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Ornate Soil-crevice Skink (Notoscincus ornatus)

The Ornate Soil-crevice Skink is a small terrestrial skink recorded across the Northern Territory, Queensland, South Australia and Western Australia. It can be encountered during vegetation clearing and ground disturbance, particularly where logs, bark, leaf litter, rocks and soil cracks remain. Its protection varies by jurisdiction, including Rare in South Australia and Priority 4 in Western Australia, while Queensland and Northern Territory records identify it as Least Concern.

Conservation status

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

Breeding season

The Ornate Soil-crevice Skink is poorly known, and no species specific breeding calendar has been recorded. The seasonal pattern below uses recorded detections and the general pattern for Australian skinks, with activity likely to vary between the tropical north, inland areas and southern parts of the range.

Breeding mode: Not recorded.

Clutch size: Not recorded.

Incubation: Not recorded.

Nest or breeding site: Not recorded. Protect soil cracks, fallen timber, bark, leaf litter and surface rocks as potential shelter and breeding microhabitat.

Dependent young: Not recorded.

Age at maturity: Not recorded.

Breeding frequency: Not recorded.

Timing may shift between years and regions, so survey and clearing decisions should account for local temperatures, rainfall and recent records.

  • General activity, warmer periods: Activity is expected to be greater in warmer months, although animals may remain active during mild winter conditions, especially in northern areas.
  • Indicative breeding activity: Spring to summer breeding is a general skink pattern only and has not been confirmed for the Ornate Soil-crevice Skink.
  • Recorded survey detections: The species was recorded during surveys in April, April to May, September and November, but these records do not define seasonal abundance.
  • Highest clearing risk: Use heightened precautions from September to February, when warm season activity and possible breeding could increase the chance of harming adults, eggs or dependent young, while treating occupied shelter habitat as a risk year round.

Identification: Appearance

The Ornate Soil-crevice Skink is a small, ground-dwelling skink with a distinctive striped appearance. It is not well covered by field descriptions, so photographs and confirmation by an experienced herpetologist are useful where identification affects clearing decisions.

Look for big eyes, a coppery brown body and a black stripe along the side. Some individuals have dots on the back.

Identification: Size, calls and similar species

A dependable body size is not established in the available field information. No call, echolocation or species-specific similar-species description is recorded.

Treat small brown skinks as potential Ornate Soil-crevice Skinks until they are checked, especially where the animal has a strong dark side-stripe and is found in ground cover or soil crevices.

Identification: Field signs

Direct sightings are the most useful field sign. No distinctive droppings, nests, stains, odour or calls are described for this species.

  • Search around fallen timber, loose bark, decorticating bark, deep leaf litter, surface rocks and visible soil cracks.
  • Record a clear photograph of the head, side stripe, back pattern and habitat where safe to do so.
  • Avoid turning heavy material back onto an animal. Replace light cover carefully after inspection.

Identification: Handling and confirmation

Use an appropriately qualified fauna spotter catcher during clearing. Keep handling to the minimum needed for identification, safety and relocation under the approved clearing procedure.

  • Record the date, location, habitat feature, photograph and action taken.
  • Seek expert confirmation where the animal cannot be separated confidently from another small skink.

Distribution: Australian range

The species is mapped in the Northern Territory, Queensland, South Australia and Western Australia. Available project records show that it can occur in inland and dryland landscapes, but they do not define a complete site scale range.

The Ornate Soil-crevice Skink occurs in the Northern Territory, Queensland, South Australia and Western Australia. Queensland records include the Mitchell Grass Downs and Mareeba local government area, and project surveys have recorded the species in central Queensland sites.

  • Northern Territory records include desert sandplain and desert dune field land systems within the relevant atlas search area.
  • The available records do not establish a continuous distribution or reliable regional limits within each state.
  • No overseas range is identified.

Distribution: Interpreting records

A database record confirms occurrence at or near the record location, but a lack of records does not demonstrate absence. Some area reports include records from up to 1 km outside the reporting area, and location precision can be as broad as 10,000 m.

  • Check current state wildlife databases and project survey records before clearing.
  • Use suitable habitat, recent records and the results of targeted searches together when assessing risk.

