European hake

Stock Status Score: 0.25

Northern hake is fully fished and not subject to overfishing.

Stock assessments are carried out by the International Council for the Exploration of the Sea (ICES). The most recent assessment was published in 2026 using data up to 2026. The next assessment is expected in 2027.

The stock assessment defines reference points for fishing pressure (F) and biomass (B). For fishing pressure, there is a target to keep F at or below Maximum Sustainable Yield (MSY). For biomass, there is no target. However, there is a trigger point (MSY Btrigger). Below this level, F should be reduced to allow the stock to increase. Because BMSY is not defined, the Good Fish Guide applies its own definition of 1.4 x MSY Btrigger. 

The stock assessment was benchmarked in 2022. Estimates of spawning stock biomass (SSB) now only include females, whereas previously they included males as well.

The spawning-stock biomass (SSB) has increased substantially from being below biologically safe levels (Blim) in 2006 (around 45,000 tonnes) to peak at around 293,000t in 2015. It has since declined to 98,611 t in 2026. This is still above MSY Btrigger (78,405t) but has dropped below the GFG proxy for BMSY (109,767t). The stock is therefore not in an overfished state.

Fishing mortality (F) decreased significantly between 2005 and 2012, and has been fluctuating at or below levels associated with Maximum Sustainable Yield (FMSY, 0.24) since 2009. In 2025 it was 0.24, equal to FMSY. The stock is therefore not subject to overfishing.

ICES advises that when the MSY approach is applied, catches in 2027 should be no more than 46,824 tonnes. This is a 15% decrease on the previous year's advice, because of the decreasing trend in stock size.

There is some uncertainty in this stock assessment. The biomass surveys don't cover the entire stock distribution area, and changes in distribution are known to increase uncertainty in the assessment. Analyses show that the new assessment tends to revise historical SSB downwards and F upwards when a new year’s data is added. If this pattern continues, this may result in an inflated advised catch.

Management of the Target Stock Score: 0.5

Alignment with Scientific Advice Score: 0.25

Monitoring, Control and Surveillance Score: 0.25

Emergency management of this stock in 2001 has recovered it to very good levels. Ongoing management measures appear to be controlling the fishery, but discarding can be an issue in some areas and catch limits do not cover all of the countries accessing the stock.

Northern hake is a shared stock between the UK, EU, and Norway. There is no joint management plan, although one is being considered. The main management measure is to set catch limits (Total Allowable Catches, TACs).

ICES recommends catch limits for the northern hake stock as a whole. However, TACs apply only to the UK and EU member states and waters, so there is potential for overfishing if other states are accessing the stock (e.g. Norway). The agreed TACs were set in line with scientific advice for some of the last 5 years (2022 – 2026) However, in 2022 and 2025, the TACs exceeded the advice by 5% and 6% respectively. In both cases, ICES had recommended a greater than 20% decrease in catch, but hake TACs can't change by more than 20% in one year, so TACs remained above the advice.

Between 2021 and 2025, actual catches remained below the scientific advice. This could be an indication that the stock biomass has been overestimated. Caution is needed because hake are fast growing with a high natural mortality rate, so if the biomass starts to decline it could drop rapidly. A Harvest Control Rule would help to mitigate this, as it would reduce exploitation rates when certain biological reference points are approached.

Overall, currently, catch limits appear to be set in line with scientific advice and actual catches are within these limits.

Other measures include:

• Minimum conservation reference size: hake can legally be caught and sold at 27cm (30cm in Skagerrak and Kattegat). Below this size, hake have to be landed but can't be sold for human consumption and so have a lower value. Hake mature at around 35-45cm, so this doesn't prevent juveniles from being caught.
• Landing obligation: it is illegal to discard unwanted (e.g. below-minimum-size, BMS) hake at sea. Overall, around 6% of the catch has been discarded in the last three years, and discarding rates have decreased since 2015. However, discarding of juvenile hake (both above and below MCRS) can be substantial in some areas and fleets, particularly gillnetting. Recently, discarding of large individuals increased because of quota restrictions in certain fleets. Continued monitoring is required.

An Emergency Plan was brought in in 2001 to recover the stock, involving a TAC reduction and minimum mesh size of 100mm (depending on vessel size, location and proportion of hake in the total catch). It included targets for increasing stock size and reducing fishing mortality, and limited changes in TAC from year to year. The stock is now in a very good state, and fishing pressure is at sustainable levels, although this has been strongly influenced by good spawning years in 2008 and 2012.

The EU and UK both have fishery management measures, which can include catch limits, population targets, and gear restrictions. However, compliance in the EU and UK has been inconsistent, with ongoing challenges in implementing some regulations. The goal of reaching Maximum Sustainable Yield (MSY) by 2020 was missed, with less than half of UK TACs in 2024 following ICES advice. In 2024, the EU and UK reaffirmed their commitment to sustainable fisheries by aligning management with scientific advice to gradually approach MSY. However, no new target date has been set for achieving MSY across all fisheries. The Landing Obligation (LO), an EU law retained by the UK post-Brexit, requires all quota fish to be landed, even if unwanted (over-quota or below minimum size). It aims to encourage more selective fishing methods, reduce bycatch, and improve catch reporting. However, compliance is poor, and accurate discard levels are hard to quantify with current monitoring programmes. The UK is in the process of replacing the LO with country-specific Catching Policies.   

