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Painted Honeyeater (Grantiella picta)

The Painted Honeyeater is a small, nomadic woodland bird that depends mainly on fruiting mistletoes growing on mature eucalypts, acacias and other woodland trees. It is listed as Vulnerable nationally and in the ACT, New South Wales, Northern Territory, Queensland and Victoria, so clearing or degrading mistletoe-bearing woodland can affect both breeding and non-breeding habitat on project sites.

Conservation status

Commonwealth, EPBC Act 1999: Vulnerable.

Queensland, Nature Conservation Act 1992: Vulnerable.

New South Wales, Biodiversity Conservation Act 2016: Vulnerable.

Victoria, Flora and Fauna Guarantee Act 1988: Vulnerable.

Northern Territory, Territory Parks and Wildlife Conservation Act 1976: Vulnerable.

Australian Capital Territory, Nature Conservation Act 2014: Vulnerable.

Breeding season

Timing varies with mistletoe fruiting and differs between breeding strongholds and non-breeding areas. The pattern below is a practical national summary, not a site-specific calendar.

Survey guidance recommends early spring to late summer, especially November to January in southern Queensland, when birds are more likely to gather, display and call. Daylight searches are best conducted within two hours after sunrise or two hours before sunset, in suitable weather.

  • Breeding: Breeding usually occurs from October to March, with breeding in the ACT region reported from November to February. Timing follows mistletoe fruiting.
  • Young: Eggs and nestlings occur during the breeding period. Both parents incubate, brood and feed the young. The supplied documents do not give fledging or dependence durations.
  • Post-breeding movement: Many birds move after breeding to semi-arid areas of north-eastern South Australia, central and western Queensland, and central Northern Territory. Movement is governed mainly by mistletoe fruiting.
  • Non-breeding presence: Non-breeding birds can occur singly or in small groups outside core breeding habitat wherever mistletoe is fruiting. They may be difficult to detect because calling is infrequent and movements are nomadic.
  • Highest clearing risk: Clearing or major canopy disturbance is most likely to harm the species from October to March because nests, eggs and dependent young may be present. Food trees and mistletoe should also be retained outside this period because non-breeding birds move through fruiting woodland.

Identification

The Painted Honeyeater is a distinctive small to medium honeyeater with a pink bill, red eye and strong black, white and yellow plumage. It is usually encountered singly, in pairs or in small groups in mistletoe-bearing woodland.

Adults have black upperparts, white underparts with fine black streaks or spots on the flanks, and yellow edges to the flight and tail feathers.

The bill is deep pink or mostly pink, often with a darker tip, and the eye is red. The combination of a pink bill, almost white underparts and yellow-edged wings is distinctive among Australian honeyeaters.

Body length: About 14 to 16 cm.

Weight: About 20 to 25 g.

Typical grouping: Usually alone or in pairs, less often in small flocks.

Identification: Sex and age differences

Females are smaller and greyer or browner on the upperparts than males. They commonly have less streaking or spotting on the breast and flanks.

Juveniles are paler and browner than adults, with paler yellow feather edges and a brown bill.

Identification: Field signs

The most useful field signs on a clearing or construction site are the bird's distinctive plumage, pink bill, association with fruiting mistletoe and a small, delicate cup nest in outer tree foliage.

During breeding, the male may fly high above the canopy while calling repeatedly. Survey guidance recommends searching for birds, calls and nesting habitat in mistletoe-rich woodland.

The supplied documents do not describe diagnostic tracks, scats, sloughs or eyeshine for this species. Nests should be treated as sensitive signs, and close inspection during breeding or feeding should be avoided.

Nest position: Outer foliage, usually 3 to 20 m above ground.

  • Look for a flimsy cup nest made from plant fibres, spider webs and rootlets.
  • Search drooping outer branches of eucalypts, she-oaks, paperbarks and mistletoe clumps.
  • Record fruiting mistletoe, mature trees and repeated bird activity around the same woodland patch.

