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Golden-tailed Gecko (Strophurus taenicauda)

The golden-tailed gecko is a small, mostly arboreal and nocturnal gecko of eastern Australia. It can use isolated trees, roadside vegetation and small remnants, so it may be encountered during clearing even in modified landscapes. It is Near Threatened in Queensland, where it is protected wildlife and disturbance to a breeding place requires a species management program.

Conservation status

Queensland, Nature Conservation Act 1992: Near threatened.

Breeding season

The golden-tailed gecko breeds in spring and summer, with females laying eggs during this period. Timing may vary between regions and years, and detailed species-specific seasonal information remains limited.

Breeding mode: Egg-laying. The golden-tailed gecko is oviparous.

Clutch size: Two eggs per clutch.

Breeding frequency: Females may lay more than one clutch in a season.

Breeding sites: Not recorded. Daytime shelter includes loose bark and tree hollows, which should be retained during works.

Incubation period: Not recorded.

Age at maturity: Not recorded.

Young: Hatching timing, dependence and dispersal of young are not recorded.

Seasonal activity can shift with local temperature, rainfall, latitude and shelter conditions, so site observations should guide daily work decisions.

  • Breeding, mating and laying: Breeding is recorded in spring and summer, with females laying two eggs and sometimes producing more than one clutch.
  • Eggs and young: Eggs and newly hatched young may be present during the spring and summer breeding period, but hatching and dependence periods are not recorded.
  • Nocturnal activity: Adults are mostly active at night, with activity generally expected to increase during warmer weather.
  • Reduced winter and dry season activity: Queensland reptiles generally reduce activity during winter or the dry season, although individuals can emerge on warm days.
  • Highest clearing risk: Clearing is most likely to harm eggs, hatchlings and breeding adults from spring through summer, so retain trees, bark, hollows, ground cover and shrub cover throughout this period.

Identification: Appearance and size

The golden-tailed gecko is a small, strikingly patterned gecko that is most often detected at night. It is mainly arboreal, but may also occur on the ground among leaf litter and debris.

The species is about 70 mm in snout to vent length. It lacks spines and tubercles on the body and tail.

Bright tail striping is a useful field feature. Body pattern and eye colour vary between the recognised subspecies.

Typical position: Tree trunks and outer branches, especially during night searches.

Defensive behaviour: Like other Strophurus geckos, it can direct a sticky, irritating secretion from glands in the tail.

  • Southern golden-tailed gecko, Strophurus taenicauda taenicauda, has a red to orange eye, large dorsal spots and one tail stripe.
  • Northern golden-tailed gecko, Strophurus taenicauda albiocularis, has a pale eye, smaller dorsal spots and one straight edged tail stripe.
  • Central golden-tailed gecko, Strophurus taenicauda triaureus, has an amber eye, small dorsal spots and three tail stripes.

Identification: Night detection

Use a head torch during night searches and look for the characteristic eyeshine. When an animal is high in a tree, binoculars can help confirm its shape and markings.

Eyeshine alone should not be used for species identification. Confirm the animal from its body pattern, tail striping and other visible features where possible.

  • Search trunks, outer branches, shrubs, fence posts and ground debris.
  • Move quietly and scan vegetation systematically before approaching or disturbing it.

Identification: Similar species

The golden-tailed gecko can occur with other arboreal geckos, particularly the dubious dtella, Gehyra dubia. The dubious dtella is more widespread and uses a broader range of habitats.

Amalosia jacovae, Amalosia rhombifer, Gehyra catenata and Gehyra dubia can be encountered in the same general region. They can generally be separated from the golden-tailed gecko without capture, provided the animal is viewed clearly.

  • Do not capture an animal solely because eyeshine is present.
  • Photograph the animal in place where safe and permitted, including the back, tail and head.

Identification: Field signs

No distinctive nest, dropping, stain or odour field sign is available for routine site searches. Direct night detection is the preferred method.

A tail held over the back, followed by release of a sticky secretion, may be seen if the animal is handled or threatened. Avoid provoking this behaviour.

