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Hooded Plover (Thinornis cucullatus)

The Hooded Plover is a small, resident Australian shorebird that nests on open beaches, dunes, estuaries and, in Western Australia, inland salt lakes. It matters on works sites because its camouflaged nests and flightless chicks occur in areas used by vehicles, machinery, dogs and people. The eastern subspecies is listed as Vulnerable nationally, Critically Endangered in New South Wales and Vulnerable in Victoria, South Australia and Tasmania, and the western population is Priority 4 in Western Australia.

Conservation status

Commonwealth, EPBC Act 1999: Vulnerable. This listing covers only the eastern subspecies, Thinornis cucullatus cucullatus.

New South Wales, Biodiversity Conservation Act 2016: Critically endangered. This listing covers only the eastern subspecies, Thinornis cucullatus cucullatus.

Victoria, Flora and Fauna Guarantee Act 1988: Vulnerable.

South Australia, National Parks and Wildlife Act 1972: Vulnerable. This listing covers only the eastern subspecies, Thinornis cucullatus cucullatus.

Western Australia, WA Threatened and Priority Fauna List: Near threatened. Priority 4 (rare, near threatened) on the Western Australian priority fauna list. Priority species are not listed under the Biodiversity Conservation Act 2016 but should be considered in assessments.

Tasmania, Threatened Species Protection Act 1995: Vulnerable. This listing covers only the eastern subspecies, Thinornis cucullatus cucullatus.

Breeding season

The Hooded Plover breeds in Australia mainly from August to March. Treat July to March as the broader breeding-risk period, because timing varies between regions and subspecies, with western birds generally breeding from September to February.

Breeding mode: Ground-nesting beach shorebird. It lays eggs in a simple scrape on sand, usually above the high-water mark, on the foredune, sparsely vegetated dunes or suitable stony shorelines.

Clutch size: Usually 1 to 3 eggs. Clutches of 1 to 4 eggs have also been reported.

Incubation: About 28 days. The western subspecies has an incubation period of about 26 to 28 days.

Young: Chicks are precocial and leave the nest soon after hatching. They can feed themselves, but remain vulnerable and dependent on adult protection.

Fledging: Chicks can fly at about 35 days after hatching, or about five weeks.

Age at maturity: About 1.7 years for the western subspecies. Most juveniles begin breeding in their second breeding season after hatching.

Breeding frequency: Pairs may lay multiple clutches in one year, particularly in the western subspecies.

Timing can shift with region, rainfall, water levels and local conditions, particularly in Western Australia, where breeding may occur around inland salt lakes as well as coastal sites.

  • Breeding, laying and nesting: Breeding and nesting occur mainly from August to March, with some records extending from July and western breeding generally concentrated from September to February.
  • Eggs and incubation: Eggs may be present during the breeding period and take about 26 to 28 days to hatch.
  • Flightless and dependent chicks: Flightless chicks may be present during the breeding period, and usually need about five weeks after hatching before they can fly.
  • Foraging and coastal presence: Hooded Plovers are resident or locally nomadic, foraging along the waterline, wrack line, beaches, estuaries and suitable salt-lake margins throughout the year.
  • Highest clearing risk: The highest risk is July to March, when clearing, vehicle access, dogs, people and construction can harm eggs, nests or flightless chicks, so use local records and a targeted field check before works.

Identification: Appearance and size

The Hooded Plover is a stocky, small shorebird with a distinctive dark hood and white collar. It is often difficult to see on a beach because adults, eggs and chicks blend into sand, shell and beach debris.

Adults have a black or dark hood, a white collar, white underparts and pale brownish-grey upperparts. The bill is red or pinkish red with a black tip. The legs are dull orange pink, and the eyes are dark with a pale or red eye ring.

The bird is about 19 to 23 cm long. It generally weighs 75 to 125 g.

  • Juveniles are dull grey brown and lack the adult black hood.
  • A juvenile has a mostly dark bill with a pale or orange base.
  • In flight, the bird shows a broad white wing bar.

Identification: Calls and similar species

Calls are not a reliable identification feature for routine site work. Watch for adults giving alarm calls, displaying distraction behaviour or moving repeatedly between a nest area and the waterline.

Adults are distinctive, but juveniles can be confused with other small plovers and sandpipers. Red-capped Plover chicks can resemble Hooded Plover chicks. An unattended Hooded Plover chick has a white nape.

Identification: Field signs

The nest is a simple, shallow scrape on bare sand, shell, gravel or sparse beach vegetation. It may contain small pieces of shell, stone, seaweed or other beach material.

