy breaking mechanisms in concert with standard Tetrazolium tests would be carried out at the ASDP at the start of the storage process and every ten years thereafter by way of monitoring the efficacy of storage procedures. 1.4 Soil seed bank studies (Research Leaders: Albrecht, Nano, and University researchers – extension of ongoing research) While it is assumed that many of the NT’s plant species would have some form of a persistent soil seed bank, very little is currently known regarding the nature and dynamics of these in situ seed stores. Such information (especially as it relates to variation in seed bank longevity) is considered of vital importance for the management of fire sensitive species and of species confined to habitats worst affected by highly suppressive environmental weeds such as Cenchrus ciliaris. While it is possible to extrapolate to some degree from studies of the longevity of ex situ stores (see section 1.3), research should also focus on the behaviour of seeds in their natural setting given the potential for variable survival rates under differing conditions. It is proposed therefore, that research involving seed bank half-life experiments be undertaken to address these issues. 1.5 Classification of species according to their principal dispersal agent (PDA) (Research Leaders: Albrecht, Seed Curator/Biologist – ongoing project to enhance database) The fate of sown seeds used in conservation programmes is determined not only by environmental constraints on germination and establishment, but also by their mode of dispersal. Relationships between plants and animals are often most complex given that while at times seed removal may provide a reproductive advantage through dispersal and/or dormancy breaking, it may otherwise merely constitute seed theft. Likewise, the influence of wind and water on seed fate must also be taken into account in seed sowing programmes to ensure effective population establishment. It is intended therefore that this research would also focus on this aspect of seed biology in an effort to further facilitate the success of future seed use projects. Information relating to seed dispersal will be collated according to i) the mechanism that accounts for the majority of seed dispersal (the principal dispersal agent or PDA) and ii) 9 morphological features of the seed or diaspore that facilitate dispersal. The five categories used in the Seed Information Database (SID), would be adopted for the construction of the PDA database, these being: Animal (zoochory) Wind (anemochory) Water (hydrochory) Methods originating from the parent plant or diaspore (autochory) Unassisted (Barochory) Dispersal prevented (atelochory, antitelochory). The classification of dispersal-related morphological attributes used in the NT plant attribute database will be used in this research programme. These attribute classes are: Lacking features Wings/papery pods Awns/bristles/spines Boyancy Fleshy Elaiosomes/arils Adhesive All dispersal data compiled in this research programme will also be submitted to Kew for inclusion in SID. 1.6 Documentation of morphological seed features for a range of species (Research Leaders: Albrecht, Seed Curator/Biologist – ongoing project to enhance database) Existing gaps in the documentation of morphological seed features would be addressed by this research programme through the development of a seed image library and descriptive accounts. This data-set would then be merged with existing databases associated with the MSBP and made readily available for further seed research. The information would also be incorporated into taxonomic keys and plant descriptions which are currently being developed by the NT herbarium. 1.7 Documentation of Indigenous knowledge of seed biology and uses (Research Leaders: Nano, Traditional Ecologist, Park Anthropologist- ongoing) The NT Government is currently working towards the full-time employment of a traditional ecologist by way of ensuring that indigenous knowledge is properly incorporated into the MSBP research programme. Information relating to phenology, threatening processes, and medicinal and nutritional plant use will be captured in database form, and through proper channels of negotiation, would be made accessible to indigenous communities and the wider public. 