Monsoon Vine Thickets on the Coastal Sand Dunes of the Dampier Peninsula
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INTERIM RECOVERY PLAN NO. 383 Monsoon vine thickets on the coastal sand dunes of the Dampier Peninsula 2018 – 2023 February 2018 1 Foreword Interim Recovery Plans (IRPs) are developed within the framework laid down in Department of Parks and Wildlife (now Biodiversity, Conservation and Attractions) Corporate Policy Statement No. 35 (DPaW 2015a) and Corporate Guideline No. 35 (DPaW 2015b). Corporate Policy Statement No. 35 states that the department will prepare recovery plans or conservation advices that document the conservation requirements, recovery or management actions and information requirements of threatened species and ecological communities (TECs), identify threatening processes impacting threatened species or TECs, and implement programs to mitigate the threats. Interim recovery plans outline the recovery actions that are required to urgently address those threatening processes most affecting the ongoing survival of threatened species or ecological communities, and begin the recovery process. While the Department of Biodiversity, Conservation and Attractions (DBCA) is committed to ensuring that threatened ecological communities are conserved through the preparation and implementation of Recovery Plans (RPs) or IRPs, there is no statutory requirement to implement recovery actions identified in this plan. This plan identifies responsibilities for specific actions and largely refers to the department initiating and guiding actions. However, the implementation of recovery actions by the Department of Biodiversity, Conservation and Attractions or any other organisation will be done within the context of regional and statewide priorities and technical and resource capacity. The provision of funds identified in this plan is dependent on budgetary and other constraints affecting the Department of Biodiversity, Conservation and Attractions, as well as the need to address other priorities. This plan was given regional approval on 13 June 2017 and was approved by the Executive Director of Science and Conservation on 20 February 2018. This plan will operate from February 2018 to January 2023 but will remain in force until withdrawn or replaced following a review of the need for further recovery actions, and whether a revised plan needs to be prepared. Information in this IRP was accurate at August 2017. ACKNOWLEDGMENTS This Interim Recovery Plan was prepared by Valerie English. Cover photograph by Valerie English. The following people provided valuable advice and assistance in the preparation of this Interim Recovery Plan: Ms Louise Beames Environs Kimberley Mrs Ayesha Moss Environs Kimberley Dr Malcolm Lindsay Environs Kimberley Mr Dave Dureau Broome Botanical Society Mr Tim Willing Broome Botanical Society Mr Phil Docherty Society for Kimberley Indigenous Plants and Animals Bardi Jawi Rangers Nyul Nyul Rangers Mr Troy Sinclair Previously Biodiversity, Conservation and Attractions, Kimberley Region Ms Sharon Ferguson Previously Biodiversity, Conservation and Attractions, West Kimberley District Mr Charla Clements Kimberley Land Council Ms Tracy Sonneman Biodiversity, Conservation and Attractions, West Kimberley District Mr Todd Quartermaine Previously Kimberley Land Council 2 Mr Kevin George Kimberley Land Council Dr Ryan Vogwill Previously Biodiversity, Conservation and Attractions, Kensington Mrs Erica Shedley Previously Biodiversity, Conservation and Attractions, Kimberley Region Mr Ben Ansell Previously Biodiversity, Conservation and Attractions, West Kimberley District Ms Bel Catcheside Previously Biodiversity, Conservation and Attractions, West Kimberley District Ms Nina Stick Previously Biodiversity, Conservation and Attractions, Kensington CITATION This Interim Recovery Plan should be cited as: Department of Biodiversity, Conservation and Attractions (2018). Interim Recovery Plan 2018-2023 for the Monsoon vine thickets on the coastal sand dunes of Dampier Peninsula. Interim Recovery Plan No. 383. DBCA, Perth. 3 CONTENTS Summary ....................................................................................................................................................... 5 Background ................................................................................................................................................... 8 History, defining characteristics of the community, and conservation significance ...................................... 8 Biological and ecological characteristics ..................................................................................................................... 11 Geology and Hydrology ...................................................................................................................................................... 14 Threatening processes ......................................................................................................................................................... 15 Evaluation of the Plan's Performance ............................................................................................................................ 21 Conservation status .............................................................................................................................................................. 21 IRP objective and criteria ......................................................................................................................... 21 Habitat critical to the survival of the community, and important occurrences ..................................... 22 Benefits to other species/ecological communities ................................................................................................... 23 International obligations .................................................................................................................................................... 24 Role and interests of Aboriginal people ....................................................................................................................... 24 Recovery Actions ....................................................................................................................................... 24 Table 1: Summary of costs for each recovery actions ........................................................................ 41 References .................................................................................................................................................. 42 Appendix 1: Location and size of occurrences ..................................................................................... 45 Appendix 2: Threats .................................................................................................................................. 52 Appendix 3: Survey currency and aboriginal sites ............................................................................... 61 Appendix 4: Location of occurrences ..................................................................................................... 65 Appendix 5: Key to occurrence names................................................................................................... 66 Appendix 6: Vascular plants in occurrences ......................................................................................... 69 Appendix 7: Status of flora taxa ............................................................................................................. 72 4 SUMMARY Name: Monsoon vine thickets on the coastal sand dunes of Dampier Peninsula (hereafter termed ‘vine thickets’). Description The vine thickets of the Dampier Peninsula are a very distinctive type of rainforest in the Kimberley region. This type of vine thicket is confined to the Peninsula between Broome and Derby, along with the coastal dune formations on which it occurs. The community occurs as semi-deciduous vine thicket on leeward slopes of coastal sand dunes on the Dampier Peninsula. Many occurrences include scattered discrete vine thicket patches located in swales throughout the dune system and are likely to be indicators of the movement of the dune system over time. The community generally occurs on deep dune sands with a dark superficial grey organic layer, with a surface layer of moist leaf litter, but it can occur on other substrates due to other influences. Vine thickets occur as discrete areas of dense vegetation and can occur as a stand of a few trees or as larger patches. The 90 known occurrences vary in size from about 0.3 ha up to 507 ha, with a mean size of about 33 ha. They can occur as clumps or narrow linear stands (Black et al. 2010). There are about 2,887 ha of the vine thickets currently mapped on the Department of Biodiversity, Conservation and Attractions Threatened Ecological Community (TEC) Database. The vine thicket community contains many plants with fleshy fruits that provide important food sources for fauna such as agile wallabies, bats, bower-birds and fruit-doves. They are also an important traditional resource for Indigenous people. DBCA Region: Kimberley DBCA District: West Kimberley Local Government: Shire of Broome IBRA Subregions: Dampierland DL1 Fitzroy Trough subregion and DL2 Pindanland subregion Current Status Ranked as Vulnerable in Western Australia in 2001, and ranked Endangered in February 2013 under the Commonwealth Environment Protection and Biodiversity Conservation Act 1999 (EPBC Act). Habitat Characteristics This vine thicket community is largely restricted to the east and west coastlines of the Dampier Peninsula