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Jagara Hairy Crayfish (Euastacus jagara)

The Jagara Hairy Crayfish is a freshwater crayfish found in highland rainforest streams of Main Range National Park in south-east Queensland. Its habitat of clear, flowing headwater creeks beneath rainforest is important to consider where works may affect streams or surrounding forest.

Conservation status

Commonwealth, EPBC Act 1999: Critically endangered.

Queensland, Nature Conservation Act 1992: Critically endangered.

Seasonal planning

The breeding season starts between May and July in streams.

Seasonal evidence: From published sources for this species.

Timing varies between sites and years.

  • Breeding season: The breeding season starts between May and July in streams.

Identification: Appearance

It is dark green or green-blue to orange-brown on top, with a blue tint on the underside.

It is dark green or green-blue to orange-brown on top, with a blue tint on the underside.

Identification: Confirming identity

Confirm the identity of any suspected record with a specialist and a photograph or voucher, as required by the relevant permit.

Distribution: Known range

It is known from a small number of headwater creeks in Main Range National Park, Queensland, on both sides of the Great Dividing Range. Records include Flaggy and Shady creeks and tributaries of Dalrymple Creek.

It is known from a small number of headwater creeks in Main Range National Park, Queensland, on both sides of the Great Dividing Range. Records include Flaggy and Shady creeks and tributaries of Dalrymple Creek.

Distribution: National mapping

The Commonwealth species distribution model (SNES) maps where the species or its habitat is known, likely or may occur. Use it with local records and site inspection.

Habitat: Habitat

It inhabits clear, flowing, well-shaded headwater streams in highland rainforest, at elevations above about 700 metres. It occurs in riffles and pools, and its downstream range corresponds closely with the transition from rainforest to open forest.

It inhabits clear, flowing, well-shaded headwater streams in highland rainforest, at elevations above about 700 metres. It occurs in riffles and pools, and its downstream range corresponds closely with the transition from rainforest to open forest.

Foraging habitat: Diet

Not documented in the published sources used for this profile.

Not documented in the published sources used for this profile.

Breeding habitat: Breeding

Larger adults appear to spend most of the year in burrows and emerge into the creeks during the breeding season.

Larger adults appear to spend most of the year in burrows and emerge into the creeks during the breeding season.

Sheltering habitat: Shelter

It constructs large, intricate burrow systems with multiple entrances in streambanks or in nearby forest. Juveniles have also been found in damp seepage areas away from the creeks.

It constructs large, intricate burrow systems with multiple entrances in streambanks or in nearby forest. Juveniles have also been found in damp seepage areas away from the creeks.

Threats: Threats

Its restricted highland rainforest habitat is threatened by bushfire, climate change and feral predators. Surveys have also indicated a contraction at lower elevations.

Its restricted highland rainforest habitat is threatened by bushfire, climate change and feral predators. Surveys have also indicated a contraction at lower elevations.

Threats: Works risk

Works that damage or alter its shaded headwater streams, rainforest or streambanks could affect its habitat and burrow systems. Its range is closely associated with rainforest rather than open forest, and burrows may extend into streambanks or nearby forest.

Survey methodology: 1. Commonwealth guidance

Use methods consistent with the Commonwealth survey guidelines and engage a specialist with the right permits.

For EPBC Act referrals, survey effort and methods should be consistent with the on-ground surveys and data for referred actions under the EPBC Act, read with the Significant impact guidelines 1.1.

Survey methodology: 2. Limits

A non-detection is not proof of absence. Match survey timing to the species and season, and record effort.

Vegetation associations: Rainforest or vine thicket

Source-checked associations and automatically indexed candidates are separated below. An association does not establish site presence, preference or dependence.

It inhabits clear, flowing, well-shaded headwater streams in highland rainforest, at elevations above about 700 metres.

Automatically indexed from existing profile text. Not a verified preference, mapped occurrence or habitat requirement. Check the original source and regional qualifiers before use.

