Grey Honeyeater (Conopophila whitei)

Conservation status

South Australia, National Parks and Wildlife Act 1972: Rare.

Breeding season

The Grey Honeyeater breeds mainly from August to November. Breeding can continue to May after summer rain. The species is probably sedentary, with some nomadic movement, and no regional difference in breeding timing is established.

Breeding mode: Probably biparental. Both sexes probably incubate and feed the young.

Clutch size: 1 or 2 eggs.

Incubation: Not recorded.

Fledging: Not recorded.

Age at maturity: Not recorded.

Nest site: A small, frail cup nest in slender twigs in the outer foliage of a mulga shrub. The nest is made from fine grass stems, hair and plant down, bound with spider web.

Breeding frequency: Not recorded.

Breeding activity may vary between years and regions with rainfall, so check suitable mulga and acacia scrub before clearing, particularly after summer rain and from August to November.

• Nesting and laying: Nesting and laying are expected from August to November, with breeding possibly continuing to May after summer rain.
• Eggs and dependent young: Eggs and dependent young may be present during the breeding period, but incubation and fledging dates are not recorded.
• Foraging and local presence: The Grey Honeyeater is probably present throughout the year, foraging in mulga and similar acacia scrub for insects, nectar and mistletoe berries.
• Highest clearing risk: Clearing and construction have the greatest potential to harm nests, eggs and dependent young from August to November, and during any breeding that continues after summer rain.

Identification: Appearance and size

The Grey Honeyeater is a tiny, plain-looking bird that can be difficult to detect in dense scrub. Careful attention to calls, movement and associated mixed-species flocks is useful during site inspections.

Adults are generally cold grey above and paler below, with the underparts becoming browner until the next moult. The tail and flight feathers are blackish brown, with tail tips that are white and may become buffish with age.

The bill is short, slightly down-curved and grey, becoming black towards the tip. A slightly darker mark extends across the eye to the bill, and a faint buff-tinted eye ring is present.

• Length: 10.5 to 12 cm.
• Iris brown.
• Legs steel grey.

Identification: Calls and similar species

The call may be a piercing, metallic, quick double squeak, described as “chirra-wik-chirra-wik”. Other reported calls include “cre-seek” and a weak, high-pitched “troo-whee, troo-whee” series.

Do not rely on colour alone. The Grey Honeyeater can resemble the Western Gerygone, Yellow-rumped Thornbill and other thornbills. It should also be distinguished from the female Redthroat.

• Listen for repeated calls from dense mulga foliage.
• Check the bill shape, eye marking, tail pattern and overall grey appearance.
• Record associated species where the bird occurs in a mixed-species flock.

Identification: Field signs

The species is generally detected by a brief view, repeated calls or movement through outer foliage. It often occurs with Western Gerygones, Yellow-rumped Thornbills and other Acanthiza species.

No distinctive droppings, whitewash, stains or odour are recognised as reliable field signs for this species. A nest is a more useful breeding sign and should be treated as an active breeding place if birds are attending it.

• Look for quick foliage gleaning and short hovering flights.
• Use photographs and audio recordings where identification is uncertain.
• Avoid flushing birds repeatedly from dense shrubs.

Distribution: Australian range

The Grey Honeyeater is endemic to Australia and has a broad but patchy inland distribution. It is rare to uncommon and may be missed during short surveys, particularly where vegetation is dense or flowering and insect activity is low.

The range extends across the mid-west to the centre of the Australian continent. It is especially associated with inland areas of Western Australia and the Northern Territory.

• Western Australia, including the Pilbara and Murchison regions.
• Northern Territory, including the southern and central parts of the Territory.
• New South Wales, Queensland and South Australia are also within the mapped Australian range.

Distribution: Examples of known localities

Recorded localities include Lake Austin, Wanjarri Nature Reserve south of Wiluna, and Tom Price in Western Australia. In the Northern Territory, it has been recorded at Olive Pink Botanic Garden near Alice Springs.

