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Pacific Golden-Plover (Pluvialis fulva)

The Pacific Golden-Plover is a migratory shorebird that breeds in Arctic tundra and spends the non-breeding period across Pacific islands, Australia, New Zealand and parts of Asia. In Australia it can use beaches, mudflats, coastal marshes, short grass, agricultural fields, airport grounds and other open sites, so clearing and construction can remove feeding habitat or disturb birds during their Australian stay.

Conservation status

Victoria, Flora and Fauna Guarantee Act 1988: Vulnerable.

Breeding season

Pacific Golden-Plovers are present in Australia during the non-breeding period. Timing varies among populations, but the supplied sources describe southward movement mainly in August and September and departure by April or May.

The seasonal pattern is a broad guide. Confirm local arrival, departure, feeding and roosting dates from current Australian records before scheduling works.

  • Breeding: Breeding occurs in Alaska and Siberia from May to July, not in the Australian range described in the supplied sources.
  • Young: Chicks hatch from May to August in the breeding range. They leave the nest soon after hatching and fly at about 26 to 28 days.
  • Southward migration and arrival in Australia: Southward migration to Pacific islands, Australia, New Zealand and Asia occurs mainly in August and September. Some birds make long nonstop flights from Alaska to Hawaii and continue south.
  • Australian non-breeding presence: Birds remain in non-breeding areas until April or May. Australian sites may therefore be occupied from late winter or spring through autumn, depending on the population and site.
  • Highest clearing risk: Clearing or disturbance is most likely to harm the species while birds are using Australian feeding or roosting habitat, especially during the main spring to summer presence period. Risk also occurs during arrival and departure in August to May.

Identification

Pacific Golden-Plovers are medium-sized, compact plovers that forage on open ground by running, stopping and pecking. Identification can be difficult because they closely resemble American Golden-Plovers.

Adults are about the size of a robin. They have a short, black bill, dark brown eyes, grey to black legs and feet, pointed wings and a short, rounded or square-tipped tail. Non-breeding birds are mottled brown, grey, yellow and white, with a golden appearance on the upperparts.

Length: 23 to 28 cm.

Wingspan: 61 to 71 cm.

Weight: 120 to 200 g.

  • In breeding plumage, the upperparts are golden and black. The male has a strongly defined black face, throat and underparts bordered by white, while the female is usually less sharply marked and has more mottling.
  • Juveniles have yellow, black and brown mottling on the head and back, with pale underparts.

Identification: Separating similar plovers

The species is very similar to the American Golden-Plover and the two may not always be identifiable in the field. Pacific Golden-Plovers are generally slimmer and shorter, with longer legs and usually brighter golden markings on the back. They commonly show more white along the sides in breeding plumage and have shorter wingtips than American Golden-Plovers.

Pacific Golden-Plover length: About 23 to 26 cm in the Animal Diversity Web account.

American Golden-Plover length: About 24 to 28 cm in the comparison provided.

  • Treat uncertain records as Pacific or American Golden-Plover unless an experienced observer can make a reliable identification.
  • Do not rely on plumage alone in worn, juvenile or non-breeding birds. Use overall shape, wing projection, leg length, back colour and the extent of white on the sides together.

Identification: Field signs and calls

The usual call is a mellow, rising whistle described as quee-lee-lee. Breeding displays include repeated plaintive whistles. Birds usually walk or run on the ground and are unlikely to leave distinctive tracks or scats that can be identified reliably during a site inspection.

Nests are shallow scrapes on the ground, lined with lichen, moss, grass and leaves. A nest contains pale buff to cinnamon eggs with bold black and brown blotches. No specialised den, hollow or burrow is used.

  • Record repeated rising whistles, especially where birds are defending open ground or displaying in spring and summer on the Arctic breeding grounds.
  • Search for birds rather than relying on signs. Their mottled upperparts provide camouflage against bare ground, short grass and tundra vegetation.
  • Treat any ground scrape containing eggs or attended by an adult as a protected breeding site and stop disturbance pending ecological advice.

Distribution

The species has a broad Pacific migration system. It breeds in Alaska and Siberia and spends the non-breeding period in Australia, New Zealand, Pacific islands and parts of Asia.

In Australia, Pacific Golden-Plovers are non-breeding visitors. The supplied sources confirm Australia as part of the non-breeding range, but do not provide a state-by-state distribution, named Australian strongholds or a bioregional map.

