Striped Honeyeater (Plectorhyncha lanceolata)

Conservation status

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

Breeding season

The Striped Honeyeater is a resident Australian honeyeater that breeds in Australia. Breeding is documented in August, but timing may vary between regions and years, so active nests should be checked whenever suitable habitat is being cleared.

Breeding mode: Usually breeds as simple pairs and nests solitarily.

Breeding distribution: Breeds throughout its distribution range.

Nest sites: Usually nests in drooping foliage at the end of a branch in a tall shrub or low tree, including Casuarina, Melaleuca, Acacia and mallee eucalypts. Sites may be near or overhanging water.

Clutch size: Not recorded.

Incubation period: Not recorded.

Fledging and dependence: Not recorded.

Breeding frequency: Not recorded. Pairs may use the same or adjoining trees over two or more seasons.

Timing may shift between regions and years, and the species is poorly known in some parts of its range, so pre-clearing surveys should look for adults, alarm calls, nest material and suspended cup or bag-shaped nests whenever suitable habitat is present.

• Breeding activity: Breeding is documented in August, although the full breeding window may be broader in some regions or years.
• Nesting and dependent young: Treat suitable drooping foliage in shrubs and low trees as potential nesting habitat during the documented breeding month.
• Foraging and local movement: Foraging is mainly arboreal, with birds using foliage, flowers, branches and bark in woodland, mallee and other suitable habitats.
• Loose-group activity: Outside breeding, birds may occur in loose mobile groups and may join mixed-species feeding groups with other honeyeaters.
• Highest clearing risk: August is the highest documented risk period because clearing may disturb nests, eggs or dependent young, but active nests can occur outside this month.

Identification: Appearance and field marks

The Striped Honeyeater is a medium sized, greyish brown honeyeater with strong dark streaking. It is usually detected by movement and calls in woodland foliage rather than by distinctive ground signs.

Adults are light greyish brown above, with dark centres to the feathers giving a striped appearance. The head and back of the neck are particularly streaked.

The underparts are whitish with fine belly streaks. Long pointed feathers on the throat and upper breast give the head a slightly spiky appearance.

The bill is short, straight and sharply pointed. It is dark blue grey, becoming grey black at the tip and around the nostrils. The legs and feet are blue grey.

• Body length is 22 to 25 cm.
• Wings and tail are moderately long with rounded tips.
• Both sexes look similar.
• Juveniles are browner and less clearly streaked than adults.

Identification: Calls and similar species

The song has been described as a repeated chirp, chirp, cherry, cherry. The contact call is a sharp chewee, and the alarm call is a shrill whistle.

No single look alike is identified for field work. Other honeyeaters commonly occur nearby, including Spiny cheeked Honeyeaters, Yellow throated Miners and Singing Honeyeaters. Check the bill shape, streaked head and pale underparts before recording a sighting.

• Listen for sharp contact calls from dense canopy and upper branches.
• Record associated honeyeater species, but do not assume a mixed flock contains Striped Honeyeaters.
• Use photographs or a clear description where the bird is seen briefly or in poor light.

Identification: Field signs

The species forages mainly in foliage, twigs and branches, so birds may be detected by movement in the canopy. It often moves quickly between trees and may remain in each tree for only a short time.

No distinctive droppings, stains, odour, whitewash or roost sign is available for reliable site identification. Nests are the most useful breeding sign, but they can be concealed by foliage and nesting material.

• Search the 2 to 10 m canopy and upper branches during fauna inspections.
• Listen for contact calls before entering dense woodland or starting noisy works.
• Treat a suspected nest as active until it has been assessed by a suitably qualified person.

Distribution: Range in Australia

The Striped Honeyeater occurs mainly in eastern and inland Australia. It is mapped in New South Wales, Queensland, South Australia and Victoria, with records extending from inland Queensland to south eastern South Australia and coastal New South Wales.

The species occurs in semi arid to subtropical areas of eastern Australia. It is reported from central and south eastern Queensland, inland and coastal New South Wales, north western and south eastern Victoria, and mallee areas of South Australia.