• Treat records from nearby suitable mulga or acacia scrub as relevant to project planning.
• Do not assume that a lack of recent records means the species is absent.

Distribution: Conservation status and project implications

The species is profiled as an EVNT species. It is listed as Rare in South Australia under the National Parks and Wildlife Act 1972, and as Priority 4 in Western Australia, a non-statutory DBCA category for rare and near threatened species that require monitoring.

In Queensland, near threatened animals are protected wildlife. Tampering with a breeding place may require a species management program. Confirm current approvals and species-specific requirements before clearing or construction.

• Use targeted surveys and habitat assessment where inland acacia scrub will be cleared.
• Retain suitable habitat where practicable and investigate records before finalising clearing limits.
• Escalate confirmed records or active nests to the project ecologist and relevant state authority.

Habitat: Vegetation to look for

Look for the Grey Honeyeater in semi-arid mulga and other inland acacia scrublands. Habitat value may increase where mature shrubs, mistletoe and a relatively intact understorey are present.

The main habitat is mulga, Acacia aneura, together with similar acacia scrub. The species may use dense or scattered shrublands where foliage provides cover and supports insects.

• Mature mulga shrubs and regenerating acacia scrub.
• Mixed acacia vegetation with dense outer foliage.
• Areas containing mistletoe within or near the shrub canopy.

Habitat: Site features

Suitable habitat may occur across broad inland scrublands rather than being restricted to a particular landform. Retain connected patches of acacia vegetation where possible, especially around known records and areas with mistletoe.

• Inspect intact scrub, creekline acacia and shrub patches within otherwise cleared landscapes.
• Include apparently sparse mulga in habitat assessments, not only dense stands.
• Map mature shrubs and mistletoe before designing access tracks, pads and clearing areas.

Habitat: Habitat condition

Mulga can take many years to recover after uncontrolled fire. Repeated disturbance, heavy grazing and removal of mature shrubs can reduce the cover and food resources available to this small honeyeater.

• Record fire history and visible grazing impacts during habitat assessments.
• Avoid unnecessary vehicle movement through intact scrub.
• Protect retained vegetation from indirect damage during construction.

Foraging habitat: Foraging behaviour

The Grey Honeyeater forages actively through shrub foliage and may be detected as it moves quickly between leaves and outer branches. Food resources can vary with flowering, insect activity, rainfall and the presence of mistletoe.

It mainly gleans foliage surfaces for lerp and similar insects. It also hovers to take flying insects and probes deep, tubular flowers for nectar.

• Search outer and middle foliage of mulga and other acacias.
• Watch for short hovering flights around flowering shrubs.
• Listen for calls from within dense foliage before entering a patch.

Foraging habitat: Food plants and resources

Nectar and berries from mistletoe are used, and nectar from tubular flowers such as Eremophila is also taken. Mistletoe occurrence may help explain why otherwise similar scrub patches differ in use.

• Map mistletoe-bearing shrubs within the clearing footprint.
• Record flowering Eremophila and other nectar-producing plants.
• Retain food plants in habitat buffers or no-go areas where practicable.

Foraging habitat: Survey considerations

Short visual searches can miss this species. Combine quiet observation with call detection and searches of mixed-species flocks, particularly in suitable mulga and acacia scrub.

• Survey during suitable daylight conditions when birds are active.
• Pause at habitat edges and listen before moving through vegetation.
• Repeat searches when initial results are negative but suitable habitat is present.
• Record the location and vegetation structure of all detections.

Breeding habitat: Nest and breeding place

Breeding generally occurs from August to November, and may continue to May after summer rain. Nests are small and easily overlooked, so vegetation clearing in suitable scrub requires a careful pre-clearance inspection.

The nest is a small, frail and untidy cup placed in slender twigs in the outer foliage of a mulga shrub. It is made from fine grass stems, hair and plant down, with spider web used for binding.