1.8 Determination of plant functional groups (Research Leaders: Nano, Albrecht, and Kings Park – ongoing) Research effort would also be directed towards an investigation of plant attribute relationships with the ultimate aim of producing a functional group classification of 10 the NT flora. This is widely considered the best means of dealing with the seed response patterns of a large and diverse flora. While in the main, species would be scored against the characters used in the newly developed NT flora Ecological Attribute database, effort would also be made to ensure that the data are compatible with those provided in SID (e.g. species would be classified according to the Raunkiaer life form scheme). Ultimately this exercise would seek to relate seed biology characters such as dormancy type, seed size, and germination cues to life form, root/shoot allocations, regeneration strategy, habitat type, and to external environmental conditions and disturbance factors. Particular emphasis would be placed on the elucidation of patterns in relation to latitudinal gradients in the NT and climatic clines in arid Australia (the latter in collaboration with interstate colleagues). Suggested student projects: A. Seed dormancy, germination requirements and seed bank dynamics in a group of threatened central Australian acacias. Species involved This research programme covers a group of four threatened acacias, each with small, disjunct populations in arid Australia. The species are: Acacia latzii, Acacia peuce, Acacia pickardii and Acacia undoolyana (Leguminosae-Mimosoideae). All species are endemic to Australia and have a global and national conservation status of Vulnerable under the EPBC Act 1999. Threats The occurrence of a species as a series of small, disjunct populations presents a number of inherent threats to its long-term persistence because of the increased likelihood of extinction through stochastic disturbance events, inbreeding and minimal seed output. Additional threats in the case of these species relate to inappropriate fire regimes, weed invasion of critical habitat and pressure from introduced herbivores. Project justification and outline Detailed ecological research is a prerequisite for the proper management of each of these vulnerable species. This research project is designed to assist the formulation of species management strategies especially in relation to fire use and the amelioration of threatening processes such as weed invasion. Two avenues of research are proposed: 1. Seed dormancy and germination requirements. Given that populations of each of the species currently require some form of active management, it is imperative that dormancy-breaking requirements of soil-stored seed, especially in relation to fire, critical climatic factors, and resource availability be properly understood. So that this goal may be achieved, research carried out as part of this project should seek to identify cues and thresholds for seed dormancy and germination in each of these threatened species. 2. Soil seed bank studies. While it is assumed that each of these five threatened species would have some form of a persistent soil seed bank, very little is currently known regarding the nature and dynamics of these in situ seed stores. Such information (especially as it relates to variation in seed bank longevity) is considered of vital importance for the management of fire sensitive species and of species occurring in habitats affected by the highly suppressive environmental weed Cenchrus ciliaris. 11 B. Seed biology of species in Buffel Grass-threatened communities Project justification The introduced perennial grass Cenchrus ciliaris (Buffel Grass) is having a profound ecological impact on a range of plant communities in central Australia. Those communities at greatest risk occur along drainage corridors and on floodplains, and on rises, hills and ranges with high pH and/or fertile soils. In suitable habitat Buffel Grass can dominate the understorey, significantly impacting on native species diversity through: 1. competition for resources 2. rendering vegetation more flammable and at greater risk of local species extinctions due to hotter, more frequent fires, and 3. (possibly) allelopathy Small scale control of Buffel Grass at various locations near Alice Springs has shown that to varying degrees a viable soil-stored seed bank of native species still exists under dense Buffel Grass infestations. Gaining a better understanding of the relative persistence of seed banks, germination cues and heat thresholds for a range of species occurring in Buffel Grass threatened communities will assist in formulating management regimes for maximising native species persistence. Project outline Several avenues of research are proposed: 1. Soil seed bank studies. Investigate the abundance and distribution of viable and non-viable soil stored propagules in areas with differing Buffel Grass density. Identify those species that lack a soil-stored seed bank or have low levels of viable soil-stored seed that may require re-colonisation from adjacent Buffel-free areas. 