Brown Honeyeater (Lichmera indistincta)

Conservation status

South Australia, National Parks and Wildlife Act 1972: Rare. This listing covers only Lichmera indistincta indistincta.

Breeding season

The Brown Honeyeater breeds in Australia from June to January. Timing may vary between regions, particularly across its broad range, so use local observations to refine site controls. It is listed as Rare in South Australia and as Priority 4 in Western Australia, so apply targeted habitat and nest checks where clearing is proposed, with added care around active breeding places in Queensland.

Breeding mode: Egg laying in small, cup-shaped nests.

Breeding season: June to January.

Clutch size: Up to three eggs.

Eggs: Matt white.

Nest site and materials: Small cup-shaped nests made from bark strips, grasses and sometimes spiderwebs, lined with down or hair.

Incubation period: Not recorded.

Fledging, weaning and age at maturity: Not recorded.

Breeding timing may vary between years and regions, so local records, pre-clearance checks and observations during works should be used to adjust controls.

• Breeding and nesting: Breeding is recorded from June to January, but the timing of mating, laying and nest completion within that period is not defined.
• Eggs and nestlings: Egg and nestling periods are likely to occur within the recorded June to January breeding season, but their duration is not recorded.
• Dependent young: Dependent young may be present during the breeding season, so do not assume that a vacant nest means breeding has finished.
• Foraging and flower visitation: The Brown Honeyeater forages throughout the year on flower nectar and insects taken during visits to flowers.
• Highest clearing risk: Clearing and construction are most likely to harm nests, eggs and dependent young from June to January, so check flowering vegetation and dense shrubbery before works and manage active breeding places under applicable state requirements.

Identification: Appearance and size

The Brown Honeyeater is a small, modestly plumaged honeyeater with a long, curved bill. It can be active and conspicuous around flowering plants, but its plain appearance means it may be overlooked during clearing inspections.

Adults are 110 to 160 mm long. The bill is lengthened and curved for probing flowers.

The tongue has a frayed tip. The sides curl upwards to form a more or less closed tube, an adaptation for taking nectar.

Group: Bird

Family: Meliphagidae

Typical appearance: Small and modestly plumaged

Identification: Calls and similar species

The Brown Honeyeater has a loud, spirited song. During the nesting season, the song has been likened to that of the Reed-warbler.

Call identification should be checked with a reference recording or an experienced observer, particularly where several small honeyeaters are present.

• Use the whole combination of bill shape, size, plumage, behaviour and call.
• Do not rely on song alone when making a clearing decision.

Identification: Field signs

Look for the bird itself, repeated visits to flowering plants and active feeding around shrubs, street trees and gardens.

Small cup-shaped nests may be present in suitable vegetation during June to January. Nests can be difficult to see because they are made from bark strips and grasses and may be lined with down or hair.

• Inspect shrubs and low vegetation before clearing.
• Pause work if an active nest or a bird repeatedly carrying nesting material is detected.
• Record the location of sightings, nests and regularly used flowering plants.

Distribution: Australian range

The Brown Honeyeater is widespread in Australia and is mapped in New South Wales, the Northern Territory, Queensland, South Australia, Victoria and Western Australia. In Western Australia it occurs across coastal and inland areas, with habitat use changing between wetter forest regions and arid country.

The species is mapped in New South Wales, the Northern Territory, Queensland, South Australia, Victoria and Western Australia.

In Western Australia it occurs throughout the state, including coastal and inland areas.

• Expect records in both developed and undeveloped landscapes.
• Treat a suitable site as potentially occupied even if the species has not been recorded there previously.

Distribution: Regional patterns

In the south-west Jarrah forest belt, Brown Honeyeaters tend to use more open areas, including areas where settlement has been established.

In more arid parts of the country, they are associated with dense shrubbery around granite outcrops and with towns that have street trees and gardens.

Distribution: Project survey approach

Plan surveys around the vegetation and flowering resources present on the site, rather than relying only on broad regional distribution maps.

Check retained vegetation, garden plantings, shrub patches and edges of open woodland. Repeat observations can help confirm regular use where the species is detected.

• Include nearby retained vegetation and connected shrub patches in the site assessment.
• Record the date, location, habitat and behaviour of each observation.
• Consider the species during pre-clearing checks in all mapped states.

Habitat: Vegetation types

Brown Honeyeaters use a range of terrestrial habitats, from open woodland and scrub to planted vegetation in towns. Retained flowering shrubs, trees and dense patches around landforms can remain useful even where a site is partly developed.

