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B2. Sustainable fisheries

a. Percentage of marine fish (quota) stocks of UK interest harvested sustainably

b. Percentage of marine fish (quota) stocks of UK interest with biomass at levels that maintain full reproductive capacity

Type: Pressure (a) and state (b) Indicator

This indicator was updated in 2023.

Introduction

Sustainable fisheries help to ensure our marine ecosystems remain diverse and resilient, providing a long-term and viable fishing industry.

Changes were made to the indicator in the 2021 publication to bring it in line with the Multi-Annual Plans (MAPs) for fisheries. The indicator is therefore not directly comparable with previous versions of the indicator pre-2021. This indicator has been developed to meet the needs of the UK Marine Strategy and uses quota-fish assessments for UK commercial fisheries to assess Good Environment Status for the UK Marine Strategy. Data have been updated to 2020 for both fishing pressure and spawning stock biomass.

Key results

The revised indicator includes a category for stocks that are fished in acceptable mortality range (in FMSY range). Estimates show that the percentage of UK quota-fish stocks (including Norway lobster, Nephrops norvegicus) fished at or below FMSY, and/or within acceptable mortality range levels, has increased from 11% in 1990 to 56% in 2020. In 2020, 21% of UK quota-fish stocks were assessed to be fished at levels of fishing pressure above both FMSY and the upper FMSY range where this estimate is available.

To maintain the reproductive capacity of stocks, each stock’s spawning biomass (SSB) should be at or above the level capable of producing maximum sustainable yield (MSY Btrigger). The revised indicator introduced a zone ‘below MSY Btrigger but above Blim’ to indicate conditions where a stock is at low risk of reproductive impairment relative to those stocks at high risk. The percentage of stocks subject to quota management and achieving SSB at or above MSY Btrigger increased from 28% in 1990 to 58% in 2020. However, 16% of stocks remain with SSB below MSY Btrigger, with a further 3.5% with SSB below MSY Btrigger but above Blim.

Overall, a positive trend towards a greater proportion of stocks fished sustainably is evident in both the long term and short term. There is also a positive trend for fish within safe biological limits in the long term, however no change in the short term. For stocks fished sustainably, the percentage of stocks with an ‘unknown status’ is decreasing and is 23% in 2020. Whereas the percentage of stocks fished within safe biological limits with an ‘unknown status’ is increasing, and in 2020 is 23%.

Figure B2a. Percentage of marine fish (quota) stocks of UK interest harvested sustainably, 1990 to 2020 (sustainably harvested – fishing mortality ≤ FMSY or in FMSY range; unsustainably harvested – fishing mortality > FMSY)

Figure B2a is a stacked bar chart showing from 1990 to 2020 the percentage of marine fish (quota) stocks of UK interest harvested sustainably. The percentage has increased from 11% in 1990 to 56% in 2020.

Figure B2b. Percentage of marine fish (quota) stocks of UK interest with biomass at levels that maintain full reproductive capacity, 1990 to 2020 (full reproductive capacity – spawning stock biomass (SSB) ≥ MSY Btrigger; stocks with SSB < Blim require the greatest degree of management action)

Figure B2b is a stacked bar chart showing from 1990 to 2020 the percentage of marine fish (quota) stocks of UK interest with biomass at levels that maintain full reproductive capacity. The percentage of stocks subject to quota management and achieving SSB at or above MSY Btrigger increased from 28% in 1990 to 58% in 2020

Notes about Figures B2a and B2b:

  1. Based on 57 stocks of UK interest for which data are available from ICES (International Council for the Exploration of the Sea) stock assessments.
  2. Changes were made to the indicator in the 2021 publication to bring it in line with the Multi-Annual Plans (MAPs) for fisheries. The indicator is therefore not directly comparable with previous versions of the indicator pre-2021.

Source: Centre for Environment, Fisheries and Aquaculture Science (see: Lynam, C., Allison, C., Ribeiro, J., Campon-Linares, V., Garnacho E. (2022) International (ICES) and national UK fish stocks and shellfish data from 2020 assessment year. https://doi.org/10.14466/CefasDataHub.130

Assessment of change in stocks harvested sustainably and at full reproductive capacity

  Long term Short term Latest year
Percentage of fish stocks harvested sustainably

Improving

1990–2020

Improving

2015–2020

Increased

(2020)

Biomass of stocks at full reproductive capacity

Improving

1990–2020

Little or no overall change

2015–2020

Little or no change

(2020)

Notes for Assessment of Change table:

Long- and short-term assessments are based on a 3% rule of thumb. The base years for these assessments use a three-year average.  See Assessing Indicators.

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Indicator description

The indicator uses quota-fish assessments developed to assess good environment status (GES) for the UK Marine Strategy. It comprises of two measures: the percentage of fish stocks in seas around the UK that are harvested sustainably; and those at full reproductive capacity.  It is based on a group of 20 species in 57 stocks for which there are estimates available for fishing mortality and/or spawning stock biomass (SSB), together with MSY reference points for fishing mortality (including FMSY ranges) and SSB (including a management reference point MSY Btrigger and a lower limit, Blim) that allow the sustainability of the stocks to be evaluated.