Distribution: States and territories

The Painted Honeyeater is endemic to mainland Australia and is sparsely distributed from south-eastern Australia to Queensland and the eastern or north-eastern Northern Territory. It is nomadic, with seasonal north to south movements linked mainly to mistletoe fruiting.

The species occurs in the Australian Capital Territory, New South Wales, Queensland, Victoria, South Australia and the Northern Territory. The supplied material identifies it as Vulnerable in the ACT, New South Wales, Queensland, Victoria and the Northern Territory, and Rare in South Australia.

The main breeding range is inland and extends from the Grampians in Victoria through inland New South Wales to Roma in Queensland. Birds also occur in western Queensland, north-eastern South Australia and the central and eastern Northern Territory, particularly outside the breeding period.

  • Australian Capital Territory: rare breeding visitor, with records from box woodland, riverine woodland and other mature woodland sites.
  • New South Wales: widespread but sparse records across inland and south-western regions, including the Brigalow Belt South, Cobar Peneplain, Darling Riverine Plains, Nandewar, Riverina, South Western Slopes, South Eastern Highlands and Sydney Basin.
  • Queensland: mainly west of the Great Dividing Range, including the Brigalow Belt South, Mulga Lands, Channel Country and adjoining inland regions.
  • Victoria: mainly inland woodland areas, including the Murray Darling Depression and adjoining areas.
  • South Australia: mainly the north-eastern and semi-arid parts of the state, particularly during non-breeding movements.
  • Northern Territory: records extend into the eastern and central parts of the Territory, mainly during post-breeding movements.

Distribution: Strongholds and population structure

The greatest concentrations and almost all breeding records are south of 26 degrees south, on the inland slopes of the Great Dividing Range between the Grampians and Roma.

The species is considered to comprise one population because of its dispersive movements. Local numbers can vary considerably when mistletoe fruiting is strong, as shown by the influx of at least 35 birds recorded in the ACT region during spring and summer 2002 to 2003.

Estimated total population: Less than 10,000 individuals.

Recent population trend: Suspected decline of 20 to 29 percent over the last three generations, estimated as 17 years in the national assessment.

Population structure: One population is recognised because the species is dispersive.

Estimated extent of occurrence: About 2,800,000 km².

Estimated area of occupancy: About 1,000 km².

  • Important habitat includes inland slopes and floodplain woodlands in New South Wales, Victoria and southern Queensland.
  • Non-breeding birds may occur well outside breeding strongholds, including semi-arid parts of South Australia, Queensland and the Northern Territory.
  • Records from predicted distribution areas do not confirm that birds occur throughout the mapped subregion. Site-level habitat assessment is still required.

Distribution: Project interpretation

A site outside the main breeding strongholds can still be important if it contains fruiting mistletoe, mature host trees or woodland used during seasonal movements. A single observation should therefore be assessed in relation to the surrounding woodland and nearby mistletoe resources, rather than treated as an isolated occurrence.

Habitat: Woodland types

Painted Honeyeaters use open forests and woodlands that support abundant mistletoe, particularly where mature trees provide many host branches. They use both broad woodland remnants and, where food is sufficient, narrow roadside strips and isolated trees.

Recorded habitat includes box-gum woodland, box-ironbark-yellow gum woodland, boree and weeping myall woodland, brigalow woodland, acacia-dominated woodland, paperbark woodland, casuarina woodland and callitris woodland.

Riparian woodland dominated by river red gum, black box or river oak is also used, particularly where acacias or mistletoe-bearing trees are present. Trees on farmland and in gardens can provide habitat when they retain suitable mistletoe.

  • Boree or weeping myall woodland dominated by Acacia pendula.
  • Brigalow woodland dominated by Acacia harpophylla.
  • Box-gum, box-ironbark and yellow box woodland.
  • Belah or bull-oak woodland, including Casuarina cristata and Allocasuarina luehmannii.
  • White cypress pine woodland where mistletoes are abundant.
  • River red gum, black box and river oak riparian woodland.