Look for open woodland, scrub, open areas within denser forest, street trees and gardens.

In the south-west, more open parts of the Jarrah forest belt may be used, particularly around settled areas.

• Open woodland with flowering trees or shrubs.
• Dense scrub patches and shrub edges.
• Street trees, gardens and other planted vegetation.

Habitat: Landforms and landscape features

In arid areas, dense shrubbery around granite outcrops can provide habitat. Towns with street trees and gardens may also support the species where surrounding vegetation is sparse.

Map these features before ground disturbance and include them in the site habitat assessment.

• Granite outcrops with dense surrounding shrubbery.
• Vegetated edges and openings within forest.
• Connected patches of shrubs and flowering trees.

Habitat: Site inspection points

Walk the proposed clearing footprint and the margins of access tracks, compounds and work areas. Note flowering plants, dense shrubs and trees that will be retained or removed.

A habitat assessment should cover the full area likely to be affected, including temporary disturbance areas and vegetation beside work zones.

• Mark high quality flowering vegetation on plans.
• Identify retained habitat that could be isolated by clearing.
• Keep access routes and stockpile areas away from dense shrub patches where practicable.

Foraging habitat: Food resources

The Brown Honeyeater feeds mainly on flower nectar and also takes insects during visits to flowers. Flowering plants within a clearing footprint, along site edges and in nearby gardens can therefore attract regular use.

Inspect flowering trees, shrubs and garden plants for feeding birds. The species uses its curved bill to probe flowers.

Insects form a substantial part of its diet, so flowering vegetation may be used for both nectar and insect foraging.

• Flowering shrubs and small trees.
• Open woodland with flowering trees.
• Garden and street plantings, especially in towns and arid areas.

Foraging habitat: Foraging behaviour to record

Record repeated visits, birds moving between flowering plants and birds taking insects from flowers. These observations can help identify habitat that is being used even when no nest is found.

Surveyors should allow time to watch flowering patches rather than relying only on a quick walk through the site.

• Note the plant or vegetation type being used where it can be identified.
• Record whether birds are feeding, moving through or defending an area.
• Photograph flowering plants and habitat features for the site file.

Foraging habitat: Management during works

Retain flowering vegetation where possible, especially where it forms a connected patch with other shrubs or trees. Avoid unnecessary removal of street trees, gardens and dense shrubbery in otherwise open or arid landscapes.

Where clearing cannot be avoided, stage works and retain nearby feeding habitat where practicable.

• Fence retained flowering plants before works begin.
• Keep machinery and materials out of retained feeding areas.
• Rehabilitate disturbed areas with locally appropriate vegetation where required by the project.

Breeding habitat: Nest and breeding features

Breeding occurs from June to January. The species builds small cup-shaped nests in vegetation, so low shrubs and other dense plants within or beside a clearing footprint need a careful pre-clearing inspection during this period.

The nest is small and cup-shaped. It is made from bark strips, grasses and sometimes spiderwebs, and lined with softer material such as down or hair.

A clutch may contain up to three matt white eggs.

Breeding season: June to January

Nest form: Small cup-shaped nest

Nest materials: Bark strips, grasses and sometimes spiderwebs, with down or hair lining

Clutch size: Up to three eggs

• Inspect dense shrubs and low vegetation closely.
• Look for birds carrying bark, grass, spiderweb or lining material.
• Watch for repeated adult visits to one location.

Breeding habitat: Pre-clearing checks

Complete a targeted pre-clearing check during the breeding season and immediately before vegetation removal. Search the entire footprint, including access routes, temporary work areas and vegetation along edges.

Use a suitably experienced fauna spotter catcher or ecologist to inspect shrubs and other potential nest sites.

• Search from more than one angle where vegetation is dense.
• Check for adults alarm calling, carrying material or repeatedly entering cover.
• Clearly mark any nest and stop work in the immediate area until the appropriate project response is confirmed.

Breeding habitat: Protection during construction

Avoid clearing active nests. Keep workers, vehicles and machinery away from occupied nest areas and minimise disturbance while breeding is underway.

The exact response should follow the approval conditions and the relevant state requirements. In Queensland, tampering with a protected animal's breeding place may require a species management program.

• Brief all workers on nest awareness and stop-work procedures.
• Maintain the nest location on the site map and communicate it at pre-starts.
• Reinspect retained vegetation if works are staged or delayed.

Sheltering habitat: Potential shelter features

Specific roosting and sheltering sites are not well documented for the Brown Honeyeater. For field planning, treat dense shrubs, woodland vegetation, gardens and sheltered vegetation edges as potential cover, especially where they are close to flowering food plants.

