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Wood Sandpiper (Tringa glareola)

The Wood Sandpiper is a small migratory shorebird that uses shallow inland freshwater wetlands in Australia, especially ponds and pools with emergent grass or reeds, surrounding tall plants, trees and fallen timber. It is globally listed as Least Concern, but it is listed as Endangered in Victoria and may be encountered during wetland clearing, construction and infrastructure works.

Conservation status

Victoria, Flora and Fauna Guarantee Act 1988: Endangered.

Breeding season

The Wood Sandpiper is a full migrant, but the supplied documents do not give month-by-month Australian arrival or departure dates. The calendar below therefore identifies the documented northern breeding cycle and marks Australian presence as occurring during the non-breeding or passage period without assigning unsupported peak months.

Use local records, wetland water levels and pre-clearance surveys to establish site-specific timing. Do not assume that absence during one visit means the wetland is not used.

  • Movement and migration: The species is a full migrant and is recorded in Australia as a migratory or non-breeding visitor. Exact Australian presence months are not supplied.
  • Breeding: Breeding is reported from May to mid-July. Breeding areas are reoccupied from late April, or early June in northern Russia.
  • Young: The supplied documents do not provide hatching, fledging or dependency dates. This row follows the documented May to mid-July breeding period and should not be used as an Australian young-bird calendar.
  • Non-breeding habitat use: Outside the breeding season the species uses shallow freshwater wetlands, muddy marshes, stream banks, temporary pools, swamps, flooded grassland and irrigation channels. Australian timing is not specified.
  • Highest clearing risk: Any month with birds present can carry risk where clearing removes shallow freshwater wetland habitat or repeatedly disturbs feeding and sheltering birds. The supplied documents do not support Australian peak-risk months.

Identification

The Wood Sandpiper is a small, slim wader with a dark upper body and white underparts. It is wary and often flies before an observer can approach closely.

Adults are dark grey-brown above, with light flecks or spots, and white below. The breast is lightly mottled, the legs are yellow-green and the bird has a distinct white brow line.

In flight, look for a square white rump, no wing bars and strong, clipped wing beats. The species may zig-zag away when disturbed, then glide back to suitable wetland habitat.

Size: Small shorebird, 15 to 30 cm size class.

Weight: Not stated in the supplied documents.

Colour: Dark grey-brown, light-spotted upperparts, white underparts and yellow-green legs.

Identification: Calls and field signs

The main call is a shrill, whistled ‘chiff-iff-iff’. The alarm call is a sharper ‘chip’ repeated rapidly.

The supplied documents do not describe diagnostic tracks, feathers, scats or other ground signs. A nest is a shallow scrape lined with grass and leaves, but nests are in the northern breeding range rather than normally in Australian non-breeding habitat.

Identification: Similar species

BirdLife Australia identifies the Curlew Sandpiper as a similar species, but the supplied material does not provide a formal comparison of measurements or plumage characters.

For field identification, record the white brow line, yellow-green legs, square white rump and absence of wing bars, together with the use of shallow freshwater wetlands. Confirm difficult records with clear photographs, flight views and call recordings where possible.

Distribution: Australian range

The Wood Sandpiper is recorded across much of Australia, mainly at inland freshwater wetlands outside its northern breeding range. The supplied Australian sources identify records from seven states and territories but do not provide a national bioregion map or named Australian strongholds.

BirdLife Australia lists the species from Victoria, New South Wales, South Australia, Western Australia, the Australian Capital Territory, the Northern Territory and Queensland.

The species is associated with inland freshwater wetlands in Australia and is described in the supplied records as a migratory or non-breeding visitor. Exact Australian arrival, departure and concentration dates are not given.

  • Check shallow freshwater wetlands in all listed states and territories where suitable habitat is present.
  • Treat records from Victoria as particularly significant because the species is listed as Endangered there.

Distribution: Population and strongholds

The global population is estimated at approximately 3.1 to 3.5 million individuals, with a stable overall trend. The supplied documents do not give an Australian population estimate, Australian trend, named strongholds or defined subpopulations.

The North-west Marine Region report lists the species as a migratory marine species under relevant international agreements, although its Australian habitat is chiefly inland freshwater wetland.

Global population: Approximately 3.1 to 3.5 million individuals.

Global trend: Stable overall; some populations have unknown trends.

Australian strongholds: Not identified in the supplied documents.