Distribution: Australian range

The golden-tailed gecko is centred on the Brigalow Belt of Queensland and extends into northern New South Wales. Its distribution is fragmented across eastern Australia, but the species can persist in small remnants and modified areas where suitable trees and cover remain.

The species occurs in Queensland and northern New South Wales, mainly in the Brigalow Belt North and Brigalow Belt South bioregions. Records extend from the western slopes of the Great Dividing Range to the Carnarvon area, and from around Emerald south to Inglewood and Millmerran.

The nominate southern subspecies occurs in southern Queensland and has also been recorded in the Pilliga Scrub region of northern New South Wales. The northern subspecies occurs across the northern half of Brigalow Belt South and the southern half of Brigalow Belt North. The central subspecies has a limited range in the north eastern part of Brigalow Belt South.

  • Southern study areas include the country between Chinchilla and Miles.
  • Central records occur north of Roma and west of Taroom.
  • Northern records occur east and south east of Blackwater, extending east to Duaringa.

Distribution: Mapping and project checks

The species is mapped in the Northern Territory and Queensland for this profile. Before works begin, check the current state, territory and local mapping layers, together with recent records and the relevant approval conditions.

Queensland records show that the species can occur throughout broad project landscapes, including around the Surat region and near Barakula. A lack of a local record does not demonstrate that suitable habitat is unoccupied.

  • Treat suitable cypress, brigalow, belah, bull oak and ironbark vegetation as potential habitat.
  • Include regrowth, roadside strips, isolated trees and small urban or agricultural remnants in the habitat check.

Distribution: Subspecies and local context

The central subspecies has a limited range and was not covered by the Surat surveys described in the field studies. Confirm which subspecies or population applies to the work area before relying on regional survey information.

No overseas range is recognised for the species.

Habitat: Vegetation types

Look for the golden-tailed gecko wherever suitable trees, bark and ground cover remain, including in narrow or isolated remnants. Tree structure and grazing condition are often more useful indicators than patch size alone.

The species is associated with dry open forests and woodlands. Common habitat trees include brigalow, Acacia harpophylla, belah, Casuarina cristata, bull oak, Allocasuarina luehmannii, narrow leaved ironbark, Eucalyptus crebra, and white cypress, Callitris glaucophylla.

Northern and central populations are predominantly associated with Eucalyptus woodlands. Southern populations commonly occur in brigalow, belah, bull oak, ironbark and white cypress vegetation.

  • Inspect remnant woodland and open forest.
  • Inspect cypress dominated regrowth and mature stands.
  • Retain shrub layers, especially Acacia and Callitris.

Habitat: Remnants and modified sites

The species has been recorded in continuous vegetation, small remnants, roadside strips, isolated trees in parkland, cemetery trees and regrowth. The smallest recorded patch in the field study was 1.11 hectares.

Detection was reported in 40 per cent of small sites, 56 per cent of medium sites and 78 per cent of large sites. These results support surveying small patches rather than excluding them because of their size.

  • Check vegetation around access tracks, construction footprints and easements.
  • Include isolated mature trees and linear connections between larger remnants.
  • Retain links to substantial habitat patches where practicable.

Habitat: Habitat condition

Higher tree basal area is associated with greater likelihood of occurrence. In small patches, white cypress basal area and low or absent grazing were associated with presence and higher abundance.

Useful habitat features include large live eucalypts, unthinned or unlogged cypress, small live trees, dead trees, litter and a well developed shrub layer.

  • Record tree species, canopy cover, tree basal area where required, hollows, peeling bark, dead trees, litter and grazing pressure.
  • Map areas with abundant cypress and dense shrub cover as higher quality habitat.

Foraging habitat: Foraging places

The golden-tailed gecko feeds on insects and other invertebrates. Its mostly nocturnal foraging occurs in trees and shrubs, although individuals may also move through leaf litter and ground debris.

Search the trunks, branches and foliage of brigalow, cypress, ironbark, belah, bull oak and other mature woodland trees. Bark crevices and dense shrubs may provide both hunting surfaces and access to prey.