They may occur in coastal and inland open habitats, including beaches, mudflats, coastal marshes, agricultural fields, pastures, airport fields, lawns and golf courses. The supplied Victorian listing indicates that the species is of conservation concern in Victoria.

Australian range: Non-breeding range includes Australia, but the supplied sources do not specify all occupied states.

Victorian status: Vulnerable, according to the listing supplied with the brief.

Australian bioregions: Not specified in the supplied documents. Suitable mapped habitat includes coastal wetlands, beaches, tidal flats, short grass and open agricultural or urban areas.

  • For project assessments, check current state atlases and local wetland records rather than assuming that absence from a broad range map means absence from a site.
  • Give particular attention to open coastal wetlands, tidal flats, short grass and other known shorebird feeding areas.

Distribution: Migration and population

Alaskan birds may fly directly to Hawaii and some continue to Australia or New Zealand. Birds from eastern Russia may winter in Australia, Southeast Asia and the South Pacific. Southward movement generally occurs in August and September, with birds remaining in non-breeding areas until April or May.

The global population is large but decreasing. The main broad-scale concerns identified in the sources are habitat alteration, climate change, severe weather, sea-level rise and hunting in parts of Asia.

Estimated global population: About 190,000 to 250,000 individuals; one source gives about 220,000.

Population trend: Decreasing.

Breeding range: Arctic tundra in Alaska and Siberia.

  • Expect the species in Australia mainly from August or September through April or May.
  • Use recent records and targeted surveys to identify local concentrations because wintering birds can defend small territories and return to the same territory in successive years.

Habitat: Australian habitat

Pacific Golden-Plovers use open, low-growing habitats rather than dense woodland. Habitat use changes between the Arctic breeding grounds and Australian non-breeding grounds.

In Australia, suitable habitat includes beaches, tidal mudflats, coastal marshes, short grass, flooded pastures, agricultural fields, airport fields, lawns and golf courses. The species is primarily terrestrial while feeding, even when it occurs near the coast.

Open ground with short vegetation allows birds to detect prey and run between feeding stops. Coastal sites also provide mud and exposed sediment where small crustaceans and molluscs are available.

  • Retain open feeding areas and avoid placing spoil, stockpiles, fencing or temporary facilities across regularly used short-grass or intertidal areas.
  • Map adjacent mudflats, beaches, saltwater wetlands, pasture and short grass as connected feeding habitat during project planning.

Habitat: Breeding habitat and structure

Breeding habitat is open Arctic tundra ranging from dry to moist ground, often among lichen-covered rocks, grasses and sedges. In western Alaska, Pacific Golden-Plovers generally nest at lower elevations than American Golden-Plovers, in wetter tundra with taller vegetation.

The supplied sources do not give a breeding elevation range for the species and do not identify an Australian breeding population.

Breeding vegetation: Open tundra with lichen, grasses and sedges.

Breeding ground: Dry to moist open ground, including wetter tundra with taller vegetation in western Alaska.

Known elevation limit: Not provided in the supplied documents.

  • Do not infer Australian breeding habitat from Australian winter records. Australian sites are used during the non-breeding period.
  • Where open wetland or grassland habitat is being cleared, retain the feeding surface, shallow wet areas and nearby undisturbed roosting areas.

Foraging habitat: Diet

The species feeds mainly on open ground during daylight. It uses sight to locate prey and follows a repeated run, stop, scan and peck method.

The diet includes insects such as beetles, flies, grasshoppers and caterpillars, as well as spiders, worms, small crustaceans, molluscs, berries, seeds and leaves. Local diet varies with habitat and season.

On Australian shores and tidal flats, small crustaceans and molluscs may be important. In short grass, pasture and fields, terrestrial insects and other invertebrates are likely to be the main available prey.

Feeding method: Runs or walks a few steps, pauses, scans the ground and pecks at prey.

Main prey groups: Insects, spiders, worms, small crustaceans and molluscs.

Plant food: Berries, seeds and leaves.

  • Protect exposed mud, short grass, wet pasture margins and beach wrack or sediment areas that support invertebrate prey.
  • Avoid unnecessary pesticide use in feeding habitat because it can reduce insect prey and may expose birds to poisoned invertebrates.

Foraging habitat: Foraging area

Wintering birds often forage singly within defended territories, while non-territorial birds may feed in loose groups. Reported winter territories are about 0.4 to 0.5 ha, although birds also use communal or extra-territorial feeding areas.

