Species identified in the CITES Non-detriment Finding for the Queensland Coral Fishery were assessed in the Species Vulnerability Assessment and those that justified further consideration were assessed in the Ecological Risk Assessment.
The Ecological Risk Assessment entailed a two-day workshop in May 2013. In attendance were fishery practitioners from the north, central and southern parts of the fishery; fishery managers from Queensland, Western Australia and the Northern Territory; the Great Barrier Reef Marine Park Authority; representatives from the Australian Government Environment department, including the CITES division, and the Australian Government Fisheries department; coral reef scientists; and representatives from environmental advocacy groups adjacent the Cairns and Keppel Coral Collection Areas plus a representative from WWF Australia.
The analysis assigned a level of consequence (from negligible to catastrophic) and the likelihood of this consequence occurring (from remote to likely) for each species assessed.
When considering the level of consequence or likelihood, participants made an assessment in context of what existing control measures and management arrangements are already in place. A ten year forecast was considered when determining consequence and likelihood levels. This time frame equates to at least one generation of growth for most coral species. The allocated risk ranking dictates the amount of justification required and also the extent of management likely to be needed to address the risk.
The process follows the following structure:
Consequence |
|
Negligible (0) |
Insignificant impacts to populations, (dynamics/structure/size). Unlikely to be measurable against background variability for this population. |
Minor (1) |
Possibly detectable, but minimal localised impact on population size and none on dynamics. |
Moderate (2) |
Noticeable local impact, likely minimal impact on regional populations. Short-term recruitment/dynamics not adversely impacted. |
Severe (3) |
Significant impacts on populations. Affecting recruitment levels of stocks/or their capacity to increase. |
Major (4) |
Long-term local depletion if continued. Likely to cause local extinctions, if continued in longer term (i.e. probably requiring listing of species in an appropriate category of the endangered species list e.g. CITES Appendix I). |
Catastrophic (5) |
Local extinctions are imminent/immediate |
Likelihood |
|
Remote (1) |
Never heard of, but not impossible |
Rare (2) |
Happens only very rarely |
Unlikely (3) |
Unlikely, but has been known to occur elsewhere |
Possible (4) |
Is expected to occur only infrequently |
Occasional (5) |
Is expected to occur moderately |
Likely (6) |
Is expected to occur often |
The overall level of risk assigned to each species is based on the group’s assessment of the perceived consequence multiplied by the perceived likelihood.
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Consequence | ||||||||
Negligible | Minor | Moderate | Severe | Major | Catastrophic | |||
0 | 1 | 2 | 3 | 4 | 5 | |||
Likelihood | Remote | 1 | 0 | 1 | 2 | 3 | 4 | 5 |
Rare | 2 | 0 | 2 | 4 | 6 | 8 | 10 | |
Unlikely | 3 | 0 | 3 | 6 | 9 | 12 | 15 | |
Possible | 4 | 0 | 4 | 8 | 12 | 16 | 20 | |
Occasional | 5 | 0 | 5 | 10 | 15 | 20 | 25 | |
Likely | 6 | 0 | 6 | 12 | 18 | 24 | 30 | |
Adapted from Fletcher, W, Chesson, J, Fisher, M, Sainsbury, K, Hundloe, T, Smith, A & Whitworth, B. 2002, National ESD Reporting Framework for Australian Fisheries: The ‘How To’ Guide for Wild Capture Fisheries. FRDC Project 2000/145, Canberra, Australia. |
Risk profiles are used to develop appropriate mitigation measures to be implemented through the Performance Measurement System and Stewardship Action Plan 2013: Mitigating Ecological Risk in a Changing Climate.
Risk | Reporting | Management Response | |
Negligible | 0 | Short justification only | Nil |
Low | 1-6 | Full justification needed | None specific |
Moderate | 7-12 | Full performance report | Continue current management arrangements |
High | 13-18 | Full performance report | Changes to management required |
Extreme | 19-30 | Full performance report | Substantial additional management needed urgently |
Results
The Ecological Risk Assessment of the Queensland Coral Fishery in 2013 identified 17 species at the moderate level of risk. A further 63 species were judged to be at low risk in the fishery.