Dense shrubbery around granite outcrops is relevant in arid areas. Shrubs, street trees, gardens and open woodland can also provide cover in settled or more productive landscapes.

Retain connected vegetation where practicable, particularly where it links feeding areas with denser cover.

• Dense shrub patches.
• Vegetated woodland edges and openings.
• Street trees and gardens in towns.
• Shrubbery around granite outcrops.

Sheltering habitat: Inspection and work planning

During site walks, note where birds retreat after being approached and where they spend time between feeding bouts. These observations can identify locally important cover.

Avoid placing compounds, access tracks or stockpiles in dense retained vegetation where another practical location is available.

• Map dense vegetation and likely movement links.
• Keep retained cover clearly fenced and signed.
• Use gradual clearing and a fauna spotter catcher where required by the project.

Sheltering habitat: Knowledge limits for field decisions

The species is not well documented in relation to specific roost structures or shelter requirements. Use direct observations and habitat condition to guide decisions rather than assuming that only large trees or mature forest are relevant.

A small shrub patch may still provide useful cover when it is part of a larger habitat network.

• Record cover used by observed birds.
• Include low vegetation and planted habitat in the assessment.
• Escalate uncertain observations to the project ecologist before clearing.

Threats: Vegetation clearing

Development can affect Brown Honeyeaters by removing feeding and breeding vegetation or by disturbing birds during the breeding season. The strongest site response is to identify occupied habitat early, avoid unnecessary clearing and protect retained vegetation throughout the works.

Clearing open woodland, scrub, flowering plants, street trees or gardens can remove food and cover. Loss of dense shrubbery around granite outcrops may be particularly relevant in arid areas.

Include temporary work areas, laydown areas and access tracks when assessing clearing impacts.

• Avoid clearing flowering vegetation where practicable.
• Reduce the clearing footprint and retain connected shrub patches.
• Clearly fence vegetation that is to remain.

Threats: Breeding place disturbance

Clearing during June to January can destroy small cup-shaped nests or disturb adults attending nests. Nests may be concealed in shrubs and can be missed during a rapid inspection.

Use a pre-clearing check and a clear stop-work process for active nests.

• Schedule vegetation removal outside the breeding season where practicable.
• Inspect immediately before clearing when work occurs during June to January.
• Do not disturb an active nest until the required ecological and regulatory response is confirmed.

Threats: Habitat fragmentation and site use

Breaking up flowering vegetation and dense cover can reduce the usefulness of retained habitat. Machinery, stockpiles and compounds can also prevent birds from using otherwise suitable vegetation.

Plan works to keep retained habitat connected and free from avoidable disturbance.

• Keep access routes away from retained shrub and woodland patches.
• Maintain links between flowering plants and sheltering vegetation.
• Rehabilitate temporary disturbance areas with suitable local vegetation where required.

Threats: Listing and compliance

The Brown Honeyeater 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 need monitoring.

In Queensland, near threatened animals are protected wildlife, and tampering with their breeding place needs a species management program. Confirm the current approval, permit and fauna management requirements for the state and project.

South Australia: Rare

Western Australia: Priority 4, a non-statutory DBCA category

Queensland: Protected wildlife provisions apply to near threatened animals, including requirements relating to breeding places

• Scale survey effort to the quality of habitat, planned clearing and likelihood of breeding use.
• Use experienced fauna personnel for pre-clearing checks in suitable habitat.
• Document observations, nest checks, avoidance measures and any stop-work actions.

Survey methodology: 1. Desktop assessment

Brown Honeyeaters are small, active birds that can be detected by their loud song, calls and visits to flowering plants. Survey effort should focus on suitable flowering and nesting habitat, and should cover the conditions and season when works may occur.

Map open woodland, scrub, flowering vegetation, street trees, gardens and dense shrubbery around granite outcrops. In the south-west Jarrah forest belt, include more open areas and settled sites.

Identify vegetation that could support cup nests, including shrubs and small trees. Check whether the site is in South Australia, Western Australia or Queensland, where additional conservation or wildlife requirements may apply.

• Review recent records, habitat mapping, aerial imagery, flowering resources and previous ecological reports.
• Confirm the current state conservation listing and any project approval conditions before finalising survey effort.
• Check whether the project needs an EPBC Act referral, a Queensland species management program, or state wildlife, threatened species or clearing approvals.