In New South Wales it has been recorded in the Moree district, south western mallee and woodland near Buronga and Mungo, and coastal areas south to the Tuggerah Lakes. Coastal swamp forest records extend from south eastern Queensland to the central New South Wales coast.

• South western New South Wales includes Black Oak woodland, mallee and mixed Black Oak and mallee woodland.
• South Australian records include mallee landscapes.
• Small movements or irruptions have been recorded outside the usual range, including the Grampians and Adelaide Plains.

Distribution: Site assessment

Do not rule out the species because a site is small, modified or close to development. It has been recorded in farms, orchards, reserves, gardens and other areas containing suitable native or exotic trees and shrubs.

Records may be uneven because the species is mobile, often quiet while feeding and partly hidden by foliage. A site assessment should consider nearby connected woodland, riparian vegetation and mallee, not only the area proposed for clearing.

• Check state and local records before clearing or construction.
• Map retained woodland, mallee, riparian trees, dense shrubs and flowering or fruiting plants.
• Treat a record in suitable habitat as relevant to the wider vegetation patch, not only the point of observation.

Distribution: Conservation status and survey response

The species is profiled as an EVNT species. South Australia lists the Striped Honeyeater as Rare under the National Parks and Wildlife Act 1972.

In Queensland, near threatened animals are protected wildlife. Interference with a breeding place may require a species management program. Confirm the current approval and management requirements before works begin.

• Use targeted searches where suitable habitat will be cleared or heavily disturbed.
• Repeat observations across suitable daylight survey periods because birds move between trees and may form mobile groups.
• Escalate any breeding record, repeated sighting or concentration of birds to the project ecologist and relevant state authority.

Habitat: Woodland and mallee

Look for the Striped Honeyeater in open woodland and shrub dominated vegetation with a developed canopy and varied foliage. Mixed woodland appears particularly useful, especially where Black Oak and mallee occur close together.

Recorded habitats include Black Oak woodland, mallee woodland and mixed Black Oak and mallee woodland. In south western New South Wales, the species appeared most common in mixed woodland and least common in dense mallee.

The species also uses drier open forest, mulga, riparian woodland, heathland, coastal mangrove and swamp forest. Riparian trees may include River Red Gum, Bimble Box and Black Box with lignum or saltbush understorey.

• Casuarina and Allocasuarina woodland.
• Mallee with Broombush or Emu bush thickets.
• Acacia dominated semi arid scrub, including lancewood.
• Native pine woodland on sand ridges.
• Paperbark and Casuarina swamp forest.

Habitat: Vegetation structure

Prioritise sites with trees and shrubs from about 2 to 10 m high, dense foliage, live and dead branches, loose bark and a connected canopy. The species may use both mallee dominated and Black Oak dominated areas.

Western Rosewood can be present but was little used for foraging in one study area. Habitat value is likely to depend on the overall mix of trees, shrubs and feeding resources rather than on one plant species alone.

• Retain groups of mature and regenerating woodland trees where practicable.
• Avoid isolating small patches of mallee, Black Oak or riparian woodland.
• Inspect vegetation that appears sparse from ground level, as birds may be feeding in the upper canopy.

Habitat: Construction site indicators

Potential habitat includes road reserves, farm shelterbelts, orchard margins, creek lines, reserves, gardens and other developed areas with suitable trees and shrubs.

A site has higher survey priority where woodland types meet, flowering trees are present, or dense shrubs occur beneath taller trees. Nearby water is relevant because nests may be placed in vegetation near or overhanging water.

• Map habitat on both sides of access tracks, easements and proposed clearing limits.
• Include retained vegetation that may be used during construction, even if it is outside the direct impact area.
• Inspect tree and shrub lines before trimming, slashing, earthworks or night lighting installation.

Foraging habitat: Foraging plants

The Striped Honeyeater is mainly insectivorous and forages in foliage, twigs, branches and flowers. Its short pointed bill is used to probe bark, crevices and woody fruits as well as to glean insects from vegetation.