The Marine Conservation Society views Remote Electronic Monitoring (REM) with cameras is one of the most cost-effective tools for providing reliable fisheries data and aiding informed management decisions. Fully monitored fisheries enhance collaboration, data accuracy, stock recovery, and reduce impacts on marine wildlife and habitats. However, the full potential of REM may only be achieved when it tracks fishing location and documents catch and bycatch, particularly where vulnerable species and habitats are at risk. As of January 2024, the EU is introducing a Remote Electronic Monitoring (REM) mandate for EU vessels, including CCTV cameras on vessels 18m or more that pose a potential risk of non-compliance, within the next 4 years. Across the UK, different approaches to REM are being taken and legislation is expected to be in place across all 4 countries within the next few years. 

The Fisheries Act (2020) requires the development of Fisheries Management Plans (FMPs) (replacing EU Multi-Annual Plans) in the UK. 43 FMPs have been proposed and are at various stages of development and implementation, these should all be published by the end of 2028. FMPs have the potential to be very important tools for managing UK fisheries, although data limitations may delay them for some stocks. It is also essential the UK governments define and adopt a standardised approach or model across the four nations to a universally defined FMP design, to ensure the consistence, quality and coherence of all the proposal FMPs. 

The Marine Conservation Society is keen to see publicly available Fishery Management Plans for all commercially exploited stocks, especially where stocks are depleted, that include: 

• An overview of the fishery including current stock status, spatial coverage, current fishing methods and impacts 

• Targets for fishing pressure and biomass, and additional management when those targets are not being met, based on the best scientific evidence 

• Timeframes for stock recovery 

• Improved data collection, transparency, and accountability, supported by technologies such as Remote Electronic Monitoring (REM) 

• Consideration of wider environmental impacts of the fishery, including habitat impacts and minimising bycatch 

• Stakeholder engagement 

Capture Method Score: 0.75

Habitat Impacts: 0

Bycatch Impacts: 0.25

Vulnerable and ETP Species: 0.75

Ecosystems and Trophic Webs: 0.5

Gillnets in this area can encounter bycatch of non-target fish, mammals and birds. This includes the harbour porpoise, which is vulnerable in Europe.

Hake is caught by longlines, gillnets, and bottom trawls in mixed fisheries alongside megrim, anglerfish and Norway lobster.

Gillnets and fixed nets can be very size selective, but can bycatch species such as sharks, cetaceans and other marine mammals. There is concern about bycatch of harbour porpoise. The IUCN lists harbour porpoise as being of least concern globally, but vulnerable in Europe. OSPAR has included the species on its List of Threatened and / or Declining Species and Habitats for the Greater North Sea and Celtic Seas, owing to evidence of a decline in populations, their sensitivity and the threat of incidental capture and drowning in fishing nets. They are also classified as a priority species in UK and EU law, under which there are explicit bycatch requirements. To comply with this, the UK recently designated five Special Areas for Conservation for harbour porpoises, but these areas are not yet managed. The UK Dolphin and Porpoise Conservation Strategy lists harbour porpoise as having 'medium' vulnerability to gillnetting for the UK as a whole. This is based on the species having a high sensitivity to gillnetting and medium exposure.

The area of most concern is in the Celtic Seas, southwest of the UK, where most of the UK's gillnetting activity takes place. Exposure to gillnetting is high. A review of activities in the Bristol Channel Approaches Harbour Porpoise SAC lists "commercial fisheries with bycatch (predominantly static nets)" as a high risk, and a strandings report by Cornwall Wildlife Trust also shows that common dolphin bycatch is very high in this area.

There is also bycatch of elasmobranch species which may be threatened or endangered. Porbeagle sharks are being caught as bycatch in gillnets but as they are a prohibited species, there is no official data on the numbers being caught and discarded. Spurdog bycatch is also thought to be of concern. The National Evaluation of Populations of Threatened and Uncertain Elasmobranchs (NEPTUNE) highlighted continued problems of spurdog bycatch and despite a supposed real time avoidance programme being implemented, 50 tonnes were still landed in Cornish ports in 2019.

There is a relative lack of knowledge on the overall impact of fishing on seabird populations in Europe. Increasing evidence over the last decade has shown that seabirds are suffering mortality from bycatch, particularly in gillnets. Bycatch of seabirds in gillnet fisheries alone is estimated to kill around 400,000 birds globally each year. Diving seabirds, such as guillemots and cormorants, are generally more vulnerable to bycatch in gillnets than surface feeding seabirds. Most of the UK’s gillnetting takes place in the Celtic Seas, southwest of the UK and therefore there is concern for seabird populations here. In particular, species of concern include the razorbill (listed as Near Threatened in Europe by IUCN), puffin (listed as Endangered in Europe by IUCN) and the herring gull, arctic skua and roseate tern which are all classified in the UK as Red under the Birds of Conservation Concern 4: the Red List for Birds (2015).

Some pilot projects are underway to improve reporting of bycatch and find ways to reduce it. This includes trialling various types of 'pingers' that would discourage cetaceans from approaching the nets. Pingers have been very effective at reducing porpoise and dolphin bycatch in some fisheries but haven't been adopted on a large enough scale to significantly tackle the issue. Testing and trials are crucial and may need to be supported by other measures such as seasonal closures.

Because of gillnets' durability (they are made of nylon), if lost, they can continue to fish for several weeks before becoming tangled and bundled up, a phenomenon known as 'ghost fishing'. However, static nets, as with all gear, represent an investment by fishermen, and therefore there are incentives to avoid losing or damaging gear.