Habitat: Key structure

The species prefers woodland with a higher number of mature trees because mature trees support more mistletoe. Wider remnants are generally used more often than narrow strips, although breeding can occur in narrow roadside vegetation when mistletoe fruit is plentiful.

Retain mature trees, mistletoe host trees, mistletoe clumps, outer canopy branches and woodland regeneration. Avoid assuming that regrowth has little value, because regrowth can contain similar or higher mistletoe densities than remnant woodland.

  • Map mature trees carrying mistletoe before clearing.
  • Check isolated paddock trees and roadside trees as well as continuous remnants.
  • Assess adjacent woodland and mistletoe-bearing trees outside the project footprint because the species moves between food patches.

Habitat: Climate and elevation

The documents do not provide a defined elevation limit. Breeding is concentrated south of 26 degrees south, while post-breeding movements extend into semi-arid regions of South Australia, Queensland and the Northern Territory.

Habitat availability appears to be governed more by mature tree and mistletoe resources, and by seasonal fruiting, than by a stated elevation threshold.

Foraging habitat: Food resources

The Painted Honeyeater is highly specialised for mistletoe fruit. Foraging activity is concentrated around fruiting mistletoe in mature woodland, with nectar and arthropods supplementing the diet.

Mistletoe fruit makes up most of the diet. The species prefers mistletoes of the genus Amyema, including grey mistletoe Amyema quandang, needle-leafed mistletoe Amyema cambagei and maiden's mistletoe Amyema maidenii.

Nectar from flowering mistletoe and eucalypts, and possibly banksias, is also taken. Arthropods are particularly important for adults during breeding and for nestlings.

Primary food: Mistletoe fruit.

Supplementary food: Nectar and arthropods.

Recorded alternative fruit: Fruit from pepper-corn trees and grapes has also been recorded.

  • Search fruiting mistletoe clumps in mature eucalypts, acacias, casuarinas and riparian trees.
  • Record the mistletoe species, abundance, fruiting condition and host tree species.
  • Retain food trees even where the project footprint contains little continuous woodland.

Foraging habitat: Foraging pattern

Birds move seasonally in response to mistletoe fruiting. After breeding, many move to semi-arid parts of north-eastern South Australia, central and western Queensland, and central Australia.

Outside the breeding season, individuals may occur singly or in small groups in areas outside core habitat where mistletoe is fruiting. Calling is less frequent and birds are more nomadic at this time.

  • Survey fruiting mistletoe even when the site is outside the main breeding range.
  • Use early morning and late afternoon searches, particularly during the breeding season.
  • Treat a food tree or mistletoe clump as part of a wider foraging area rather than as an isolated feature.

Breeding habitat: Breeding biology

Breeding is closely matched to mistletoe fruiting and usually occurs from spring to early autumn. Nests are placed in outer foliage, often near abundant fruiting mistletoe.

Breeding season: Usually October to March. In the ACT region, breeding may occur from November to February.

Nest type: A flimsy cup made from plant fibres, spider webs and rootlets.

Nest height: Usually 3 to 20 m above ground.

Clutch size: Usually 2 to 3 eggs.

Incubation: Both parents incubate the eggs, but the incubation period is not stated in the supplied documents.

Parental care: Both parents brood and feed the young.

Age at maturity: Not stated in the supplied documents.

Lifespan: Maximum longevity in the wild is estimated at 10.1 years.

Generation length: Estimated at 5.8 years.

Breeding habitat: Nest habitat

Nests are usually suspended in the outer foliage of eucalypts, she-oaks, paperbarks or mistletoe branches. The species appears to prefer mistletoe as a nest substrate and selects sites where mistletoe prevalence and parasitism rates are high.

Breeding habitat includes mature woodland with fruiting mistletoe, including riparian woodland and narrow roadside remnants where food resources are adequate.

Reported nesting success: About 43 percent in tree foliage and about 17 percent within mistletoe clumps.

Main recorded cause of nest failure: Predation accounted for 83 percent of nest failures in the cited study.