• Inspect outer shrub foliage from several angles.
• Look for small cups secured among fine twigs.
• Treat attending birds, alarm behaviour or repeated movements to one shrub as signs requiring closer assessment.

Breeding habitat: Breeding timing

The usual breeding period is August to November. Breeding may extend through to May when summer rain provides suitable conditions.

• Give particular attention to active nests during August to November.
• After substantial summer rain, continue to consider breeding risk through to May.
• Where practicable, schedule vegetation clearing outside likely breeding periods.

Breeding habitat: Eggs and parental care

Clutches contain 1 or 2 eggs. The eggs are swollen oval, slightly glossy white and spotted with reddish brown. Both sexes are probably involved in incubation and feeding young.

• Do not disturb a nest to confirm its contents.
• Stop work near a suspected active nest and seek advice from the fauna spotter catcher or project ecologist.
• Apply state approval conditions and species management requirements where a breeding place is affected.

Sheltering habitat: Shelter in shrub foliage

Specific roosting and shelter sites have not been described, but the species is closely associated with shrub foliage. Dense mulga and other acacia cover should therefore be treated as potential sheltering habitat during works.

The outer foliage used for nesting is also likely to provide concealment from weather and predators. Retained shrubs should be protected from unnecessary trimming, dust and vehicle damage.

• Retain dense shrub patches around confirmed records where practicable.
• Avoid creating isolated remnant shrubs where connected habitat can be retained.
• Keep machinery and stored materials out of retained vegetation.

Sheltering habitat: Roosting information

No particular roost type, hollow, cave, burrow or colony has been identified for the Grey Honeyeater. Do not limit habitat checks to hollow-bearing trees or large trees.

• Inspect low and mid-storey acacia cover as well as taller vegetation.
• Include shrub patches in pre-clearance fauna inspections.
• Use repeated observations to identify regular shelter areas.

Sheltering habitat: Pre-clearance handling

If birds are present in vegetation marked for removal, allow the fauna spotter catcher to assess the area before disturbance. Avoid driving birds into adjoining work zones or repeatedly flushing them through active construction areas.

• Check retained vegetation after clearing for displaced birds.
• Keep escape routes into suitable retained scrub where safe and practicable.
• Document sightings, vegetation affected and any follow-up actions.

Threats: Clearing and habitat fragmentation

The main risks on works sites are loss and fragmentation of mulga or other acacia scrub, direct disturbance to breeding birds, and damage from fire, grazing or construction activity. Because the species is rare to uncommon and state listed in parts of its range, a precautionary approach is appropriate.

Removal of mature mulga, mistletoe-bearing shrubs and connected acacia scrub can reduce nesting cover, shelter and food resources. Narrow clearing corridors can also divide otherwise suitable habitat.

• Use existing disturbed areas for access and infrastructure where feasible.
• Minimise the clearing footprint and retain mature shrubs and mistletoe.
• Mark no-go areas clearly before machinery enters the site.

Threats: Fire and grazing

Uncontrolled fire can remove habitat, and mulga may take many years to recover. Introduced-animal grazing can damage vegetation and reduce habitat quality.

• Use fire prevention and response controls suited to the site.
• Avoid unnecessary fuel loads and disturbance around retained scrub.
• Manage grazing impacts in retained habitat where this is part of the project.

Threats: Breeding disturbance

Clearing or construction near an active nest can injure birds, destroy a breeding place or cause abandonment. The small cup nest is difficult to see in outer shrub foliage.

• Undertake a targeted pre-clearance search in suitable scrub.
• Use an exclusion area around an active nest based on site conditions and advice from the project ecologist.
• Do not disturb or relocate a nest without appropriate approval and specialist advice.