Recorded foraging plants include Black Oak, Yorrell, Red Mallee, Sugarwood, Western Rosewood and Wilga. Most recorded foraging was on Casuarina, Eucalyptus and Myoporum.

Black Oak cladodes and apical shoots were important substrates. Yorrell flowers were probed, and Red Mallee loose bark and rough bark crevices were used.

• Black Oak, Casuarina pauper.
• Yorrell, Eucalyptus gracilis.
• Red Mallee, Eucalyptus socialis.
• Sugarwood, Myoporum platycarpum.
• Western Rosewood, Alectryon oleifolius.
• Wilga, Geijera parviflora.

Foraging habitat: Foraging behaviour

Birds generally forage from a perch in an upright position. They sometimes hang upside down and may break or manipulate dead twigs while probing them.

Hawking for insects has been observed. Birds may feed independently or move together in loose, mobile groups, including mixed groups with Yellow throated Miners.

• Gleaning from leaves, twigs and live or dead branches.
• Probing under loose bark and into rough bark crevices.
• Probing among the woody fruits of Black Oak and mallee eucalypts.
• Probing flowers for nectar or insects.

Foraging habitat: Management during works

Retain mature trees, dead branches that are safe to keep, loose bark habitat and flowering shrubs where possible. Avoid removing a whole line of feeding trees when a staged or narrower clearing option is available.

Dust, noise and clearing can reduce the usefulness of feeding vegetation. Keep machinery within approved footprints and protect retained canopy from damage, soil compaction and root disturbance.

• Schedule vegetation inspections before clearing and after major design changes.
• Retain links between Black Oak, mallee, riparian and shrub habitats.
• Control weeds and manage fire so that the varied canopy and shrub structure is maintained.

Breeding habitat: Nest sites

The Striped Honeyeater breeds throughout its range, usually as solitary pairs. Nests are suspended in drooping foliage and may be difficult to see from the ground.

Nests are usually placed at the end of a drooping branch and suspended from twigs or foliage. Nest sites may be in Casuarina, Melaleuca, Acacia or mallee eucalypts.

A nest may be a deep cup or a bag shaped structure. It is made from fine dry grass, plant down, feathers, wool, spider webs, hair and rootlets. The outer coating can hide the grass framework.

• Search low trees and tall shrubs with drooping foliage.
• Inspect vegetation near or overhanging water.
• Look for a thick walled nest with a slightly inward turned lip.
• Check adjoining trees because pairs may reuse the same or nearby trees over more than one season.

Breeding habitat: Breeding behaviour

The species nests solitarily and does not form breeding colonies. It often nests near a nesting butcherbird.

Nesting material from earlier nests is commonly reused. A nest may therefore be present in a tree even when adult birds are not immediately visible.

• Do not rely on an adult bird carrying nesting material as the only breeding indicator.
• Inspect likely nest trees from several angles and avoid shaking or disturbing branches.
• Record nest position, tree or shrub species, height and surrounding vegetation.

Breeding habitat: Protection on works sites

Before clearing, trimming or relocating vegetation, check for active nests and recently used nest structures. If a nest is found, stop work in the immediate area and obtain advice from the project ecologist.

In Queensland, tampering with the breeding place of protected near threatened wildlife may require a species management program. In South Australia, the Rare listing should be considered when assessing clearing, disturbance and mitigation options.

• Establish a site specific no work area around any active nest, based on professional advice and approval conditions.
• Use fauna spotter catchers where required by the approval or management plan.
• Retain adjoining trees and shrubs where they form part of the nesting territory.

Sheltering habitat: Likely shelter features

Specific roost sites are not well documented for this species. For site planning, treat dense foliage, connected woodland and sheltered tree and shrub cover as likely resting and refuge habitat.

The species spends much of its time in woodland canopies and upper branches. Mallee, Black Oak, riparian trees, paperbark and dense shrub layers can provide cover between feeding movements.

Retain vegetation with overlapping foliage, drooping branches and a range of tree sizes. These features may also provide protection from weather and predators.