Survey methodology: 2. Field detection

Survey on calm days with good visibility, preferably during the early part of the day when birds are active and singing. Avoid relying on a single visit during heavy rain, strong wind, extreme heat or poor visibility.

Listen for the Brown Honeyeater's loud, spirited song and watch flowering plants for nectar feeding and insect capture. Inspect dense shrubbery and small trees for cup nests made from bark strips, grasses and sometimes spiderwebs.

• Walk slowly through or beside suitable habitat and pause regularly to listen and scan the canopy, shrubs and flowering plants.
• Use binoculars where practical. Do not approach a suspected nest closely unless this is necessary for an approved pre-clearance inspection.
• Repeat surveys where habitat is extensive, visibility is limited, flowering is variable, or the first visit produces uncertain results.
• Include surveys during June to January when works could affect nesting birds. Do not assume that birds are absent outside this period.

Survey methodology: 3. Effort and conditions

Set survey coverage and repeat visits according to the size, habitat complexity and risk of the clearing activity. Increase effort where dense vegetation, poor access or construction noise may reduce detection.

There is no reliable basis for treating one negative visit as proof that the site is unused. Brown Honeyeaters may be inconspicuous when not singing or when moving between flowering areas.

• Record the date, start and finish time, weather, wind, visibility, surveyors, route and area covered.
• Record every sighting, call, direction of travel, feeding location, pair or dependent young, suspected nest and observed breeding behaviour.
• Map flowering plants, dense shrubbery, nest locations and areas that will be cleared or retained.
• Keep photographs, GPS points and audio records where they can be collected without causing disturbance.

Survey methodology: 4. Interpretation and reporting

Treat a nest, dependent young, repeated adult activity or regular use of flowering habitat as a constraint requiring review before works proceed. Have a suitably experienced ecologist assess uncertain records.

Separate confirmed observations from assumptions. State the survey limitations, habitat that was not searched and the conditions that may have reduced detection.

• Provide a site plan showing records, proposed clearing, retained habitat and any recommended no-go areas.
• Give the site supervisor and fauna spotter catcher a plain language summary of identification features, likely habitat and stop-work triggers.
• Update the assessment if clearing is delayed into a different season or if the design changes.

Before habitat disturbance: 1. Approvals and legal checks

Plan to retain flowering and nesting habitat wherever practicable. The Brown Honeyeater breeds from June to January, so works in this period need stronger pre-clearance controls and close supervision.

Confirm the conservation status that applies at the site. The species is listed as Rare in South Australia and as Priority 4 in Western Australia. In Queensland, near threatened animals are protected wildlife, and tampering with a breeding place may require a species management program.

The Brown Honeyeater is profiled as an EVNT species. Do not assume that this profile alone creates an EPBC listing. Check the current EPBC protected matters information and obtain advice on referral requirements if the project may affect a listed matter.

• Obtain required state permits, clearing approvals and wildlife authorisations before disturbance.
• In Queensland, confirm whether a species management program is required before tampering with a breeding place, and comply with its conditions.
• Use only fauna spotter catchers and other personnel who are authorised for the relevant work and handling activities.
• Record approval numbers, conditions and stop-work requirements in the site environmental plan.

Before habitat disturbance: 2. Avoidance and timing

Retain mature flowering trees, shrubs, dense vegetation around granite outcrops, street trees and garden habitat where possible. Protect connected patches of vegetation that allow birds to move between feeding and nesting areas.

Where practicable, schedule high-disturbance works outside June to January. There is no established migration period to use as a general timing rule, so manage the site on the basis of local observations and breeding evidence.

• Redesign work areas to avoid active nests, dependent young and the surrounding vegetation used for access and feeding.
• Stage clearing so that retained habitat remains available while works progress.
• Use a site-specific buffer around any active nest or breeding place. Set the distance with the ecologist and approval conditions, considering noise, machinery, visibility and the bird's response.
• Stop and reassess if adults repeatedly alarm, carry nesting material or food, or remain near a suspected nest.

Before habitat disturbance: 3. Pre-clearance survey

Complete a targeted pre-clearance inspection shortly before clearing. Search flowering plants, dense shrubs and small trees for the small cup-shaped nests used by this species.

Survey the full disturbance footprint and likely escape habitat. Include edges, stockpiles, access tracks and vegetation that may be damaged by machinery or access.

• Search from the ground and use binoculars to inspect vegetation without shaking or disturbing it.
• Look for matt white eggs, chicks, adults carrying nesting material or food, and repeated adult movement to one location.
• Mark active nests and nearby no-go areas on the ground and on the site plan.
• Repeat the inspection if clearing is postponed, the footprint changes, or vegetation conditions change substantially.