Australian bioregions: Not identified in the supplied documents.

Habitat: Wetland types

In Australia, the Wood Sandpiper uses shallow freshwater wetlands rather than typical coastal mudflats. Habitat quality depends on shallow water, exposed or soft mud, emergent vegetation and nearby cover.

Recorded non-breeding habitats include the margins of inland freshwater lakes and reservoirs, muddy marshlands, grassy stream banks, sewage farms, wet paddyfields, small temporary pools, permanent swamps, flooded grassland and irrigation channels.

The species rarely occurs in coastal habitat, but may use creeks in saltmarshes and mangrove swamps.

Habitat: Structural features

BirdLife Australia describes a preference for ponds and pools with shallow water, grass or aquatic plants protruding above the water, tall plants, trees and much fallen timber.

Wetland edges with muddy substrate and open shallow water are important because the species wades and probes while feeding.

  • Inspect shallow wetland margins, muddy pools and grassy or reed-fringed edges before clearing.
  • Include nearby trees, dead trees and fallen timber in habitat assessments, even where the planned works are centred on the wetland edge.

Habitat: Breeding range and climate

The species breeds in the northern Palearctic, in open swampy areas in boreal forest, wet heathlands, mossy or sedgy marshes, open tundra and scrub between tundra and coniferous forest.

The supplied documents do not provide an Australian elevation limit, climate limit or mapped Australian bioregion range.

Foraging habitat: Diet

The Wood Sandpiper feeds in shallow water and wet or dry mud. It usually forages at the wetland edge, where aquatic prey are accessible from the surface, mud or shallow water.

The diet includes aquatic and terrestrial insects and their larvae, worms, spiders, crustaceans, gastropod molluscs, small fish up to 2 cm long, frogs and some plant material such as seeds.

On breeding grounds, the diet is chiefly small insects, including aquatic beetles, Hemiptera and midge larvae.

Recorded animal prey: Insects and larvae, worms, spiders, crustaceans, gastropods, small fish up to 2 cm and frogs.

Plant food: Seeds are recorded as part of the non-breeding diet.

Foraging habitat: Foraging behaviour

The species wades in belly-deep water, pecks at insects on the surface, sweeps its bill from side to side under water and probes mud. It may submerge its head and can swim while feeding.

It high-steps through shallow water and may forage in moist or dry mud. The supplied documents do not state a typical foraging distance or home range.

  • Survey both open water and adjacent mud, grass and aquatic vegetation rather than checking only the deepest part of a wetland.
  • Search around emergent plants, shallow pools, wet mud and stream or channel margins.
  • Record the wetland edge and nearby cover used by birds when they flush.

Breeding habitat: Breeding habitat

Breeding occurs in northern breeding grounds outside Australia. Australian project work is therefore more likely to affect feeding and resting birds than nests, but the breeding habitat requirements are relevant to the species’ full annual cycle.

Breeding habitat includes open swampy areas in boreal forest, wet heathlands, extensive mossy, sedgy or grassy marshes, open tundra and scrub between tundra and coniferous forest.

The nest is placed on the ground in dense vegetation, on a tussock or slight ridge, sometimes surrounded by water. The species may also use an abandoned tree nest of another species.

Breeding season: May to mid-July in the cited general account, with breeding areas reoccupied from late April, or early June in northern Russia.

Clutch size: Not stated in the supplied documents.

Incubation: Not stated in the supplied documents.

Age at maturity: Not stated in the supplied documents.

Lifespan: Not stated in the supplied documents.

Breeding habitat: Breeding behaviour

The species nests as well-dispersed solitary pairs. Reported breeding densities range from 1 to 10 pairs per square kilometre to 50 pairs per square kilometre in forest tundra.

The breeding display is a switchback flight followed by a glide to the ground, with short trilling calls.

Breeding density: 1 to 10 pairs per square kilometre, rising to 50 pairs per square kilometre in forest tundra.

Sheltering habitat: Cover and refuge

Australian birds shelter in and around freshwater wetlands, particularly where wetland vegetation, trees and fallen timber provide cover. The supplied documents do not describe a species-specific roost size or structure.

Suitable sheltering habitat includes emergent reeds and grass, tall plants around ponds and pools, trees, dead trees and fallen timber near shallow water.

When disturbed, the species bursts into flight, zig-zags away while calling and may glide back to wetland habitat.