  • Inspect the outer canopy and mistletoe clumps of mature trees before pruning, clearing or access-track construction.
  • Avoid close-range inspection of active nests during breeding and feeding.
  • Protect mature mistletoe-bearing trees and nearby canopy that may support additional nests.

Sheltering habitat: Canopy shelter

The supplied documents do not identify specialised roosts, hollows, burrows or dens for the Painted Honeyeater. Shelter and resting habitat are associated mainly with woodland canopy, mistletoe clumps and mature trees.

Adults use eucalypt, acacia, casuarina, paperbark, callitris and riparian woodland canopies. Mistletoe clumps provide feeding, nesting and likely concealment opportunities, but a separate roost structure is not described.

Retain mature trees, dense outer foliage, mistletoe hosts and connected woodland where practicable. These features support birds during both breeding and seasonal movements.

Known shelter structures: No separate roost, hollow, burrow or den is specified in the supplied sources.

Known nest height: 3 to 20 m above ground.

  • Avoid unnecessary removal of mistletoe clumps and their host branches.
  • Protect canopy links between retained trees and woodland remnants where construction allows.
  • Stage noisy or clearing works away from active nesting areas during the breeding season.

Sheltering habitat: Site assessment

For project works, assess the full tree and canopy structure rather than checking only for hollows or ground refuges. A mature tree with mistletoe can provide food, nesting substrate and cover even if it has no visible hollow.

  • Record mature trees, mistletoe host trees, mistletoe clumps and dense outer foliage.
  • Check trees along roadsides, waterways, fence lines and isolated paddocks.
  • Include nearby retained woodland in the assessment where works could interrupt access to food or nesting trees.

Threats: Clearing and fragmentation

The main project-related risks are loss and degradation of mistletoe-bearing woodland, removal of mature trees and disturbance or destruction of nests. Risks can occur in both breeding habitat and seasonal non-breeding habitat.

Clearing of breeding and non-breeding woodland is a key threat. Habitat has been reduced to ageing, widely spaced trees in some box-ironbark and boree woodlands, while regrowth and narrow roadside remnants may also be cleared.

Removing mature trees reduces the number of mistletoe hosts. Fragmentation can leave isolated trees and narrow strips without enough connected woodland or replacement trees.

  • Avoid clearing woodland with regular Painted Honeyeater records.
  • Retain mature mistletoe-bearing trees, isolated paddock trees and roadside vegetation where practicable.
  • Protect regrowth woodland where it supports mistletoe, because it may contain similar or higher mistletoe densities than remnant woodland.
  • Plan access tracks, compounds and infrastructure to avoid breaking links between mistletoe-bearing trees.

Threats: Grazing and vegetation degradation

Livestock, native macropods and rabbits can suppress tree seedlings and suckers. Poor recruitment leaves mature trees without replacement and can reduce future mistletoe resources.

Mistletoe removal from rural trees and production forests directly reduces the main food and nesting resource.

  • Control grazing pressure in retained woodland and protect tree regeneration.
  • Do not remove mistletoe solely because it is present on a retained tree.
  • Manage weeds and invasive grasses where they simplify woodland understorey and prevent regeneration.

Threats: Disturbance, fire and roads

Inappropriate fire regimes can alter woodland structure, reduce regeneration and affect mistletoe-bearing trees. Firewood collection can also remove trees and branches used by the species.

Vehicle collision is an identified threat, particularly where roads pass through woodland or where birds move between food patches.

  • Keep fire planning compatible with retention of mature trees, mistletoe hosts and woodland regeneration.
  • Limit firewood collection in occupied or suitable habitat.
  • Manage vehicle speeds and driver awareness near retained woodland and known bird activity areas.
  • Avoid locating temporary works, lighting and high traffic close to active nests.

Threats: Predators and competition

Nest predation has been recorded from pied currawongs, pied and grey butcherbirds, and crows and ravens. Black rats are also identified as invasive predators.

Aggressive exclusion by overabundant Noisy Miners can reduce access to woodland habitat.

