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Hooded Robin (Melanodryas cucullata)

The Hooded Robin is a small Australian woodland bird that forages mainly on or near the ground in open eucalypt, acacia and cypress woodlands. The south-eastern form is listed as Critically Endangered under the EPBC Act and is vulnerable to clearing, fragmentation, loss of fallen timber, inappropriate fire, predators and aggressive competition from Noisy Miners, so even apparently degraded woodland remnants should be assessed before works.

Conservation status

Commonwealth, EPBC Act 1999: Critically endangered.

Queensland, Nature Conservation Act 1992: Endangered.

New South Wales, Biodiversity Conservation Act 2016: Endangered.

Victoria, Flora and Fauna Guarantee Act 1988: Endangered.

Northern Territory, Territory Parks and Wildlife Conservation Act 1976: Critically endangered.

Australian Capital Territory, Nature Conservation Act 2014: Endangered.

Breeding season

The Hooded Robin is generally sedentary, although its home range expands outside the breeding season. Timing varies across Australia, so the calendar below is a practical guide for the south-eastern form rather than a substitute for local observations.

Conduct pre-clearing surveys and nest checks at the time required by the project approval and local fauna management plan. Do not rely on seasonal timing alone because nesting attempts can vary and the species may breed outside the main period.

  • Breeding: Breeding is mainly July to November, with eggs laid in spring and summer. Pairs may make multiple nesting attempts.
  • Young: Incubation is about 15 to 16 days, nestlings remain for about 12 to 13 days, and fledglings may remain dependent for about eight weeks.
  • Movement and home range: The species is generally sedentary. Breeding territories are about 6 ha, expanding to about 18 ha in winter and sometimes 30 to 50 ha.
  • Highest clearing risk: Clearing and disturbance are most likely to harm the species from July to November when nests, eggs and dependent young may be present. Low nests and fledglings can remain exposed after the nestling period.

Identification

The Hooded Robin is a quiet, medium-small woodland bird with a short slender bill, a moderately long square-tipped tail and conspicuous white flashes in the wings and tail during flight. It is often detected from exposed perches, ground pouncing and soft calls rather than from prolonged activity in the canopy.

Adult males have a black hood, back and throat, white underparts, black wings, a white shoulder bar and white wing markings. Females are greyer and browner, with a grey-brown head, dark brown wings and white wing markings.

Juveniles are dark brown with off-white speckling and white markings on the upper body and underparts. Birds are usually seen in pairs or small groups and can be shy and unobtrusive.

Length: About 16 cm.

Weight: About 22 g.

  • Record the bird's sex, age class, plumage, perch type, direction of flight and association with woodland edges or clearings.
  • Look for a short, swift, undulating flight with obvious white in the wings and tail.

Identification: Similar species

Male Hooded Robins can resemble the Pied Honeyeater, but the Pied Honeyeater has a longer downcurved bill, blue skin below the eyes, and is more active and noisy in the canopy. Female and juvenile Hooded Robins can resemble Jacky Winters, but Jacky Winters are smaller and browner, with white restricted mainly to the outer tail edges.

Male red-breasted Petroica robins are smaller and lack the Hooded Robin's white through the base of the tail. On the Tiwi Islands, juvenile Hooded Robins can resemble mangrove robins, but the two taxa occupy different habitats.

Identification: Calls and field signs

Calls are quiet trills and occasional piping whistles. The species is often quiet during the day but may be among the first woodland birds to call at dawn.

Search for repeated use of exposed dead branches, stumps, low limbs and ground foraging points. A Hooded Robin may sit on a perch before dropping or pouncing onto prey.

Nests are open cups made from leaves, bark, plant fibres and cobweb. They are placed in a low live or dead fork, branch, tree crevice, hollow, stump or occasionally a fallen tree or limb, usually up to about 5 m above ground.

  • Do not rely on tracks or scats for detection. Bird presence is better assessed from visual observations, calls, flight behaviour, perches, foraging activity and nests.
  • Treat a low cup nest, adult alarm behaviour or repeated use of a small woodland patch as a trigger for ecological advice before vegetation or timber is removed.