Eggs and chicks are well camouflaged. A broken-wing display, where an adult appears injured and leads a person or predator away, is a strong warning that a nest or chick is nearby.

  • Adults repeatedly alarm calling or moving away from a particular area.
  • A small scrape above the high-water mark, on a foredune, dune or stony terrace.
  • Tiny, mobile chicks sheltering beside rocks, vegetation or beach debris.
  • Tracks and signs of regular movement between the nest area and the waterline.

Distribution: Range by state and region

The Hooded Plover is endemic to southern Australia. It is resident overall, but local movements between beaches, wetlands and salt lakes can be substantial.

The species occurs along the southern and south-eastern coasts, including New South Wales, Victoria, Tasmania and South Australia. It is widely dispersed rather than concentrated in large breeding colonies.

In New South Wales, the range is mainly on the southern coast. The species has declined from parts of its former range farther north.

In South Australia, it occurs along southern ocean beaches from the eastern Great Australian Bight to the Victorian border. It also occurs on Kangaroo Island and some inland or near-coastal lakes.

In Victoria and Tasmania, it occurs widely along suitable sandy and dune-backed beaches.

The western form occurs along the south-west Western Australian coast from Cape Naturaliste to Eyre. It also occurs around inland salt lakes, including lakes well inland from the coast.

Distribution: Forms and listing coverage

The eastern Hooded Plover is the form covered by the Commonwealth Vulnerable listing. It occurs in south-eastern Australia, including New South Wales, Victoria, Tasmania and parts of South Australia.

The western form occurs in Western Australia, including the south-west coast and inland salt lakes. Western Australia lists it as Priority 4, a non-statutory category for rare or near threatened species that need monitoring.

State and territory obligations can differ from the national listing. Check the current approval and permit requirements before clearing, access works or construction.

  • New South Wales: Critically Endangered.
  • South Australia: Vulnerable.
  • Tasmania: Vulnerable (eastern subspecies) for this profile.
  • Western Australia: Priority 4.
  • Commonwealth: Vulnerable for the eastern Hooded Plover.

Habitat: Coastal habitat

Look for Hooded Plovers on open coastal margins where sand, shell, seaweed and low dunes meet. The most suitable sites are broad beaches with a relatively open upper beach and access to feeding habitat at the waterline.

Preferred coastal habitat includes sandy ocean beaches, creek mouths, inlet entrances, estuaries and the edges of coastal lakes and lagoons.

Suitable beaches are often backed by sparsely vegetated dunes and contain beach-cast seaweed or other wrack. Beach width, dune condition and the availability of a wide wave-wash zone influence habitat use.

  • Wide, flat beaches.
  • Open foredunes and low, sparse beach vegetation.
  • Creek mouths and inlet entrances.
  • Seaweed, shell banks, driftwood and other beach debris.
  • Sheltered bays as well as exposed, high-energy beaches.

Habitat: Western inland habitat

In Western Australia, the western form also uses the edges of near-coastal and inland salt lakes. Look for open mud, salt-covered mud, sand and shell banks, shallow water and nearby wetland areas.

Birds may occur hundreds of kilometres inland. Wetland condition and recent rainfall can influence where birds gather.

  • Inland salt lake margins.
  • Saltpans and shallow wetland edges.
  • Nearby grassy freshwater seepages.
  • Open areas with little tall vegetation.

Habitat: Site assessment

Assess the entire beach unit, not just the proposed work footprint. Pairs can use a long stretch of beach, and broods may move away from the nest to feed or shelter.

Check beach entrances, vehicle tracks, access paths, dune edges, creek mouths and wrack lines. These areas often attract both birds and people.

  • Walk the upper beach, foredune and waterline where safe.
  • Search around seaweed deposits, shell banks and open sand.
  • Check adjacent dunes, creek mouths, lagoons and salt lake margins.
  • Record signs of recent vehicle, dog, horse and pedestrian use.

Foraging habitat: Coastal feeding areas

Hooded Plovers forage along the waterline and across the wave-wash zone. Chicks commonly feed near the water’s edge and among beach-cast seaweed, so feeding areas can extend well beyond a nest or temporary fence.

Adults and chicks use the waterline, wet sand, wrack line and the lower beach. Beach-cast seaweed supports invertebrates that provide food.

Foraging may extend from the water’s edge to the base of the foredune. Adults can also use creek mouths, estuaries, lagoons and saltpans.