Distribution: Works site planning

Assume the species may be present in suitable ground habitat where the mapped range overlaps a project area. Plan pre-clearance checks before machinery enters areas containing logs, bark, litter, rocks or cracked soil.

  • Mark habitat to be retained before clearing starts.
  • Include the species in the fauna spotter catcher's pre-clearance briefing.
  • Record positive and negative search results with the survey conditions and effort.

Habitat: Vegetation and landscape

Species-specific habitat information is limited, but project surveys recorded the skink in landscapes containing woodland and grassland. The most useful site indicators are intact ground cover and small refuges close to the soil surface.

Inspect woodlands and grasslands, particularly where native ground cover has been retained. The species has also been considered in dry desert land systems, including sandplains and dune fields.

  • Native grass cover and litter layers.
  • Open woodland with fallen timber and loose bark.
  • Dry sandy or cracking soils and low-relief ground with scattered cover.
  • Areas with a mix of exposed soil and nearby refuge features.

Habitat: Microhabitat features

Look closely at the junction between vegetation, litter and bare ground. Soil cracks, surface rocks, fallen timber, bark crevices and decorticating bark are useful search features for the reptile assemblage and should be treated as potential skink habitat.

  • Logs and branches lying on or slightly above the ground.
  • Loose slabs of bark and shedding bark on trees or on the ground.
  • Deep leaf litter, especially beside timber and shrubs.
  • Surface rocks and naturally formed soil crevices.

Habitat: Habitat condition

The species can be overlooked in disturbed landscapes because it is small and ground dwelling. Retain connected patches of ground cover where practicable, rather than leaving isolated refuge piles surrounded by bare or compacted soil.

  • Avoid unnecessary removal of logs, bark and rocks.
  • Keep vehicle movements to approved tracks and work areas.
  • Limit soil disturbance and maintain links between retained habitat patches.

Foraging habitat: Likely feeding areas

The diet and detailed foraging habitat of the Ornate Soil-crevice Skink are poorly documented. As a practical field assumption, search areas where leaf litter, bark, rocks and surface soil provide both prey and cover for a small terrestrial skink.

Search along the edges of litter, logs, bark and rocks, where small invertebrates are likely to occur. Warm, sheltered ground with nearby retreat sites may be used during suitable weather.

  • Leaf litter beneath or beside woodland vegetation.
  • Edges of logs, bark sheets and surface rocks.
  • Native grass bases and lightly open ground with cracks.
  • Moist or sheltered pockets after rain, while avoiding unsupported assumptions about seasonal use.

Foraging habitat: Survey approach

Use slow diurnal habitat searches and inspect likely cover carefully. Project surveys detected the species through funnel traps, pitfall traps and active searches, including searches beneath logs, bark, deep leaf litter and surface rocks.

  • Search before clearing and again immediately ahead of progressive clearing where risk remains.
  • Lift small cover objects from the safe edge and replace them in their original position.
  • Use traps only under an approved vertebrate fauna survey plan, with appropriate checking and animal welfare controls.

Foraging habitat: Site management

Retain natural foraging cover wherever practicable. Salvage selected logs and other habitat resources only under the clearing management plan, and place them in suitable retained habitat rather than creating isolated piles in active work areas.

  • Minimise dust, compaction and unnecessary removal of ground cover.
  • Control weeds and pests that reduce native ground habitat.
  • Progressively rehabilitate disturbed areas and reduce the time that soil remains bare.

Breeding habitat: What to look for

Breeding places and breeding timing are not established in the available field information. Until better local information is available, manage intact ground cover and soil refuges as potential breeding habitat.

Do not expect a conspicuous nest or colony. Inspect soil cracks, spaces beneath bark, litter pockets and other protected ground features for small skinks, eggs or recently hatched young, while avoiding unnecessary disturbance.

  • Cracked or friable soil with stable cover nearby.
  • Undisturbed litter beneath shrubs or grass tussocks.
  • Sheltered spaces beneath logs, bark and rocks.
  • Connected habitat that allows adults and young to move between refuges.