The species may also be encountered on the ground between trees, particularly among leaf litter, fallen timber and other debris.

  • Inspect outer branches and trunks with a head torch.
  • Include shrub layers and ground cover in night searches.
  • Check isolated trees, roadside vegetation and regrowth, not just intact forest.

Foraging habitat: Night survey approach

Night spotlighting is suitable because the species is active at night and can be located by eyeshine. Search effort should cover representative habitat condition, including both high quality remnants and modified habitat with retained trees.

Record the search date, start and finish times, weather, observers, area searched, tree structure and animal position. These details help interpret a non detection.

  • Use quiet, systematic searches rather than relying on a single pass.
  • Use binoculars to check animals high in the canopy.
  • Confirm identification from visible markings rather than eyeshine alone.

Foraging habitat: Lighting and disturbance

Artificial lighting can change insect activity and may alter reptile foraging behaviour. Keep unnecessary work lighting away from retained habitat, shrub layers and vegetation connections.

Avoid directing bright lights into retained trees during night works unless required for safety or animal rescue.

Breeding habitat: Breeding period and eggs

Breeding information for the golden-tailed gecko is limited, but females lay eggs in spring or summer. Any tree, bark or ground feature that could support eggs or sheltering adults should be treated carefully during clearing.

Females lay a clutch of two eggs in spring or summer. More than one clutch may be produced in a season.

The precise location of egg laying and the incubation period are not established well enough to use as routine field screening criteria.

Clutch size: Two eggs.

Breeding season: Spring and summer.

  • Plan detailed pre clearing searches before spring and summer clearing where the program allows.
  • Do not assume that a tree without a visible hollow is unsuitable for breeding.

Breeding habitat: Breeding places on a site

Potential breeding and shelter features include tree hollows, loose or peeling bark, hollow limbs, ground cover and other protected spaces around standing trees. Retain these features wherever they occur in potential habitat.

Because breeding places are not readily identified from the ground, avoid unnecessary removal of mature trees, dead trees, hollow limbs and exfoliating bark.

  • Mark habitat trees and retained vegetation before clearing.
  • Have a fauna spotter catcher inspect trees and debris immediately before removal.
  • Stop and reassess if a gecko, eggs or a suspected breeding place is found.

Breeding habitat: Queensland compliance

In Queensland, the golden-tailed gecko is protected wildlife and is Near Threatened. Tampering with its breeding place requires a species management program.

Project managers should confirm approval, permit and species management requirements before clearing or disturbing potential breeding habitat.

Sheltering habitat: Tree shelters

Daytime shelter is likely to be in or on trees, with ground cover also contributing to available refuge. Retaining shelter features reduces the chance of injury during clearing and helps animals persist after construction.

The species shelters under loose bark and in tree hollows. Hollow limbs and peeling bark on standing trees may be particularly useful features.

Inspect mature live trees, dead trees, hollow limbs, trees with dead vents and trees with loose bark before removal.

  • Mark trees with hollows or peeling bark for retention where possible.
  • Avoid pushing felled trees into retained vegetation until they have been checked.
  • Use a qualified fauna spotter catcher during tree clearing.

Sheltering habitat: Ground and shrub cover

Ground cover, leaf litter, fallen timber and debris can provide shelter when animals are on the ground. Dense Acacia and Callitris shrub layers are also associated with higher quality habitat.

Limit soil stripping, unnecessary slashing and removal of litter outside the approved disturbance footprint.

  • Keep machinery within marked work areas.
  • Retain ground cover and fallen timber in undisturbed habitat.
  • Control grazing and weeds without removing useful native refuge cover.

Sheltering habitat: Handling and release

If a gecko is found, keep it shaded and protected from traffic, machinery and excessive handling. Follow the project fauna management plan and the instructions of the authorised spotter catcher.

Do not translocate or release the animal away from the work area unless this is authorised and directed under the applicable management arrangements.