  • Inspect vegetated wetland margins and timber-strewn edges before machinery enters the site.
  • Treat nearby trees, dead trees and fallen timber as part of the wetland habitat rather than as isolated non-wetland features.

Sheltering habitat: Roosting groups

Outside the breeding season, the species may occur singly, in small scattered groups or in larger flocks of 20 to 50 birds. Concentrations can exceed 1,000 birds during migration.

No specific roost dimensions, minimum vegetation height or required buffer distance are given in the supplied documents.

Typical non-breeding group size: Small scattered groups or larger flocks of 20 to 50 birds.

Migration concentration: Concentrations can exceed 1,000 birds.

Threats: Clearing and hydrology change

For Australian projects, the main practical risks are loss or alteration of shallow freshwater wetland habitat and disturbance of birds using wetland edges. The supplied documents provide stronger evidence for wetland drainage, habitat destruction and disease than for roads, fire or introduced predators.

Drainage and destruction of peatlands, marshes and other wetlands for forestry and agriculture are documented threats in parts of the species’ range.

At Australian development sites, clearing wetland vegetation, filling shallow pools, removing muddy margins, altering inflows or drainage, and reducing seasonal inundation can remove feeding and sheltering habitat.

  • Map shallow pools, wet margins, grassy edges, emergent vegetation and nearby trees or fallen timber before works begin.
  • Prevent sediment, spoil and fill from entering shallow water and mud used for feeding.
  • Retain wetland hydrology and avoid changes that dry shallow pools or convert them to deeper, unvegetated water.

Threats: Disturbance and fragmentation

The Wood Sandpiper is wary and nervous and flies when disturbed. Repeated machinery, vehicle, lighting or pedestrian disturbance can displace birds from shallow feeding and sheltering areas, although the supplied documents do not quantify disturbance distances.

Fragmenting a wetland edge can remove the combination of shallow water, mud, vegetation and nearby timber used by the species.

  • Use pre-clearance searches and spotter checks around shallow freshwater wetlands before vegetation removal or earthworks.
  • Keep machinery, access tracks and laydown areas away from wetland margins where practicable.
  • Stop and reassess works if birds repeatedly flush from the work area or nearby wetland.

Threats: Disease and other pressures

The species is susceptible to avian botulism and avian malaria, and future outbreaks are identified as potential threats.

The supplied documents do not provide species-specific evidence on road mortality, fire, introduced predators or Australian disease outbreaks. These pressures should still be considered where they affect wetland condition or bird movement.

  • Report sick or dead waterbirds through the relevant state or territory wildlife disease pathway.
  • Avoid creating stagnant, polluted or poorly connected wetland conditions during construction.
  • Assess road and predator risks where works isolate wetlands or concentrate birds at remaining waterbodies.

Survey methodology: 1. Daytime wetland searches

The Wood Sandpiper is a small migratory wader that uses shallow freshwater wetlands, rather than mainly coastal mudflats. Surveys should target wetland margins, shallow water, mud, emergent grass and reeds, and areas with trees or fallen timber.

Search all shallow freshwater wetlands, ponds, pools, marshes, flooded grassland, irrigation channels and wet depressions within or near the project area.

Walk slowly around the wetland margin and scan shallow water, exposed mud, emergent vegetation, grass and fallen timber with binoculars or a telescope.

Record birds that are feeding, roosting, swimming or moving between wetland areas, and map the locations of all observations.

The species is wary and may burst into flight when approached, so observers should use cover, avoid rapid movements and scan the wetland before entering the margin.

Typical size: Small shorebird, 15 to 30 cm

Useful detection features: White brow line, yellow-green legs, square white rump in flight and no wing bars

Typical group size: Singly or in small flocks in non-breeding areas; concentrations can exceed 1,000 birds during migration

  • Survey during daylight when shallow water, mud and wetland vegetation can be viewed clearly.
  • Search both occupied and recently inundated habitat because the species may feed in temporary pools, muddy margins and wet grassland.
  • Where a bird is flushed, record the original location, flight direction, landing location and any connected wetlands it may use.

Survey methodology: 2. Wetland vantage scans

Establish fixed observation points that provide views across each wetland, shallow pool and adjoining muddy or grassy margin without requiring observers to enter sensitive habitat.

Use a telescope where the wetland is broad, the bird is distant or other waders are present, and scan systematically from one end of the wetland to the other.

