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Hyperoglyphe antarctica
Also known as:
Mature, Stone Eye, Bonita, Bream, Griffin's Silver Fish, Blue Eye Trevella
LAST UPDATED: 1 October, 2020

The largest domestic bluenose fisheries occur in BNS 1 and 2. Historically, catches in BNS 2 were predominately taken in the target alfonsino and bluenose trawl fisheries, but have been primarily taken by target bottom longline fishing in recent years. There is a target line fishery for bluenose in the Bay of Plenty and off Northland (BNS 1).

The first fully quantitative stock assessment modelling for bluenose was carried out in 2011. Following the 2011 stock assessment, a rebuild plan was put in place with phased reductions to the TACCs for bluenose stocks. In 2011, TACCs were reduced in BNS 1, BNS 2, and BNS 3. In 2012, TACCs were further reduced for all bluenose stocks. From October 2017, following the assessment being updated to include information up to the end of the 2015–16 year,  TACCs have been further reduced to ensure that BNS stocks rebuild towards the target at an appropriate rate consistent with the NZ Harvest Strategy Standard.

TACCs were first established for bluenose upon introduction to the Quota Management System (QMS) in 1986–87. Catch performance against the TACC has varied, with the combined TACC being undercaught by an average of 9% to 20% from 1987 to 2008.

Bluenose is also targeted by recreational fishers around deep offshore reefs using line fishing methods.

The risk assessment covers nearly 90% of bluenose caught in New Zealand.

For more information download the full Risk Assessment Report.

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

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 is 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 the 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
Commercial catch allowance 2020/21
Commercial catch 2018/19
Historic catch quantity data
Estimated recreational catch
Estimated customary catch
Fishing Methods
Hook & Line
Fishing Season
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 Ministry for Primary Industries reports that bluenose stock boundaries are unknown, but the similarity in trends in catch and catch per unit effort (CPUE) across fisheries occurring in each of the five New Zealand bluenose Quota Management Areas suggests the possibility that there may be a single bluenose stock across all these areas, or of some close relationship between stocks in these areas.

The most recent estimates of stock size in 2016 ranged from 17–27% of the unfished biomass. Biomass was estimated to have declined continuously from the 1980s to 2011 and then to have either leveled off or increased slightly. Biomass has been below the default 40% unfished biomass target since around 2000.

Although the ‘true’ level of natural mortality is not known with certainty, it is not clear from the most recent model results that there is at least a 70% probability of the stock being above 20% of the unfished biomass.  On this basis, the medium-risk scoring guidepost is not met.  Nevertheless, for at least plausible estimates of mortality the stock is estimated to be above 20% of the unfished biomass.

The harvest strategy has the key elements needed to ensure that exploitation is reduced as the point of recruitment impairment is approached; a sound and measurable index of relative biomass, a suite of performance measures based on these estimates of relative biomass, and a total catch adjustable annually.   While there is no formal mathematical harvest control rule (HCR) for this stock, there is a process in place to identify, examine and respond to issues of declines in the bluenose stock, and a suite of available tools to implement reductions in exploitation if needed.  Action taken to reduce the TACCs in response to the 2011 stock assessment provides evidence that the management system is willing to reduce exploitation as the point of recruitment impairment is approached.

Bycatch and ecosystems

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

Limited publicly available information has been found on catch composition for the bluenose longline or trawl fisheries, albeit more detailed information may be available through MPI observer coverage.  Qualitative and quantitative information is insufficient to estimate the impact of the fishery on at least some main other species with respect to status.  The Ministry for Primary Industries notes that other commercially important species taken when longlining for bluenose are ling, hapuku, and bass. There are no estimates of current biomass are available for hapuku/bass and it is not known if current catches or the TACCs are sustainable or at levels that will allow these stocks to move towards a size that will support the maximum sustainable yield.  Alfonsino forms the dominant bycatch in the BNS 2 and BNS 3 trawl fisheries targeting bluenose.  It is not known if the recent catch levels or the current TACCs are sustainable.

The main potential endangered, threatened and protected (ETP) species interactions in the bluenose fishery are with seabirds and protected corals.

Notwithstanding limited observer coverage in the bottom longline sector, some quantitative information is available which has been able to support risk assessments for key ETP species (e.g. seabirds) and analysis of likely interactions (e.g. corals).  The Ministry's protected species bycatch database contains good records and analysis of fisheries interactions by gear, vessel size, and ETP bird, mammal, and reptile species across New Zealand commercial fisheries. The extent to which the bluenose bottom longline sector is contributing to overall black petrel mortalities is uncertain given the very low rate of observer coverage (0-2% between 2002-03 and 2014-15).  While the measures in place (offal management, streamer lines, night setting/line weighting) could be considered likely to work, recent modelling indicates the median risk to black petrel across New Zealand fisheries remains above its sustainability targets (albeit with considerable uncertainty).

The bluenose targeted trawl fishery’s contribution to overall interactions with seabirds is likely to be very small. It is probably highly unlikely that bluenose targeted trawl fisheries will hinder recovery of protected corals as well.

Management systems

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

The Fisheries Act 1996 (the Act) and subsequent amendments provide a binding legislative and legal framework for delivering the objectives of Components 1 and 2.  Sections 10, 11, and 12 of the Act establish the requirements for the decision-making process, and Section 10 further requires the use of the best available information for all decisions. This results in measures and strategies to achieve the fishery-specific objectives. The Act requirement for best available information leads to scientific evaluation in advance of decisions. The 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.

While objectives broadly consistent with Components 1 and 2 are specified in the Act and Fisheries 2030 and are therefore implicit in the fishery specific management system, it is not clear that explicit short and long-term objectives for bluenose fisheries are in place at this stage.

Summary of main issues

Main issues highlighted by the assessment are:

  • Depending on the estimate of natural mortality used, the bluenose stock is estimated to range from 17–27%.
  • Following the 2011 stock assessment, a rebuilding plan was introduced which involved stepped reductions in the TACC. Stock projections at the current TACC of 900 t indicate the stock should grow, although the rate of growth depends on estimates of stock-recruitment, steepness, and natural mortality used.
  • The stock status of main bycatch species, including hapuku (longline) and alfonsino (trawl), is unknown.
  • The bluenose bottom longline fishery has a bycatch of black petrels. Recent preliminary risk modelling indicates the median risk ratio for black petrels across all New Zealand commercial fisheries is higher than its population sustainability threshold.


The outlook below provides a qualitative judgment 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 - Improving: All stock projections point to an increase in the stock in the coming years.  Work is underway on a management procedure to guide the rebuilding plan.
  • Bycatch and ecosystems (BNS1_BLL) - Uncertain: Estimates of risk to seabird species have been continuously refined over recent years and have generally resulted in lower estimates of overall risk, including to the highest risk species taken in the bluenose bottom longline fishery, black petrel.  Additional independent observations of seabird interactions will better inform risk assessments.
  • Bycatch and ecosystems (BNS2_Trawl & BNS3_Trawl) - Stable:  No major changes are expected to bycatch and ecosystem risk scoring.
  • Management systems - Stable:  No major changes are expected to management system 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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