2. Seed longevity studies. Using a seed burial methodology, investigate seed longevity for a range of species occurring in Buffel Grass-threatened communities. 3. Germination cues. Investigate germination cues for a range of species occurring in Buffel Grass-threatened communities. A dense Buffel Grass may be producing a shading effect; light will also be tested as a treatment. 4. Heat thresholds. As Buffel Grass fires are hotter than fires occurring in areas dominated by short-lived native grasses, the seed of some native species may not be able to tolerate temperatures generated in Buffel Grass fires. The issue of heat thresholds will be investigated by heating seeds in an oven at various temperatures and durations. Treated seed will be sown to determine mortality rates. 5. Allelopathy. Investigate effect of Buffel Grass leaf and root extracts on the germination of a range of species occurring in Buffel Grass-threatened communities. 6. Seedling emergence and early seedling survival. In the field, study the emergence and survival of seedlings from a range of species in areas with differing Buffel Grass density. Amount and timing of rainfall are factors that will be taken into account in the design of this aspect of research. Theme 2: The ex situ preservation of NT seed biodiversity The goal of the project is the development of an effective ex situ conservation program for plant biodiversity in the NT. This goal would be met through the establishment at the ASDP Seed Bank and, in parallel, at the Kew Seed Bank at RBG Kew of a verified and well-documented seed collection of wild native species from the Northern Territory. The proper management of both these collections such that they both remain effective, requires that research into seed storage behaviour i.e. seed longevity and viability loss, be undertaken. 12 Standard collecting and processing methods would be applied to both collections. There is the requirement therefore, that testing be carried out to assess seed storage behaviour under the differing conditions. For the duplicate Kew collection, an assessment of seed desiccation tolerance to 15% relative humidity and ability to withstand freezing to -20 0C (requirements for banking as part of the MSBP) would need to be conducted. This research would provide the basis for the classification of seeds as Orthodox, Recalcitrant or Intermediate as per the scheme used by Kew Gardens and would thereby isolate those species that cannot be stored using conventional seed banking techniques Other related research might also be carried out to assist the development of the most effective short term storage methodology for the ASDP collection. The development of an efficient viability monitoring methodology would be useful for the management of the ASDP collection. More detailed storage experimentation might additionally be undertaken as part of this research programme. These could involve drying seeds down to different moisture contents, storing them at various temperatures and monitoring viability and longevity. In addition to being of direct relevance to the management of the banked seeds, this information, through its inclusion in SID, would also serve to direct further seed science studies. Seedlings of threatened species produced during standard germination tests and research projects could be planted out at the ASDP and GBDBG as part of their exsitu conservation program. 1.3.5. Seed collection costs Kew will finance field costs associated with NT Government technical staff in accordance with the budget set out below (Table 2). 