Acanthastrea bowerbanki |
Acanthastrea lordhowensis |
Acanthophyllia deshayesiana |
Acropora multiacuta |
Acropora nana |
Cycloseris cyclolites |
Cynarina lacrymalis |
Duncanopsammia axifuga |
Entacmaea quadricolor |
Euphyllia ancora |
Euphyllia cristata |
Euphyllia divisa |
Euphyllia fimbriata |
Euphyllia glabrascens |
Micromussa amakusensis |
Scolymia australis |
Trachyphyllia geoffroyi |
Acropora acuminata |
Acropora aspera |
Acropora bushyensis |
Acropora chesterfieldensis |
Acropora digitifera |
Acropora horrida |
Acropora hyachinthus |
Acropora listeri |
Acropora millepora |
Acropora palmerae |
Acropora paniculata |
Acropora plana |
Acropora prostrata |
Acropora subglabra |
Acropora verweyi |
Actinia tenebrosa |
Balanophyllia europaea |
Blastomussa merleti |
Blastomussa wellsi |
Catalaphyllia jardinei |
Caulastrea curvata |
Caulastrea echinulata |
Caulastrea furcata |
Cladiella spp. |
Clavularia spp. |
Cryptodendrum adhaesivum |
Dendrophyllia spp. |
Diaseris fragilis |
Euphyllia paraancora |
Euphyllia paradivisa |
Favites abdita |
Favites flexuosa |
Favites pentagona |
Fungia repanda |
Goniastrea australensis |
Gorgoniidae various |
Heliofungia actiniformis |
Heliopora coerulea |
Heteractis aurora |
Heteractis crispa |
Heteractis magnifica |
Heteropsammia cochlea |
Leptoseris incrustans |
Leptoseris papyracea |
Leptoseris yabei |
Montipora caliculata |
Moseleya latistellata |
Pachyclavularia spp. |
Pachyseris rugosa |
Pavona cactus |
Plerogyra sinuosa |
Scolymia vitiensis |
Sinularia spp. |
Stichodactyla gigantea |
Stichodactyla haddoni |
Stichodactyla mertensii |
Turbinaria bifrons |
Turbinaria conspicua |
Turbinaria frondens |
Turbinaria heronensis |
Turbinaria mesenterina |
Turbinaria patula |
Turbinaria reniformis |
The Ecological Risk Assessment of the Queensland Marine Aquarium Fish Fishery in 2008 identified two species at the moderate level of risk. A further seven species were judged to be at low risk in the fishery.
The next Ecological Risk Assessment for the Queensland Marine Aquarium Fish Fishery is due in 2014. It is expected that that assessment will mirror the rigour applied to the Queensland Coral Fishery and will also demand finer scale reporting of fishery data.
When the 2014 Ecological Risk Assessment is carried out, identified risks will be updated on the Pro-vision Reef Inc. website to keep the initiative current.
Chaetodontoplus duboulayi |
Chaetodontoplus meredithi |
Amphiprion latezonatus |
Amphiprion melanopus |
Amphiprion ocellaris |
Amphiprion percula |
Choerodon fasciatus |
Cleidopus gloriamaris |
Paracanthurus hepatus |
Commonwealth Coral Sea Fishery
The ‘Reducing Uncertain Stock Status’ project undertaken by the Australian Bureau of Agricultural and Resource Economics and Sciences in 2011 clarified the status of stocks accessed by the aquarium sector of the Commonwealth Coral Sea Fishery.
The project found the potential maximum footprint achievable by the fishery, with the two existing fishery practitioners, to be around 7.4% of the estimated suitable habitat area in a given fishing season. The estimated extraction rate for the 2008–09 fishing season (the largest catch season) for all key commercial families was less than 0.02% of potential population size.
The risk assessment considered 623 species. All were found to be at low risk or very low risk. Consequently, no action will be taken in Stewardship Action Plan 2013: Mitigating Ecological Risk in a Changing Climate in regard to the Commonwealth Coral Sea Fishery assessment. This could change over time and participating businesses stand ready to respond should risks be identified in the future.