Breeding territories are much larger, about 10 to 50 ha, but these measurements come from the breeding range rather than Australia.

Winter territory: About 0.4 to 0.5 ha where territories are held.

Breeding territory: About 10 to 50 ha on the breeding grounds.

Activity period: Mainly diurnal.

  • Survey the full open feeding area around a detection, not only the point where the bird was seen.
  • Maintain access between feeding areas and night roosts where these areas are separated by roads, drains or built infrastructure.

Breeding habitat

Pacific Golden-Plovers do not breed in Australia according to the supplied distribution information. They breed during the Arctic spring and summer, then migrate south with adults and juveniles.

Breeding occurs in May, June and July in Alaska and Siberia. The male makes a shallow scrape in open tundra, usually on dry ground surrounded by wet tundra, and lines it with lichen, moss, grass and leaves.

Both parents incubate the eggs, defend the nest and protect the chicks. The chicks leave the nest shortly after hatching and find their own food while remaining under parental protection.

Breeding season: May to July in Alaska and Siberia.

Clutch size: Typically 4 eggs.

Incubation: About 25 days, shared by both parents.

Age at first flight: About 26 to 28 days after hatching.

Age at maturity: Sexual maturity can occur at 1 year, although breeding may not occur until later.

Recorded lifespan: At least 21 years and 3 months.

  • Treat any Pacific Golden-Plover nest found in Australia as an exceptional record requiring immediate confirmation, because the supplied sources describe Australia as non-breeding range.
  • On Australian projects, manage the species primarily as a migratory visitor using feeding and roosting habitat.

Breeding habitat: Breeding site features

Breeding sites are shallow ground scrapes in open tundra with low vegetation, lichen, moss, grasses and nearby wet ground. The eggs are cryptic against the tundra surface.

Males use high flight displays and repeated whistles to advertise and defend territories. Both adults may distract or defend against predators.

  • Keep people, vehicles and machinery away from any confirmed nest and surrounding open tundra habitat during the breeding period.
  • Do not remove low vegetation, lichen or surface substrate around a confirmed nest without species-specific ecological approval.

Sheltering habitat

The species does not use dens, tree hollows or burrows. It relies on camouflage, open ground and communal night roosts, with shelter provided by distance from disturbance and suitable surface conditions.

On breeding grounds, birds shelter and nest on the ground among lichen, moss, grasses, sedges and low tundra vegetation. Chicks leave the nest soon after hatching and return to the adults for warmth and protection.

On wintering grounds, most birds use open feeding territories and communal roosts at night. The supplied sources do not provide roost dimensions or a standard roost buffer.

Nest type: Shallow scrape on the ground.

Nest lining: Lichens, moss, grass and leaves.

Night shelter: Communal roosts on open ground; size not specified.

Special refuge structures: No den, hollow or burrow is described.

  • Inspect open coastal flats, marsh margins, short grass, pasture and nearby undisturbed ground for roosting birds before night works or early morning disturbance.
  • Keep dogs, vehicles, lighting and people away from known communal roosts where practicable.
  • Do not expect tree hollows, dens, burrows or elevated perches to be important shelter features for this species.

Threats: Clearing and habitat change

The main documented threats are loss and alteration of open coastal and wetland habitat, climate change, sea-level rise, severe weather, hunting in parts of Asia and collisions with human structures. Australian projects should manage direct habitat loss and disturbance while birds are present.

Clearing or filling mudflats, beaches, coastal marshes, short grass, pasture and open fields can remove feeding habitat. Development can also reduce access between feeding areas and night roosts.

Climate-driven sea-level rise threatens low-lying Pacific wintering areas. Changes to vegetation cover, flooding and sediment conditions can reduce the value of feeding sites.

  • Avoid clearing or filling mapped feeding and roosting habitat during the Australian presence period where practicable.
  • Stage works to retain open feeding areas, tidal access and nearby roosts, and prevent spoil or sediment from covering mudflats or short grass.
  • Control runoff, sediment and altered drainage so that wetland and tidal-flat food resources are not reduced.

Threats: Disturbance, collisions and predators

The species can occur on airport fields and other developed open areas, where collision risk is documented. Collisions with human-made structures and aircraft have been recorded. Predation occurs on breeding and wintering grounds, including by raptors, Arctic Foxes and mongooses in some regions.