1.4 PROJECT CONTEXT AND RATIONALE The 2002 delegates at the Sixth meeting of the Conference of the Parties to the Convention on Biological Diversity (CBD) agreed to a Global Strategy for Plant Conservation (GSPC). The strategy is binding for all signatories to the CBD, including Australia. The GSPC comprises sixteen targets to be achieved by 2010, with each target specifically designed to guide and measure the conservation of threatened plant species and ecosystems. The Project is directly consistent with Target 8 of the GSPC: “60 per cent of threatened plant species in accessible ex situ collections, preferably in the country of origin, and 10 per cent of them included in recovery and restoration programs”. Storage of seed (or seed banking) is arguably the most efficient and effective means of ex situ plant conservation, and as such, seed banking is recognised as a vital component of the integrated conservation strategies designed to counter the loss of plant genetic diversity within Australia (Touchell et al., 1997). The Partnership provides the NT Government with an opportunity to enhance its capacity to effectively conserve the Northern Territory’s threatened and priority plant species, as 13 well as being at the forefront of activities within Australia to contribute to the ex situ conservation targets set by the GSPC. The Environment Protection and Biodiversity Conservation Act 1999 was ratified to enhance Australia’s capacity to conserve its biodiversity. The Project will contribute directly to the requirements of the Act as described in Section 3, Subsection 2e: “Protecting native species and in particular prevent the extinction, and promote the recovery of threatened species…” and “…promotion of off-reserve conservation measures”. The Territory Parks and Wildlife Conservation Act 2000 supports this at a jurisdiction level, with specific reference to Sections 28, 29, 30 that classify the Northern Territory’s endangered, vulnerable and rare plant species. The Project has also been closely aligned with one of the primary goals in the National Strategy for the Conservation of Australia’s Biological Diversity. That is: “There is a pressing need to strengthen the current activities and improve policies, practices and attitudes to achieve conservation and sustainable use of biological diversity.” More specifically the Project outputs and activities directly address the actions described in Objective 1.9 (ex situ conservation) of the National Strategy for the Conservation of Australia’s Biological Diversity: “To complement in situ measures, establish and maintain facilities for ex situ research into and conservation of plants, animals and micro-organisms, particularly those identified by action taken in accordance with Objective 1.1”. Furthermore, to facilitate Objective 1.2 (bioregional planning and management) of the National Strategy for the Conservation of Australia’s Biological Diversity: “Manage biological diversity on a regional basis, using natural boundaries to facilitate the integration of conservation and production-oriented management”, Finally, as a signatory to the CBD, Australia recognises its responsibility to develop frameworks for access to and utilisation of genetic resources. In response to this, the Nationally Consistent Approach for Access to and the Utilisation of Australia’s Native Genetic and Biochemical Resources was developed and endorsed in 2002. The Nationally Consistent Approach reiterates Australia’s commitment to work with stakeholders to provide ecologically sustainable access to biota. The Project has been developed to be consistent with the following Objectives of the Nationally Consistent Approach: 14 “facilitate continued access for non-commercial scientific research, particularly taxonomic research”, and “ensure that the collection of native biological material is undertaken in an ecologically sustainable and ethical way”. 1.5 TARGETS AND COLLECTION CRITERIA The landscape of the NT encompasses a great range of habitat types. Rainfall seasonality within the region is related to latitude, with areas north of Alice Springs receiving summer rainfall and areas south of Alice Springs receiving both winter and summer rainfall. The occurrence of winter and summer rainfall within the arid region has allowed the development of a flora that includes arid-temperate and arid-tropical elements. The climate of the Top End is Monsoonal with all rainfall occurring between October and May. The NT flora contains some 4200 taxa, 635 of which are endemic. Included are representatives of as many as 198 indigenous