• Dense mallee and mixed mallee woodland.
• Black Oak and Casuarina canopy.
• Riparian woodland with lignum or saltbush understorey.
• Paperbark, Acacia and Melaleuca shrub cover.
• Connected vegetation along creek lines, drainage lines and woodland edges.

Sheltering habitat: Shelter during construction

Keep retained habitat continuous where possible. Avoid creating isolated trees surrounded by cleared ground, particularly beside active work areas.

Limit unnecessary night lighting, prolonged noise and repeated vehicle movement beside retained vegetation. These measures also reduce disturbance to other woodland fauna.

• Fence and clearly mark retained vegetation before works start.
• Keep stockpiles, compounds and access tracks outside retained canopy and shrub cover.
• Maintain escape routes through connected vegetation during staged clearing.
• Use progressive clearing rather than removing all vegetation at once where practicable.

Sheltering habitat: Survey and monitoring

Search sheltered canopy and dense foliage during daytime fauna inspections. Listen for contact calls and watch for small groups moving rapidly between trees.

Because group size and movement can vary, a single quiet visit should not be treated as proof that the species is absent from suitable habitat.

• Record birds using retained vegetation, not only birds within the clearing footprint.
• Repeat checks after clearing stages or major changes to the work area.
• Report repeated use of retained habitat to the site ecologist so controls can be reviewed.

Threats: Vegetation clearing and fragmentation

The main work site risks are the loss of woodland and shrub habitat, removal of nesting vegetation and disruption of habitat connections. Management should be scaled to the EVNT profile and the applicable state listing.

Clearing Black Oak, mallee, riparian woodland, shrub thickets and mixed woodland can remove feeding, sheltering and nesting resources. Fragmentation may reduce movement between nearby patches.

Prioritise avoidance, then minimise the width and duration of clearing. Retain connected habitat and protect trees and shrubs outside the approved footprint.

• Avoid clearing where woodland types meet or where dense shrub cover occurs beneath trees.
• Retain habitat corridors along creek lines and drainage lines.
• Rehabilitate disturbed edges with locally appropriate native vegetation.

Threats: Loss of breeding places

Removing low trees, drooping shrubs or vegetation near water can destroy nests or reduce future nesting options. Repeated trimming can also remove the branch and foliage structure used for suspended nests.

Survey before clearing and trimming. Apply nest protection and fauna handling procedures required by approvals and state legislation.

• Inspect likely nest trees and shrubs before works.
• Stop work and seek advice if a nest or dependent young is found.
• Do not remove nearby vegetation until the breeding site has been assessed.

Threats: Fire, weeds and altered structure

Intense or poorly timed fire, weed invasion and excessive understorey removal can simplify woodland structure. This may reduce the mix of foliage, bark, branches and flowering plants used for foraging and cover.

Fire and vegetation management should maintain a range of tree ages, shrubs, canopy cover and safe deadwood where feasible.

• Avoid broadscale removal of shrub layers without an ecological assessment.
• Control weeds while retaining native foliage and nesting structure.
• Plan fuel reduction works around known habitat and breeding records.

Threats: Survey and compliance actions

Use targeted habitat assessment and bird surveys for projects that will clear or substantially disturb suitable habitat. Survey effort should increase where the species is recorded, where a nest is suspected, or where a project affects a large or connected woodland patch.

Check the current state listing, approval conditions and permit requirements before works. South Australia lists the species as Rare, and Queensland requirements apply to protected wildlife and potential breeding places.

• Keep records of sightings, calls, group size, habitat type and GPS location.
• Provide induction material for spotter catchers, supervisors and machine operators.
• Update the construction environmental management plan when new records or breeding signs are found.

Survey methodology: 1. Desktop assessment

Survey for Striped Honeyeaters in suitable woodland, mallee, riparian and coastal vegetation, especially where Casuarina, Eucalyptus, Melaleuca, Acacia or mixed woodland occurs. The species is often detected by its calls, movement between trees and loose feeding groups, but it can be overlooked in dense vegetation.