Food: Polychaete worms, molluscs, crustaceans, insects, sand hoppers and other small invertebrates. Seeds and plant material are also recorded in the diet.

  • Wet sand and shallow wave-wash areas.
  • Beach-cast seaweed and wrack.
  • Shell banks and damp sand.
  • Creek mouths, estuarine margins and lagoon edges.

Foraging habitat: Inland feeding areas

The western form forages on the margins of salt lakes, saltpans and shallow wetlands. It feeds from the surface of sand, shell, mud and salt-covered mud.

Newly hatched chicks mainly take insects. Broods can move up to 2 km in a day, so a nest search alone does not define the area that needs protection.

Foraging habitat: Implications for works

Do not assume that a fenced nest contains all birds associated with the site. Parents and chicks may leave the fenced area to reach the waterline or wrack.

Avoid driving, stockpiling materials, placing compounds or walking dogs through the upper beach, wrack line and waterline while birds are present.

  • Keep access routes away from known nests and regular feeding paths.
  • Retain beach-cast seaweed unless its removal is authorised and assessed.
  • Inspect the broader beach before moving machinery or opening temporary access.
  • Use a fauna spotter catcher familiar with beach-nesting birds where works cannot avoid suitable habitat.

Breeding habitat: Nest sites

Breeding pairs use open ground with little vegetation, usually above the high-water mark. Nests are exposed and camouflaged, and breeding birds often return to the same area each year.

Look for shallow scrapes on flat beach, foredune or sparsely vegetated dune. Nests may also occur on stony terraces, shell banks and open margins around inland salt lakes.

Coastal nests are generally between the high-water mark and the foredune, or in adjacent dunes. Some nests can shift downhill and become exposed to waves or vehicles.

Nest type: A simple, shallow scrape with little or no nest structure.

Clutch: Usually 1 to 3 eggs in eastern populations, and about 2 to 3 eggs in the western form.

Incubation: About 26 to 28 days. Both adults incubate.

  • Bare sand, shell or small stones.
  • Sparse beach vegetation rather than dense cover.
  • Open foredune slopes and dune toes.
  • Salt lake margins with sand, shell, mud or shallow water nearby.

Breeding habitat: Breeding period

In eastern and South Australian populations, nesting generally occurs from August to March, and sometimes into April. In the western form, breeding generally occurs from September to February and is influenced by rainfall and water levels.

Several attempts may occur in one breeding season. Treat suitable habitat as breeding habitat even when no nest is found during an initial inspection.

  • Expect breeding activity during spring and summer.
  • Allow for regional variation, especially around inland salt lakes.
  • Recheck sites after rain, storms, flooding or changes in beach access.

Breeding habitat: Chicks and broods

Chicks leave the nest soon after hatching. They feed themselves but depend on adults for protection, warning calls and guidance to shelter.

Chicks are flightless for about five weeks. They may crouch beside rocks, vegetation or beach debris, or move towards the waterline to feed.

  • Search slowly and scan the ground ahead before walking or driving.
  • Watch for adults giving alarm calls or using a broken-wing display.
  • Stop work if an adult repeatedly leads people away from a particular area.
  • Do not handle eggs or chicks unless directed under an approved wildlife procedure.

Sheltering habitat: Chick shelter

Adults and young use open beach and wetland margins, with nearby cover for refuge. Shelter is usually low and natural, rather than a permanent roost structure.

Flightless chicks commonly crouch beside or beneath rocks, beach debris, low vegetation, driftwood and small dune features. Parents may call chicks into cover when a person, dog, vehicle or predator approaches.

The cover may be outside a nest fence. Inspect the area between the nest, the dune and the waterline before starting work.

  • Small rocks and shell banks.
  • Beach-cast seaweed and driftwood.
  • Low dune vegetation.
  • Wrack piles and shallow hollows in the upper beach.

Sheltering habitat: Non-breeding flocks

Outside the breeding period, birds may occur in pairs or small groups, with larger flocks around coastal salt lakes and inland wetlands. Western birds can gather in flocks of hundreds.

Wetland conditions can change the location of flocks. A site that appears unused during one inspection may be occupied after rainfall or changing water levels.

  • Coastal salt lakes and lagoons.
  • Inland salt lakes and saltpans.
  • Estuary margins and shallow wetland edges.
  • Open beaches near reliable feeding areas.

Sheltering habitat: Inspection approach

Adult roost structures and fixed roost distances are not well defined for this species. Use a broad, low-disturbance search and avoid flushing birds repeatedly.