Threats: Clearing and construction injury

The main risks on development sites are loss of trees and shelter, degradation of the understorey, and injury during clearing. The species can tolerate fragmentation, but this tolerance is stronger where grazing is limited and cypress, shrubs, ground cover and tree features remain.

Vegetation removal, topsoil stripping, trenching, vehicle movements and material storage can kill or injure animals sheltering in trees, bark, litter and debris.

Use the smallest practical disturbance footprint. Complete pre clearing searches and fauna spotter catcher inspections before tree and ground disturbance.

  • Clearly mark no go areas and retained habitat.
  • Sequence clearing towards retained vegetation so animals have an opportunity to move away.
  • Keep rescued fauna out of active work areas and record all encounters.

Threats: Habitat loss and fragmentation

Removing mature trees, hollow limbs, dead trees, cypress stands and shrub layers reduces habitat quality. Small patches and isolated trees can still support the species, so they should not be dismissed as low value solely because they are fragmented.

Retain large intact remnants and vegetated connections to habitat north and south of a development site where practicable.

  • Avoid unnecessary widening of linear clearings.
  • Retain stepping stones of trees between larger patches.
  • Protect regrowth that has developed suitable tree and shrub structure.

Threats: Grazing, weeds and understorey loss

Grazing can reduce ground cover and affect presence and abundance, particularly in small patches. Weeds such as lantana and invasive pasture grasses such as buffel grass can alter refuge conditions and shade or replace native ground cover.

Manage weeds and grazing without removing native shelter features or opening additional areas of habitat.

  • Fence or otherwise protect retained habitat from excessive grazing.
  • Keep weed control targeted and avoid broad disturbance of litter, logs and shrubs.
  • Monitor retained cypress and shrub dominated areas after construction.

Threats: Roads, vehicles and artificial light

Individuals have been recorded crossing dual lane roads during warm summer nights. Vehicle movements, new roads and construction traffic can therefore cause direct mortality and may divide habitat.

Noise, vibration and artificial light may also disturb reptiles or alter prey activity. These effects are not well documented for this species, so use precautionary controls around retained habitat.

  • Apply low speed limits and fauna awareness controls in potential habitat.
  • Minimise night traffic through retained vegetation.
  • Direct lights away from trees, shrubs and habitat connections where safety allows.
  • Inspect roads and work areas for reptiles during warm night operations.

Survey methodology: 1. Desktop assessment

Golden-tailed Geckos are small, mostly arboreal and active at night. The most effective survey method is nocturnal spotlighting, with head torches used to detect eyeshine and binoculars used where animals are high in trees.

Map remnant vegetation, regrowth, isolated trees, roadside strips and linear connections before planning works.

Prioritise brigalow, belah, bull oak, ironbark and cypress communities. Give extra attention to areas with abundant cypress, shrubs, ground cover, standing trees, hollows and loose or peeling bark.

Treat advanced regrowth aged 10 years or more as potential habitat where the applicable mapping rules classify it as remnant vegetation.

Check recent records, local subspecies range, regional ecosystem mapping, grazing condition and nearby habitat connections. Small patches can support the species, including patches as small as 1.11 hectares.

Activity: Mostly nocturnal

Size: Approximately 70 mm snout to vent length

Breeding period: Spring and summer

Known movement: Migration has not been documented

  • Map trees that may be retained, removed or affected by access, trenching, laydown and machinery movement.
  • Identify nearby refuges and habitat connections that should remain undisturbed.
  • Confirm the current Queensland conservation status and all approval requirements before finalising the work method.

Survey methodology: 2. Nocturnal spotlighting

Search tree trunks, outer branches, shrubs and ground debris after dark. Scan slowly with a head torch and look for eyeshine, then confirm the animal using its shape, pattern and tail markings.

Use binoculars to inspect animals high in the canopy. Do not identify the species from eyeshine alone.

Search warm, still nights when reptiles are likely to be active. Spring and summer, or the warmer part of the wet season, are suitable periods. Avoid relying on a single visit after cold, windy or wet conditions.