Evidence: Unreviewed profile-derived candidate

Confidence: Not independently verified

Region: Scope as described in the quoted profile text; not independently verified. Profile states: QLD.

Habitat use: general

Vegetation associations: Eucalypt forest

It occurs in riffles and pools, and its downstream range corresponds closely with the transition from rainforest to open forest.

Automatically indexed from existing profile text. Not a verified preference, mapped occurrence or habitat requirement. Check the original source and regional qualifiers before use.

Evidence: Unreviewed profile-derived candidate

Confidence: Not independently verified

Region: Scope as described in the quoted profile text; not independently verified. Profile states: QLD.

Habitat use: general

Ecosystem associations

Source-checked associations and automatically indexed candidates are separated below. An association does not establish site presence, preference or dependence.

No species-specific ecosystem association has been indexed or source-checked in this evidence library. This is an evidence gap, not evidence of no association.

Soil and substrate associations

Source-checked associations and automatically indexed candidates are separated below. An association does not establish site presence, preference or dependence.

No species-specific soil association has been indexed or source-checked in this evidence library. This is an evidence gap, not evidence of no association.

Water and wetland associations: Water-associated habitat mentioned in profile

Source-checked associations and automatically indexed candidates are separated below. An association does not establish site presence, preference or dependence.

It inhabits clear, flowing, well-shaded headwater streams in highland rainforest, at elevations above about 700 metres.

Automatically indexed from existing profile text. Not a verified preference, mapped occurrence or habitat requirement. Check the original source and regional qualifiers before use.

Evidence: Unreviewed profile-derived candidate

Confidence: Not independently verified

Region: Scope as described in the quoted profile text; not independently verified. Profile states: QLD.

Habitat use: general

Fauna records and mapped habitat: Not yet analysed

Record locations can be overlaid with mapping, but record frequency alone does not measure habitat preference. No species is excluded from desktop assessments by this analysis.

No quality-controlled record-to-map analysis has been completed for this species. The existing generalised distribution dots and indicative range polygons have not been treated as precise occurrence coordinates.

A defensible run needs dated, independently attributable records, coordinate uncertainty, duplicate and captive-record checks, layer versions and regional scope. Preference and absence require additional survey-effort and detection evidence.

Habitat limitations and contrary evidence: No supported exclusion recorded

Not recorded is not the same as cannot occur. Low suitability, resident habitat, breeding habitat and occasional movement are different conclusions.

This library has not established a vegetation, ecosystem or soil-type exclusion for this species. This does not mean all habitat is suitable; the evidence needed to justify an exclusion has not been assembled.

Habitat limitations and contrary evidence: Before using a negative association

  • Confirm the taxon, geographic region, life stage and habitat function covered by the evidence.
  • Check survey methods, season, repeated effort and detectability before interpreting non-detection.
  • Investigate credible contradictory records and microhabitats absent from broad mapping.
  • Do not convert a missing map class, low record count or failed data request into species absence.

Before disturbance: 1. Desktop and approvals

Confirm whether the project could affect the species before works begin.

Check national mapping, state records and recent surveys for the site. An action likely to have a significant impact on this nationally listed species needs EPBC Act referral, and state permits apply where it is state listed.

Before disturbance: 2. Plan to avoid

Design the footprint, timing and access to avoid known or likely habitat, and brief crews on what to look for and who to call.

During disturbance: 1. Controls

Keep works inside the approved footprint and conditions.

Fence or mark habitat to be retained and keep machinery, stockpiles and spoil out of it.

During disturbance: 2. Stop and report

If the species is found unexpectedly, stop work at that spot and contact the project ecologist and the relevant agency.

After disturbance: 1. Records

Record outcomes.

Record sightings, habitat lost or retained and any injury or death, and report them under the approval conditions.

Rehabilitation: 1. Restore

Restore disturbed habitat where possible.

Reinstate disturbed ground with local species, return logs, rocks and litter, and control weeds and erosion until the site is stable.

Sources