plant families, reflecting the wide range of habitat types and climatic diversity throughout the region. Families with the greatest representation include Poaceae (628 spp.), Cyperaceae (307 spp.), Leguminosae (including subfamilies Caesalpinioideae 71 spp., Papilionoideae 444 spp., and Mimosoideae 273 spp.), Myrtaceae (248 spp.) and Asteraceae (248 spp.). The NT flora is noteworthy in that it is largely intact with no known extinctions having taken place in recent times. This is in large part due to the fact that unlike many other regions throughout Australia (e.g. the West Australian wheat belt), the NT has not experienced large-scale habitat loss through land clearing. The situation therefore, offers somewhat of a unique opportunity to sample an intact flora prior to any significant loss of genetic variability. While the flora of the NT is currently intact, various threatening processes are in operation, which in the long term, may result in plant extinctions. Pressures on the flora arise through habitat degradation as a result of grazing, weed infestation and inappropriate fire regimes. Some horticultural development has also recently been established – the consequences of which are currently unknown. Given this likelihood of future degradation of the NT’s flora, we regard that this is an extremely opportune time for seed research and conservation. 1.5.1 Targets The flora of the Northern Territories is comprised of approximately 4200 vascular taxa. Presently, 73 taxa are listed as threatened (critically endangered, endangered or vulnerable) under Commonwealth and / or Territory Legislation (Table 1), 694 are poorly known, with a further 404 considered to be rare or at risk in the wild if no actions are taken to secure their future. Each year it is proposed to undertake collections from at least 92 species, totalling a minimum of 550 species new to the collections at the Kew Seed Bank by the end of the Project. During the early stages of the Project an annotated target species collection list will be compiled. 15 1.5.2. Collection criteria Northern Territory plant species have been tentatively prioritized for seed collection and research according to the following six criteria 1. Endemic species Six hundred and thirty-five species are endemic to the NT. Approximately 87% of the NT endemics occur in the northern half of the Territory. As these species are unique to the NT they are an obvious focus for this project. 2. Threatened, near threatened and data deficient species The flora of the NT is characterised by a large number (476) of threatened (critically endangered, endangered, and vulnerable) and rare plant species (near threatened). Management of this group of species is particularly difficult, not least because most occur as small disjunct populations, but also because so little is known with regard to their habitat and life history requirements. It is expected that information relating to the seed biology of many of these threatened species will therefore greatly enhance appropriate management practice. Seventy-three NT species are listed as threatened according to IUCN criteria mainly in recognition of their vulnerability as small, isolated populations with restricted ranges (Table 1). Many of these species (43%) are endemic to the NT and as such they require the focus of local conservation bodies such as NT Government. Species recovery plans are currently being developed for some of the NT’s threatened flora and information generated from the joint NT Government/MSB project will contribute to the implementation of recovery actions. As many as 680 NT species are classified as ‘data deficient’, reflecting the lack of records and knowledge with regard to their distribution, biology and conservation status. It is expected that substantial amounts of information will be obtained for populations of many of these species as a ‘spin off’ from seed collecting trips as part of the joint NT Government/MSB project. 3. Species restricted to habitats where the threat of weed invasion and other forms of land degradation are greatest. Certain species, though not presently regarded as threatened, are currently subject to pressures, which will ultimately lessen their chances of persistence in the wild. Of greatest concern are those species that are restricted to habitats (e.g. alluvial flood plains) that are currently worst affected by the invasion of the highly competitive perennial grass species Cenchrus ciliaris. Evidence suggests that this exotic species successfully suppresses the emergence of less competitive native species. Species with short-lived seed banks (many of which would exhibit physiological dormancy) will require the greatest research focus. 