Primary method: Active nocturnal searches and spotlighting

Detection aid: Head torch eyeshine detection

High canopy aid: Binoculars with a head torch

  • Walk all habitat types that may be affected, including isolated trees and narrow roadside remnants.
  • Search both retained and proposed clearing areas so that animals can be moved away from immediate hazards where authorised.
  • Use experienced observers who can distinguish the species from other arboreal geckos recorded in the region.

Survey methodology: 3. Survey effort and conditions

Scale effort to the listing, habitat quality, proposed impact and likelihood of detection. Near threatened status warrants a targeted survey wherever suitable habitat will be cleared or heavily disturbed.

Repeat searches when the first visit has poor conditions or when habitat is extensive, fragmented or difficult to inspect. Record the effort clearly so that a non-detection is not treated as proof that the species is absent.

Where construction may affect trees, inspect trunks, loose bark, hollows, shrubs and ground cover during the day as well as at night.

  • Record date, start and finish time, observers, weather, temperature if measured, wind, rain, moon conditions where relevant, search route and area covered.
  • Record the number of observers, torch type, binocular use and time spent searching each habitat type.
  • Record every animal, including location, height, substrate, behaviour, photograph and whether it was captured or moved.
  • Record other geckos that could be confused with the species, particularly arboreal dtellas and velvet geckos.

Survey methodology: 4. Identification and reporting

Confirm records from photographs or examination by a suitably experienced ecologist. The three recognised forms differ in eye colour, dorsal spot size and tail striping.

The southern form has a red to orange eye and one tail stripe. The northern form has a pale eye and one straight-edged tail stripe. The central form has an amber eye and three tail stripes.

Report locations accurately and retain photographs with the project fauna records.

  • Do not handle an animal solely to confirm a record if a clear photograph can establish its identity.
  • Record the relevant subspecies or regional form only where identification is reliable.
  • Submit significant records to the project database and the relevant Queensland biodiversity record system.

Before habitat disturbance: 1. Approvals and permits

Avoiding habitat is the preferred control. Before clearing, confirm the legal pathway, complete targeted searches and brief every person who may encounter a gecko, tree, bark refuge or breeding place.

Confirm the current listing before work starts. In Queensland, the Golden-tailed Gecko is near threatened under the Nature Conservation Act 1992 and is protected wildlife.

Obtain the approvals, permits and authority required for the project, including any Queensland wildlife handling or animal rehabilitation permissions. Only authorised and appropriately experienced people should capture, hold, move or rehabilitate fauna.

A species management program is required in Queensland where the activity tampers with the breeding place of protected near threatened wildlife. Obtain and follow the approved program before such work begins.

The species is not listed under the EPBC Act in the assessment information used for this profile. Check the current EPBC list and seek an EPBC referral if the species becomes listed or if another matter of national environmental significance may be affected.

Queensland status: Near threatened

Queensland legislation: Nature Conservation Act 1992

Breeding-place control: A species management program may be required where a breeding place is tampered with

EPBC status: Not listed in the assessment information used here, subject to current status checks

  • Have the environmental authority, development conditions, species management program and wildlife permits available at the work front.
  • Confirm whether state permits are needed for capture, temporary holding, relocation, rehabilitation or damage to protected wildlife habitat.
  • Do not assume that a near threatened listing removes the need for Queensland approvals.

Before habitat disturbance: 2. Avoidance and site layout

Retain large intact remnants, cypress-rich areas, shrub layers, standing trees, hollows, loose bark, ground cover and vegetated connections wherever practicable.

Keep clearing to the minimum needed for the approved footprint. Avoid isolated mature trees and narrow vegetation links where they provide the only remaining arboreal habitat.

Use site-specific no-go areas around retained habitat and any confirmed animal, refuge or breeding place. Set the boundary in the field with visible markers and explain it to operators. A universal species-specific buffer is not established for this gecko, so the ecologist should set buffers according to the animal, tree, machinery and task.

