Grey-headed Flying-fox Management Strategy for the Lower Hunter Grey-headed Flying-fox



Download 1.72 Mb.
Page2/22
Date19.10.2016
Size1.72 Mb.
#4690
1   2   3   4   5   6   7   8   9   ...   22

Illustrations



Tables



Plates



Appendices

This management strategy for the Grey-headed Flying-fox (GHFF; Pteropus poliocephalus) in the Lower Hunter is part of the Australian Government’s Sustainable Regional Development (SRD) program, facilitated under the Environment Protection and Biodiversity Conservation Act 1999 (EPBC Act) to protect matters of national environmental significance (MNES) where high demand for growth and development is expected (Section 1). This strategy aims to identify how to improve or maintain habitat and ecological processes critical to GHFFs and how future development and growth can proceed without affecting current and future use of the Lower Hunter by foraging and roosting GHFFs. The GHFF is listed as a threatened species (Section 2) under the federal EPBC Act and the NSW State Threatened Species Conservation Act 1995. Due to their behavioural ecology and mobility, all GHFFs form one population that encompasses their entire distribution with an array of camps scattered over this range, some large and permanent, others small and temporary (Section 4). These aspects make the GHFF a complex species to manage. The Lower Hunter is a rich and diverse area (Section 3), important to the GHFF for its Spotted Gum forests and other foraging areas (Section 6). It is also an area where the species tends to increase in numbers over warmer months, a period coinciding with the birth and raising of young. As such, the Lower Hunter is an important area for this species.


The Lower Hunter supports 20 known camps of the GHFF (Section 5), although it is likely that additional camps occur, particularly within the western parts of the Cessnock Local Government Area (LGA). Seven GHFF camps are identified as critical to the survival (CTS) of the GHFF in the Lower Hunter: Millfield, Martinsville, Morisset, Blackbutt Reserve, Anna Bay, Medowie and Tocal. Six camps were clearly not CTS of the GHFF: Black Hill, Belmont, Glenrock, Hannan Street, Italia Road and Raymond Terrace. Three camps are in remote areas and limited information is available to determine their importance to the GHFF: Bobs Farm, Fullerton Cove and Snapper Island. Four other sites are newly established camps for which patterns of use have not yet been established: East Cessnock, Lorn, Throsby and Blackalls Park.
The GHFF readily roosts in urban areas, resulting in conflict with humans. Most of the areas identified for future development in the Lower Hunter Regional Strategy (LHRS) are further than 300 m from the nearest known GHFF camp (except land planned for residential development south of the East Cessnock camp). Unfortunately, it is not possible to predict where flying-foxes may establish new camps, however we assessed current and potential site attributes for proposed LHRS development sites and identified areas that could potentially meet criteria for a flying-fox camp site (Section 7). Alongside the risk of creating a new conflict site at East Cessnock, there is potential for GHFF camps to establish adjacent to or within many of the targeted areas for future urban expansion. A significant portion of the proposed LHRS development areas also contain high conservation value GHFF foraging habitat (89%; Section 7). Clearing for development outside of LHRS identified areas could further reduce the ability of GHFFs to persist in the Lower Hunter, as the volume of foraging habitat is much greater in these areas than within LHRS identified development sites
Opportunities exist in the Lower Hunter to manage the impact of development on GHFFs (Section 8). Areas surrounded by high quality foraging habitat and containing favourable landscape roost site features (e.g. presence of rivers and coastal floodplains), could potentially be rehabilitated where current vegetation cannot support roosting GHFF. Such areas occur in the Cessnock and Maitland LGAs and also within the western portion of Port Stephens LGA. The increased availability of roosting habitat in these areas may relieve pressure on other nearby camps and possibly increase the options available for the management of contentious urban camps such as Lorn. 7,233 ha of cleared land suitable for foraging habitat restoration were identified where the restoration of forested habitat would be consistent with the primary land use aims. Most of the suitable area occurs to the north-west of Hexham Swamp Nature Reserve. Extensive, but fragmented, areas are also scattered throughout the Lake Macquarie LGA with moderate amounts of suitable sites in Port Stephens and Maitland LGA. Opportunities for offsetting the loss of habitat through conservation of existing high quality unprotected GHFF foraging habitat occur within 103,124 ha, occurring across all five Lower Hunter LGAs.
A range of recommended management actions are presented in Section 9 to support the maintenance of habitat for the GHFF in the Lower Hunter.
Overview