Threats: Status-based management response

For a listed EVNT species, confirmed records should inform the clearing method, timing and retention plan. In South Australia, the species is Rare. In Western Australia, Priority 4 is a non-statutory category that supports monitoring of rare and near threatened species. In Queensland, check requirements relating to protected wildlife and tampering with breeding places.

• Use targeted survey effort where suitable habitat is present, even if the species has not previously been recorded.
• Refer confirmed records, active nests and proposed habitat loss to the relevant approval pathway.
• Monitor retained habitat where construction may cause indirect disturbance.

Survey methodology: 1. Desktop assessment

The Grey Honeyeater is small, quiet and easily overlooked in semi arid acacia country. Survey effort should focus on mulga and similar scrub, especially where mistletoe, flowering shrubs or mixed species flocks occur.

Map remnant and regrowth mulga, other acacia scrub, mistletoe stands, flowering Eremophila and areas affected by fire or grazing. Check recent records and local habitat descriptions before setting the survey design.

Treat the species as poorly known at sites outside its established range. Use local records, habitat condition and the scale of the proposed disturbance to set survey effort.

• Review records from government databases, local land managers, conservation groups and nearby surveys.
• Identify proposed clearing, access tracks, laydown areas, fire breaks and other indirect impacts.
• Check whether the site supports breeding habitat during August to November, or later after summer rain.
• Confirm the current conservation status in each relevant state and whether the project triggers EPBC Act requirements.

Survey methodology: 2. Field detection

Search methodically through the outer foliage of mulga and other acacias. Look for a small, cold grey honeyeater with a pale eye ring, darker markings through the eye, blackish brown wings and tail, and white to buff tail tips.

Listen for the piercing, metallic double squeak, described as chirra wik chirra wik, and the high pitched calls described as cre seek or troo whee. The species may occur in mixed species flocks with Western Gerygones, Yellow rumped Thornbills and other thornbills.

• Survey in daylight, preferably during the cooler and quieter part of the morning, in calm conditions with good visibility.
• Move slowly and pause regularly to scan foliage and listen for calls. Use binoculars where vegetation is dense or birds remain high in shrubs.
• Search both sides of drainage lines, shrub edges and patches containing mistletoe or flowering plants.
• Use call playback only where permitted and only when needed for identification. Avoid repeated playback during the breeding season, and record any response rather than persistently drawing birds from cover.

Survey methodology: 3. Timing and repeat visits

The main breeding period is August to November. Breeding can continue to May after summer rain. The species is probably sedentary, with some nomadic movement, so a single negative survey does not demonstrate absence.

• Schedule surveys in suitable weather and include the breeding period where works could affect nesting habitat.
• Repeat surveys when habitat is extensive, records are nearby, conditions are poor, or the first visit is inconclusive.
• Increase attention after rain when birds may be more active around flowering plants and food resources.
• Do not describe the species as absent unless the survey design and detection conditions support that conclusion.

Survey methodology: 4. Survey records

Record enough information for another ecologist to relocate the observation and assess the risk to habitat and breeding places.

• Record date, start and finish time, weather, observers, survey method and areas searched.
• Map every sighting, call detection, flock and suspected nest location with coordinates and an accuracy estimate.
• Record the number of birds seen, behaviour, direction of movement, associated species, food plants and whether birds repeatedly used one shrub or patch.
• Photograph habitat and nests where this can be done without approaching or disturbing birds.
• Record recent fire, grazing, weed invasion, mistletoe abundance and the condition of surrounding scrub.

Before habitat disturbance: 1. Approvals and planning

Plan the work around habitat retention and the avoidance of active breeding places. The Grey Honeyeater has a small, frail cup nest in slender twigs in the outer foliage of a mulga shrub, so apparently minor shrub removal can affect a breeding attempt.

Confirm the species status and approval pathway before finalising the clearing footprint. The South Australian listing is Rare and the Western Australian Priority 4 category applies to a rare or near threatened species that needs monitoring. Confirm the relevant population or subspecies if a state listing is geographically limited.