The supplied documents do not quantify species-specific effects of Australian roads, fragmentation or fire. These risks should still be assessed where roads, traffic, fencing, machinery, smoke or changed ground cover affect open feeding and roosting habitat.

  • Use vehicle speed controls and fauna spotter checks around known feeding or roosting areas.
  • Avoid night lighting and night works near communal roosts unless they are necessary and can be managed.
  • Use wildlife-friendly fencing or mark wires where fencing crosses regular movement routes.
  • Keep domestic dogs and other introduced predators away from feeding and roosting areas.

Threats: Hunting and climate

The species was formerly hunted during migration in Hawaii and remains vulnerable to hunting for food in parts of eastern and southeastern Asia. Climate change, severe weather and sea-level rise are identified as broad-scale threats, despite the global IUCN status of Least Concern.

No species-specific disease threat is identified in the supplied documents.

Global status: Least Concern.

Trend: Decreasing.

Documented broad-scale threats: Habitat alteration, climate change, severe weather, sea-level rise and hunting in some regions.

  • Do not assume that a Least Concern global status removes the need to protect locally important Australian feeding and roosting sites.
  • Record unusual mortality and report suspected poisoning, collision events or disease signs through the relevant wildlife authority.

Survey methodology: 1. Habitat and timing assessment

Survey this migratory shorebird in open, short-vegetation habitat and coastal wetlands that may be used during the non-breeding period. No species-specific Australian survey effort or guideline is provided in the source material, so set effort to the extent and risk of suitable habitat and document the basis for the survey design.

Map and inspect beaches, mudflats, coastal marshes, flooded pasture, short-grass areas, agricultural fields, airport-type open areas and other open ground within the project area.

Prioritise surveys during the Australian non-breeding period, when birds may be present from about August or September to April or May.

Record habitat condition, water level, vegetation height, nearby roosting areas and any flocking or foraging birds.

Breeding habitat: Open, dry to moist Arctic tundra in Alaska and Siberia.

Non-breeding habitat: Coasts, beaches, mudflats, coastal marshes, flooded pasture, short-grass fields and other open spaces.

Non-breeding presence: Generally August or September to April or May, with local variation.

  • Complete a desktop review of recent bird records and mapped wetlands before field work.
  • Survey all suitable habitat that could be cleared, filled, drained, isolated or disturbed by construction access, compounds or machinery.
  • Treat apparently modified sites such as lawns, golf courses and other short-grass areas as potential habitat where they occur near suitable coastal or wetland areas.

Survey methodology: 2. Daylight searches

Use systematic daylight searches across suitable open habitat, including the margins of wetlands, beaches, mudflats, grassed areas and disturbed short-grass sites.

Search by walking transects or scanning fixed vantage points, and record the area covered, start and finish times, weather, visibility, tide or water conditions where relevant, and the number of observers.

Allow time for repeated scans because the species often runs a few steps, pauses and pecks at the ground, and may be missed when moving through short vegetation.

Identify birds carefully because Pacific Golden-Plovers can be difficult to separate from American Golden-Plovers.

Adult length: 23 to 28 cm.

Wingspan: 61 to 71 cm.

Typical behaviour: Run or walk, stop, scan and peck at the ground.

  • Use binoculars or a spotting scope to inspect distant birds without entering roosts or feeding groups.
  • Record plumage, size, leg colour, back colour, underwing or breast pattern, flock size, behaviour and photographs where identification is uncertain.
  • Do not rely on calls alone, although the species has a mellow, rising whistle call.

Survey methodology: 3. Roost and disturbance checks

Inspect communal roosts and likely high-tide or overnight resting areas where these occur within or beside the project area.

Repeat observations at times when birds are likely to concentrate, including before or during migration movements and when feeding habitat is inundated, but set the exact timing to local tides, water levels and bird activity.

Check for birds using more than one habitat type because the species may feed inland in short grass as well as on shores and mudflats.

  • Keep observers, vehicles and dogs away from roosting and feeding groups during searches.
  • Record the location of roosts, feeding areas, flight paths and regular movement between habitat patches.
  • Use additional survey effort if weather, tide, flooding, dense vegetation or disturbance reduces visibility.

Survey methodology: Minimum effort and reporting

Because the supplied documents do not specify a minimum number of visits, nights, hours, trap nights, transect length or survey area for this species, justify the selected effort against the mapped habitat, project footprint, season, detectability and disturbance risk.

Report negative results with the area searched, survey dates, times, observers, weather, visibility, tide or water conditions, methods and limitations.