  • Minimise avoidable disturbance around active nests, which can increase exposure to predators.
  • Assess whether extensive canopy thinning or removal of dense woodland is likely to favour Noisy Miners.
  • Manage food waste and construction materials so they do not attract rats or other predators.

Threats: Other project considerations

The supplied documents do not identify a species-specific disease threat or a defined hydrology threshold. Changes to riparian woodland, drainage or water availability should nevertheless be assessed where they could affect river red gum, black box or river oak woodland, mistletoe hosts and tree recruitment.

  • Avoid drainage, flooding or earthworks that could damage riparian host trees or prevent their replacement.
  • Include disease hygiene measures used for other native vegetation works where equipment moves between woodland remnants.
  • Recheck retained mistletoe-bearing trees after construction if dust, pruning, fire or altered drainage may affect tree health.

Survey methodology: 1. Area searches

Painted Honeyeaters are nomadic, occur at low densities and are most detectable where mistletoe is abundant and fruiting. Survey effort should target suitable woodland, particularly mature trees carrying mistletoe, during the breeding season when birds are more vocal and may gather in small groups.

Search on foot through all suitable woodland and riparian habitat within the project area, including mature eucalypts, acacias, river red gums, black box, river oaks, casuarinas, paperbarks and callitris carrying mistletoe.

Search for birds, calls, feeding activity, fruiting mistletoe, nests and other signs of use.

Give particular attention to woodland with abundant mistletoe fruit and to wider remnant blocks, while also checking narrow roadside strips where mistletoe fruit is plentiful.

Recommended technique: Systematic area searches on foot

Target habitat: Woodland and riparian habitat with abundant, preferably fruiting, mistletoe

  • Record the location and condition of mistletoe clumps, mature host trees and any observed birds or nests.
  • Avoid close approach to active nests and minimise disturbance during feeding and breeding.

Survey methodology: 2. Timing and conditions

Conduct primary surveys from early spring to late summer, when mistletoe fruit and flowers are more likely to be available and Painted Honeyeaters are more detectable.

For breeding season work, survey between October and March. In the ACT region, breeding may occur between November and February.

Survey during daylight, preferably within 2 hours after sunrise and within 2 hours before sunset.

Avoid rain, strong wind and other conditions that reduce visibility or bird activity.

Breeding period generally: October to March

Preferred survey periods: Early morning and late afternoon, within 2 hours of sunrise or sunset

ACT breeding period: November to February

  • Schedule repeat visits across the suitable seasonal window rather than relying on one visit.
  • If surveying outside the breeding season, increase search effort because birds may occur singly or in small groups, call less often and appear in areas outside their core habitat near fruiting mistletoes.

Survey methodology: 3. Effort and detection notes

Apply the Queensland guideline effort rate to each 50 ha area of suitable habitat, or scale the effort to the actual area of suitable habitat where the project area is smaller.

Search systematically for at least 4 hours over a minimum of 4 days per 50 ha of suitable habitat, for example, at least 1 hour per day for 4 days.

Treat a failed survey as inconclusive where mistletoe is not fruiting, weather is unsuitable or the survey occurs outside the breeding period.

Use both visual observation and listening because birds are more vocal and easier to detect during breeding displays, but calling is infrequent during the non-breeding season.

Minimum effort guide: 4 hours over 4 days per 50 ha of suitable habitat

Typical daily example: At least 1 hour of area searching per day for 4 days

Published detection probability: No published detection probabilities are available

  • Map all suitable habitat searched and identify the area in hectares.
  • Record survey dates, start and finish times, weather, wind, rainfall, mistletoe flowering or fruiting, observers and search hours.
  • Record whether observations were single birds, pairs or groups, and whether birds were feeding, nesting or moving through the site.