Table 1.1The Grey-headed Flying-fox and the Lower Hunter

The Grey-headed Flying-fox (GHFF; Pteropus poliocephalus) is listed as a matter of national environmental significance (MNES) under the federal Environment Protection and Biodiversity Conservation Act 1999 (EPBC Act). There are significant challenges for the conservation and management of this species. This nomadic bat follows temporal and spatial changes in its food supply across eastern Australia. A highly social animal, it roosts in aggregations which, at times, accommodate vast numbers of individuals which operate autonomously, determining individually their movements and camping sites. Strong community opposition to urban GHFF camps competes with the conservation needs of the species. Alongside other aspects of the ecology of the GHFF, these characteristics confound its management, complicating predictions of development impacts and habitat removal and the setting of priorities for habitat conservation.
The Lower Hunter is located in central eastern NSW and is diverse in its natural and social environs. Vast coastal rivers and valley floodplains adjoin the Pacific Ocean and accommodate cities and agricultural pursuits. Upland regions to the south contain patches of extensive vegetated lands, supporting agriculture, grazing and timber production. To the north, upland coastal valleys have been more extensively cleared. Conservation areas are increasing through establishment of new reserves and additions to existing reserves. Together with ecotourism opportunities, lands set aside for conservation occur across all parts of the Lower Hunter Valley landscape. Internationally recognised wetlands occur within the Hunter River estuary and its associated swamps, forming significant areas for breeding migratory species, whilst other areas support a diverse range of threatened species and endangered ecological communities (DoP 2006).
The Lower Hunter is also an area of expected high growth and development over the next 25 years (DoP 2006). Already the sixth largest urban area in Australia, further growth is expected as people are drawn to the area for lifestyle and work opportunities (DoP 2006).

Table 1.2Sustainable Regional Development Program

This management strategy for the GHFF in the Lower Hunter has been prepared as part of the Australian Government’s Sustainable Regional Development (SRD) program. This program is facilitated under the EPBC Act to protect MNES in selected regions where high demand for growth and development is expected. This four-year program started mid-2011 and is one of the measures under Sustainable Australia – Sustainable Communities: A Population Strategy for Australia (http://www.environment.gov.au/sustainability/regional-development/index.html). In essence, the Australian Government recognises the need to proactively manage growth and development to ensure sustainability across all sectors – environmental, social and economic. Programs are being funded to support holistic approaches to achieving long-term sustainability in regional areas with current or projected high levels of growth. The Lower Hunter is the first region to benefit from SRD program. Assessments of MNES in the Lower Hunter include this study and another similar study for the Swift Parrot and Regent Honeyeater. Further details about the program can be found on the Australian Government’s Lower Hunter Regional Sustainability Planning and Strategic Assessment webpage (http://www.environment.gov.au/sustainability/regional-development/lower-hunter/index.html).


The GHFF is ideally suited to landscape-based assessments underpinned by fine-scale and locally-based knowledge of habitat uses, and provides an excellent subject for a management strategy under the SRD program.

Table 1.3Purpose and Structure of this Study

The purpose of this study is to:


  • identify habitat critical for the survival of the GHFF in the Lower Hunter;

  • analyse the current status of this habitat within the Lower Hunter and assess the likely impacts of development on the GHFF;

  • identify areas of GHFF habitat that are not adequately protected;

  • identify strategic areas for protection, enhancement or restoration;

  • identify situations for biodiversity offsetting that would benefit the GHFF; and

  • identify other management strategies for the protection of the GHFF and its habitat within the Lower Hunter.

Broadly speaking, this strategy aims to identify how to improve or maintain habitat and ecological processes critical to the GHFF, and how development and growth can proceed without affecting the ongoing and future use of the Lower Hunter by foraging and roosting GHFFs.


Section 2 provides the legislative context for the management of the GHFF in the Lower Hunter. Section 6 describes the Lower Hunter, while Section 9 describes the GHFF generally and as it occurs in the Lower Hunter.
Sections 11 and 14 describe the roosting and foraging (respectively) habitat of the GHFF at a local level and identify environmental features critical to the survival of the GHFF within the Lower Hunter. Knowledge of the foraging and roosting behaviour of the GHFF in the Lower Hunter is identified through synthesis of contemporary and historical knowledge held by all levels of government, non-government groups, research bodies and individuals.
Section 16 details the current status of GHFF habitat in the Lower Hunter, and describes the effects of planned and potential development on the foraging and roosting habitat of the GHFF. It identifies which habitats are likely to be impacted and the significance of these areas.
Section 18 identifies areas required to support foraging and roosting GHFF, prioritises areas for conservation, and identifies mechanisms that could be employed to achieve protection of important habitat for the GHFF. Mechanisms explored include habitat retention, rehabilitation and enhancement and offsetting with existing high quality habitats.
To supplement the conservation strategies, Section 20 details management actions that would support GHFF conservation and future growth needs of the Lower Hunter. An important component of the management of the GHFF is social issues associated with human–flying-fox conflict. This strategy considers the social impacts of future growth and development within the Lower Hunter on the protection and management of GHFF.
A landscape (broad) and proactive approach to the management of the GHFF is proposed through this management strategy, as a mechanism to support sound impact assessment, appropriate consideration of cumulative impacts of habitat loss, sound decision-making with regard to regional and site-based planning decisions, and the management and protection of this complex species in the Lower Hunter, given the area’s projected growth and development needs. It is intended to be a living document that is updated as further studies and research contribute to an improved understanding of the GHFF in the Lower Hunter, and more effective management tools for foraging and roosting habitat conservation and conflict resolution.