Map all native vegetation and mature trees within and beside the work area. Give particular attention to Black Oak, mallee, river red gum, bimble box, black box, paperbark, Casuarina, Acacia and Melaleuca communities.

Review recent records, vegetation mapping, flowering and fruiting information, water features, riparian corridors and nearby connected woodland. Do not assume that developed areas are unsuitable, as the species can use gardens, farms, orchards, reserves and caravan parks with native trees and shrubs.

• Check whether the project occurs in New South Wales, Queensland, South Australia or Victoria, and identify the relevant state listing and permit requirements.
• Treat South Australian records as relevant to the state Rare listing and EVNT assessment process.
• Check whether the action may affect a matter of national environmental significance and obtain ecological advice on whether an EPBC referral is required.

Survey methodology: 2. Field detection

Search the canopy and upper branches of woodland trees, generally from 2 to 10 m above ground. Look for light greyish brown birds with dark streaking, a striped head and nape, whitish underparts, and a short, sharply pointed bill.

Listen for the repeated chirp, chirp, cherry, cherry song, the sharp chewee contact call and shrill alarm notes. Record groups moving rapidly between trees, birds feeding briefly in several trees, and mixed feeding groups with miners or other honeyeaters.

Inspect foliage, twigs, live and dead branches, loose bark, rough-bark crevices, woody fruits and flowers. The species commonly gleans and probes rather than remaining in one place.

• Survey during calm conditions with good visibility and low background noise.
• Use more than one visit where habitat is suitable, particularly when the first visit is affected by wind, rain, heat, poor visibility or dense foliage.
• Include quiet observation periods from outside the proposed clearing area. Avoid relying only on playback or close approach.

Survey methodology: 3. Timing and effort

Plan visits across the period when works could affect the site. Include the local breeding period where practicable, because the species breeds throughout its distribution and may nest in drooping foliage of shrubs or low trees.

There is no reliable fixed migration period to use as a clearance rule. The species can move in response to weather and habitat conditions, so absence on one visit does not demonstrate that the site is unused.

Survey enough times and for long enough to cover all suitable habitat, canopy layers and accessibly visible trees. Increase effort where the habitat is continuous, mixed woodland is present, or birds are heard but not located.

• Prioritise early morning and other periods of high bird activity, subject to safe site access and weather.
• Repeat surveys at a different time or under different conditions when detection is poor.
• Carry out a targeted nest inspection before clearing, even where no Striped Honeyeaters were recorded during general surveys.

Survey methodology: 4. Records and mapping

Map each observation, flock, pair, nest, suspected breeding place, feeding tree and movement corridor. Record whether birds were alone, in a loose group or in a mixed-species flock.

Describe the vegetation, dominant trees, tree height, canopy condition, flowering or fruiting, water nearby, and the height and position of the birds. Record whether birds were gleaning, probing bark, visiting flowers, hawking or carrying nest material.

Photograph habitat and nests where this can be done without disturbance. Do not use photographs as a substitute for a clear written description.

• Record date, start and finish time, weather, wind, visibility, observers, survey route and survey method.
• Record all calls heard, including direction and estimated location when birds are not seen.
• Submit records to the project ecologist and relevant biodiversity databases where required by the approval or permit.

Before habitat disturbance: 1. Approvals and responsibilities

Use avoidance as the first response. Before works begin, confirm the species status, approvals, site controls and responsibilities, then complete a targeted pre-clearance inspection close to the start of disturbance.

Confirm whether the project needs an EPBC Act referral or approval before clearing. A state approval does not replace an EPBC assessment where a nationally protected matter may be affected.

In Queensland, obtain the required authority for an EVNT species and assess whether tampering with a breeding place requires a species management program. Do not start work until any required Queensland SMP is approved and its conditions are understood.

In South Australia, treat the species as Rare under the National Parks and Wildlife Act 1972. Obtain the relevant state approvals and permits before disturbing birds, nests or habitat. Check the equivalent requirements in New South Wales and Victoria before works commence.