Survey methodology: Minimum effort and reporting

  • Use the 4 hours over 4 days per 50 ha effort guide where suitable habitat is present, and document any justified variation.
  • Submit confirmed records to the relevant state wildlife database, such as the NSW BioNet Atlas or Queensland WildNet, and follow the database requirements for location accuracy and evidence.
  • Report the species, number of birds, behaviour, breeding evidence, habitat type, mistletoe condition, survey effort and photographs or audio where available.
  • Retain survey data and maps with the project environmental records and provide them to the relevant approval authority when required.

Before habitat disturbance: Avoid and minimise habitat loss

Plan the project around retention of mature woodland, mistletoe and habitat connectivity. The species is nationally Vulnerable and depends mainly on mistletoe fruit in woodland and riparian habitats.

Avoid clearing woodland in which Painted Honeyeaters have been recorded, including remnant roadside vegetation and regrowth.

Retain mature trees and trees carrying mistletoe, because mature trees support more mistletoe and the species prefers these resources.

Retain connected woodland blocks and avoid reducing habitat to isolated trees or narrow strips where a practicable alternative exists.

Do not remove mistletoe from retained host trees unless authorised by the project approval and supported by a species management assessment.

Main food: Mistletoe fruit

Key habitat feature: Mature woodland trees carrying mistletoe

General breeding period: October to March

  • Map mature trees, mistletoe clumps, fruiting mistletoe and known or potential nesting areas before finalising the disturbance footprint.
  • Set site-specific no-go areas around retained woodland and mistletoe resources, with the extent based on the ecological assessment, approval conditions and risk of indirect damage.
  • Avoid clearing during the main breeding period, October to March, where practicable, particularly when nests or dependent young are present.

Before habitat disturbance: Approvals and work planning

Check whether the proposed action may significantly affect this nationally Vulnerable species or its habitat and obtain environmental approval or make an EPBC Act referral where required.

Check state and territory threatened species legislation, permits and survey or relocation requirements before works begin.

Prepare a fauna management plan that identifies the disturbance footprint, retained habitat, survey method, stop-work triggers, fauna handling arrangements and reporting pathway.

Stage clearing and construction so that retained woodland, mistletoe host trees and movement routes remain available throughout the works.

  • Include the species in the project risk register and clearing permit system.
  • Confirm the qualifications, licences and authority of the fauna spotter catcher before clearing starts.
  • Brief machinery operators and supervisors on the species, no-go areas, nest disturbance limits and stop-work procedure.

Before habitat disturbance: Pre-clearance preparation

Complete a pre-clearance survey of all habitat that may be disturbed, with particular attention to mature trees, mistletoe clumps, fruiting mistletoe and the outer foliage of trees where nests may occur.

Mark retained trees, mistletoe, exclusion areas and approved access routes on the ground and in the construction plans.

Install exclusion fencing where it can protect retained woodland, host trees, mistletoe and narrow habitat links from machinery and storage impacts.

Confirm an arrangement with a veterinarian or wildlife carer before works begin for any injured animal found during clearing.

  • Reinspect the site immediately before clearing if the interval since the survey is long enough for conditions or habitat use to have changed.
  • Do not rely on a single absence record to clear habitat, particularly outside the breeding season when detectability is lower.
  • Provide the fauna spotter catcher with current maps, survey results, permit conditions and emergency contact details.

During habitat disturbance: Daily clearing controls

Use a controlled clearing process that protects retained habitat and allows any Painted Honeyeater or other fauna to move away safely. The spotter catcher must have authority to pause work when fauna, nests or unplanned habitat features are found.

Inspect exclusion fencing, no-go markers, retained trees and mistletoe before machinery enters the work area each day.

Keep machinery within the approved footprint and prevent stockpiling, vehicle parking, refuelling and access tracks from damaging retained host trees or mistletoe.

Use a slow, staged clearing sequence that gives mobile fauna time to leave towards retained woodland.

Maintain a fauna spotter catcher in the active clearing zone whenever the risk assessment or approval requires it.

  • Stop work if clearing moves outside the approved footprint, a marked habitat feature is damaged, or a nest or fauna species is found that cannot be managed under the approved plan.
  • Keep personnel and machinery away from active nests and avoid unnecessary noise, vibration and lighting near retained breeding habitat.
  • Do not chase, herd or repeatedly flush a Painted Honeyeater.