  • Fence and sign exclusion areas before machinery arrives.
  • Keep stockpiles, vehicle parking, lighting towers and access tracks outside retained habitat.
  • Protect retained trees from root damage, trunk impact, bark removal and unnecessary pruning.
  • Control grazing and prevent new disturbance in retained habitat.

Before habitat disturbance: 3. Pre-clearance inspection

Complete a final inspection shortly before clearing, including the canopy, trunks, loose bark, hollows, shrubs, ground cover and debris. Use nocturnal spotlighting where the habitat and risk assessment indicate that animals may be missed during daylight.

Inspect trees scheduled for removal from the ground before felling. A qualified spotter catcher should direct the inspection and determine whether a staged removal method is needed.

If an animal is found, stop work in the immediate area and apply the approved handling and relocation procedure.

  • Mark trees with hollows, loose bark or other likely shelter features for careful treatment.
  • Search isolated trees and regrowth as well as remnant patches.
  • Record animals, shelter features, breeding evidence and the location of each finding.
  • Reinspect areas where clearing has been delayed or where conditions have changed.

Before habitat disturbance: 4. Timing and crew induction

The species lays two eggs in a clutch during spring and summer, and females may lay more than one clutch in a season. Avoid disturbing suspected breeding places during this period where practicable, and obtain advice under the species management program where avoidance is not possible.

There is no documented migration period for this species. Plan around local activity conditions rather than a presumed migration window. Warm summer nights may increase movement, and animals have been recorded crossing dual-lane roads.

Give all workers a short fauna induction before clearing begins.

  • Explain the species appearance, nocturnal activity and likely tree and bark refuges.
  • Show the location of exclusion zones and the stop-work process.
  • Tell workers never to chase, collect, keep or relocate a gecko without direction from the authorised fauna officer.
  • Include instructions for reporting injured animals, eggs, hatchlings and any suspected breeding place.

During habitat disturbance: 1. Sequential clearing

Clearing should proceed in a controlled sequence, with the fauna spotter catcher able to stop work immediately. The aim is to give animals a safe opportunity to move, while preventing injury from machinery, falling vegetation and handling.

Clear from the edge of the approved footprint towards retained habitat, where the site layout allows animals to move into safe vegetation. Remove ground cover and smaller vegetation only after the area has been checked.

Use staged tree removal for trees with hollows, loose bark, dense foliage or a confirmed gecko. The spotter catcher should decide the sequence and exclusion zone for each tree.

Lower branches and trunks in a controlled manner rather than allowing them to fall through retained habitat or onto ground refuge features.

  • Stop machinery before each high-risk tree is cut or felled.
  • Inspect cut material, bark sheets, hollows, forks and the ground beneath each removed tree.
  • Keep people and machinery out of the fauna exclusion zone until the spotter catcher releases it.
  • Prevent unnecessary night lighting near retained habitat.

During habitat disturbance: 2. Spotter catcher authority and handling

Give the fauna spotter catcher clear authority to stop work, alter the clearing sequence and establish an immediate exclusion zone.

Only authorised and suitably trained people may capture, hold, examine, transport or release a Golden-tailed Gecko. Use the minimum handling needed to protect the animal and comply with the permit or species management program.

Do not use glue traps, adhesive materials, fumigants or unapproved exclusion devices.

  • Use clean, suitable equipment and keep handling time as short as practicable.
  • Keep the animal shaded, quiet and protected from heat, crushing and escape during temporary holding.
  • Release the animal only at an approved nearby habitat site selected by the fauna ecologist.
  • Record the reason for capture, time held, condition, release location and handler.

During habitat disturbance: 3. Breeding places and shelter features

If eggs, hatchlings, a guarding female, repeated use of a hollow or another suspected active breeding place is found, stop work in the immediate area.

Treat loose bark, tree hollows, dense shrubs and ground cover as potential shelter features. A confirmed or suspected breeding place must be managed under the approved Queensland species management program and any project approval conditions.

Do not remove, open, relocate or destroy the feature until the authorised fauna ecologist has assessed it and confirmed the lawful method.