• Nominate the project ecologist and authorised fauna spotter catcher in writing.
• Keep approval conditions, permits, the management plan and emergency contacts at the site office and in each clearing crew vehicle.
• Confirm who can stop work, handle fauna, approve nest controls and contact the regulator.

Before habitat disturbance: 2. Avoidance and site controls

Redesign the work area to retain connected woodland, mature trees, dense mallee, riparian vegetation and trees used for feeding or nesting. Retain drooping shrubs and low trees where they can support suspended nests.

Use clearly marked no-go areas around retained habitat and any active breeding place. Set the buffer according to the approval, species management program and advice from the project ecologist. Where no prescribed buffer exists, establish a conservative exclusion area that prevents noise, machinery, people and falling material from disturbing the nest.

Protect retained vegetation from stockpiling, vehicle access, dust, trenching, root damage, lighting and accidental clearing.

• Fence and sign exclusion areas before machinery arrives.
• Use spotters to check that clearing limits remain visible after grading, dust or weather.
• Schedule noisy or intrusive work away from an active nest where practicable, and follow any breeding-place conditions in the approval.

Before habitat disturbance: 3. Pre-clearance inspection

Complete a final inspection shortly before each clearing stage. Search drooping foliage and the ends of hanging branches in Casuarina, Melaleuca, Acacia and mallee eucalypts, including trees near water.

Look for deep cup-shaped or bag-shaped nests with thick walls, plant down, feathers, wool, grass, spider webs, hair or rootlets. Check for adults carrying food or nesting material, repeated visits to one location, alarm calls, fledglings and eggs or young.

Inspect vegetation that will be felled, lopped, pruned, crushed or isolated. Treat a suspected nest as active until the project ecologist determines otherwise.

• Complete the inspection in daylight and under conditions that allow the canopy and lower foliage to be seen.
• Use binoculars where possible and avoid touching or shaking foliage.
• Mark the location of every suspected breeding place and brief the clearing crew before work begins.

Before habitat disturbance: 4. Induction and exclusion

Induct all operators, supervisors, fauna spotters, subcontractors and visitors before they enter the clearing area. Explain the species appearance, calls, nesting places, exclusion markings and stop-work process.

Tell workers not to chase, feed, photograph closely, handle or remove birds, eggs or nests. The species may occur in small groups, so one bird can indicate that others or a nest are nearby.

Keep dogs, unnecessary personnel and vehicles out of retained habitat and exclusion areas.

• Use photographs and call descriptions in the induction material.
• Place a simple fauna response card in machinery and spotter catcher vehicles.
• Require every worker to report a bird, nest, injured animal or unexpected habitat immediately.

During habitat disturbance: 1. Sequential clearing

Clear in a controlled sequence from retained habitat towards the edge of the work area. The fauna spotter catcher must have authority to stop work whenever an animal, nest or unexpected habitat feature is found.

Clear in stages so fauna can move towards retained habitat rather than becoming surrounded by machinery. Remove understorey and lower vegetation first where this is safe, then progressively address larger vegetation under spotter catcher supervision.

Avoid felling a tree or shrub that contains a suspected nest until the project ecologist has assessed it and any approval conditions have been met.

Pause work when visibility is lost through dust, smoke, heavy rain, darkness or unsafe operating conditions.

• Keep the next clearing area small enough for the spotter catcher to inspect properly.
• Check each felled tree, lopped branch and fallen shrub before it is chipped, mulched, burned or removed.
• Maintain communication between the operator, spotter catcher, supervisor and ecologist throughout the clearing sequence.

During habitat disturbance: 2. Stop-work and breeding-place response

Stop all relevant work if a Striped Honeyeater, nest, egg, young bird or suspected breeding place is found inside or beside the impact area. Prevent people and machinery from approaching until the authorised ecologist has assessed the situation.

Do not move an active nest, cut a nest-bearing branch or separate adults from young. The species nests solitarily and may use the same or adjoining trees over more than one season, so nearby trees may also need protection.

If a breeding place is confirmed, apply the approved buffer, Queensland SMP, permit condition or other regulator direction. Resume work only when the responsible person confirms that the controls are in place.