Distribution: National range

The Hooded Robin species occurs across much of mainland Australia, but the south-eastern form occupies south-eastern Australia from south-east Queensland through NSW and Victoria to south-east South Australia. Distribution has contracted markedly in parts of south-eastern Australia, particularly in fragmented eastern woodland areas.

The species occurs across most of continental Australia except the humid south-eastern forests. The south-eastern subspecies occurs from extreme south-east Queensland through most of non-coastal NSW, Victoria and south-east South Australia.

In Victoria, records are concentrated across the Lowan Mallee, Murray Mallee, Wimmera, Goldfields, Central Victorian Uplands, Victorian Riverina, Northern Inland Slopes and East Gippsland Uplands bioregions. The highest historical density of Victorian records was in the semi-arid north-west.

Australian range: Most mainland states and territories, with the south-eastern form extending from south-east Queensland through NSW and Victoria to south-east South Australia.

Victorian bioregions reported: Lowan Mallee, Murray Mallee, Wimmera, Goldfields, Central Victorian Uplands, Victorian Riverina, Northern Inland Slopes and East Gippsland Uplands.

  • When assessing a project, use current state databases and local records because historic range maps include areas from which the species has declined or disappeared.
  • In Victoria, give particular attention to remnant woodlands and reserves in the western districts, Victorian Riverina, Goldfields and north-east woodland areas.

Distribution: Strongholds and local populations

Important Victorian areas include the Lowan and Murray Mallee, Wimmera, western districts, Goldfields, Victorian Riverina and remnant woodland around Chiltern and north-east Victoria. Reported conservation areas include Little Desert, Murray-Sunset, Wyperfeld, Greater Bendigo and Chiltern-Mt Pilot national parks, together with surrounding private woodland remnants.

The species is associated with larger, structurally diverse remnants and deep, sheltered woodland edges. It has declined or become locally absent in several heavily cleared areas, including the Cumberland Plain, parts of the Central Tablelands, Mornington and Bellarine peninsulas, French Island and West Gippsland.

  • Check both reserves and adjoining private remnants because woodland edges and private vegetation can form part of a local territory.
  • Do not treat absence from a single survey as proof of absence, particularly where suitable woodland remains and survey effort is limited.

Distribution: Population size and trend

The national conservation assessment estimated about 68,000 mature individuals for the south-eastern form, with a range of 36,000 to 113,000, but noted low reliability. It also reported a decline of more than 50% over the previous ten years.

An older NSW review estimated about 500,000 individuals across NSW, Victoria and South Australia, but rated that estimate as low reliability. In NSW, reporting rate declined by 41% between the 1977 to 1981 and 1998 to 2002 bird atlases, and local declines of 50% to more than 90% were reported at some eastern sites.

Mature individuals, later assessment: 68,000, with an estimated range of 36,000 to 113,000; reliability low.

Recent assessed decline: More than 50% over the previous ten years in the later conservation assessment.

NSW atlas trend: 41% decline in reporting rate between 1977 to 1981 and 1998 to 2002.

Older broad estimate: About 500,000 across NSW, Victoria and South Australia, with low reliability.

Habitat: Habitat types

Hooded Robins use open, structurally diverse woodland rather than dense forest or urban vegetation. Habitat value depends on the combination of canopy, shrubs, native grasses, ground cover, standing timber and fallen woody material, not simply on tree cover alone.

The main habitat is dry eucalypt and acacia woodland and shrubland with an open understorey, some grassy areas and a complex ground layer. Structurally diverse sites may contain mature eucalypts, saplings, small shrubs, moderately tall native grasses, standing dead trees, stumps, rocks, logs and fallen branches.

The species is positively associated with larger patch size and with woodland edges, especially deep and sheltered edges. It is not normally found in urban areas or densely forested vegetation.

  • Map all native woodland, shrubland, open grassy areas, dead trees, stumps, logs and fallen branches within and beside the clearing footprint.
  • Retain links between woodland patches and avoid creating narrow isolated remnants where practicable.