  • Mark the location and establish a temporary exclusion zone.
  • Prevent vibration, machinery entry, excessive lighting and unnecessary handling near the site.
  • Contact the project ecologist and approval holder before work resumes.
  • Document the finding with photographs, location, tree or substrate details and actions taken.

During habitat disturbance: 4. Injured or dead animals

Treat an injured gecko as protected wildlife. Keep people, pets and machinery away and contact the authorised fauna spotter catcher or wildlife rehabilitator.

Do not offer food or water, apply treatment or release an injured animal without advice from an appropriately authorised person.

If an animal is dead, leave it in place until it has been photographed and examined, unless leaving it creates a safety risk.

  • Use a secure, ventilated container only when directed by the authorised handler.
  • Keep the container shaded and at a stable temperature during transfer.
  • Record the injury, likely cause, location, time, photographs, handler and destination.
  • Report any death or serious injury under the project approval, permit or species management program.

During habitat disturbance: 5. Daily field records

Maintain a daily fauna log for all searches, sightings, captures, relocations, injuries, deaths, stop-work events and breeding-place findings.

Link each record to the clearing area, tree number, work activity and permit or approval condition.

  • Record observer names, weather, work hours, clearing method and area cleared.
  • Map each animal and each exclusion zone with coordinates or a clear site reference.
  • Record when the spotter catcher released the area for work.
  • Keep photographs and copies of permits with the daily environmental records.

After habitat disturbance: 1. Post-clearance checks

After clearing, check the work area and retained habitat before removing fauna controls. Use the results to improve the remaining works and report all incidents through the project environmental system.

The spotter catcher should inspect the cleared footprint, felled trees, bark, hollows, branch piles and ground debris after each clearing stage. Check for live, injured or trapped animals before machinery moves into the area.

Recheck retained trees and adjoining habitat where clearing may have damaged branches, bark, roots or ground cover.

Keep exclusion fencing in place until the fauna officer confirms that the area is clear and safe for the next activity.

  • Search beneath felled material and around machinery before loading or removal.
  • Check trenches, pits, pipes and stored materials for trapped fauna at the frequency required by the project risk assessment and approval conditions.
  • Record all additional finds and the response taken.

After habitat disturbance: 2. Relocated animals

Inspect the approved release site after relocation to confirm that it remains suitable and free from immediate construction hazards. Do not repeatedly move an animal between sites.

Use release sites with suitable trees, bark, hollows, shrubs and ground cover, and with a safe connection to surrounding habitat where practicable.

The species is tolerant of some fragmentation, but relocation should not be used as a substitute for habitat retention or avoidance.

  • Release animals during suitable conditions selected by the fauna ecologist, normally when they can shelter safely and are not exposed to excessive heat or cold.
  • Record the release location, habitat condition, date, time, animal condition and person responsible.
  • Do not release an injured animal until a qualified rehabilitator or veterinarian has cleared it.

After habitat disturbance: 3. Monitoring and reporting

Report clearing completion, fauna interactions, breeding-place findings, injuries, deaths, permit breaches and corrective actions to the project manager and relevant regulator where required.

Where impacts are substantial or habitat is retained as an offset or management area, monitor the retained habitat and the species response using repeat nocturnal spotlighting.

Monitoring should use consistent routes, observers, weather recording and search conditions so that results can be compared between visits.

  • Compare records with pre-clearance findings and nearby baseline data.
  • Monitor tree retention, cypress abundance, shrub cover, grazing pressure, ground cover and connectivity.
  • Investigate a sustained decline in detections, increased mortality or new habitat damage.
  • Submit records required by approval conditions and update the project fauna register.

After habitat disturbance: 4. Incident review

Review every unexpected animal death, breeding-place disturbance, escape, permit issue or repeated stop-work event before the next clearing stage.

Include the spotter catcher, site supervisor, ecologist and project manager in the review.

  • Identify the task, cause, location, people involved and environmental conditions.
  • Change the clearing sequence, exclusion controls, induction or supervision where needed.
  • Share the revised controls with all crews before work restarts.
  • Close out corrective actions in the project environmental management system.