Where a flock or family group is present, map the area used for resting, feeding and movement before setting out access routes or work areas.

  • Use binoculars where possible.
  • Approach from the landward side and avoid walking directly along the waterline towards birds.
  • Record the location of birds, shelter features, wrack and access points.
  • Keep machinery, vehicles, dogs and people away from occupied areas until the site is assessed.

Threats: Vehicles, machinery and access

The main works-site risk is disturbance or direct damage to eggs and flightless chicks. Because the birds nest in open public areas, even short-term access changes can affect breeding success.

Vehicles can crush eggs and chicks, damage shallow scrapes and compact feeding habitat. New tracks, informal access points and parking areas can bring people and vehicles into nesting zones.

Plan access before mobilisation. Keep vehicles off beaches wherever possible and use existing approved routes that avoid occupied habitat.

  • Do not drive over the upper beach, foredune or salt lake margin without an ecological assessment.
  • Do not park beside nest fencing or signs.
  • Close or rehabilitate redundant vehicle tracks.
  • Use a spotter catcher during works where birds or suitable breeding habitat are present.

Threats: People, dogs and recreational use

People, off-leash dogs, horses and frequent beach activity can flush adults from nests. Repeated disturbance can expose eggs to heat, cold, flooding and predators.

Use clear signs, fencing and supervised access where works overlap with public areas. Remember that chicks can move outside a temporary fence to feed.

  • Keep dogs on leads near beaches and wetland margins.
  • Keep workers out of signed or fenced areas.
  • Keep pedestrian routes near the water’s edge only where this avoids birds and is safe.
  • Use on-site education or guardians during busy periods where practical.

Threats: Predators and habitat change

Foxes, feral cats, domestic dogs and some other predators can take eggs, chicks and adults. Litter can attract predators and should be removed from work areas and access routes.

Coastal development, weed invasion, dune alteration, erosion, storm surge and sea level rise can reduce or fragment suitable habitat.

  • Control foxes on mainland Australia where authorised and appropriate.
  • Manage feral cats in accordance with the site’s pest management plan.
  • Remove litter and food waste from compounds and access points.
  • Avoid unnecessary removal of wrack, dune vegetation and natural shelter.

Threats: Protection and compliance

The eastern Hooded Plover is nationally Vulnerable. New South Wales lists the species as Critically Endangered, South Australia as Vulnerable, Tasmania as Vulnerable, and Western Australia lists the western form as Priority 4.

Confirm the applicable Commonwealth, state and local requirements before clearing or construction. Where a nest, chick or breeding territory is found, stop nearby works and obtain ecological advice before proceeding.

  • Record nest, adult and chick locations with photographs and coordinates.
  • Establish a site-specific exclusion area based on the birds’ observed movements and the work risk.
  • Brief all workers, contractors and visitors before access begins.
  • Monitor the site throughout the breeding period and after major weather or access changes.

Survey methodology: 1. Desktop assessment

Hooded Plovers are small, well camouflaged beach nesting shorebirds. Surveys need to cover the upper beach, foredune, wrack line, creek mouths, inlet entrances and nearby salt-lake margins, not just the waterline.

Check current records, local population information, coastal bird monitoring data and land tenure before attending site. Confirm whether the site supports the eastern or western form where this distinction is relevant.

Map beaches, dunes, seaweed deposits, creek mouths, inlet entrances, salt-lakes, mudflats, shallow water and likely roost areas. Check proposed access tracks, work areas, laydown areas, lighting and areas that may be affected indirectly by noise or people.

Breeding habitat: Flat beaches above the high-water mark, stony terraces, sparsely vegetated dunes and, for the western form, inland and near-coastal salt-lake shores

Breeding period: Generally August to March in south-eastern Australia, and September to February for the western form

  • Check the Commonwealth listing and the relevant state listing before planning works.
  • Treat records as sensitive and avoid publishing nest or breeding-place locations unnecessarily.
  • Seek advice from the relevant state wildlife agency where taxonomy or subspecies boundaries affect the approval pathway.

Survey methodology: 2. Field survey

Use experienced shorebird observers who can distinguish adults, juveniles and flightless chicks from beach debris and other small plovers. Walk slowly through the full proposed disturbance area and the adjacent beach, dune and feeding areas.

Search the upper beach, foredune, dune face, wrack line, creek mouths and inlet entrances. For the western form, include salt-lake edges, shell or sand banks, open mud, salt-covered mud and shallow water.