Habitat: Site condition and structure

Suitable habitat may occur in moderately mature regrowth as well as older woodland, but a site can be suboptimal when the ground layer lacks rocks, coarse woody debris, logs, fallen branches, litter or tree stumps.

The species is sensitive to patch size, canopy cover, shrub cover and ground cover. Overgrazing, frequent fire, firewood collection and vegetation tidying can simplify these features and reduce habitat quality.

  • Before clearing, record canopy density, tree age classes, shrubs, native grass cover, litter, rocks, logs, stumps, standing dead timber and the depth of the woodland edge.
  • Avoid describing a remnant as unsuitable solely because it has been disturbed. Retained habitat may still support foraging, dispersal or breeding.

Habitat: Elevation and climate

The supplied documents describe a broad inland and south-eastern distribution but do not provide a defined elevation limit. Records span semi-arid mallee and inland woodland areas, tablelands, slopes and eastern uplands.

The species is generally associated with dry woodland and shrubland, rather than humid south-eastern forests.

  • Use local records, vegetation mapping and field habitat assessment rather than applying an unverified altitude threshold.

Foraging habitat: Diet

Hooded Robins forage mainly from exposed perches and on or near the ground. Fallen timber, logs, branches, litter, trunks and open ground provide both prey and foraging surfaces.

The diet consists mainly of insects and other invertebrates. The species also takes some small vertebrates, including skinks and froglets, and occasionally seeds.

Prey is taken from the ground, among logs and coarse woody debris, from trunks and branches, and sometimes in the air.

Main food: Invertebrates, mostly insects.

Additional food: Some skinks and froglets, and occasional seeds.

Foraging surfaces: Ground, logs, coarse woody debris, trunks, branches and air.

  • Retain logs, fallen branches, coarse woody debris, litter, stumps and standing dead timber within retained habitat.
  • Avoid removing woody material from the site as a general clean-up measure unless it presents a demonstrated safety or access risk.

Foraging habitat: Foraging behaviour and area

The bird commonly sits on an exposed dead branch, stump or other perch before dropping or pouncing onto prey. It may forage alone, in a pair or with a family group.

Breeding territories in NSW are about 6 ha, while winter home ranges are about 18 ha and can reach 30 to 50 ha. These areas indicate that a small clearing can affect habitat used beyond the immediate works footprint.

Breeding territory: About 6 ha in NSW, with a reported range of 4.5 to 9.5 ha.

Winter home range: About 18 ha, with reported ranges of 8.3 to 25.5 ha and occasional areas of 30 to 50 ha.

  • Inspect woodland edges, clearings, open ground and timber-rich patches as well as the canopy.
  • Assess the surrounding patch, not only the vegetation proposed for removal, because foraging movements can extend across several hectares.

Breeding habitat: Breeding biology

Hooded Robins breed in monogamous pairs and may receive help from other group members. Breeding habitat combines low nesting sites with open woodland, ground foraging resources and sufficient structural complexity around the nest.

The main breeding period is July to November, although eggs are described as being laid in spring and summer. Pairs may make multiple nesting attempts, but usually only one brood succeeds in a season.

The nest is an open cup made from leaves, bark or other plant fibres bound with cobweb. It is placed in a low live or dead fork, branch, crevice, hollow, stump or occasionally a fallen tree or limb. Nests may be up to about 5 m above ground.

Breeding season: Mainly July to November; eggs may be laid in spring and summer.

Clutch size: Usually 2 to 3 eggs, sometimes 1.

Incubation: About 15 to 16 days.

Nestling period: About 12 to 13 days.

Post-fledging dependence: About 8 weeks.

Broods: Usually one successful brood per season, although multiple nesting attempts can occur.

Age at maturity: Not stated in the supplied documents.

Lifespan: Not stated in the supplied documents.

  • Search retained woodland, stumps, low forks, dead limbs and fallen timber for nests before clearing or pruning.
  • If an active nest or dependent young are found, stop work around the nest and obtain site-specific fauna management advice.

Breeding habitat: Breeding habitat features

Habitat critical to survival includes dry eucalypt and acacia woodland or shrubland with an open understorey, some grassy areas and a complex ground layer. Structurally diverse sites include mature eucalypts, saplings, small shrubs, moderately tall native grasses, standing dead or live trees and stumps.