• Mark the exclusion area clearly and record its location.
• Observe from a distance to determine whether adults are attending the nest.
• Contact the regulator or wildlife authority where the approval or permit requires notification.

During habitat disturbance: 3. Fauna handling and injury response

Only authorised and appropriately trained fauna personnel may capture, handle, assess or relocate a Striped Honeyeater. Workers must not attempt to catch a healthy bird.

If a bird is injured, stop work nearby, keep people and machinery away, and contact the project fauna handler or wildlife carer. Place the bird in a secure, ventilated container only when directed and safe to do so.

Do not give food or water unless directed by a qualified wildlife professional. Record the location, apparent cause, time found and treatment or transfer details.

• Use the approved wildlife rescue provider and transport pathway for the project.
• Check for a nearby nest or dependent birds before an injured adult is removed from the site.
• Report collisions, crushing, electrocution, vehicle strikes and other incidents under the project approval.

During habitat disturbance: 4. Daily records

Maintain a clearing log for every work area and shift. Record searches, sightings, nests, animals handled, exclusions, stop-work events, releases, injuries and deaths.

Record the habitat removed and retained, the tree or shrub type, the location of any nest, and the name of the person who made each decision.

Photograph marked exclusion areas and unusual incidents where this does not disturb fauna.

• Include date, time, weather, clearing method, machinery, observers and the work stage.
• Document any departure from the approved method and the corrective action taken.
• Provide daily records to the project ecologist and retain them for compliance reporting.

After habitat disturbance: 1. Post-clearance checks

Complete a systematic check after each clearing stage and before the area is handed back to construction. Use the results to confirm that no animals, nests or isolated habitat features remain at risk.

Inspect the cleared footprint, retained edges, felled vegetation, stockpiles, trenches, pipes and temporary structures for trapped or injured birds and overlooked nests.

Check retained trees and shrubs for disturbance, broken branches, exposed nests and changed access. Confirm that exclusion fencing and signs remain intact.

Search areas around water, dense foliage and connected woodland where birds may have moved during clearing.

• Complete checks before the next stage of construction and after major changes to the work area.
• Keep trenches, pits and pipes covered or fitted with fauna escape measures when unattended.
• Escalate any bird, nest or breeding-place finding under the stop-work procedure.

After habitat disturbance: 2. Relocation and release records

Record the fate and location of every relocated or released animal. The project ecologist should select release habitat with suitable native foliage, shelter, food plants and connectivity, and should avoid releasing into an occupied nest territory where this could create conflict.

Do not relocate nests or dependent young unless specifically authorised and directed by the wildlife authority or project ecologist. Where an adult is moved, check whether it was attending a nest or dependent young.

Record any failed release, repeat capture, mortality or evidence that the animal returned to the impact area.

• Use the approved release and rehabilitation provider.
• Record time, coordinates, habitat description, handling duration and condition at release.
• Follow permit conditions for transport, rehabilitation and reporting.

After habitat disturbance: 3. Monitoring and compliance

Monitor retained habitat and restoration areas where the project approval requires it, with attention to feeding groups, calls, nesting activity and use of retained trees.

Use the same observation points, routes and recording methods where possible so results can be compared over time. Include nearby control or reference habitat when required by the management plan.

Review whether clearing reduced connected woodland, flowering resources, shelter or suitable nesting vegetation.

• Report results at the frequency set by the approval or management plan.
• Trigger additional ecological assessment if birds stop using retained habitat, repeated injuries occur, or active nests are found after work resumes.
• Keep monitoring records with maps, photographs, weather details and observer names.

After habitat disturbance: 4. Incident review

Review every stop-work event, injury, nest discovery, unauthorised disturbance and mortality with the site supervisor, ecologist and fauna spotter catcher.

Identify whether the cause was inadequate survey, poor marking, equipment movement, lighting, noise, induction failure or a change in the work sequence.

Update the clearing method, induction and exclusion controls before the next stage.