Rehabilitation actions: 1. Restore habitat structure

Rehabilitation should restore the structure and features used by this arboreal gecko, not just plant a canopy cover. Retain existing habitat first, then rebuild trees, shrubs, ground cover and connections over the long term.

Reinstate native woodland species suited to the local regional ecosystem, including cypress, brigalow, belah, bull oak and ironbark where they naturally occur.

Restore a layered habitat with live trees, small trees, shrubs, fallen material, leaf litter and ground cover. Retain standing dead trees and loose bark where they are safe.

Link rehabilitation areas to retained remnants, roadside vegetation and other habitat rather than creating isolated planting islands.

  • Use local provenance plants where suitable and approved.
  • Protect young plants from grazing, vehicle damage and compaction.
  • Retain natural bark, hollows and woody debris during site clean-up where they do not create a safety hazard.
  • Do not over-clear regrowth that is developing into suitable habitat.

Rehabilitation actions: 2. Shelter and breeding features

The species uses loose or peeling bark and tree hollows for daytime shelter. Ground cover and shrub cover may also be important. Protect these features during rehabilitation and maintenance.

Species-specific evidence for artificial breeding structures is limited. Do not install generic bat boxes or nest boxes and assume they will benefit Golden-tailed Geckos.

Use replacement boxes, bark shelters or other artificial structures only where a qualified reptile ecologist has designed them for the local habitat and the approval permits their use.

  • Retain natural hollows and bark before considering artificial structures.
  • Place any trial structures in retained habitat, away from machinery, flood damage, bright lights and frequent human access.
  • Record structure type, location, installation date and inspection results.
  • Remove or modify structures that trap animals, overheat or attract unsuitable species.

Rehabilitation actions: 3. Weeds, grazing and fire

Control weeds that shade out refuge sites or alter the ground layer, including lantana and invasive pasture grasses such as buffel grass where they occur.

Manage grazing so that cypress regeneration, shrubs, leaf litter and ground cover can recover. Low or absent grazing was associated with better occupancy in small patches.

Plan fire and fuel treatments with the ecologist. Avoid broad removal of shrubs, bark, fallen timber and ground cover that may be used for shelter.

  • Use targeted weed treatment and prevent herbicide drift onto retained bark, hollows and native regeneration.
  • Keep vehicles and livestock out of recovering areas.
  • Inspect rehabilitation after storms, fire, weed treatment and grazing changes.
  • Document weed cover, grazing condition and ground cover during monitoring.

Rehabilitation actions: 4. Water and lighting

The Golden-tailed Gecko is not known to depend on artificial water points. Do not install permanent water solely for this species unless the broader rehabilitation plan requires it and the design will not create weed, disease or predator problems.

Limit artificial light near retained and rehabilitated habitat. Night lighting can change invertebrate activity and may alter reptile foraging behaviour.

Use the lowest practical light level, direct light away from vegetation and switch lights off when they are not needed.

  • Keep water infrastructure clean and prevent standing water from becoming a hazard or mosquito breeding site.
  • Avoid illuminating tree trunks, shrubs and retained bark refuges.
  • Use shielding and timers for unavoidable construction or security lighting.
  • Inspect light spill after commissioning and adjust fittings where needed.

Rehabilitation actions: 5. Long-term monitoring

Monitor rehabilitation during establishment and then at intervals set by the approval, risk assessment and habitat trajectory. Use nocturnal spotlighting with consistent routes and conditions.

Assess both the gecko and its habitat. A lack of detections on one visit should not be treated as proof of absence, particularly in small or fragmented patches.

Use results to adapt grazing, weed, fire, lighting and planting controls.

  • Record detections, eyeshine observations, photographs, habitat type, tree condition and survey conditions.
  • Track cypress and other canopy establishment, shrub cover, ground cover, hollows, loose bark and connectivity.
  • Inspect any artificial structure for use, overheating, damage and animal welfare problems.
  • Report monitoring results and corrective actions to the land manager and regulator where required.

Sources