Nest appearance: A simple shallow scrape on sand or sparse beach vegetation, usually above the high-water mark

Chick mobility: Chicks leave the nest shortly after hatching and can move outside temporary fenced areas to feed

  • Survey in daylight and include the period when birds are likely to be using the site. Low tide is useful for checking waterline feeding areas, but do not restrict the survey to low tide.
  • Use a route that avoids walking directly towards birds or likely nest scrapes.
  • Scan from a distance with binoculars and stop regularly to check for adults that are sitting low, broken-wing displays, eggs, chicks, tracks and alarm calls.
  • Repeat the survey when conditions or access prevent a confident inspection.

Survey methodology: 3. Timing and survey effort

Plan breeding surveys during the local breeding period, especially before works that affect beaches, dunes, salt-lakes or access routes. A single visit may miss a nest because eggs and chicks are camouflaged and adults may leave the nest when approached.

Use repeat visits where a breeding place is suspected, where habitat is suitable, or where works will continue through the breeding period. Set the number and spacing of visits according to habitat, project risk, weather, access and advice from the relevant authority or species specialist.

Incubation: About 28 days in the eastern form, and about 26 to 28 days in the western form

Chick flight: About five weeks after hatching

  • Avoid surveys during heavy rain, strong winds, storm surge or poor visibility unless the purpose is to assess storm damage or an urgent risk.
  • Recheck after storms, high tides, flooding, major visitor events or changes to beach access.
  • For inland salt-lakes, survey after suitable rainfall as well as during dry conditions because water levels and flock locations can change.
  • Do not rely on absence during one visit as evidence that a breeding place is unused.

Survey methodology: 4. Records and reporting

Record enough information to support decisions, repeat surveys and compliance reporting. Map observations without disclosing sensitive locations more widely than necessary.

  • Record date, start and finish time, observers, weather, tide or water conditions, route, survey area and visibility.
  • Record each adult, pair, juvenile, nest, egg, chick, flock, roost and alarm response separately where possible.
  • Describe the location using coordinates and a site map. Photograph habitat and signs of breeding from a safe distance.
  • Record beach use, dogs, horses, vehicles, predators, weeds, litter, storm damage and other disturbance sources.
  • Report suspected breeding places, injured birds, mortalities and unexpected concentrations to the project ecologist and relevant wildlife authority.

Before habitat disturbance: 1. Approvals and permits

Avoidance is the preferred measure for a Hooded Plover breeding place and its feeding and movement areas. Treat a beach, dune or salt-lake margin as occupied until a suitably experienced ecologist has assessed it and the relevant approval pathway is clear.

Confirm the Commonwealth and state requirements before clearing, construction, access changes or other disturbance. The Hooded Plover is listed as Vulnerable under the EPBC Act, with additional state listings that may be more restrictive.

The eastern form is the EPBC listed unit identified in the Commonwealth profile and occurs in New South Wales, Victoria and Tasmania. The western form occurs in Western Australia and inland and coastal salt-lake systems. State records and legal instruments should be checked for the exact population or taxon affected.

Commonwealth status: Vulnerable

State and territory context: Critically endangered in New South Wales, Vulnerable in South Australia, Priority 4 in Western Australia, and treated as a threatened or conservation-significant species in Victoria and Tasmania

  • Refer the action under the EPBC Act if the project may have a significant impact on the listed population or its habitat.
  • Obtain the relevant state permit, consent or licence before handling birds, eggs, chicks or nests, or before disturbing a protected breeding place.
  • In Queensland, obtain advice before any work that may affect protected wildlife or a breeding place. A species management program may be required where breeding-place tampering is proposed.
  • In South Australia, account for the Vulnerable listing and any local management requirements. In Western Australia, account for the Priority 4 category and obtain DBCA advice where the western form or its habitat may be affected.
  • Do not assume that a planning approval authorises wildlife handling or nest disturbance.

Before habitat disturbance: 2. Avoidance and work design

Keep works, vehicles, storage, lighting, people and dogs away from breeding places and regular feeding or roost areas. The breeding place may extend along about 1 km of beach, and chicks can move well beyond a nest.

Use the smallest practical work footprint. Retain open beach, sparse foredune, wrack, creek mouths, inlet entrances and salt-lake margins that support feeding or shelter.