4. Representative range of functional traits Research work should take account of the range of functional traits present in the NT flora. The selection of study species should therefore reflect the range of seed sizes, taxonomic groups, growth-forms, life histories and dispersal modes. Information obtained from this research will be fed into an existing ecological traits database 16 developed by the NT Herbarium staff. Data generated will ultimately allow for the creation of a functional group classification of the NT’s flora. This classification will in turn facilitate predictions for distributional shifts on local and regional scales in relation to threatening processes such as inappropriate fire and grazing regimes, weed invasion, and climate change. The determination of group-level factors such as germination cues and seed longevity will also be of value in mine site rehabilitation work and horticultural pursuits. 5. Poorly reserved species The widely acknowledged bias towards the inclusion of unproductive mountainous country in the Northern Territory parks estate means that many of the NT’s plant species are currently unreserved. This is of particular concern given the lack of proper fire and weed management in many areas outside of the reserve system. The proposed NT Government/MSB project would therefore provide an ideal opportunity for the ex situ conservation of many species in this category. 6. Species of economic / cultural importance to indigenous Australians Plants of economic and cultural value to Aboriginal people are well documented and a strong plant use knowledge base still exists within the indigenous communities situated throughout the NT. This provides for a good opportunity to identify and conserve species that are of importance to Aboriginal people that do not otherwise meet any of the priority criteria outlined above. Because of their economic value, certain species such as Quandong (Santalum acuminatum) are subject to considerable harvest pressure and as such may warrant particular research and conservation attention. 1.6 PROJECT ADMINISTRATION The Project shall be co-ordinated in the Northern Territory by the NT Government Regional Manager and by one of the International Program Co-ordinators for Australia at the Seed Conservation Department, Kew. Funds will be disbursed annually to NT Government via electronic transfer in Australian dollars to a designated account on the basis of annual plans and reports drawn up between the Partners. Formal reporting will be on an annual basis. 1.7 PROJECT RESOURCES To undertake the proposed activities, the Partners have agreed a detailed budget, set in Table 2. NT Government will provide appropriate administrative and managerial support to successfully implement the project. Kew will provide appropriate administrative support for the co-ordination of seed duplication, project reporting, financial disbursement and the logistics of visits by NT Government staff to Kew in the United Kingdom. 17 1.8 ACCESS TO NORTHERN RESOURCES - PIC TERRITORY PLANT GENETIC The Northern Territory Government of Australia represented by the Minister for Parks and Wildlife, and the Board of Trustees of the Royal Botanic Gardens, Kew have entered into an Access and Benefit-Sharing Agreement. Through this agreement, the Northern Territory Government of Australia, inter alia, gives its Prior Informed Consent (PIC) and approval to the Probect in accordance with Article 15 of the CBD. 1.9 REFERENCES Baskin, C.C. and Baskin, J.M. (1998). Seeds: Ecology, Biogeography, and Evolution of Dormancy and Germination. Academic Press. 