Moderately deep to deep soils, rocks and fallen timber provide foraging habitat around breeding territories. Large remnant patches are important because the species tends to persist in substantial areas of remnant habitat, with the later conservation assessment referring to at least 20 ha around observed birds.

Habitat patch associated with persistence: The conservation assessment assumed at least 20 ha of suitable habitat within a patch where Hooded Robins were observed.

  • Retain nest trees, low forks, standing dead timber, stumps, logs, rocks and native ground cover.
  • Maintain a buffer around active nests and avoid noisy or ground-disturbing works near nests during the breeding season where practicable.
  • Assess the wider woodland patch for breeding function, even where the proposed clearing area is small.

Sheltering habitat: Resting and roosting structure

The Hooded Robin does not use dens, burrows or tree hollows as a mammal would. Its shelter and resting structure is provided by woodland vegetation, low trees, stumps, dead timber, shrubs and ground cover.

The species uses exposed branches, dead branches and stumps for hunting and likely uses low live or dead vegetation, shrubs and woodland cover for resting and concealment. Standing dead trees, stumps, logs and fallen branches are also associated with nesting and foraging.

The supplied documents do not give a separate roost structure or roost height. Do not remove dead timber or low forks on the assumption that they have no habitat value.

  • Retain standing dead trees, stumps, low forks, logs, fallen limbs, shrubs and native ground cover within exclusion zones.
  • Keep retained habitat connected to larger woodland where practicable, particularly at sheltered edges.

Sheltering habitat: Nests and shelter from predators

Nests are low and can be within reach of cats and other predators. They may be placed in forks, crevices, hollows, stumps or fallen limbs, generally at low height and sometimes up to about 5 m.

Ground foraging also exposes Hooded Robins to cats, foxes and other predators. Simplified or cleared ground can remove both cover and prey substrates.

Nest height: Usually low, with records of nests up to about 5 m above ground.

  • Inspect low vegetation and timber before clearing, slashing, pruning or moving logs.
  • Control access by domestic animals and manage feral cats and foxes around retained habitat in accordance with the project environmental management plan.

Threats: Clearing and fragmentation

The main risk to Hooded Robins on development sites is loss or simplification of open woodland habitat. Fragmentation is particularly important because the species has a high patch size and habitat complexity threshold and may not readily recolonise isolated remnants.

Clearing removes nesting, foraging and shelter structure and can divide a territory or woodland patch. The species is positively associated with patch size, canopy, shrub cover, ground cover, logs, branches and litter.

The species has disappeared from many cleared or highly fragmented areas, and recolonisation after local extinction is considered unlikely in some parts of its range.

  • Avoid clearing mature and regrowth woodland, standing dead trees, stumps, logs, fallen branches and native ground cover.
  • Use exclusion fencing and clearly marked no-go areas before earthworks begin.
  • Assess indirect loss from access tracks, stockpiles, drainage, edge effects, lighting and increased human activity as well as direct vegetation removal.

Threats: Fire and vegetation simplification

Large or frequent fires can alter woodland structure, remove hollows, leaf litter and woody debris, and promote dense regrowth that is unsuitable for the species. Spring burning can reduce breeding success.

Firewood collection, tidying, overgrazing and frequent disturbance reduce logs, branches, stumps, litter and invertebrate prey. Weed invasion and exotic grasses can also reduce foraging habitat.

  • Avoid planned burning during the main breeding period from July to November where practicable.
  • Retain patches of unburnt woodland, fallen timber and native ground cover during fire management and construction.
  • Prevent unnecessary removal of timber and litter from retained habitat.

Threats: Predators and competitors

Feral cats and foxes can prey on ground-foraging birds and low nests. Native predators, including artificially elevated numbers of Pied Currawongs, can also reduce breeding success.

Noisy Miners can aggressively exclude Hooded Robins from woodland patches, particularly preferred edge habitat.