Submit confirmed records, including zero counts where required by the relevant programme, to the relevant state wildlife database and retain records in the project environmental file.

  • Do not use spotlighting, trapping or cage trapping as default methods for this diurnal shorebird when daylight observation is suitable.
  • Do not describe a site as unused solely because birds were not detected during one visit.
  • Obtain advice from the relevant state agency or a qualified ornithologist when the project affects a wetland, roost, flock or suspected regular feeding area.

Before habitat disturbance: Avoid and minimise

Avoid disturbance to open feeding areas, wetland margins and roosts wherever practicable. Plan works around the species' migratory use of Australia and confirm all Commonwealth and state requirements before disturbance.

Retain beaches, mudflats, coastal marshes, flooded pasture, short-grass feeding areas and open wetland margins within and beside the work area.

Maintain connected movement routes between feeding areas, roosts and nearby retained habitat where these functions are identified.

Avoid placing access tracks, stockpiles, lighting, compounds and spoil on regularly used feeding or roosting areas.

  • Keep the project footprint as small as practicable in open wetland and coastal habitat.
  • Use existing cleared access routes where this avoids additional disturbance to suitable habitat.
  • Design drainage, dewatering and sediment controls so they do not remove or contaminate shallow feeding habitat.

Before habitat disturbance: Approvals and work planning

Check the current Commonwealth and state conservation status before works because the supplied profile records no EPBC listing and a Vulnerable state listing in Victoria.

Confirm whether the action may affect a listed migratory bird, wetland or other protected environmental value, and obtain any required approvals, permits or authorisations before clearing.

Prepare a fauna management plan that identifies suitable habitat, survey findings, exclusion areas, stop-work triggers, authorised personnel, incident reporting and post-work checks.

Commonwealth status in supplied profile: Not listed under the EPBC Act.

State status in supplied profile: Victoria, Vulnerable.

  • Time clearing and high-disturbance works to avoid the period when birds are present, where local surveys and agency advice support that approach.
  • Stage works so retained feeding and roosting habitat remains available while each work area is completed.
  • Brief machinery operators and all contractors on the species, exclusion areas and the process for reporting a sighting.

Before habitat disturbance: Site preparation

Complete a pre-clearance inspection of all suitable habitat immediately before disturbance and confirm whether birds are present.

Mark retained wetlands, mudflats, beaches, grassed feeding areas, roosts and access exclusions on plans and on the ground.

Install exclusion fencing or other visible controls where they can prevent vehicles, plant and people entering retained habitat without creating a barrier to bird movement.

  • Remove food waste and other attractants from work areas.
  • Plan sediment, dust, lighting, noise and runoff controls before mobilisation.
  • Nominate an authorised fauna spotter catcher and provide a clear communication method between the spotter catcher and plant operators.

During habitat disturbance: Daily controls

Keep disturbance controlled and make the fauna spotter catcher's directions effective. This species is primarily ground-dwelling and may be difficult to see in short vegetation, so operators must not rely on birds moving away before entering habitat.

Inspect the work area and exclusion controls at the start of each shift and after breaks, weather events or changes in the work footprint.

Keep vehicles, plant, workers, dogs and unnecessary lighting out of retained feeding and roosting habitat.

Control dust, sediment, runoff, noise and sudden lighting that could reduce feeding access or displace birds from retained habitat.

  • Use low-speed plant movement near retained habitat and keep the work front compact.
  • Stop machinery before entering any area that the fauna spotter catcher is checking.
  • Keep a current map of active work areas, exclusion zones, sightings and cleared areas in the site office and in the field vehicle.

During habitat disturbance: Spotter catcher and machinery interface

The fauna spotter catcher must inspect the work area before clearing and remain able to see the active clearing front.

The spotter catcher must maintain direct communication with the operator and give a clear stop instruction before approaching a bird or checking ground habitat.

Operators must stop immediately when directed and must not resume until the spotter catcher confirms that the area is clear or the fauna management plan has been followed.

  • Clear progressively from the disturbed edge towards retained habitat only where this does not drive birds into traffic, active plant or unsuitable habitat.
  • Use binoculars or a spotting scope to identify birds without unnecessary approach.
  • Do not chase, herd or force a bird towards water, roads, machinery or the edge of a wetland.

During habitat disturbance: Animal response and stop-work triggers

If a Pacific Golden-Plover is found, stop the relevant activity, establish a temporary exclusion area and allow the authorised fauna personnel to assess the bird.