During habitat disturbance: Fauna handling and habitat features

The fauna spotter catcher should first allow an uninjured Painted Honeyeater to move naturally to nearby retained habitat.

Handle the bird only when necessary, and only under the relevant wildlife authority, permit and project fauna management plan.

Use an appropriately ventilated temporary container and minimise handling time if capture is required for safety or veterinary assessment.

Relocate an uninjured bird only to nearby retained habitat that provides woodland and mistletoe resources, and record the release location.

Typical nest height: 3 to 20 m above ground

Typical clutch: 2 to 3 eggs

Nest type: Flimsy cup nest in outer foliage, often associated with mistletoe

  • Inspect trees, outer foliage, mistletoe clumps, logs, rocks, ground cover, burrows and wet areas progressively as clearing proceeds, because these features may shelter fauna even though the Painted Honeyeater nests in outer foliage.
  • Do not fell or push a tree containing an active nest until the authorised fauna specialist has assessed the nest and the action is permitted.
  • Treat hollow-bearing trees, large logs and other habitat features as fauna resources for the broader site fauna and retain or handle them under the approved fauna procedure.
  • Take injured or distressed birds to the nominated veterinarian or licensed wildlife carer as soon as practicable.

During habitat disturbance: Findings, triggers and records

Stop work in the immediate area if a Painted Honeyeater, active nest, dependent young, injured bird or unapproved habitat feature is found.

Protect the location while the fauna spotter catcher and environmental officer assess the finding against the approval and fauna management plan.

Escalate any repeated sightings, breeding activity or concentration of birds to the project ecologist and approval authority where required.

Record every observation, handling event, relocation, injury, mortality, nest and stop-work event.

  • Record the date, time, coordinates, number of birds, behaviour, habitat, machinery activity, action taken and final outcome.
  • Photograph the location and habitat where this can be done without disturbing the bird or nest.
  • Resume work only after the authorised person confirms that the control measure is in place and the environmental officer records the decision.

After habitat disturbance: Post-clearance checks

Post-clearing work must confirm that the approved footprint was followed and that retained woodland, mature trees and mistletoe remain functional. Use monitoring to detect damage or continued use that requires further management.

Inspect the cleared boundary and retained habitat for unapproved tree removal, mistletoe damage, soil disturbance, machinery encroachment and breaks in habitat connectivity.

Complete a fauna and nest check of retained trees and mistletoe at the end of each clearing stage and after any unexpected event.

Confirm that any relocated, injured or deceased fauna has been recorded and reported under the project and statutory requirements.

Remove temporary exclusion fencing only when construction risks have ended and the environmental officer approves its removal.

  • Map the final cleared area and all retained mature trees, mistletoe clumps and woodland links.
  • Repair damaged exclusion fencing and barriers before the next work shift.
  • Keep machinery and materials away from retained habitat during follow-on construction.

After habitat disturbance: Monitoring and reporting

Monitor retained habitat and known Painted Honeyeater sites during the project and through the period specified by approval conditions or the fauna management plan.

Repeat targeted searches where works occur near fruiting mistletoe, known records or retained breeding habitat.

Compare observations with the pre-clearance survey, including bird numbers, behaviour, mistletoe condition and evidence of breeding.

Report breaches, injuries, mortalities, nests and unexpected species records to the project environmental officer and relevant authority within the required timeframe.

  • Submit verified records to the relevant state wildlife database, including NSW BioNet Atlas or Queensland WildNet where applicable.
  • Keep survey sheets, photographs, maps, incident reports, relocation records and rehabilitation inspections in the project file.
  • Use monitoring results to modify access, lighting, noise, grazing, fire or vegetation management where these affect retained habitat.

After habitat disturbance: Offsets and residual impacts

Assess residual loss or degradation of Painted Honeyeater habitat after avoidance, minimisation and rehabilitation measures have been applied.