Breeding habitat: Breeding timing

No reliable breeding months or regional breeding period are established. Avoid imposing a fixed seasonal clearance window without a project-specific assessment and advice from the relevant authority.

  • Schedule pre-clearance checks when animals are likely to be detectable under local weather conditions.
  • Repeat checks if clearing is delayed or site conditions change.
  • Treat records of juveniles, gravid females or eggs as a trigger for ecological review.

Breeding habitat: Clearing controls

Use progressive clearing, a fauna spotter catcher and a clear procedure for animals found before or during works. Stop or adjust work if a suspected breeding place is encountered until the site is assessed under the applicable approval.

  • Delineate approved clearing areas before work begins.
  • Retain habitat outside the approved footprint.
  • Document any breeding evidence, the location, habitat feature and management response.

Sheltering habitat: Shelter features

The Ornate Soil-crevice Skink is a soil and ground-cover species, so shelter is likely to be close to the surface. Retaining small refuge features can reduce direct harm during clearing and construction.

Potential shelter includes soil cracks, spaces beneath surface rocks, fallen timber, loose bark, decorticating bark and deep leaf litter. These features may be used for refuge from heat, predators and site disturbance.

  • Leave stable logs, bark and rocks in place where they are outside the approved footprint.
  • Maintain litter and native grass bases where practicable.
  • Avoid sealing or compacting natural soil cracks unnecessarily.

Sheltering habitat: Search and capture

Search likely refuges before machinery starts. A spotter catcher should manage animals encountered during clearing in accordance with the approved fauna handling and relocation procedure.

  • Inspect cover systematically rather than moving large quantities of material at once.
  • Keep captured animals shaded and secure for the shortest practical time.
  • Relocate only to suitable nearby habitat approved under the project procedure.

Sheltering habitat: Construction and rehabilitation

Keep work areas, stockpiles and vehicle routes away from retained refuge habitat where practicable. Progressive rehabilitation should restore ground cover and reconnect retained patches.

  • Use existing tracks where practicable.
  • Keep temporary disturbance to the minimum required.
  • Control erosion and sediment so soil cracks and ground refuges are not buried or washed out.
  • Use site speed limits and safe-driving procedures to reduce vehicle strike risk.

Threats: Vegetation clearing and habitat loss

The main works site risks are habitat loss, removal of ground refuges and injury during clearing. General land management pressures can also reduce habitat quality and make animals harder to detect or relocate safely.

Clearing can remove woodland, grassland and the logs, bark, litter and rocks used by ground-dwelling reptiles. Fragmentation can leave small habitat patches exposed to heat, predators and further disturbance.

  • Stage clearing progressively.
  • Delineate the approved disturbance footprint.
  • Retain connected native vegetation and ground cover wherever practicable.
  • Salvage suitable habitat resources under the clearing management plan.

Threats: Ground disturbance

Vehicles, grading, trenching, stockpiling and earthworks can crush animals and destroy soil cracks and surface refuges. Erosion and sedimentation can bury or destabilise remaining habitat.

  • Use existing tracks where practicable.
  • Limit soil disturbance and avoid unnecessary compaction.
  • Install and maintain erosion and sediment controls.
  • Keep stockpiles and laydown areas out of retained habitat.

Threats: Operational impacts

Vehicle strike, dust, noise, vibration, artificial light, weeds, pests, hydrological change and bushfire can affect reptile habitat and movement. Grazing and other disturbance may further reduce ground cover.

  • Apply project speed limits and safe-driving procedures.
  • Manage weeds and pest animals.
  • Minimise dust and unnecessary night lighting near retained habitat.
  • Maintain drainage and fire controls that protect retained ground habitat.

Threats: Protection and compliance

The species is listed as Rare in South Australia and Priority 4 in Western Australia. Queensland and Northern Territory records identify it as Least Concern, but animals and their habitat still need to be managed under the applicable wildlife, clearing and project approval requirements.

South Australia: Rare under the National Parks and Wildlife Act 1972, treated as the near threatened equivalent for this profile.

Western Australia: Priority 4, a non-statutory DBCA category for rare and near threatened species that need monitoring.