Typical nest position: Above the high-water mark, on the foredune, dune or sparsely vegetated beach

Breeding territories: Western form territories are about 37 ha and nests are dispersed

  • Realign access tracks, compounds and work areas away from the beach and foredune where practicable.
  • Keep vehicles off beaches. Use existing formal access routes and close redundant informal tracks.
  • Plan work outside the local breeding period where possible. If work must occur during breeding, obtain site-specific ecological advice and approval before starting.
  • Do not clear dunes, beach vegetation or seaweed without checking for nests, chicks and feeding habitat.
  • Design lighting away from beaches, dunes and salt-lake margins. Use the lowest practical intensity and avoid unnecessary night lighting.

Before habitat disturbance: 3. Pre-clearance survey and exclusion

Complete a pre-clearance inspection shortly before works begin and again after any delay that could allow birds to establish a nest. Use a suitably experienced shorebird ecologist, particularly where the site is on a known breeding beach or salt-lake.

Set exclusion areas around nests, chicks, adults showing alarm behaviour and any breeding place. The boundary must include the nest, likely chick routes, waterline feeding areas and access points that could expose birds to repeated disturbance.

Chick development: Chicks are flightless after hatching and usually become able to fly at about five weeks

Nest risk: Nests and chicks are highly camouflaged and can be crushed by people or vehicles

  • Use temporary fencing and clear signs where they will reduce trampling, vehicle access and visitor disturbance.
  • Place fencing so birds can still reach the waterline, wrack line and shelter. Check outside the fence because families can move beyond it to feed.
  • Use a site-specific buffer set by the ecologist and relevant authority. Do not apply a generic distance where it fails to protect the full breeding place.
  • Inspect the exclusion boundary after storms, tides, vandalism, vehicle entry or movement of fencing.
  • Keep dogs, horses and non-essential people outside the exclusion area.

Before habitat disturbance: 4. Crew induction and readiness

Give every worker, contractor, spotter catcher and visitor a short site induction before entering the work area. The induction should use photographs or maps showing the exclusion area and access route.

Nominate one person to manage wildlife issues and confirm who can stop work. Ensure all crew members know that a bird moving away from a nest is a warning sign, not evidence that the area is clear.

  • Explain the species appearance, broken-wing display, alarm calls, eggs, chicks and likely hiding places.
  • Mark exclusion areas, permitted routes, vehicle limits and dog controls on the site plan and in the field.
  • Provide the project ecologist, wildlife authority and wildlife carer contact details before work starts.
  • Keep first aid materials, a ventilated box and clean cloth available for an injured bird, but do not allow untrained staff to handle wildlife.
  • Record the induction date, attendees and any changes to the control measures.

During habitat disturbance: 1. Sequential work and active supervision

Work slowly and keep disturbance predictable. The fauna spotter catcher or nominated ecologist must have clear authority to stop work whenever a Hooded Plover, nest, chick, breeding place or unexpected roost is found.

Start with low-risk areas and progress towards higher-risk areas only after checks are complete. Maintain an experienced observer while works are occurring near beaches, dunes, salt-lakes or known feeding areas.

Keep machinery, vehicles and people on approved routes. Do not chase, herd or surround birds.

  • Stop the relevant activity if a Hooded Plover enters the work area, shows alarm behaviour, uses a broken-wing display or cannot move safely away.
  • Keep workers and machinery still until the ecologist has assessed the situation.
  • Move back along the approved route rather than crossing the bird's path to the waterline or dunes.
  • Recheck the work area after breaks, shift changes, storms and movement of temporary fencing.
  • Do not work at night near breeding habitat unless specifically assessed and approved.

During habitat disturbance: 2. Active breeding place or roost

If an active nest, egg, flightless chick, breeding pair, flock or roost is found, stop work in the affected area. Establish a temporary no-entry area and obtain advice from the project ecologist and relevant authority before resuming.

Do not move a nest, egg or chick. Do not dismantle fencing or signs because the birds appear absent. Adults may be feeding or may be keeping away from the nest because of disturbance.

Nest movement: Western form nests may move downhill by up to about 4 m and can become exposed on the beach

Brood movement: Western form broods may move up to 2 km in a day

  • Mark the location from a safe distance without approaching the nest or chick.
  • Prevent vehicles, plant, dogs, horses and non-essential people from entering the area.
  • Assess whether the work can be redesigned, delayed or completed from outside the exclusion area.
  • Allow only authorised wildlife handlers to capture or handle an animal, and only where the approval and welfare requirements permit it.
  • Treat a flock or roost as a site feature requiring protection, particularly for the western form where large flocks may occur on inland wetlands and coastal salt-lakes.