• Check whether the action may affect a matter protected under the EPBC Act. Make an EPBC referral where required, and follow any approval conditions.
• In Queensland, obtain the required approval and species management program before tampering with a breeding place of this near threatened animal.
• Obtain relevant state or territory wildlife, clearing, threatened species and animal handling permits before work starts.
• Include the Grey Honeyeater in the construction environmental management plan, clearing protocol and incident response procedure.
• Have an ecologist confirm any state specific buffer, timing or reporting conditions before mobilisation.

Before habitat disturbance: 2. Avoidance and buffers

Retain intact mulga and other acacia scrub wherever possible. Retain mistletoe, flowering shrubs and connected habitat, as these may provide food and help maintain local use of the site.

There is no general species specific clearing buffer stated for the Grey Honeyeater. Set a site specific no go area around each nest and repeatedly used habitat, based on the nest location, vegetation structure, activity and approval conditions.

• Redesign the footprint to avoid nests, nest shrubs and dense breeding habitat.
• Mark exclusion areas clearly with durable bunting, fencing or signs before clearing begins.
• Prevent vehicles, storage, spoil, dust, fire and drainage changes from entering retained habitat.
• Keep buffers in place until the breeding attempt has finished and the ecologist confirms that work can proceed.
• Do not clear an apparently unused nest shrub without checking whether birds are still attending it.

Before habitat disturbance: 3. Pre clearance inspection

Complete a targeted pre clearance inspection close to the start of works. Search the outer foliage of every mulga and similar shrub within the disturbance area, and check retained vegetation that could be affected by machinery or access.

• Inspect during daylight and listen for calls as well as looking for birds and nests.
• Search for the small untidy cup nest made from fine grass, hair and plant down, bound with spider web.
• Look for adults carrying nesting material, feeding young, repeatedly entering one shrub, alarm calling or making short movements near a nest.
• Map and photograph any nest from a safe distance, then establish the exclusion area and notify the site supervisor.
• Repeat the inspection if works are delayed, the footprint changes, rain causes breeding activity, or vegetation is disturbed before clearing.

Before habitat disturbance: 4. Induction and work controls

All personnel should know how to recognise the Grey Honeyeater, its calls, its nest and the site stop work process. Keep the controls simple and visible to plant operators, spotter catchers and subcontractors.

• Include the species, habitat, nest appearance, exclusion markings and reporting contacts in the site induction.
• Explain that only authorised fauna handlers may capture, handle, contain or release wildlife.
• Provide the spotter catcher with approved authority to stop work when a bird, nest or other fauna risk is identified.
• Brief operators to stop immediately if a bird is injured, trapped, repeatedly entering a shrub, or behaving as though a nest is nearby.
• Keep an up to date map of exclusion areas in the site office and in each clearing crew vehicle.

During habitat disturbance: 1. Sequential clearing

Clear in a controlled sequence from low risk areas towards retained habitat. A spotter catcher should be present or available as required by the approval and should have clear authority to stop work.

Use a staged approach that gives mobile birds an opportunity to move into retained habitat. Retain connected shrub cover and avoid isolating small patches during the works.

• Complete the final pre clearance check immediately before each clearing stage.
• Clear non habitat areas first, then work progressively towards retained vegetation under spotter catcher supervision.
• Use low speed machinery and pause regularly around dense acacia scrub, mistletoe and flowering shrubs.
• Do not fell or push a nest shrub until the spotter catcher and ecologist have confirmed that no active breeding place will be affected.
• Keep machinery, workers and vehicles outside marked exclusion areas.

During habitat disturbance: 2. Stop work and active breeding places

Stop work immediately if an active nest, dependent young, repeated nest attendance or a suspected breeding place is found. Do not touch the nest, eggs or young, and do not prune the nest shrub to make the work easier.