Queensland and Northern Territory: Records cited for these jurisdictions identify the species as Least Concern.

  • Confirm the current listing and permit requirements in each state before work starts.
  • Use a fauna spotter catcher for pre-clearance and active clearing where required.
  • Keep records of searches, captures, relocations, injuries, mortality and retained habitat.
  • Escalate any concentration of animals, suspected breeding place or unexpected mortality to the project ecologist and relevant authority.

Survey methodology: 1. Desktop assessment

The Ornate Soil-crevice Skink is a small, ground-dwelling skink that can be difficult to detect. Use a combination of active searches and trapping, with effort focused on loose bark, logs, leaf litter, surface rocks and soil cracks.

Check current records, land-system mapping, habitat condition and previous survey reports before finalising the survey design. Treat a lack of records as insufficient evidence that the species is absent.

Confirm the regulatory status for the work area. The species is Least Concern in Queensland and the Northern Territory. It is listed as Rare in South Australia and Priority 4 in Western Australia, where the listing requires a more precautionary survey and management response. No Commonwealth listing is identified here.

  • Map retained woodland, grassland, open ground, fallen timber, decorticating bark, leaf litter, rocks and soil cracks.
  • Review WildNet, state fauna databases, local government records and project survey records.
  • Give additional attention to areas within the South Australian Rare or Western Australian Priority 4 range.
  • Document the search area, date of database checks, mapped habitat, previous records and data limitations.

Survey methodology: 2. Active searches

Search suitable microhabitats during daylight and, where practical, in the warmer part of the day when skinks are more likely to be active. Search effort should cover both intact habitat and disturbed areas that retain shelter.

Active searches used for this species have included logs, bark, deep leaf litter, surface rocks and shedding bark. Move habitat carefully and replace it immediately after inspection.

  • Search systematically through representative habitat units rather than concentrating only on the easiest ground to access.
  • Inspect the edges and undersides of loose bark, logs and rocks, and check soil cracks without damaging them.
  • Use repeated searches where conditions are cool, wet, windy or unusually dry, as detectability may be reduced.
  • Coordinate searches with trapping so that weather and habitat information can be compared.

Survey methodology: 3. Trapping and seasonal coverage

The species has been recorded in funnel traps, pitfall traps and during active searches. Project records include surveys in September, November and April to May, but there is no established species-specific minimum effort or breeding-season window.

Use more than one survey period where the project has a large footprint, substantial clearing risk or a South Australian Rare or Western Australian Priority 4 listing.

  • Use pitfall and funnel arrays, with drift fencing, only where they can be installed and operated safely and lawfully.
  • Check traps at the frequency required by the approved fauna survey method and weather conditions, and close or shade traps during unsafe heat, flooding or other hazardous conditions.
  • Keep trap sites clear of hazards, provide suitable shelter and moisture management, and release animals promptly at the point of capture unless an authorised relocation is required.
  • Record the number and type of traps, trap nights, active-search hours, personnel, weather, temperature, rainfall, habitat searched and any trap closures.

Survey methodology: 4. Identification and records

Field identification should be confirmed by an experienced herpetologist where possible. Useful field characters include big eyes, coppery brown colour, a black side-stripe and, in some individuals, dots on the back.

Record observations even when identification remains at genus level, and retain photographs where this can be done without handling the animal.

  • Record date, time, GPS location, habitat, microhabitat, behaviour, survey method and identification confidence.
  • Photograph the animal in place when practicable. Include a scale only if it can be done without restraint or delay.
  • Submit confirmed records to the relevant state database and project fauna register.
  • Record negative survey results with the same detail as positive records.

Before habitat disturbance: 1. Approvals and regulatory checks

Plan clearing around habitat retention and fauna welfare, not only around the clearing boundary. The species has no documented migration period or breeding season that can be used to set a universal timing rule, so use site evidence and a precautionary approach.

Confirm the approvals that apply before ground disturbance begins. The absence of a Commonwealth listing does not remove the need to check whether the project could affect a protected matter or trigger an EPBC Act referral.