666 pp. Baskin, C.C. and Baskin, J.M. (2003). Classification, Biogeography, and Phylogenetic Relationships of Seed Dormancy. In: Smith, R.D. et al. (eds.) Seed Conservation – turning science into practice. Royal Botanic Gardens, Kew. Pp. 517-544. Nikolaeva, M. (1969). Physiology of deep dormancy in seeds. Translated from the Russian by Z. Shapiro. Published for the USA National science Foundation by the Israel Program of Scientific Translations. Jerusalem, Israel, iv + 220 pp. Nikolaeva, M. (1977). Factors controlling the seed dormancy pattern. In: Khan, A.A. (ed.) The physiology and biochemistry of seed dormancy and germination. North Holland, Amsterdam, The Netherlands. Pp. 51-74. Touchell, D.H., Richardson, M. and Dixon, K.W. (1997). Germplasm Conservation Guidelines for Australia. Australian Network for Plant Conservation, Canberra. Convention on Biological Diversity, 1992. Environmental Protection and Biodiversity Conservation Act 1999 (Cwlth). Global Strategy for Plant Conservation, 2002. Nationally Consistent Approach for Access to and the Utilisation of Australia’s Native Genetic and Biochemical Resources, 2002. Territory Parks and Wildlife Conservation Act 2000. National Strategy for the Conservation of Australia’s Biological Diversity. Department of the Environment, Sport and Territories, 1996. 18 Table 1. The threatened Northern Territory Flora including endemic and recalcitrant seed species (CR = critically endangered; V = vulnerable; EN = endangered). Bolded taxa are non-flowering species. Classification Endemic Recalcitrant Taxon ELAEOCARPACEAE Elaeocarpus miegei Weibe CR Endangered ANNONACEAE Xylopia D30127 Melville Island EN ARACEAE Typhonium jonesii A.Hay EN ARACEAE Typhonium mirabile (A.Hay) A.Hay EN ARACEAE Typhonium taylori A.Hay EN ARECACEAE Ptychosperma macarthurii (H.Wendl. ex Veitch) H.Wendl. ex EN Hook.f. BURMANNIACEAE Burmannia D61177 Bathurst Island EN CLUSIACEAE Garcinia warrenii F.Muell. EN CYPERACEAE Baumea arthrophylla (Nees) Boeck. EN CYPERACEAE Bolboschoenus caldwellii (V.Cook.) Sojak EN ELAEOCARPACEAE Dubouzetia australiensis Coode EN HYMENOPHYLLACEAE Cephalomanes obscurum (Blume) K.Iwats. EN LAURACEAE Cryptocarya hypospodia F.Muell. EN LENTIBULARIACEAE Utricularia dunstaniae F.E.Lloyd EN LENTIBULARIACEAE Utricularia subulata L. EN MIMOSACEAE (Leguminosae – Mimosoideae) Acacia peuce F.Muell. EN ORCHIDACEAE Habenaria rumphii Lindl. EN ORCHIDACEAE Nervilia plicata (Andrews) Schltr. EN RUBIACEAE Tarennoidea wallichii (Hook.f.) Tirveng. & Sastre EN SAPINDACEAE Toechima D55598 East Alligator EN STERCULIACEAE Helicteres D2164 Glenluckie Ck EN Vulnerable ADIANTACEAE Adiantum capillus-veneris L. V ANNONACEAE Mitrella D24710 Melville Is. V APIACEAE Actinotus schwarzii F.Muell. V APIACEAE Platysace saxatilis Keighery V ARECACEAE Livistona mariae F.Muell. subsp. mariae V ASCLEPIADACEAE Hoya australis R.Br. ex J.Traill subsp. oramicola V P.I.Forst. & Liddle ASTERACEAE Minuria tridens (D.A.Cooke) Lander V ASTERACEAE Olearia macdonnellensis D.A.Cooke V CONVOLVULACEAE Ipomoea A83192 Stirling V CUCURBITACEAE Mukia A90788 Tobermorey Station V CYCADACEAE Cycas armstrongii Miq. V CYPERACEAE Eleocharis papillosa Latz V CYPERACEAE Mapania macrocephala (Gaudich) K.Schum. in Warb. V DICHAPETALACEAE Dichapetalum timoriense (DC.) Boerl. V EUPHORBIACEAE Ricinocarpos gloria-medii J.H.Willis V FABACEAE Indigofera schultziana F.Muell. V GLEICHENIACEAE Gleichenia microphylla R.Br. V GLEICHENIACEAE Sticherus flabellatus (R.Br.) St.John var. compactus V (C.T.White & Goy) D.A.Sm. HERNANDIACEAE Hernandia nymphaeifolia (C.Presl.) Kubitzki V LAMIACEAE Wrixonia schultzii (F.Muell. ex Tate) Carrick V LAURACEAE Endiandra limnophila B.Hyland V LENTIBULARIACEAE Utricularia singeriana F.Muell. V 19 Y Y? Y Y Y Y ? ? ? Y Y Y Y ? Y Y? Y Y Y Y? Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Table 1 (continued). The threatened Northern Territory Flora including endemic and recalcitrant seed species (CR = critically endangered; V = vulnerable; EN = endangered). Bolded taxa are non-flowering species. Taxon MALVACEAE Alyogyne cravenii Fryxell MALVACEAE Hibiscus brennanii Craven MARATTIACEAE Angiopteris evecta (G.Forst.) Hoffm. MELASTOMATACEAE Pternandra coerulescens Jack MIMOSACEAE (Leguminosae – Mimosoideae) Acacia latzii Maslin MIMOSACEAE (Leguminosae – Mimosoideae) Acacia pickardii Tindale MIMOSACEAE (Leguminosae – Mimosoideae) Acacia praetermissa Tindale MIMOSACEAE (Leguminosae – Mimosoideae) Acacia undoolyana G.J.Leach MYOPORACEAE Eremophila A48866 Rainbow Valley MYRTACEAE Lithomyrtus linariifolia N.Snow & Guymer MYRTACEAE Thryptomene hexandra C.T.White ORCHIDACEAE Calochilus caeruleus L.O.Williams ORCHIDACEAE Luisia teretifolia Gaudich. ORCHIDACEAE Malaxis latifolia Sm. ORCHIDACEAE Malaxis marsupichila Upton ORCHIDACEAE Thrixspermum congestum (Baill.) Dockrill ORCHIDACEAE Zeuxine oblonga