Before habitat disturbance: 4. Induction and exclusion

Give all workers a short site induction before clearing starts. The induction should cover the Brown Honeyeater's appearance, song, nesting habitat and the authority of the fauna spotter catcher to stop work.

Install visible exclusion markers around retained habitat, active nests and other sensitive areas. Keep machinery, materials, vehicles and personnel outside these areas.

• Tell workers not to feed, chase, catch, photograph at close range or handle birds.
• Explain the reporting pathway for a nest, injured bird, dead bird or suspected breeding place.
• Confirm who will contact the ecologist, wildlife carer, regulator and project manager if an incident occurs.
• Keep domestic animals and unnecessary personnel away from retained habitat.

During habitat disturbance: 1. Sequential clearing

Clear habitat progressively and keep a qualified fauna spotter catcher involved throughout the work. The spotter catcher must be able to stop machinery immediately when a bird, nest or other breeding evidence is found.

Use staged, directional clearing that allows mobile birds to move towards retained habitat. Remove non-habitat materials and loose debris first, then clear vegetation in small sections under direct supervision.

Do not fell or push vegetation containing an active nest until the ecologist and relevant authority have confirmed the lawful approach.

• Reinspect each section immediately before clearing it.
• Keep machinery at low speed near retained vegetation and stop when the spotter catcher gives the signal.
• Maintain clear access for the spotter catcher and an unobstructed route to retained habitat.
• Avoid unnecessary night lighting and night works near flowering or nesting habitat.

During habitat disturbance: 2. Stop-work triggers

Stop work if an active nest, dependent young, a distressed adult, an injured bird or a previously unidentified concentration of birds is found. Stop work also if vegetation suspected to contain a nest cannot be inspected safely.

The spotter catcher should establish a temporary exclusion area and notify the supervisor, project ecologist and approval contact. The exclusion area and next steps should follow the approval conditions and site-specific risk assessment.

• Do not move an active nest, eggs or chicks unless this is directed and authorised by the relevant wildlife authority and undertaken by an appropriately authorised person.
• Do not destroy, damage or obstruct a breeding place.
• Record the location, habitat, bird behaviour, nest status, photographs and the time of the stop-work event.
• Resume only after the authorised person or ecologist has documented the decision and the supervisor has briefed the crew.

During habitat disturbance: 3. Handling and release

Handle Brown Honeyeaters only when necessary, by people authorised and trained for wildlife handling. Most healthy birds should be left to move away from the disturbance into suitable retained habitat.

Use a secure, quiet container and minimise handling time if an authorised person decides that capture is necessary. Do not give food or water unless directed by a qualified wildlife carer or veterinarian.

• Release a healthy bird only at a suitable location agreed by the fauna spotter catcher or ecologist, with access to shelter and food plants.
• Do not relocate a nest, eggs or chicks without specific approval and a suitable specialist plan.
• Keep workers and machinery away from the release point until the bird has settled.
• Record the reason for handling, the person who handled the bird, its condition, destination and outcome.

During habitat disturbance: 4. Injured or dead animals

Treat an injured Brown Honeyeater as a wildlife incident. Keep the area quiet and prevent further contact with people, vehicles and machinery.

Obtain advice from the project ecologist, an authorised wildlife carer or a veterinarian. Follow state requirements for transport, treatment and reporting.

• Use gloves and a clean, ventilated container if an authorised person must secure the bird.
• Do not attempt treatment in the field.
• Report a death, suspected collision or machinery strike to the project manager and record the likely cause.
• Inspect the surrounding work area for additional hazards before restarting.

After habitat disturbance: 1. Post-clearance checks

A final inspection should confirm that clearing was completed within the approved footprint and that no bird, nest or retained habitat has been overlooked. Follow-up should focus on unresolved incidents, breeding evidence and the condition of retained vegetation.

Inspect the cleared area, retained vegetation, access tracks and material storage areas after work. Look for injured birds, displaced nests, dependent young and damage to exclusion zones.

Check that retained flowering plants and dense shrubbery remain connected and free from avoidable damage.

• Confirm that all active stop-work events were closed by the authorised person or ecologist.
• Remove temporary markers only when the site manager and ecologist agree that they are no longer needed.
• Record any unplanned clearing, nest damage, bird mortality or disturbance to breeding habitat.
• Arrange a further inspection if clearing occurred during June to January or if breeding behaviour was observed.