Repeat scans from different points where reeds, grass, dead trees or fallen timber obscure the margins.

Record the wetland condition, water depth category, exposed mud, emergent vegetation, surrounding trees and fallen timber, together with all shorebird species detected.

  • Complete scans when birds are likely to be feeding or roosting and visibility is not reduced by heavy rain, fog, glare or strong wind.
  • Avoid walking through the wetland before the scan, because disturbance can flush birds and reduce the chance of detecting birds that remain concealed.
  • Use the same observation points and recording format on repeat visits so changes in use can be compared.

Survey methodology: 3. Flush and flight-line checks

Use a controlled walk of the wetland perimeter only where a vantage scan cannot inspect obscured margins and where the work can be completed without damaging habitat.

Maintain a slow, consistent approach and record birds that flush, their direction of travel and the habitat where they land.

Check nearby shallow freshwater wetlands, pools and drainage features after a flush because Wood Sandpipers may move between suitable wet areas.

  • Do not use dogs, vehicles, repeated flushing or call playback to force detections.
  • Treat a flushed unidentified small wader as a potential Wood Sandpiper until it has been identified from photographs, plumage, flight features or an authorised expert review.
  • Schedule additional surveys when the wetland is inundated or has exposed muddy margins if the first inspection occurs when the habitat is dry.

Survey methodology: Minimum effort and reporting

The supplied documents do not provide a species-specific Australian survey guideline with a prescribed number of visits, transect length, observation hours or area-based effort. Set effort in the project survey plan so that every suitable wetland and connected wet area is covered, with repeat visits where access, water conditions or disturbance reduce detectability.

Document survey dates, start and finish times, observers, weather, visibility, survey route, observation points, wetland condition, effort, species counts, photographs and mapped locations.

Submit confirmed records to the relevant state wildlife database and retain the original field records with the project environmental documentation.

  • Survey the full area that may be cleared, inundated, dewatered, drained, accessed or otherwise disturbed, together with nearby retained wetland habitat that may receive displaced birds.
  • Record zero detections as well as positive detections, including the habitat searched and conditions that affected detection.
  • Obtain an experienced wader identification check for uncertain records before using the result to clear habitat or make a management decision.
  • Check current state survey, threatened species and wildlife handling requirements before fieldwork because the supplied documents do not provide those procedural requirements.

Before habitat disturbance: Avoid and minimise habitat loss

The project team should treat shallow freshwater wetlands and their margins as potential Wood Sandpiper habitat wherever they occur. The species is not listed under the EPBC Act in the supplied project information, but it is listed as Endangered in Victoria and is covered by international migratory bird agreements.

Retain shallow freshwater wetlands, temporary pools, muddy margins, emergent grass and reeds, and wet grassland wherever practicable.

Retain trees, dead trees and fallen timber around wetlands because the species commonly uses wetlands with surrounding tall plants, dead trees and much fallen timber.

Keep connected wet areas, drainage lines and nearby ponds available so birds can move between feeding and roosting sites.

Prevent sediment, contaminated runoff, concrete washout, oil and other pollutants from entering retained wetlands.

  • Place site compounds, access tracks, stockpiles, lighting and spoil areas outside wetlands and their functional margins wherever practicable.
  • Use the smallest practical disturbance footprint and keep machinery out of shallow water, wet mud and emergent vegetation unless the approved work requires entry.
  • Do not assume that a wetland is unsuitable because it is temporary or small.

Before habitat disturbance: Approvals and permits

Confirm the EPBC Act status against the current protected matters information before works begin, noting that the supplied project information identifies the species as not listed under the EPBC Act.

Obtain advice from the relevant state agency about the Victorian Endangered listing and any permit, authorisation or approval requirements that apply to the project location and proposed disturbance.

Confirm whether the proposed work affects a wetland, migratory bird habitat, protected wildlife or an approved conservation area under other Commonwealth, state or territory legislation.

  • Include the species and its habitat in the project environmental risk assessment even where no EPBC referral is required.
  • Do not allow unlicensed personnel to capture, handle, transport or release a bird.
  • Keep copies of approvals, permit conditions, survey records and fauna management procedures at the site.

Before habitat disturbance: Plan and prepare the site

Schedule clearing and wetland disturbance to avoid periods when suitable wetlands support feeding or roosting birds, based on the pre-clearance survey, current water conditions and advice from the relevant wildlife authority.