Queensland records classify the species as Least Concern. A Queensland species management program may still be required where an activity tampers with a breeding place of a near threatened animal, or where another protected wildlife requirement applies. Confirm this with the Queensland department before works.

In South Australia, confirm the requirements associated with the Rare listing. In Western Australia, treat Priority 4 records as a trigger for targeted survey, avoidance and monitoring, even though Priority 4 is a departmental category rather than a statutory threatened species listing.

  • Check EPBC Act referral requirements before finalising the footprint.
  • Check state fauna, clearing, wildlife handling and relocation permits.
  • Confirm whether a Queensland species management program, authority or other wildlife approval is required.
  • Keep approvals, conditions, maps and contact details at the work front.

Before habitat disturbance: 2. Avoidance and site layout

Retain areas with connected ground cover and shelter wherever practicable. Avoid unnecessary removal of fallen timber, loose bark, leaf litter, surface rocks and other microhabitat.

No species-specific buffer distance has been established. Set buffers around confirmed animals, breeding places or high-quality shelter habitat using the project ecologist and approval conditions.

  • Mark the approved clearing footprint with survey pegs or flagging before machinery enters.
  • Use existing tracks and previously disturbed areas where practicable.
  • Retain habitat patches that contain logs, bark, leaf litter, rocks and soil cracks.
  • Keep stockpiles, laydown areas, lighting and vehicle routes outside retained habitat.

Before habitat disturbance: 3. Pre-clearance survey

Complete a pre-clearance survey shortly before works, using active searches and targeted inspection of microhabitat within the approved footprint. The fauna spotter catcher should review the survey results before clearing starts.

If conditions are poor or the area contains extensive shelter habitat, delay works or increase survey effort until detection is more reliable.

  • Search logs, bark, deep leaf litter, rocks, shedding bark and soil cracks.
  • Inspect habitat that will be removed, pushed, crushed or buried, not only vegetation that will be felled.
  • Mark animals, breeding places and retained refuge areas on the clearing plan.
  • Define a stop-work process and emergency contacts before the crew is mobilised.

Before habitat disturbance: 4. Timing and exclusion controls

Breeding timing is not sufficiently established for this species, and no migration period is documented. Do not assume that a particular month is low risk.

Use seasonal timing as a risk reduction measure only after considering local records, weather, survey results and the advice of the project ecologist.

  • Avoid clearing during periods of very hot, wet or unsafe conditions for animals and workers.
  • Use temporary exclusion fencing only where it will not trap animals inside the work area or block access to retained habitat.
  • Inspect exclusion fencing regularly and remove it when it is no longer needed.
  • Do not disturb a suspected breeding place until the required approval, management measure and fauna specialist advice are in place.

Before habitat disturbance: 5. Crew induction

Give all workers a short induction before clearing. The induction should cover the skink's appearance, likely shelter sites and the authority of the spotter catcher to stop work.

Make the procedure simple enough to follow around machinery, stockpiles and access tracks.

  • Show photographs and describe the coppery brown colour, black side-stripe, big eyes and occasional back dots.
  • Instruct workers not to handle, chase, collect or relocate animals.
  • Require immediate notification of any skink, suspected breeding place or injured fauna.
  • Display the spotter catcher's name, stop-work authority and escalation contacts at the work front.

During habitat disturbance: 1. Sequential clearing

Clear progressively and give animals time to move into retained habitat. A fauna spotter catcher must control fauna handling and can stop work whenever an animal, breeding place or unsafe clearing situation is identified.

Clear in small, manageable stages towards retained habitat, where the site layout allows. This gives mobile animals a chance to leave and makes searching and rescue more effective.

Keep the approved clearing boundary visible throughout the work.

  • Start with low-impact preparation and remove unnecessary obstacles before heavier machinery arrives.
  • Clear from the disturbed side towards retained habitat, avoiding entrapment between machinery, stockpiles and exclusion fencing.
  • Inspect felled or moved material before it is chipped, buried, burnt or removed.
  • Stop work if the approved footprint changes or unmarked habitat is encountered.

During habitat disturbance: 2. Handling and relocation

Only an appropriately authorised fauna handler should capture or relocate an Ornate Soil-crevice Skink. Avoid handling unless the animal is at direct risk or an approval requires relocation.