  • Do not create food, shelter or access conditions that increase feral cat and fox activity around retained woodland.
  • Include feral cat and fox control, and monitoring for Noisy Miners, where the project affects occupied or suitable habitat.
  • Keep construction compounds, waste, food and domestic animals away from retained woodland.

Threats: Roads, weeds, disease and hydrology

The supplied documents do not identify a species-specific road mortality rate, disease threat or hydrology threshold. Roads and tracks can nevertheless remove habitat, increase fragmentation and improve predator access, while construction can spread weeds and alter ground cover.

Avoid assuming that drainage or water changes are harmless. The species depends on dry woodland structure and ground invertebrate habitat, so changes to runoff, waterlogging, erosion or vegetation composition should be assessed at the site scale.

  • Keep new roads and tracks out of retained woodland and avoid creating unnecessary access along woodland edges.
  • Control weeds and prevent vehicles, soil or spoil from spreading weed seed into retained habitat.
  • Maintain existing drainage patterns unless a documented assessment shows that change will not degrade woodland structure or ground foraging habitat.
  • Use targeted surveys and current conservation advice where a project may affect known or likely habitat.

Survey methodology: 1. Targeted area searches and transects

Survey the Hooded Robin where dry eucalypt or acacia woodland, shrubland, grassy openings, woodland edges, standing timber, logs or coarse woody debris may be disturbed. The south-eastern form is quiet, ground-foraging and easily missed, so survey effort should target suitable habitat and include searches for birds using exposed perches and ground-layer feeding areas.

Use systematic walking searches and transects through all suitable woodland, shrubland, grassy openings and woodland edges before clearing.

Search from exposed perches, dead branches, stumps and low tree forks, then scan the ground and nearby logs for feeding birds.

Record all Hooded Robins, pairs, family groups, nests, calls, feeding observations and the location and condition of habitat features.

Typical breeding territory: About 6 ha, with a reported range of 4.5 to 9.5 ha

Typical winter home range: About 18 ha, with a reported range of 8.3 to 25.5 ha, and sometimes 30 to 50 ha

Foraging position: On or near the ground, and from trunks, branches and exposed perches

  • Prioritise structurally diverse open woodland with eucalypts, acacias or callitris, an open understorey, grassy areas and a complex ground layer.
  • Give particular attention to habitat with mature trees, saplings, shrubs, standing dead timber, logs, fallen branches, litter, rocks and deep or moderately deep soil.
  • Treat the absence of a detected bird as inconclusive where suitable habitat is present, because the species is shy, quiet and often occurs at low density.

Survey methodology: 2. Dawn and breeding-season observations

Include observations from early morning, when Hooded Robins are more likely to give their far-carrying song.

Repeat searches during the breeding period, particularly from July to November, when pairs, nests and dependent young may be present.

Search low live or dead forks, branches, tree stumps and fallen trees for open cup nests made from plant fibres and cobweb.

Breeding period: July to November according to the Victorian species profile; spring and summer breeding is also reported for NSW

Clutch size: Usually 2 to 3 eggs

Nest height: Up to 5 m above ground in a tree fork or crevice, with nests also recorded on stumps or fallen timber

  • Use quiet observation and avoid flushing birds repeatedly from suspected nest sites.
  • Record the number of adults, juveniles, helpers, territorial behaviour, nest locations and the direction of movement between retained habitat patches.
  • Maintain a site map showing occupied habitat, suspected territories, nests and movement links before finalising the clearing boundary.

Survey methodology: 3. Habitat and feature searches

Complete a habitat assessment even if no Hooded Robins are detected, because the species is associated with patch size and several ground and understorey features.

Map the extent and condition of dry woodland, shrubland, open areas, deep sheltered edges, logs, fallen branches, litter, standing dead trees and stumps.

Inspect trees and fallen timber for nests before vegetation removal, including features close to the proposed clearing edge.

Habitat description: Dry eucalypt and acacia woodland or shrubland with an open understorey, some grassy areas and a complex ground layer

Important foraging features: Logs, fallen branches, coarse woody debris, litter, rocks, trunks and ground cover

Important nesting and roosting features: Standing dead or live trees, tree stumps, low forks, branches, crevices and hollows

  • Assess whether the site connects to larger retained woodland, because the species is associated with substantial remnants and is sensitive to fragmentation.
  • Record dense regrowth, heavy grazing, simplified ground cover, weed invasion and areas dominated by Noisy Miners as habitat condition factors.
  • Use the habitat assessment to identify areas that should be retained even where records are absent.

