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New Zealand Rock Lobster
Jasus edwardsii
Also known as:
Koura, Pawharu, Spiny rock lobster, Rock lobster, Red rock lobster, Crayfish, Southern rock lobster
LAST UPDATED: 30 July, 2018

Rock lobsters are the most commercially valuable of New Zealand’s inshore fisheries species.

Two species of rock lobsters are taken in New Zealand coastal waters. The red rock lobster (Jasus edwardsii) supports nearly all the landings and is caught all around the North and South Islands, Stewart Island and the Chatham Islands. The packhorse rock lobster (Sagmariasus verreauxi) is taken mainly in the north of the North Island.

The rock lobster fisheries were brought into the Quota Management System (QMS) in 1990, when Total Allowable Commercial Catches (TACCs) were set for each Quota Management Area (QMA).

In the commercial fishery, rock lobster are harvested using baited pots.  Total commercial catch of rock lobsters has remained stable between 1990-91 and 2014-15, albeit catches have fluctuated within individual QMAs.

The rock lobster fishery also supports important recreational and customary catches.

The National Rock Lobster Management Group (NRLMG) is the primary advisor to the Minister for Primary Industries on catch limit, regulatory and other management actions that apply specifically to rock lobster fisheries. The NRLMG is a national-level, multi-stakeholder group comprising representatives of customary, recreational and commercial fishing sectors and the Ministry for Primary Industries.  Every year the NRLMG considers the results from stock assessments and the operation of management procedures.  These determine whether catch limit changes are required for the upcoming fishing year to ensure the sustainable use of the rock lobster resource.

The risk assessment covers over 90% of rock lobster caught commercially in New Zealand.

For more information, download the full Risk Assessment Report.

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Independent risk assessment conducted by:
MRAG Asia Pacific
Lead Assessor - Duncan Souter
RISK ASSESSMENT PROCEDURES

The risk assessment framework is used to assess the relative environmental risks of Australian and New Zealand wild caught fisheries on fish stocks and the aquatic environment.

Assessments are undertaken for each species according to multiple ‘units of assessment’ (UoAs). The UoA is a combination of target species/stock and the gear type used by the fishery. Each UoA is assessed against three components for target species, bycatch and ecosystems, and management systems. Each component has a number of performance indicators, which have associated criteria, scoring issues and scoring guideposts. For each UoA, each performance indicator is assigned a risk score according to how well the fishery performs against the scoring guideposts. The summary of risk scores by UoA are presented in the table below.

An assessment of the future ‘outlook’ over the short to medium-term (0-3 years) is provided against each component. Outlook scores are provided for information only and do not influence current or future risk scoring.

All risk assessments are conducted by an independent third party. The process only takes a few days and includes opportunities for management groups and government to provide input and peer review.

The information presented on this page is extracted from the independent species Risk Assessment Report.

Fishing Areas
Catch Quantities
The commercial harvest limit
2,703t
The commercial catch
2,837t
Estimated recreational catch
260t
Estimated customary catch
85t
Fishing Methods
Pots & traps
Fishing Season
JAN
FEB
MAR
APR
MAY
JUN
JUL
AUG
SEP
OCT
NOV
DEC
Peak season
Off season

Risk Assessment Summary

Most recent assessment
Management areas assessed
The risk assessment comprises three components:
Component 1: Target species
Component 2: Bycatch and ecosystems
Component 3: Management system

Target species

Component 1 of the risk assessment looks at the health of the population of target species including the current fishing effort and estimates a risk of overfishing.

The core components of the harvest strategy are largely consistent across each of the rock lobster stocks.  The primary constraint on catch is through the application of a total allowable catch (TAC), divided into a total allowable commercial catch (TACC) and allowances for recreational and customary catches and other sources of mortality.   TACs are set using management procedures in all rock lobster fisheries except for CRA 6 and CRA 10.  In general, each procedure is designed to move or maintain stock abundance well above agreed reference levels.

Management procedures are evaluated with a modified stock assessment model, known as the ‘operating model’.  Data used in the stock assessment model include: customary, recreational, commercial and illegal catches, length frequencies of the catch from observer and industry logbook data, tag-recapture data (i.e. growth information) and larval settlement levels.  The most important inputs to the assessment are commercial catch per unit effort (CPUE) indices, which are considered to be proportional to abundance.

A substantial body of information is available on stock structure and productivity of J. edwardsii from New Zealand.  Catches in the commercial sector are closely monitored consistent with the compliance regime under the QMS, while catches in the recreational and customary sectors are estimated using fisher surveys and other techniques.  The key input into the management procedure, standardised CPUE, is monitored and estimated for each stock.   Collectively, this information is sufficient to support the harvest strategy across all stocks.