Stage works so that retained wetland habitat remains available while disturbed areas are progressively cleared, rehabilitated or made safe.

Prepare a fauna management plan that identifies survey responsibilities, exclusion zones, stop-work triggers, authorised handlers, wildlife contacts, release locations and reporting requirements.

Complete a pre-clearance survey of every wetland and wet area that may be affected, and repeat it if water conditions or the work footprint changes.

  • Mark wetland boundaries, shallow-water margins, muddy feeding areas, emergent vegetation, retained trees and fallen timber before machinery enters the site.
  • Install exclusion fencing or other visible controls where they can keep machinery, vehicles and personnel out of retained wetland habitat.
  • Brief operators and supervisors on the species, its identification features, exclusion zones and the requirement to stop when instructed by the fauna spotter catcher.
  • Provide a quiet, shaded holding container and a direct route to veterinary or wildlife care support if handling becomes necessary.

During habitat disturbance: Daily work controls

Works should be managed to prevent birds being trapped, repeatedly flushed or exposed to machinery, sediment and contaminated water. A fauna spotter catcher should have authority to pause work where an animal or unexpected habitat risk is identified.

Inspect exclusion fencing, wetland buffers, sediment controls, access routes and machinery before work starts each day.

Complete a daily fauna inspection of the active work area and any shallow wetland, muddy margin, pool or drainage feature that will be disturbed that day.

Keep machinery, vehicles and workers within the approved footprint and prevent entry into marked wetlands or retained habitat.

Maintain clean water controls and prevent sediment, fuel, chemicals, concrete and wastewater from entering retained wetland habitat.

  • Stop or modify work if birds are repeatedly flushed, trapped, unable to leave the work area or exposed to unsafe water or machinery conditions.
  • Keep noise, lighting and vehicle movements away from retained wetland habitat where practicable, particularly during periods when birds are feeding or roosting.
  • Do not chase, herd or repeatedly flush a bird to clear an area.

During habitat disturbance: Spotter catcher and machinery coordination

The fauna spotter catcher should inspect the next work area before machinery moves, remain in communication with the operator and maintain a clear view of the active disturbance zone.

The operator should stop immediately when directed by the fauna spotter catcher, environmental officer or supervisor.

The fauna spotter catcher should check behind machinery, around spoil, stockpiles, wet depressions, reeds, grass and fallen timber as work progresses.

Use staged clearing towards retained habitat only where the method has been assessed as safe for the site and does not drive birds into traffic, water hazards or active machinery.

  • Keep a safe separation between the fauna spotter catcher and machinery, and do not enter an operating plant exclusion zone.
  • Use a spotter catcher with the required state or territory authority for any capture, handling, transport or release activity.
  • Record the time, location, activity, animal response and action taken for each fauna incident.

During habitat disturbance: Animal found or injured

If a Wood Sandpiper is found, stop the immediate activity, establish a quiet exclusion zone and allow the bird a safe opportunity to leave without pursuit.

If capture is necessary, only an appropriately authorised person should handle the bird, using the least stressful method and the shortest practical holding time.

Release a healthy bird only at nearby suitable retained wetland habitat selected by the fauna spotter catcher or wildlife authority, with shallow water, mud or wet grass and low immediate disturbance.

Take an injured, exhausted or contaminated bird to a veterinarian or authorised wildlife carer as soon as practicable, and record the transfer.

  • Do not provide food, water or medication unless directed by a veterinarian or authorised wildlife carer.
  • Do not relocate a bird to an unassessed wetland, across a road or into active construction areas.
  • Treat an unidentified small wader as a potential Wood Sandpiper until identification has been resolved.
  • Stop work and notify the project environmental officer if the bird cannot safely leave, if a dead or injured bird is found, or if suitable habitat is unexpectedly within the disturbance footprint.

After habitat disturbance: Post-clearance checks

Post-work checks should confirm that no fauna remains trapped and that retained wetlands continue to provide usable shallow-water habitat. Records should support any required agency reporting and inform later rehabilitation.

Inspect the cleared area, wetland margins, excavations, pipes, pits, drains, stockpiles and temporary fencing at the end of each work shift and after major work stages.

Check retained wetlands for stranded, injured or dead birds and for changes in water quality, water level, mud exposure, emergent vegetation and access to feeding areas.

Remove or make safe temporary hazards such as open pits, uncovered pipes, netting and unsecured fencing when they are no longer required.