Survey methodology: 4. Survey conditions and detection limits

Avoid relying on a single visit, a single observer or passive desktop records where suitable habitat will be cleared.

Schedule repeat visits across suitable weather and daylight conditions, with at least some effort during the early morning calling period.

Document the dates, start and finish times, weather, observers, route, area searched, visibility, habitat condition and any limitations.

Detection behaviour: The species is shy and unobtrusive, but can give a far-carrying dawn song

Movement pattern: Generally considered sedentary, with birds occurring in pairs or small family groups

  • Do not apply the survey effort table for the Tiwi Islands subspecies to the south-eastern form, because the guideline account is for Melanodryas cucullata melvillensis and does not provide a method or effort guide for the south-eastern form.
  • Use additional targeted effort where habitat occurs in a large or connected remnant, where a potential territory crosses the clearing boundary, or where previous records are nearby.
  • Treat quiet periods, dense vegetation, poor visibility, high wind and rain as reduced detection conditions and record them in the survey report.

Survey methodology: Minimum effort and reporting

  • Complete a habitat assessment and targeted early-morning search before clearing any suitable Hooded Robin habitat.
  • Use repeat searches where suitable habitat is extensive, connected, occupied, or difficult to inspect fully, and justify the number and timing of visits in the report.
  • Submit confirmed records, negative survey results where relevant, nest locations and mapped habitat observations to the relevant state wildlife database.
  • Retain photographs, GPS tracks, field sheets, call recordings, weather data, observer details and the evidence supporting any presence or absence conclusion.
  • Escalate the assessment if a bird, nest, occupied territory or habitat likely to support the species is found within or adjacent to the impact area.

Before habitat disturbance: Avoid and minimise

Plan the work around the Hooded Robin's dependence on connected, structurally diverse woodland and ground-layer feeding habitat. The main controls are to retain suitable remnants and habitat features, avoid breaking movement links, and confirm approval requirements before vegetation is disturbed.

  • Avoid clearing dry eucalypt and acacia woodland, shrubland, grassy openings and woodland edges that contain an open understorey and complex ground layer.
  • Retain mature trees, saplings, shrubs, standing dead trees, stumps, logs, fallen branches, litter, rocks and coarse woody debris wherever practicable.
  • Retain large, connected woodland remnants and avoid reducing a patch to isolated fragments, because occurrence is positively associated with patch size and connectivity.
  • Keep deep and sheltered woodland edges and links between retained patches, particularly where a potential territory or home range crosses the work area.
  • Keep machinery, stockpiles, access tracks, lighting and temporary compounds outside retained habitat and outside mapped nest and feeding areas.

Before habitat disturbance: Approvals and work planning

  • Confirm the current Commonwealth listing and assess whether the proposed action may significantly affect the nationally listed taxon before clearing or construction.
  • Obtain any required state or territory threatened species, native vegetation, wildlife handling and vegetation removal approvals before work starts.
  • Plan high disturbance activities outside the July to November breeding period where practicable, and obtain project specific ecological advice if an occupied nest or dependent young are present.
  • Stage the works so that retained woodland, ground-layer habitat and movement links remain available while each work area is completed.
  • Prepare a fauna management plan that defines survey limits, exclusion zones, spotter catcher authority, stop-work triggers, handling arrangements, release sites, injury response and reporting.

Before habitat disturbance: Site preparation

  • Complete a pre-clearance survey shortly before works, because birds, nests and habitat conditions may change after the initial assessment.
  • Peg and fence the approved clearing boundary, retained habitat, nest exclusion zones, access routes and fauna release areas before machinery enters the site.
  • Mark logs, standing dead trees, stumps, rocks, coarse woody debris and other retained features that could be damaged by vehicles or material storage.
  • Brief all workers on the species' appearance, quiet behaviour, ground foraging, low nests and the requirement to stop and contact the fauna spotter catcher when a bird or nest is found.
  • Check the work area for domestic animals, feral cat and fox activity, weeds and fire risks that could affect retained habitat.