During habitat disturbance: 3. Injured, trapped or dead animals

Keep people, dogs and machinery away from the bird. Reduce noise and visual disturbance and contact the project ecologist or wildlife authority promptly.

Only an authorised and trained person should capture or handle the bird. Use a licensed wildlife carer or veterinarian for assessment and treatment.

  • Do not feed, water or release the bird without professional direction.
  • Place an injured bird in a secure, ventilated container lined with a clean towel if an authorised handler directs this action.
  • Record the location, condition, apparent injury, time found, action taken and destination.
  • Report mortality, collision, crushing, predation or vehicle strike through the project incident system and to the relevant authority where required.
  • Search for associated eggs or chicks from outside the affected area and follow the ecologist's direction.

During habitat disturbance: 4. Stop-work records and communication

Make wildlife observations part of the daily environmental record. The record should show how the stop-work decision was made and when the area was cleared for work.

Use a simple map and photographs taken from a safe distance. Keep sensitive breeding locations controlled.

  • Record date, time, location, species, number, life stage and behaviour.
  • Record the activity underway, plant involved, people present and the extent of any disturbance.
  • Record the name of the person who stopped work, the ecologist's advice, approvals consulted and the time work resumed.
  • Update the site plan, exclusion signs, induction material and daily pre-start briefing after any wildlife event.
  • Escalate repeated disturbance, non-compliance or damage to fencing through the project corrective-action process.

After habitat disturbance: 1. Post-clearance inspection

Hooded Plover families can move outside a fenced nest area and may be affected after the main task has finished. Complete a final inspection and keep controls in place until the ecologist and relevant authority confirm that they are no longer required.

Inspect the work area, access routes and exclusion boundary after plant has left and before the site is handed back. Look for injured or dead birds, damaged nests, eggs, chicks, vehicle tracks and new hazards.

Use a quiet inspection method and avoid repeated visits through the breeding place.

  • Check the beach, foredune, wrack line, waterline and nearby dunes.
  • Check that no trench, spoil pile, cable, mesh, fencing or sediment control structure traps or blocks birds.
  • Remove temporary materials that could attract predators or obstruct movement, unless they are still required for protection.
  • Photograph and map any residual impact.
  • Keep the site closed if post-clearance checks identify an active breeding place or unsafe condition.

After habitat disturbance: 2. Reporting and compliance

Provide the project manager, land manager and relevant authority with a concise wildlife report. Include both successful controls and any incidents or near misses.

Retain records with the project environmental documentation and any EPBC or state approval records.

  • Report survey results, nests, chicks, roosts, injuries, mortalities, disturbance events and stop-work actions.
  • Report any breach of an approval condition, exclusion area or handling requirement promptly.
  • Update the risk assessment where birds were found in an unexpected location or where controls were ineffective.
  • Keep geospatial records of sensitive locations in a restricted-access system.
  • Confirm whether further monitoring, rehabilitation or consultation is required before demobilisation.

After habitat disturbance: 3. Relocated or rehabilitated animals

Do not relocate a Hooded Plover unless this has been directed or authorised by the relevant wildlife authority and undertaken by an appropriately licensed person. Relocation can separate adults from eggs or chicks and may reduce survival.

If a bird has been taken into care, record the carer, veterinarian, treatment, release decision and release location.

  • Use the original capture location and nearby suitable habitat for release only when approved by the treating professional and authority.
  • Check the release site for traffic, dogs, predators, people, lighting and active breeding birds.
  • Do not release a bird into a fenced nest area or occupied territory without ecological advice.
  • Monitor the bird after release where this is required by the authority or rehabilitation provider.
  • Close out the animal record only when the outcome is confirmed.

After habitat disturbance: 4. Incident review

Review every injury, mortality, nest disturbance and unplanned stop work with the ecologist and site supervisor. Use the findings to improve the next work stage and future projects.

Include contractors and local land managers in the review where access, visitors or shared roads contributed to the incident.

  • Identify the immediate cause and the underlying planning or supervision failure.
  • Check whether the survey timing, exclusion boundary, signs, fencing, lighting or crew induction was adequate.
  • Change the method statement, traffic plan and environmental controls before similar work continues.
  • Share practical lessons at the next pre-start and retain them in the project close-out report.
  • Invite local wildlife groups or researchers to review monitoring data where this will improve conservation outcomes.

Rehabilitation actions: 1. Restore beach and dune habitat

Rehabilitation should restore the open beach and dune features Hooded Plovers use for nesting, shelter and feeding. The aim is a functioning coastal area, not simply a replanted work site.