• Make the area safe, withdraw machinery and establish a temporary exclusion area.
• Notify the spotter catcher, project ecologist and site supervisor at once.
• Have the ecologist assess activity, nest status, likely disturbance and the approval conditions before work resumes.
• Obtain any required Queensland species management program approval, state approval or other authorisation before tampering with the breeding place.
• Resume only after the ecologist documents the decision, controls and revised work limits.

During habitat disturbance: 3. Handling and release

Avoid capture wherever the bird can move safely into suitable retained habitat. Capture, restraint, transport and release must be carried out only by appropriately authorised and experienced wildlife personnel.

• Do not chase birds through dense scrub or use unapproved nets, poisons, smoke or deterrents.
• If a bird is contained, keep handling brief and place it in a secure, quiet, appropriately ventilated container away from heat, noise and machinery.
• Release a fit bird into suitable nearby habitat only on the advice of the authorised handler and in accordance with permit conditions.
• Do not relocate eggs, nestlings or an active nest unless specifically authorised and directed by the relevant wildlife authority.

During habitat disturbance: 4. Injured or trapped animals

Treat an injured, exhausted or trapped Grey Honeyeater as a wildlife incident. Minimise stress and keep the animal away from people, pets and plant.

• Stop the immediate activity and alert the authorised fauna handler.
• Do not provide food or water unless directed by a veterinarian or wildlife rehabilitator.
• Contact the project wildlife contact, licensed wildlife rehabilitator or veterinarian and follow their instructions for containment and transport.
• Record the location, cause, time, observed injuries, photographs where appropriate, handler and final outcome.
• Report the incident to the regulator or approval holder when required by the permit, approval or management plan.

After habitat disturbance: 1. Post clearance inspection

Check the work area after clearing and document what happened. Follow up any nest, injury, escape, unexpected record or habitat damage through the project incident system and approval conditions.

Inspect the cleared footprint, retained edges and access routes after each clearing stage. Check for stranded birds, damaged nests, injured fauna, isolated shrubs and unplanned impacts to retained habitat.

• Search fallen vegetation and machinery work areas before demobilisation from each stage.
• Confirm that exclusion markers remain in place and that no spoil, rubbish, fire or vehicle damage has entered retained scrub.
• Record all Grey Honeyeater observations after clearing, including birds using retained habitat or moving through the site.
• Have the spotter catcher sign off each cleared stage before the next stage begins.

After habitat disturbance: 2. Monitoring and relocated animals

Use follow up monitoring where the project affects known habitat, a breeding place, a retained patch or a bird that was captured or relocated. Monitoring should be designed by the project ecologist and matched to the approval conditions and level of risk.

• Revisit retained habitat after works and inspect for continued bird use, nest building, feeding activity and disturbance.
• Check any authorised release location for survival, normal movement and use of suitable shelter and food plants.
• Do not assume that a bird seen after release has established successfully. Record follow up observations and any further injury or mortality.
• Stop or modify works if monitoring shows continuing disturbance, repeated return to a damaged nest site or loss of important habitat.

After habitat disturbance: 3. Reporting and incident review

Close out the work with a clear fauna record. Use the results to improve the next clearing stage and future projects in mulga habitat.

• Prepare a map and register of sightings, nests, exclusion areas, incidents, handling events, releases and habitat retained.
• Submit reports to the relevant approval holder, regulator and land manager within the required timeframes.
• Review every stop work event, including the trigger, response, delay, outcome and any breach of the clearing plan.
• Update the induction, pre clearance checklist, exclusion design and sequencing where the review identifies a weakness.
• Share significant records with the relevant state biodiversity database or custodian where permitted and appropriate.

Rehabilitation actions: 1. Restore habitat structure

Rehabilitation should restore connected acacia scrub rather than replace it with isolated structures. The Grey Honeyeater depends on small shrubs, foliage insects, nectar and mistletoe, and its habitat may take many years to recover after uncontrolled fire.