Do not handle the bird unless handling is necessary, lawful and within the fauna spotter catcher's training and project authorisation.

If relocation is approved and needed, move the bird only to nearby retained habitat that provides suitable open feeding or roosting conditions and is away from active works.

  • Stop work if a bird is injured, trapped, repeatedly flushed, unable to leave the work area, or found in a proposed exclusion zone.
  • Stop work if a flock, regular roost or previously unrecorded wetland use is identified and obtain advice before restarting.
  • Transfer injured birds to a veterinarian or authorised wildlife carer through the approved project procedure.
  • Record each sighting, handling event, injury, relocation, release location, cause of disturbance, personnel and outcome.

After habitat disturbance: Post-clearance checks

Confirm that cleared areas and retained habitat remain safe after each work stage. Continue controls while construction traffic, lighting, drainage changes or rehabilitation works could affect feeding or roosting use.

Complete a post-clearance inspection of the work area, wetland margins, retained short-grass habitat and nearby roosting areas.

Check for injured, trapped or displaced birds, damaged exclusion fencing, sediment impacts, standing water changes and new barriers to movement.

Repeat checks after major changes to drainage, access, lighting, stockpiling or the work footprint.

  • Remove waste, surplus materials and temporary barriers that could trap or obstruct birds when they are no longer required.
  • Keep retained habitat free of machinery, spoil and construction materials.
  • Record whether suitable habitat remains available and whether birds continue to feed, roost or move through the area.

After habitat disturbance: Monitoring and reporting

Monitor retained and rehabilitated habitat during the remaining non-breeding period where surveys identified regular use or where disturbance was substantial.

Compare bird presence, flock size, feeding behaviour, roost use and habitat condition with the pre-work records.

Report incidents, unexpected habitat use, injury, mortality, non-compliance and corrective actions to the project environmental officer and relevant authorities as required.

  • Maintain exclusion fencing, sediment controls and access controls until the site is stable and the fauna management plan allows removal.
  • Submit confirmed records and significant incidents to the relevant state wildlife database or agency reporting system.
  • Assess whether additional mitigation, design changes or an offset is required under the applicable approval.

Rehabilitation actions: Habitat restoration

Rehabilitation should restore open feeding areas, shallow wetland function and safe movement between feeding and roosting sites. Use local ecological advice and the approval conditions to set the final design and monitoring period.

Reinstate open, low and varied vegetation around suitable wetlands, beaches, mudflats and other areas used for feeding.

Restore shallow wet areas and natural drainage patterns where construction has altered flooding or drying, without creating erosion or contaminated runoff.

Use locally appropriate native grasses and sedges where planting is needed, while retaining open ground and short vegetation required for run-stop-peck foraging.

  • Remove weeds that reduce access to open feeding ground or change wetland structure.
  • Prevent revegetation from forming dense, continuous cover across areas intended to remain open.
  • Do not add logs, rocks, hollows or nest boxes as a substitute for the open coastal and wetland habitat used by this species.

Rehabilitation actions: Threat and site management

Manage dogs, vehicles, artificial lighting and other avoidable disturbance around retained feeding and roosting areas.

Control introduced predators and pest species where they affect shorebird use, subject to the land manager's approved programme.

Apply fire planning that maintains suitable open habitat without burning wetland margins or causing disturbance during periods of local bird use.

  • Keep sediment, fertiliser, herbicide and other pollutants out of wetlands and mudflats.
  • Maintain safe movement between retained habitat patches and remove temporary barriers after construction.
  • Use fencing only where it protects habitat without preventing birds from reaching feeding or roosting areas.

Rehabilitation actions: Monitoring and success measures

Monitor vegetation height and structure, wetland water levels, weed cover, erosion, access controls and bird use at the restored site.

Use the pre-disturbance survey as the baseline and record Pacific Golden-Plover presence, flock size, feeding behaviour and use of restored or retained habitat.

Investigate and correct declining habitat condition, repeated disturbance, predator impacts or failure of birds to regain access to suitable habitat.

  • Set monitoring dates to cover the local non-breeding period and any identified migration concentration period.
  • Retain photographs, maps, bird records, maintenance actions and corrective actions in the project environmental file.
  • Close out rehabilitation only when the approval criteria are met and the site no longer creates an avoidable risk to feeding, roosting or movement.

Sources