  • Keep exclusion fencing and wetland protection controls in place until the environmental officer confirms that the risk has ended.
  • Repeat the check after rainfall, flooding, dewatering, major water-level changes or any event that changes wetland habitat.
  • Record the result of every check, including no detections.

After habitat disturbance: Monitoring and reporting

Monitor retained and rehabilitated wetlands during the project and after completion where they remain connected to the disturbance area or are used as release habitat.

Compare bird detections, wetland condition and disturbance observations with the pre-clearance baseline using the same observation points and recording methods where practicable.

Report incidents, handling, injury, mortality, unauthorised habitat damage and failures of controls to the project environmental officer and the relevant authority where required by approval or permit conditions.

  • Submit confirmed records and relevant incident information to the applicable state wildlife database or reporting system.
  • Review the results after each work stage and change buffers, timing, access or controls if birds continue to use the area or if disturbance is greater than predicted.
  • Assess whether any approval condition, permit condition or offset requirement has been triggered before project close-out.

Rehabilitation actions: Recreate wetland habitat

Rehabilitation should recreate shallow freshwater feeding habitat and maintain safe movement between wetlands. The aim is to provide open shallow water, muddy margins and wet vegetation, while retaining the trees and fallen timber that characterise suitable sites in Australia.

Reinstate shallow freshwater pools, wet depressions, marshy margins and drainage features where these are part of the approved rehabilitation design.

Provide a mix of shallow water, exposed muddy edge, wet grass and emergent reeds or other aquatic plants rather than a single deep or steep-sided basin.

Use local native wetland plants suited to the site, including grass and aquatic or emergent species that can provide feeding margins without completely covering the shallow water.

Retain or re-establish surrounding trees, dead trees and fallen timber where they do not create a safety or flood risk.

  • Design banks with gradual shallow margins and irregular edges where practicable to increase the amount of usable mud and shallow water.
  • Prevent steep-sided pits, deep permanent water and dense vegetation that removes all open feeding margin.
  • Do not introduce ornamental, invasive or non-local plant species.

Rehabilitation actions: Habitat protection and management

Control weeds so native wetland plants, wet grass and open muddy margins can develop.

Manage sediment, nutrients, rubbish, vehicle access and domestic animal access so water quality and feeding areas are maintained.

Control introduced predators and other threats in accordance with the approved site management plan and advice from the relevant authority.

Apply fire management that protects wetland vegetation, fallen timber and retained trees, and avoids removing all cover from wetland margins.

  • Keep rehabilitation areas free from stockpiles, repeated vehicle access and unnecessary lighting.
  • Maintain water regimes that provide shallow wet areas and muddy margins during the period when the site is used by migratory shorebirds.
  • Inspect rehabilitated areas after rain, dry periods, weed treatment and fire to identify erosion, drying, weed invasion or loss of feeding habitat.

Rehabilitation actions: Monitoring and success measures

Monitor rehabilitated wetlands for water presence, shallow-water extent, exposed mud, emergent native vegetation, wet grass, weed cover, sediment controls and use by Wood Sandpipers and other wetland birds.

Use repeat daytime vantage scans and perimeter searches at the same locations where practicable, and record survey effort, water conditions, birds detected and any disturbance.

Set project-specific completion criteria using the pre-disturbance habitat assessment and approval conditions, because the supplied documents do not provide numerical Australian rehabilitation targets for this species.

Recorded non-breeding habitat features: Shallow freshwater lakes and reservoirs, muddy marshlands, grassy stream banks, sewage farms, wet rice fields, temporary pools, permanent swamps, flooded grassland and irrigation channels

Recorded feeding behaviour: Wades in shallow water, picks insects from the surface, probes mud and may sweep its bill underwater

Recorded breeding nest features: Ground scrape among dense vegetation or on a tussock or slight ridge, sometimes surrounded by water

  • Include successful establishment of shallow freshwater habitat, safe access to feeding margins, functioning wetland connections and absence of fauna hazards in the completion assessment.
  • Investigate and correct rehabilitation failure where water does not reach the intended shallow margins, weeds dominate, erosion removes mud or birds cannot safely use the area.
  • Maintain monitoring and corrective actions for the period required by the project approval, permit or rehabilitation plan.
  • Where residual impacts remain, identify and deliver any required offset or compensatory conservation measure under the applicable approval framework.

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