Table 1.4Abbreviations

Biobanking

Biodiversity Banking and Offsets Scheme

CCC

Cessnock City Council

CMA

Catchment Management Authority

CRA

Comprehensive Regional Assessment

CTS

Critical to survival

DEC

Department of Environment and Conservation (now OEH)

DECC

Department of Environment and Climate Change (now OEH)

DECCW

Department of Environment, Climate Change and Water (now OEH)

DoP

Department of Planning

EEC

Endangered Ecological Community

EIA

Environmental Impact Assessment

EPBC Act

Environment Protection and Biodiversity Conservation Act 1999

EPI

Environmental Planning Instruments

GHFF

Grey-headed Flying-fox

HCRCMA

Hunter-Central Rivers Catchment Management Authority

LEP

Local Environmental Plan

LGA

Local Government Area

LHRS

Lower Hunter Regional Strategy

LNE

Lower North East

LMCC

Lake Macquarie City Council

MCC

Maitland City Council

MNES

matters of national environmental significance

NCC

Newcastle City Council

NPW Act

National Parks and Wildlife Act 1974

OEH

The NSW State Office of Environment and Heritage

PAS

Priority Action Statement

PVP

Property Vegetation Plan

SEPP

State Environmental Planning Policy

DSEWPaC

Department of Sustainability, Environment, Water, Population and Communities

SRD

Sustainable Regional Development program

TSC Act

Threatened Species Conservation Act 1995

VCA

Voluntary Conservation Agreement

2.

Legislation and Policy



3.To not delete these three lines (this is hidden text)

4.






Relevant to the management of the GHFF in the Lower Hunter is a range of guidelines, policies, planning instruments and laws, existing under many jurisdictions, including local, state and federal government as well as catchment-based management agencies. Each of these is described below and is considered in the conservation and management assessments in this report.

Table 4.1Federal Legislation and Policy

4.1.1Environment Protection and Biodiversity Conservation Act 1999

The GHFF is listed as Vulnerable under the EPBC Act (refer to Commonwealth Listing Advice on Pteropus poliocephalus (Grey-headed Flying-fox); Threatened Species Scientific Committee 2001). DSEWPaC is responsible for administering the EPBC Act, including functions relating to GHFF across Australia, including the Lower Hunter. Examples of its application include providing advice on the need for referral of actions that may impact the GHFF and / or its habitat, assessing referrals for actions that may impact the GHFF and / or its habitat and coordinating recovery planning for this species (described in Section 4.1.2).
There is a bilateral agreement between the Commonwealth of Australia and the State of New South Wales in relation to parts of the assessment process, with regard to gaining approvals under the EPBC Act and NSW Threatened Species Conservation Act 1995 (TSC Act) for actions involving threatened species that are listed under both Acts (http://www.environment.gov.au/epbc/assessments/bilateral/nsw.html). Whilst this agreement does not remove the requirement for dual consent, where a Species Impact Statement is prepared under the TSC Act that considers the matters that the Commonwealth needs to consider, then the Species Impact Statement prepared for NSW State Government can be used as part of the assessments required federally. This streamlines the assessment, but not the approval process under the EPBC Act. A conservation agreement is currently being explored between the States and DSEWPaC in regard to streamlining the approval process associated with problematic flying-fox camps (i.e. those in conflict with humans). If successfully negotiated, this conservation agreement will remove the need for referral of activities that are covered by the conservation agreement to the Federal Minister for the Environment, although any actions outside of the guidelines may still need referral if an impact to the GHFF and / or its habitat is likely.
To assist assessment of actions that could affect the GHFF, DSEWPaC have prepared the following guidelines:


  • EPBC Act Administrative Guidelines on Significance - Supplement for the Grey-headed Flying-fox (DEH 2003);

  • Survey Guidelines for Australia's Threatened Bats. EPBC Act Survey Guidelines 6.1 (DEWHA 2010); and

  • Flying-foxes and National Environmental Law (DSEWPaC 2012).