After habitat disturbance: 2. Monitoring and relocated animals

Monitor retained habitat and any authorised release location when required by an approval, management plan or incident response. Use the same locations and methods where repeat observations are needed.

Do not assume that a bird has survived or settled because it was released. Record later observations where practical, without repeatedly approaching the bird.

• Check for feeding, normal flight, calls and continued use of suitable vegetation.
• Escalate birds that remain grounded, cannot fly, show abnormal behaviour or are repeatedly found near machinery.
• Follow up any authorised nest or young relocation through the responsible wildlife authority or specialist.
• Keep release and monitoring records with the project environmental file.

After habitat disturbance: 3. Reporting and incident review

Prepare a concise completion report for the project manager and relevant regulators or approval holders. Include survey results, clearing dates, personnel, incidents, actions and unresolved risks.

Review any failure to detect a nest, breach of an exclusion area, injury, mortality or unapproved handling. Use the findings to improve the next work stage.

• Compare the cleared footprint with approved plans and mapping.
• Document whether timing, weather, vegetation density, noise or crew behaviour affected detection.
• Update the induction, method statement, survey timing or exclusion controls where the review identifies a gap.
• Retain photographs, maps, permits, fauna registers and correspondence according to project and approval requirements.

Rehabilitation actions: 1. Restore habitat structure

Rehabilitation should restore feeding, shelter and nesting opportunities rather than rely on artificial structures. Brown Honeyeaters use small cup nests in vegetation, so healthy flowering shrubs and trees are generally more useful than nest boxes.

Replant local native shrubs and trees that provide flowers, dense cover and suitable small branches for cup nests. Use species suited to the local soil, rainfall and fire regime.

Retain natural regeneration where it is healthy and protect planted areas from trampling, grazing and machinery.

• Restore a range of vegetation layers, including flowering shrubs and small trees.
• Link rehabilitated areas with retained woodland, scrub, street trees, gardens or other suitable habitat where the site design allows.
• Use locally appropriate provenance where available and follow the project's ecological restoration plan.
• Replace damaged topsoil and manage erosion so new plantings can establish.

Rehabilitation actions: 2. Flowering resources, water and weeds

Plan for flowering resources across the year rather than a single short flowering period. Brown Honeyeaters feed mainly on nectar and also take insects at flowers.

Provide clean water only where it can be maintained safely and where it will not create a disease, drowning or predator risk. Water is not a substitute for suitable vegetation.

• Control weeds before planting and during establishment, using methods that do not damage retained habitat or expose birds to avoidable disturbance.
• Avoid planting invasive, non-local or unsuitable species solely because they flower heavily.
• Keep pesticide use away from flowering plants and use an integrated pest management approach.
• Inspect water points regularly and remove them if they become unsafe, contaminated or unused.

Rehabilitation actions: 3. Artificial structures

Standard nest boxes are not a known replacement for the Brown Honeyeater's small open cup nest. Bat boxes and roost structures do not suit this species and should not be installed as mitigation for it.

Artificial nest sites should be considered only where a suitably experienced ornithologist has identified a local need, designed a species-appropriate structure and obtained any required approval.

• Prioritise dense native shrubs and small trees over nest boxes.
• Do not move a natural nest into an artificial structure unless directed by an authorised wildlife specialist.
• If an artificial nest site is approved, document its design, location, installation method, inspection regime and removal or maintenance requirements.
• Keep artificial structures away from areas with high predator, vehicle, lighting or public access risk.

Rehabilitation actions: 4. Lighting, disturbance and monitoring

Limit artificial light near rehabilitated vegetation. Use shielded, downward-facing lights only where safety requires them, and avoid lighting flowering shrubs and retained nesting habitat.

Monitor rehabilitation for plant survival, weed invasion, flowering, bird use and disturbance. Use results to guide replacement planting and maintenance.

• Replace dead plants and repair damaged exclusion fencing.
• Record Brown Honeyeater sightings, feeding activity, nesting evidence and use of restored habitat during follow-up surveys.
• Inspect rehabilitation during the establishment period and again after major maintenance or construction changes.
• Continue monitoring for as long as required by the approval or rehabilitation plan, with extra checks where the species was recorded breeding.

Sources

• [PDF] Brown Honeyeater - DBCA Library, WA Department of Biodiversity, Conservation and Attractions: https://library.dbca.wa.gov.au/Journals/080073/080073-12.012.pdf
• Occurrence records for the distribution map, Atlas of Living Australia: https://biocache.ala.org.au/