Bycatch and ecosystems

Component 2 of the risk assessment looks at the risks around bycatch species and other environmental impacts of the fishery.

Rock lobster potting is one of the most highly targeted fisheries in New Zealand. The pots are designed to be most effective for lobsters, so fish catch is incidental. Escape gaps provided for sublegal lobsters to escape also allow many fish and invertebrates to escape.

The results of stock assessments utilising formal management procedures provide some objective basis for confidence that stocks remain in a healthy position, and by default lobsters are likely to have maintained their functional role in the ecosystem.  CPUE analysis and previous estimates of maximum constant yield also provide some evidence for CRA 6 albeit considerably weaker.

There is limited published information on the interaction between the lobster fishery and protected species.  From the available information, the main potential interactions are likely to be with seabirds and marine mammals.

Some quantitative information is available on endangered, threatened and protected species interactions, primarily through mandatory fisher reporting and fisher surveys. Although the level of interactions in the fishery appears to be very low, there is limited independent evidence to verify fisher reporting.  In the context of the various fisheries, the main uncertainty appears to be the level of seabird interactions in the CRA 6 fishery.  Some (albeit anecdotal) quantitative data exists and this has been used to inform a strategy to manage impact through the National Plan of Action - Seabirds.

Management systems

Component 3 of the risk assessment looks at the risks around the management systems of a fishery.

The Fisheries Act 1996 and subsequent amendments provide a binding legislative and legal framework for delivering the objectives of Component 1 and 2.  Sections 10, 11, and 12 of the Fisheries Act establish the requirements for the decision-making process, and Section 10 further requires the use of best available information for all decisions. This results in measures and strategies to achieve the fishery-specific objectives. The Fisheries Act requirement for best available information leads to scientific evaluation in advance of decisions. The Fisheries Act further requires consultation with such persons or organisations as the Minister considers are representative of those classes of persons having an interest in the stock or the effects of fishing on the aquatic environment in the area concerned including Maori, environmental, commercial, and recreational interests.

The National Rock Lobster Management Group’s stock management goal is for all rock lobster fisheries: “to be managed and maintained at or above the assessed and agreed reference levels, using a comprehensive approach that recognises a range of customary Maori, amateur, commercial and environmental concerns and benefits”.  For the five of the 6 CRAs operating under formal management procedures, the goal is given practical expression through the Management Plan.   For CRA 6, the goal is achieved by setting TACs consistent with the intent of the Fisheries Act 1996 and the Harvest Strategy Standard.  Together with the objectives outlined in the Act and Fisheries 2030, these measures arguably provide short and long-term objectives consistent with Component 1.

While objectives broadly consistent with Component 2 are specified in the Act and Fisheries 2030, and are therefore implicit in the fishery specific management system, explicit short and long-term objectives consistent with Component 2 do not appear to be in place at this stage.

Summary of main issues

Main issues highlighted by the assessment are:

  • All stocks except CRA 6 are very well placed against Component 1 performance indicators. The most recent stock assessment for CRA 6 was undertaken in 1996 and the position of the stock relative to reference points is unknown.  Nevertheless, standardised CPUE has remained comparatively stable since the mid-1980s and current catch is within the range of estimates for maximum constant yield.
  • Lobster pots are generally considered a relatively benign apparatus, although there is limited analysis of the overlap between fishing effort and potentially vulnerable habitats.
  • The removal of lobsters from the ecosystem has been implicated in trophic cascades in some areas, although effects appear to be reversible. Maintenance of stock sizes above levels capable of producing maximum sustainable yield should assist to maintain the natural role of lobsters in the ecosystem.

Outlook

The outlook below provides a qualitative judgement about the likely future performance of the fishery against the relevant risk assessment criteria over the short to medium-term (0-3 years).  Assessments are based on the available information for the species and take into account any known management changes.

  • Target species (CRA 2, CRA 3, CRA 4, CRA 5 & CRA 8) - Stable: Risk scoring unlikely to change.  Fishing mortality is below the rate that, if applied constantly, would result in maximum sustainable yield for all stocks.
  • Target species (CRA 6) - Stable: No stock assessment/management procedure is planned.
  • Bycatch and ecosystems - Stable: No major changes are expected to bycatch and ecosystem risk scoring.
  • Management systems - Stable:  No major changes are expected to management systems risk scoring.

 

Please note: The risk assessment is not intended as a definitive assessment of fisheries sustainability. It is not intended to act as a replacement or alternative to formal fisheries ecolabeling programs such as the Marine Stewardship Council (MSC).

For more information, download the full Risk Assessment Report or contact us on hello@openseas.org.nz.

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