Use local provenance plants and a restoration design suited to the local semi arid community. Aim for dense, continuous shrub cover with a range of ages and retained mature mulga.

• Protect retained mulga and other acacias during earthworks, weed control and maintenance.
• Replant cleared edges and temporary work areas with locally appropriate acacias and other native shrubs.
• Retain or restore mistletoe where it occurs naturally and where the host plants can support it.
• Avoid broadscale burning in restored or retained mulga. Manage fire risk through the approved regional fire plan and protect recovering scrub from uncontrolled fire.
• Control grazing and browsing that prevents shrub regeneration.

Rehabilitation actions: 2. Food and shelter resources

Maintain a mosaic of foliage, flowering shrubs and mature acacia. The species gleans lerp and other insects, takes nectar from deep tubular flowers such as Eremophila, and feeds on mistletoe nectar and berries.

• Use local native species that provide foliage, flowers and fruit at different times of year.
• Avoid insecticide use in retained or rehabilitated habitat unless approved and necessary, and use targeted methods that minimise impacts on insect prey.
• Do not clear flowering shrubs or mistletoe solely to tidy a site.
• Provide connected vegetation between retained patches and nearby habitat where the project footprint allows.
• Do not install supplementary feeding stations.

Rehabilitation actions: 3. Nesting structures and site features

The Grey Honeyeater nests in slender twigs in the outer foliage of mulga shrubs. Nest boxes, bat boxes, artificial roosts and cave structures do not match the known nesting behaviour of this species and should not be used as a routine replacement measure.

• Restore suitable live shrubs and outer foliage instead of installing nest boxes.
• Do not attach artificial nests to shrubs unless a qualified ecologist and the relevant authority have approved a species specific trial.
• If an artificial nest site is proposed, define its purpose, design, hygiene controls, placement, monitoring and removal criteria before installation.
• Do not provide bat boxes, roost structures or other fauna infrastructure as a substitute for retaining Grey Honeyeater habitat.

Rehabilitation actions: 4. Weeds, water and lighting

Keep rehabilitation areas suitable for a small insectivorous and nectar feeding bird. New water points and artificial lighting can change predator activity, insect behaviour and movement patterns, so use them only where they have a clear ecological purpose.

• Control weeds before they set seed and use methods that protect regenerating acacias and flowering native shrubs.
• Prevent weed spread on vehicles, machinery, soil and mulch entering rehabilitation areas.
• Do not create permanent artificial water points for the Grey Honeyeater unless they are part of an approved local ecological design and can be maintained safely.
• Use downward directed, shielded lighting only where required for safety, and avoid lighting retained or rehabilitated scrub at night.
• Manage waste, food and water sources so they do not attract feral animals or increase predation risk.

Rehabilitation actions: 5. Long term monitoring

Monitor rehabilitation for establishment of acacia cover, mistletoe, flowering plants, insect activity and Grey Honeyeater use. Set the duration and frequency through the project approval and ecological risk assessment.

• Use permanent photo points and mapped vegetation plots to track shrub survival, recruitment, weeds, grazing and fire impacts.
• Record Grey Honeyeater sightings, calls, flock associations, feeding behaviour and any nesting activity during suitable seasonal surveys.
• Compare rehabilitated areas with nearby retained reference habitat where practical.
• Repair failed plantings, control new weeds and address erosion or grazing promptly.
• Continue monitoring until the site is stable and provides functional shrub habitat, not merely until planting is complete.

Sources

• [PDF] 2023 (IOC v13.1) Queensland bird species list with scientific names, BirdLife Australia: https://birdlife.org.au/wp-content/uploads/2026/01/IOC-2023-Qld_List-2colbinomial.pdf
• Grey honeyeater - Wikipedia, Wikipedia: https://en.wikipedia.org/wiki/Conopophila_whitei
• Occurrence records for the distribution map, Atlas of Living Australia: https://biocache.ala.org.au/