During habitat disturbance: Daily controls and spotter catcher roles

Use a fauna spotter catcher to control the immediate interaction between machinery and wildlife. The spotter catcher must have authority to pause work, inspect habitat features and arrange an appropriate response when a Hooded Robin, nest or occupied habitat is found.

  • Inspect the active work area, exclusion fencing, retained habitat and access routes at the start of each shift and after breaks or changes in the work sequence.
  • Keep the fauna spotter catcher in a position where they can see the vegetation being felled, machinery movement and the ground immediately ahead of the clearing front.
  • Use a slow, staged clearing sequence that allows birds to move into retained habitat before machinery advances.
  • Keep machinery out of fenced habitat, nest exclusion zones, logs, stumps, standing dead trees and other features marked for retention.
  • Stop machinery immediately when the spotter catcher identifies a Hooded Robin, nest, fledgling, injured animal or habitat feature requiring inspection.

During habitat disturbance: Habitat feature handling

  • Inspect standing dead and live trees, stumps, low forks, crevices and fallen timber for nests before removal or relocation.
  • Retain logs, fallen branches, coarse woody debris, litter, rocks and suitable ground cover in place wherever the approved design allows.
  • If a habitat feature must be moved, use the fauna spotter catcher's approved handling procedure and place it in nearby retained habitat with similar structure and ground conditions where practicable.
  • Do not burn, chip, bury or remove logs and coarse woody debris until the spotter catcher has checked them for birds, nests and other fauna.
  • Prevent sediment, dust, weeds, fuel and spoil from entering retained woodland or degrading the ground layer.

During habitat disturbance: Animal encounters and stop-work triggers

  • Do not chase, catch or handle a Hooded Robin unless the person is authorised and trained under the applicable approval and fauna management plan.
  • Pause work and establish a quiet exclusion area if a Hooded Robin, nest, fledgling, pair showing territorial behaviour or dependent young is found.
  • Allow an uninjured bird to move into nearby retained habitat where it can do so safely, and do not release or relocate it unless directed by the authorised fauna handler and approval conditions.
  • Take an injured bird to an authorised wildlife carer or veterinarian through the approved project response pathway, and minimise handling, noise and transport time.
  • Stop work if a nest or dependent young is within the clearing footprint, if exclusion fencing fails, if machinery enters retained habitat, or if the approved clearing boundary is uncertain.
  • Resume work only after the fauna spotter catcher, project ecologist and relevant approval holder have confirmed the control measures and any required authority.

During habitat disturbance: Records and incident reporting

  • Record every sighting, nest, attempted breeding observation, handling event, injury, release, mortality, stop-work event and unauthorised habitat impact.
  • Record the date, time, GPS location, habitat feature, animal condition, action taken, people involved, photographs and final outcome.
  • Update the clearing map daily to show completed areas, retained habitat, exclusion zones, release sites and any changed constraints.
  • Notify the project environmental officer and approval holder immediately of a listed species encounter, nest, injury, mortality or breach of an exclusion zone.
  • Submit confirmed records and incident information to the relevant state wildlife database and to the Commonwealth reporting system where required by approval conditions.

After habitat disturbance: Post-clearance inspection

Check the completed area for missed habitat features, injured fauna and breaches of retained habitat controls. Continue monitoring where clearing has removed part of a potential territory or reduced connectivity between woodland patches.

  • Complete a systematic inspection of the cleared footprint, retained edge and access routes after each clearing stage.
  • Search for injured or displaced birds, nests, fledglings, damaged standing trees, stumps, logs and coarse woody debris that were marked for retention.
  • Repair exclusion fencing, replace damaged habitat markers and remove machinery, spoil and waste from retained habitat.
  • Check that the final clearing footprint matches the approved design and record any variation before further work proceeds.