Remove temporary infrastructure, compacted soil, spoil and rubbish from the beach and foredune. Reinstate natural contours and drainage without creating steep edges, pits or barriers that restrict chicks.

Retain suitable open sand and sparse vegetation in areas used for nesting. Avoid dense planting across open nest habitat.

Preferred breeding setting: Open sand or sparse vegetation above the high-water mark, on beaches, fore dunes and dunes

Important food habitat: Beach-cast seaweed and the wrack line support invertebrate prey

  • Use local coastal materials and methods that are compatible with natural sand movement.
  • Stabilise erosion where necessary, but avoid hard structures or access changes that reduce the beach or wrack line without ecological assessment.
  • Reopen or formalise pedestrian routes so visitors do not cross nesting and feeding areas.
  • Keep vehicles off rehabilitated beaches and dunes.
  • Inspect restored areas after storms and high tides.

Rehabilitation actions: 2. Manage weeds and predators

Control weeds that alter open beach and dune structure, including Sea Spurge, Marram Grass, Sea Wheatgrass, Pyp Grass and Beach Daisy where they threaten suitable habitat. Stage control works outside active breeding places unless approved otherwise.

Manage foxes on mainland Australia and feral cats in accordance with approved programs and state requirements. Avoid control methods that create additional disturbance or risk to Hooded Plovers and other fauna.

  • Map weed infestations before treatment and use methods suited to the site.
  • Remove or secure food waste and litter that may attract predators.
  • Inspect fences, bins and access points for predator or dog entry.
  • Coordinate predator and weed programs with the land manager and relevant authority.
  • Monitor whether control is opening suitable nesting habitat or causing new erosion.

Rehabilitation actions: 3. Water, access and lighting

For salt-lake and wetland sites, retain the shallow water, mud, shell banks and wetland connections that support feeding and flocking. Water levels and flock locations can change with rainfall and drying.

Keep access management consistent after construction. A reopened informal track can undo rehabilitation quickly.

  • Avoid changing drainage, runoff or groundwater patterns without assessing effects on nearby wetlands and salt-lakes.
  • Keep sediment, concrete washout and contaminants out of coastal waters and wetlands.
  • Use signs and defined pedestrian paths to keep visitors away from breeding and feeding areas.
  • Remove unnecessary night lighting near beaches, dunes, salt-lakes and roosts.
  • Use shielded, low-intensity lighting directed away from habitat where lighting cannot be avoided.

Rehabilitation actions: 4. Replacement habitat and artificial structures

Hooded Plovers nest in simple ground scrapes and do not use nest boxes, bat boxes or enclosed roost structures. Artificial nest sites or replacement breeding structures should not be installed as a routine measure.

If a project removes a nesting or feeding area, first redesign the action to retain natural habitat. Any proposed artificial or assisted site must be developed by a shorebird ecologist with the relevant authority and tested against local habitat, erosion, flooding, predator and visitor risks.

  • Do not install nest boxes or bat boxes for Hooded Plovers.
  • Do not create fenced artificial sites that prevent adults or chicks reaching the waterline.
  • Use natural habitat restoration, access control, weed management and predator management as the primary compensatory measures.
  • Treat any artificial nest scrape or managed site as an experiment requiring approval, monitoring and a clear exit plan.
  • Do not move eggs, chicks or nests to an artificial site without explicit authority and an approved procedure.

Rehabilitation actions: 5. Long-term monitoring

Monitor restored beaches, dunes and salt-lake margins through the local breeding period and after major storms. Monitoring should test whether birds return, breed successfully and can reach feeding and shelter areas without excessive disturbance.

Use the same mapped routes and recording fields across seasons so results can be compared with local surveys and broader population monitoring.

Monitoring context: Volunteer and government programs conduct regular population and breeding monitoring in parts of the species' range

Movement context: The species is resident in much of its range, but the western form can move between inland wetlands and the coast

  • Record Hooded Plover presence, pairs, nests, eggs, chicks, fledged young, feeding birds and flocks.
  • Record nesting success or failure and likely causes, including people, dogs, vehicles, predators, weeds, storms and erosion.
  • Check whether fencing and signs remain effective and whether chicks move beyond the protected area.
  • Review results with land managers, community groups, researchers and the relevant wildlife authority.
  • Continue monitoring for as long as required by the approval, rehabilitation plan or site risk assessment, and adapt management when results show that birds are being disturbed or habitat is declining.

Sources