Use gentle methods that minimise restraint, heat exposure and time in captivity. Release animals into suitable nearby habitat approved by the project ecologist.

  • Keep machinery and workers clear while the handler assesses the animal.
  • Do not pass the animal between workers or place it in an unlabelled container.
  • Record the capture location, release location, time, habitat, handler and condition.
  • Do not relocate animals across roads, into isolated habitat or outside the approved relocation area.

During habitat disturbance: 3. Breeding places and occupied shelter

If an active breeding place, eggs, young or a repeatedly occupied shelter is found, stop work in the immediate area. The species has no documented nest or breeding-place type that supports a standard exclusion distance.

Obtain advice from the project ecologist and comply with the relevant approval before disturbing the site.

  • Mark and protect the location from machinery, foot traffic, vibration and material storage.
  • Do not open, excavate, flood, fill or seal a suspected breeding place without approval.
  • Document the location, evidence, photographs, habitat and actions taken.
  • Resume work only after the fauna specialist and approval holder confirm the controls.

During habitat disturbance: 4. Injured or dead animals

Treat injured animals as wildlife incidents. Keep the area quiet and prevent further contact while the authorised handler arranges assessment.

Do not provide food, water or medication unless directed by a qualified wildlife carer or veterinarian.

  • Move machinery away from the animal and establish a safe working space.
  • Place the animal in a secure, ventilated container only if directed and authorised.
  • Contact the nominated wildlife carer, veterinarian or fauna authority through the project procedure.
  • Record the injury, likely cause, location, photographs, handler, treatment and outcome.

During habitat disturbance: 5. Daily records and stop-work events

Maintain a daily fauna register. Good records support compliance, improve later surveys and show whether avoidance measures are working.

The spotter catcher should have authority to stop work without waiting for approval from the machine operator.

  • Record all animals seen, captured, relocated, injured or found dead.
  • Record clearing dates, footprint, habitat removed, retained habitat, weather, personnel and machinery used.
  • Record all stop-work events, breeding-place findings, permit decisions and corrective actions.
  • Report unexpected concentrations of skinks or repeated captures to the project ecologist before the next clearing stage.

After habitat disturbance: 1. Post-clearance checks

Finish each clearing stage with a fauna check and a record review. Use the results to adjust the next stage, particularly where animals were found or the project is within the South Australian Rare or Western Australian Priority 4 range.

Inspect the completed area after machinery has left and before it is handed over for construction. Check edges, remaining logs, soil cracks, debris piles, drainage lines and any retained shelter.

Remove hazards that could trap animals, such as open pits, pipes, uncovered tanks and unsecured construction materials.

  • Confirm that clearing stayed within the approved boundary.
  • Search the edge of retained habitat for stranded, injured or trapped animals.
  • Check temporary exclusion fencing and access points.
  • Record any animal found after clearing as a post-clearance observation or incident.

After habitat disturbance: 2. Relocated animals

Review relocation records to confirm that animals were released into suitable habitat and that containers and equipment were cleaned and removed. Do not repeatedly move animals if they return to the work area without reviewing the site controls.

Where relocation is required by an approval, complete all specified follow-up checks and reporting.

  • Verify release coordinates and habitat descriptions.
  • Check for animals trapped by fencing, trenches, drains or construction materials.
  • Report mortality or failed relocation promptly through the project fauna procedure.
  • Use relocation outcomes to refine the next clearing stage.

After habitat disturbance: 3. Reporting and compliance

Prepare a fauna report for each clearing stage and a consolidated report at project milestones. Include both detections and non-detections, with enough detail to demonstrate the survey effort and decisions made.

Escalate any breach of an approval, unexpected habitat loss, injury, death or breeding-place disturbance.

  • Report records to the relevant state database where required.
  • Attach maps, photographs, trap and search data, handling records and stop-work logs.
  • Compare actual clearing with the approved footprint and mitigation measures.
  • Notify the regulator, approval holder and project ecologist within the required timeframe for reportable incidents.