After habitat disturbance: Monitoring and reporting

Monitoring focus: Presence, pairs or family groups, nests, habitat connectivity, ground-layer complexity, logs, fallen branches, litter and standing dead timber

  • Monitor retained woodland, habitat edges and connected patches for Hooded Robins during the next suitable breeding period and during early morning activity periods.
  • Use the same mapped routes and observation points where practicable so that changes in occupancy, pairs, family groups and habitat condition can be compared over time.
  • Report changes in ground cover, logs, standing dead timber, weeds, Noisy Miner activity, foxes, feral cats and fire effects.
  • Provide the regulator, approval holder and land manager with survey results, incident records, photographs, maps and any required compliance report.

After habitat disturbance: Offsets and residual impacts

  • Calculate and document any unavoidable loss of suitable habitat, including losses of logs, standing dead timber, stumps, ground cover and woodland connectivity.
  • Apply the relevant Commonwealth, state or territory offset policy only after avoidance and minimisation measures have been demonstrated.
  • Ensure any approved offset or conservation measure protects habitat with the same structural features and supports connected woodland rather than isolated plantings.
  • Track offset delivery, site protection, management actions and performance against the approval conditions.

Rehabilitation actions: Restore structure and connectivity

Rehabilitation should recreate open woodland with a functioning ground layer, not just replace tree cover. The target is habitat that provides exposed perches, low nesting sites, ground foraging substrates and links to retained woodland.

  • Retain and protect existing mature eucalypts, acacias, callitris, standing dead trees and stumps during rehabilitation works.
  • Plant locally appropriate eucalypt and acacia species that match the surrounding dry woodland or shrubland community, using local provenance where required by the project or approval.
  • Establish an open understorey with native grasses, smaller shrubs and saplings rather than a dense regrowth structure.
  • Reinstate logs, fallen branches, coarse woody debris, rocks and suitable litter across rehabilitation areas to restore ground foraging substrates.
  • Connect rehabilitation areas to retained woodland and deep sheltered edges, and avoid narrow isolated plantings that do not provide functional habitat.

Rehabilitation actions: Manage threats

  • Control environmental weeds and exotic grasses that reduce the quality of ground foraging habitat.
  • Prevent firewood collection and other removal of logs, branches, stumps and litter from rehabilitated areas.
  • Monitor and control feral cats and foxes in accordance with approved pest management programs, especially near low nests and ground-foraging habitat.
  • Manage Noisy Miner encroachment where it is excluding Hooded Robins from retained or rehabilitated woodland, using methods approved for the site.
  • Plan fire regimes with the land manager so that repeated burning, spring burns and dense post-fire regrowth do not remove feeding substrates or reduce breeding habitat.

Rehabilitation actions: Nest and habitat features

Recorded nest placement: Tree forks or crevices, often in low live or dead branches, stumps or fallen trees, with nests reported up to 5 m above ground

Recorded food: Mostly insects and other invertebrates, with some small vertebrates and occasional seeds

  • Retain naturally occurring nesting features, including low live or dead forks, branches, stumps, tree crevices and suitable fallen timber.
  • Install nest boxes only where an ecologist identifies a site-specific shortage of natural nesting features and the management plan supports their use, because the supplied documents do not establish a standard box design or placement rate for this species.
  • Do not remove standing dead trees solely because they are dead when they are safe to retain and may provide perches, nesting sites or foraging structure.

Rehabilitation actions: Success measures and adaptive management

  • Inspect rehabilitation annually for survival and recruitment of planted woodland species, open understorey condition, native grass cover, weed cover, logs, litter, standing timber and connectivity.
  • Survey rehabilitated and reference habitat during early morning periods in the breeding season and record Hooded Robin presence, pairs, family groups, nests and foraging behaviour.
  • Use the reported breeding territory size of about 6 ha and winter home range of about 18 ha as context when assessing whether rehabilitation is large and connected enough to support use, without treating those figures as a site-specific population target.
  • Repair erosion, replace failed plantings, control weeds and reinstate lost logs or branches where monitoring shows that the target structure is not developing.
  • Continue management until the site supports a stable open woodland structure with native ground cover, habitat features and confirmed use by Hooded Robins or equivalent ecological indicators agreed in the approval.

Sources