• Close out each incident with a responsible person and completion date.
• Notify the regulator where required by the approval, permit or Queensland SMP.
• Share lessons with all crews before work restarts.

Rehabilitation actions: 1. Restore suitable habitat

Rehabilitation should restore connected native vegetation and the structure used for feeding and nesting. Because the Striped Honeyeater forages mainly in foliage and upper branches, plant structure and canopy continuity matter as much as ground cover.

Re-establish locally appropriate native woodland, mallee, riparian or coastal vegetation. Use species that provide foliage, branches, flowers, bark and woody fruits, including locally suitable Casuarina, Eucalyptus, Melaleuca, Acacia and other native trees and shrubs.

Create linked patches rather than isolated plantings where space allows. Retain existing mature trees and natural regeneration wherever possible.

Restore a range of vegetation heights, including shrubs and low trees with drooping foliage, and woodland trees that can develop feeding branches between 2 and 10 m above ground.

• Use local provenance plants where required by the project approval.
• Protect new plantings from browsing, compaction, fire damage and accidental mowing.
• Stage rehabilitation so shelter and food resources remain available during construction.

Rehabilitation actions: 2. Nesting structures

Nest boxes and bat boxes are not a direct substitute for this species' usual nest sites. The Striped Honeyeater generally suspends a cup-shaped or bag-shaped nest from drooping twigs or foliage in Casuarina, Melaleuca, Acacia or mallee eucalypts.

Prioritise planting and retaining suitable shrubs and low trees. Where an approved ecologist considers it appropriate, an artificial nest support or protected branch structure may be trialled in dense native foliage, but it must not be treated as a guaranteed replacement.

Do not install bat boxes, hollow logs or roost structures as mitigation for Striped Honeyeater nesting unless they are required for another species. They do not match the nest placement described for this bird.

• Design any artificial nest support with the project ecologist and obtain approval before installation.
• Place it away from machinery, intense lighting, public access and flood-prone locations where practicable.
• Inspect trial structures without touching nests and remove failed or unsafe structures under ecological direction.

Rehabilitation actions: 3. Food, water and weeds

Restore a mix of native foliage and flowering plants. Include suitable eucalypts and other local species that provide insects, flowers, bark, branches and seasonal fruit.

Retain natural water sources and avoid creating stagnant or unsafe water points. The species may nest near or overhanging water, but water alone does not replace suitable woodland structure.

Control environmental weeds that suppress native shrubs, regeneration or canopy development. Use methods that avoid poisoning or disturbing active nests and feeding birds.

• Schedule weed control outside active breeding places where practicable.
• Keep herbicide, dust and sediment away from retained vegetation and water.
• Use native ground cover and leaf litter to reduce erosion and support invertebrate prey.

Rehabilitation actions: 4. Lighting and long-term monitoring

Keep artificial lighting away from retained woodland, riparian edges and likely nesting vegetation. Use the lowest practical intensity, direct lights downward and avoid lighting the canopy.

Monitor rehabilitated areas for plant survival, canopy development, flowering, weed cover and use by Striped Honeyeaters. Record calls, groups, feeding behaviour and nesting attempts.

Continue monitoring for the period specified in the approval or rehabilitation plan. Adjust planting, weed control, fencing and lighting if the habitat is not developing as intended.

• Use shielded, motion-controlled or time-limited lighting where safety permits.
• Replace failed plants with locally suitable native species.
• Review monitoring results with the project ecologist and include them in final rehabilitation reporting.

Sources

• Some Observations of Foraging and Social Behaviour of ..., BirdLife Australia: https://afo.birdlife.org.au/afo/index.php/afo/article/download/326/315
• [PDF] Some Observations of Foraging and Social Behaviour of the Striped ..., BirdLife Australia: https://afo.birdlife.org.au/afo/index.php/afo/article/viewFile/326/315
• Striped honeyeater - Wikipedia, Wikipedia: https://en.wikipedia.org/wiki/Striped_honeyeater
• Occurrence records for the distribution map, Atlas of Living Australia: https://biocache.ala.org.au/