After habitat disturbance: 4. Monitoring and review

Monitoring should match the risk of the work. Use more formal follow-up where the species is listed as Rare in South Australia, Priority 4 in Western Australia, or where clearing has removed substantial shelter habitat.

There is no universal species-specific monitoring period. Set the duration and methods from the approval conditions, habitat retained, detection results and incident history.

  • Inspect retained habitat edges after major clearing stages and after heavy rain or flooding.
  • Repeat active searches or trapping where monitoring is required and use consistent methods for comparison.
  • Review records for changes in detection, shelter habitat condition, weed cover, fire effects and vehicle risk.
  • Hold a post-stage review with the spotter catcher, site supervisor and ecologist before further clearing.

Rehabilitation actions: 1. Habitat restoration

Rehabilitation should restore the ground structure used by this skink, not only replace canopy cover. Aim to reconnect retained habitat and replace natural shelter wherever it has been removed.

Reinstate a mixture of native ground cover, leaf litter, fallen timber, bark, surface rocks and suitable soil structure. Retain natural soil cracks and avoid unnecessary grading or compaction.

Use local native materials where practicable and place habitat features so they connect with retained vegetation and other shelter.

  • Spread salvaged logs, bark, rocks and suitable coarse woody material in rehabilitation areas.
  • Replace topsoil and leaf litter in a way that retains natural microrelief and shelter.
  • Limit vehicle access and soil disturbance during establishment.
  • Avoid removing rehabilitated shelter during follow-up maintenance.

Rehabilitation actions: 2. Replacement shelter and breeding structures

Natural shelter is more relevant to this ground-dwelling skink than nest boxes or bat boxes. There is no established requirement for artificial nest sites, roost structures or species-specific replacement breeding structures.

Use artificial structures only where a qualified herpetologist identifies a clear local need and the design, placement and maintenance are approved.

  • Prioritise retained and reconstructed logs, bark, rocks, leaf litter and soil refuges.
  • Do not install bird nest boxes, bat boxes or roost structures as a substitute for ground habitat.
  • If an artificial refuge trial is approved, record its design, location, condition, occupancy and maintenance.
  • Remove failed or hazardous structures rather than leaving traps in the landscape.

Rehabilitation actions: 3. Weeds, fire and pests

Manage weeds and feral animals so that ground cover and shelter can develop. Avoid maintenance methods that remove all leaf litter, logs or low shelter.

Fire planning should consider the effect of repeated hot burns on ground refuges and retained habitat.

  • Control weeds before they dominate the ground layer or increase continuous fuel loads.
  • Use targeted weed treatment that avoids direct contact with occupied shelter and follows chemical label requirements.
  • Inspect rehabilitation for erosion, sediment movement, pest activity and loss of ground cover.
  • Coordinate fire planning with the land manager and protect retained shelter where practicable.

Rehabilitation actions: 4. Water, drainage and lighting

Maintain natural drainage and prevent rehabilitation areas from becoming persistently waterlogged or eroded. The species' water requirements are not established, so do not create artificial water points unless they have a broader ecological purpose and are assessed for pest and disease risks.

Reduce artificial lighting near retained and rehabilitated habitat.

  • Prevent sediment from entering soil cracks, leaf litter and retained ground habitat.
  • Avoid directing bright lights onto habitat edges, access routes through retained vegetation or rehabilitation areas.
  • Use shielded, low-spill lighting where lighting is required for safety.
  • Inspect drains, pits, pipes and tanks for fauna entrapment during construction and maintenance.

Rehabilitation actions: 5. Long-term monitoring

Monitor whether shelter and ground cover are returning, not just whether plants have survived. Use the same active-search and trapping methods across monitoring events where approvals require fauna data.

Set monitoring triggers around habitat failure, repeated fauna incidents, weed spread, erosion and declining detections.

  • Record habitat condition, shelter features, ground cover, weeds, fire history and fauna detections.
  • Compare monitoring results with pre-clearance records and retained habitat condition.
  • Repair erosion, replace lost shelter and adjust weed or access controls when targets are not met.
  • In South Australia and Western Australia, align monitoring and reporting with the requirements attached to the Rare or Priority 4 status and any project approval.

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