R.S.Rogers & C.T.White PANDANACEAE Freycinetia excelsa F.Muell. PANDANACEAE Freycinetia percostata Merr. & L.M.Perry POACEAE Triodia D62418 Matt Wilson POACEAE Triodia fitzgeraldii N.T.Burb. PONTEDERIACEAE Monochoria hastata (L.) Solms PROTEACEAE Grevillea longicuspis McGill. PROTEACEAE Grevillea versicolor McGill. RUTACEAE Boronia quadrilata Duretto RUTACEAE Boronia tolerans Duretto RUTACEAE Boronia viridiflora Duretto SANTALACEAE Dendromyza reinwardtiana (Blume ex Kunth) Danser TILIACEAE Schoutenia ovata Korth. ZAMIACEAE Macrozamia macdonnellii (F.Muell. ex Miq.) A.DC. 20 Classification Endemic Recalcitrant V V V V V V V V V V V V V V V V V V V V V V V V V V V V V V Y Y Y Y Y Y Y Y Y Y Y Y Y Y ? ? ? Y Y Table 2. Budget with Annex 1 of the ABSA between Northern Territories and RBG Kew 2004-05 to 2009-10 (MSB cost code SC2.27 - C10311) I - Budget in Australian $$ Activity 1 1.1 1.2 1.3 1.4 2004/05 2005/06 2006/07 2007/08 2008/09 2009/10 Total in AUS $ 66500 14500 7250 68000 14500 7250 70000 14500 7250 72500 16000 7250 75000 16000 7250 77000 16000 7250 429000 91500 43500 8000 8000 8000 8000 8000 8000 48000 96250 97750 99750 103750 106250 108250 612000 2500 2500 2500 2500 2500 2500 15000 Sub total 2500 2500 2500 2500 2500 2500 15000 Training / Research visits UK - course UK - individual (WTMB) AUS interstate visits Post-graduate fees (Project contribution) 3650 2500 5000 5000 2500 5500 3650 3650 2500 6000 5000 2500 6500 3650 3650 2500 7000 5000 2500 7500 7300 25950 15000 37500 Sub total 11150 13000 15800 14000 16800 15000 85750 10000 10000 1900 21900 10000 10000 1900 21900 2000 2000 5000 2000 2000 5000 18000 121900 125250 124950 122250 127550 130750 752650 Collection programme Project staff DIPE Field allowance 2 week collection mission for 2 DIPE and 1 UK staff Employment of Traditional Owners Sub total 2 2.1 3 3.1 3.2 3.3 3.4 4 4.1 Research and data management Consumables, books, software, GIS Equipment bought in Australia DIPE (spread over 2-3 years) Sub total 5 5.1 Administration Consultant / Permit fees Totals cost in NT II - budget in UK ££ Total in UK £ 5 5.1 Equipment bought in UK Zig-Zag aspirator (incl. shipment) 8000 6 6.1 6.2 SCD support (SC2.27 general) T & S of SCD staff (MvS) T & S of SCD staff (other) 1000 1000 1000 1000 1000 1000 1000 1000 1000 1000 1000 1000 6000 6000 10000 2000 2000 2000 2000 2000 20000 Subtotal - costs in UK 1.1 3.1 3.2 4.1 8000 NOTES As per info from NT for a P2 level professional co-ordinator; includes 3% annual increase. 2 week MSB course @ £1,500 all-in. WTMB visit 4 weeks @ £80 operating + £165 lodging/subsistence per week + ticket. To be supplied mainly during first two years. Subject to advice from Keith Manger at MSB Equipment list follows discussions in November 2003. Expected to be bought in Australia: eRh Rotronic, 2 Freezers, 2 small incubators; total Aus $ 21,900 Expected to be bought in UK: zig-zag aspirator blower @ £8K 21 ANNEX 2 PRO FORMA NOTIFICATION OF TRANSFER The following Material is transferred between the Northern Territory of Australia represented by The Department for Infrastructure, Planning and Environment, P.O. Box 3146, Parliament House, Darwin NT 0801, Australia (hereafter “the NT Government”), and The Board of Trustees of the Royal Botanic Gardens, Kew, Richmond, Surrey, TW9 3AE United Kingdom (hereafter "RBG Kew") in accordance with the terms and conditions of the Access and Benefit-Sharing Agreement between the NT Government and RBG Kew, dated …………………………………….. 2004. By signing this Notification of Transfer, the NT Government hereby confirms that, to the best of its knowledge, the Material has been collected and is being transferred to RBG Kew in accordance with all applicable laws and regulations, permits, prior informed consents and/or licenses. DATE COLLECTED SEED COLLECTION No. FAMILY GENUS or SPECIES SIGNED BY: No. OF HERBARIUM DUPLICATES (IF ANY) DATE: For and on behalf of the Northern Territory of Australia Name: Title: SIGNED BY: DATE: For and on behalf of The Board of Trustees of the Royal Botanic Gardens, Kew, United Kingdom Name: Title: A copy of this document signed by the NT Government will be forwarded to RBG Kew with each seed consignment. Upon receipt of the seed and any herbarium specimens, RGB Kew will countersign this copy and return it to the NT Government as acknowledgement of receipt under the terms of the Access and Benefit-Sharing Agreement. 22