Apply any approved offset, habitat protection or recovery measure required under the EPBC Act, state legislation or project approval.

Prioritise residual actions that protect mature woodland, mistletoe host trees, regeneration and habitat connectivity across the species range.

  • Document why impacts could not be avoided and how the offset or compensatory action addresses the affected habitat values.
  • Do not count short-term planting as replacement for mature trees and established mistletoe without approval authority agreement and a suitable long-term management commitment.

Rehabilitation actions: Rebuild host woodland and mistletoe resources

Rehabilitation should rebuild woodland structure and maintain the mistletoe resources on which Painted Honeyeaters depend. Recovery is long term because mature host trees and productive mistletoe populations take time to develop.

Protect retained mature trees and allow natural regeneration of eucalypts, acacias, river red gums, black box, river oaks, casuarinas, paperbarks and callitris suited to the local vegetation community.

Use local provenance plants that recreate the woodland structure and include host trees for mistletoe.

Retain naturally occurring mistletoe and avoid treating it as a weed in habitat being restored for the species.

Where appropriate, restore host vegetation associated with mistletoe species used by the Painted Honeyeater, including grey mistletoe, Amyema quandang, needle-leafed mistletoe, Amyema cambagei, and other locally suitable Amyema species.

Mistletoe resources identified in the documents: Amyema quandang, Amyema cambagei, Amyema maidenii and other Amyema species

Important host habitat: Mature eucalypt and acacia woodland, including riparian woodland

  • Protect planted and regenerating trees from livestock, rabbits and excessive browsing until they are established.
  • Maintain connected plantings between retained woodland blocks and riparian habitat where this is consistent with the local ecological community.
  • Do not plant introduced fruiting species as a substitute for native mistletoe resources.

Rehabilitation actions: Manage threats in restored habitat

Control grazing by livestock, rabbits and other browsers so that seedlings, suckers, mature trees and mistletoe host populations can regenerate.

Control weeds that simplify woodland understorey or compete with planted and naturally regenerating native plants.

Manage fire so that retained mature trees, regenerating woodland, mistletoe and known breeding habitat are not exposed to inappropriate fire intensity or frequency.

Assess whether dense Noisy Miner populations are excluding Painted Honeyeaters from restored or retained woodland and manage the habitat in accordance with approved local conservation programs.

  • Inspect restored areas for tree recruitment, browsing, weed invasion, mistletoe persistence and fire damage.
  • Retain dead timber and logs where safe, because they provide habitat for other fauna affected by the project, but do not use them as a substitute for the mature trees and mistletoe required by Painted Honeyeaters.
  • Do not install nest boxes as a substitute for Painted Honeyeater habitat, because this species nests in outer foliage rather than tree hollows.

Rehabilitation actions: Success measures and monitoring

Set monitoring points in restored and retained woodland and inspect them at agreed intervals for survival and growth of planted host trees, natural regeneration and mistletoe condition.

Measure the area of woodland protected or restored, number and survival of host trees, mistletoe presence and fruiting, grazing and weed control outcomes, and connectivity between habitat patches.

Use repeat bird surveys during early spring to late summer and apply the recommended effort of 4 hours over 4 days per 50 ha of suitable habitat where monitoring is intended to detect Painted Honeyeaters.

Treat increasing use by Painted Honeyeaters, stable or increasing host tree recruitment, retained mistletoe and reduced habitat degradation as indicators of progress, while recognising that bird numbers vary with seasonal mistletoe fruiting.

Recommended monitoring season: Early spring to late summer

Bird monitoring effort guide: 4 hours over 4 days per 50 ha of suitable habitat

  • Record Painted Honeyeater observations, breeding evidence and feeding activity separately from vegetation outcomes.
  • Review rehabilitation methods if host trees fail, mistletoe is removed or declines, grazing prevents recruitment, or birds continue to avoid otherwise suitable habitat.
  • Report rehabilitation results and corrective actions to the approval authority where required.

Sources