DSEWPaC also administers the SRD program under the EPBC Act, for which this management strategy is being prepared.


4.1.2Draft National Recovery Plan for the GHFF

A draft National Recovery Plan for the Grey-headed Flying-Fox Pteropus poliocephalus (DECCW 2009a) is being submitted for approval at the time of preparation of this strategy. The recovery plan will:



  • consider conservation requirements throughout the species’ range;

  • address ways to reduce the impact of threatening processes (including the negative impact of artificial structures such as power lines, loose netting and barbed-wire fences);

  • set objectives for recovery, identify actions to reverse decline and ensure long-term viability;

  • address conservation requirements with regard to the GHFFs role in seed dispersal and pollination; and

  • improve the comprehensiveness and reliability of information available to guide recovery (in particular to improve knowledge of demographics and population structure).

Specific objectives relevant to the five-year duration of the recovery plan are to:



  • identify, protect and enhance key foraging and roosting habitat;

  • substantially reduce deliberate destruction associated with commercial fruit crops;

  • reduce negative public attitudes and conflict with humans; and

  • involve the community in recovery actions, where appropriate.

Actions to meet these objectives incorporate principles of sustainable development and promote procedures to minimise significant adverse social and economic impacts, such as the use of environmental incentive schemes and equitable cost-sharing arrangements.


In terms of this strategy, consistency with the draft National Recovery Plan (DECCW 2009a) has been sought with regard to the definition of habitat critical to survival for the GHFF and management policies or strategies to improve planning outcomes. This strategy takes the broad principles of the draft National Recovery Plan and refines them for the Lower Hunter.
4.1.2.1Habitat Critical to Survival

DSEWPaC are currently reviewing the definitions of roosting and foraging habitat critical to the survival of GHFF provided in previous drafts of the recovery plan. Expert workshops and extensive consultation have been undertaken by DSEWPaC, in acknowledgement of the complex nature of defining critical habitat for GHFFs.


Migration has been identified as a trait that can compound the detrimental impact of human activities on wildlife and increase extinction risk….Migratory animals are disadvantaged by extensive and complex habitat requirements, tendencies to congregate in restricted areas, and reliance on broad-scale, integrated conservation programs….Migrants are unlikely to be conserved incidentally within general programs of resource management….The problems associated with identifying and conserving critical habitat are further compounded in species with highly irregular migration paths such as Pteropus scapulatus and P. poliocephalus….” (Fleming & Eby 2003)
At the time of preparation of this strategy, the current draft National Recovery Plan (DECCW 2009a) identifies foraging habitat critical to the survival of GHFF if it meets one or more of the following criteria:

  • productive during winter and spring, when food bottlenecks have been identified (Parry-Jones & Augee 1991, Eby et al. 1999);

  • known to support populations of >30,000 individuals within an area of 50 km radius (the maximum foraging distance of an adult);

  • productive during the final weeks of gestation, and during the weeks of birth, lactation, and conception (September to May);

  • productive during the final stages of fruit development and ripening in commercial crops affected by GHFF (months vary between regions; Hunter Valley grape picking season occurs February to March); and / or

  • known to support a continuously occupied camp.

At the time of preparation of this strategy, the draft National Recovery Plan (DECCW 2009a) identifies roosting habitat critical to the survival of GHFF if it meets one or more of the following criteria:



  • is used as a camp either continuously or seasonally in >50% of years;

  • has been used as a camp at least once in 10 years (beginning in 1995, and is known to have contained >10,000 individuals—unless such habitat has been used only as a temporary refuge and the use has been of limited duration (i.e. in the order of days rather than weeks or months); and / or

  • has been used as a camp at least once in 10 years (beginning in 1995) and is known to have contained >2,500 individuals, including reproductive females during the final stages of pregnancy, during lactation, or during the period of conception (i.e. September to May).

A draft guideline defining critical habitat for the GHFF is expected to be made public once the Recovery Plan is approved.


4.1.3Federally Funded Studies

The following studies also apply to this strategy:



  • Modelled Distribution of the GHFF with Camps – Map 5 (DSEWPaC undated_a);

  • Known and Historic Campsites of the GHFF (DSEWPaC undated_b);

  • Ranking the Feeding Habitats of Grey-headed Flying-foxes for Conservation Management (Eby & Law 2008); and

  • Lower North East NSW Report (Eby & Law 2008).



Download 1.72 Mb.

Share with your friends:
1   2   3   4   5   6   7   8   9   ...   22




The database is protected by copyright ©ininet.org 2024
send message

    Main page