The indicator stocks include a range of local and widely distributed species of major importance to the UK fishing industry.

The measures are assessed as follows:

  1. An evaluation of the temporal trends in the exploitation level of stocks of UK interest with respect to the fishing mortality target FMSY and FMSY ranges where available. The aim is to increase the proportion of stocks fished at or below FMSY and reduce to zero the number of stocks of unknown status relative to FMSY.
  2. An evaluation of the temporal trends in the spawning stock biomass (SSB) of stocks of UK interest with respect to safe biological limits. The aim is to increase the proportion of stocks with SSB at or above MSY Btrigger and reduce to zero the number of stocks that have unknown status relative to MSY reference points.

The updated indicator methodology for fishing mortality accommodates complications that arise due to multi-species interactions in mixed-fisheries that characterise demersal fisheries in UK waters. The methodology allows a more flexible approach to the fishing mortality target when spawning stock biomasses are above MSY Btrigger, but a stricter approach under conditions where the biomass is below MSY Btrigger, especially where this falls below Blim. The MAP approach allows for fishing within F ranges around MSY (FMSY ranges) as advised by ICES (International Council for the Exploration of the Sea). However, fishing within the upper FMSY range (i.e. above the FMSY point estimate) is only acceptable if the stock size is above MSY Btrigger (or in the case of Nephrops: Abundancebuffer). When the biomass falls below MSY Btrigger, the MAP states that “all appropriate remedial measures shall be adopted to ensure rapid return of the stock or functional unit concerned to levels above those capable of producing maximum sustainable yield” (EC, 2018), thus the acceptable target for FMSY is reduced linearly by multiplication of FMSY by the ratio of SSB/MSY Btrigger. If the biomass were to further decrease below Blim, then the MAP states that “further remedial measures shall be taken to ensure rapid return of the stock or functional unit concerned to levels above the level capable of producing maximum sustainable yield”.

Although stocks that are fished in the ‘in FMSY range’ (Figure B2a) are not fished at the target level (≤ FMSY) such stocks can be considered acceptably fished in the short term if SSB levels are high. For the reproductive capacity measure (SSB) the revised indicator introduces a zone ‘below MSY Btrigger but above Blim’ (Figure B2b) to indicate conditions where a stock is at low risk of reproductive impairment relative to those stocks at high risk, i.e. SSB < Blim. In this way, a distinction can now be made between stocks that require the greatest degree of management action.

The assessments of change are made by applying a 3% rule of thumb to each measure (state and pressure) separately. The arithmetic mean of the first three years of the data series is compared with the last point to determine the assessment for the long-term trend, and an arithmetic mean of the year five years back in the time series and the year either side calculated to compare with the last point to assess the short-term trend.

Stocks that meet both the pressure and state thresholds (FMSY,  FMSY ranges and MSY Btrigger) are harvested sustainably and in the long term will deliver the largest possible catches under the prevailing environmental conditions. While pressure is directly manageable through implementation of management measures, the change in state is not wholly manageable. State changes are dependent on environmental conditions and predator-prey interactions and although conditions for recovery of stocks may be in place (i.e. through reductions in pressure), recovery time may still be extensive (many years).

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Relevance

Fish are an integral component of marine biodiversity. They are an important element of the food chain for seabirds, seals and cetaceans and are a source of food and employment for people. Sustainable fisheries will help to ensure marine ecosystems remain diverse and resilient and provide a long-term and viable fishing industry.

In 2004, the Royal Commission on Environmental Pollution advised significant and urgent action to avoid collapse of fisheries or harm to the marine environment. The assessments indicate an increase in the last five years in the percentage of fish stocks being harvested sustainably. However, substantial further improvements in stock status would be needed to ensure that all UK fish stocks are fished sustainably and attain biomass levels that maintain full reproductive capacity.

The Marine and Coastal Access Act was introduced in 2009 to ensure clean, healthy, safe, productive and biologically diverse oceans and seas. As a result, better systems for delivering sustainable development of marine and coastal environment are being put in place.

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Background

This UK indicator is based on a consistent set of 57 stocks since 1990. A ‘stock’ refers to a population of a species occurring in a defined sea area; a particular species may occur in multiple stocks in waters around the UK. The stocks represent a wide range of different stocks and fisheries including demersal roundfish (e.g. cod, haddock, saithe), flatfish (sole, plaice), pelagic fish (blue whiting and mackerel) and shellfish (Nephrops). Table B2i shows the species included. Many of these stocks are extremely valuable or have a high conservation profile. The indicator is intended to provide a relative trend over time. The indicator includes stocks with ‘unknown’ status if data are not adequate to allow estimation of historical biomass and fishing mortality, or for which ICES does not provide MSY reference points.

ICES classifies a stock’s status by comparing the quantity of mature fish (the spawning stock biomass) and the rate at which the stock is exploited (fishing mortality), in relation to agreed reference levels and/or ranges. The stock trends and reference levels are obtained from fishery and survey data from each zone. The UK indicator shows the percentage of the 57 stocks of UK interest that are at full reproductive capacity and harvested sustainably in each year.

Each year ICES updates the assessment of each stock with another year of commercial fishery (catch data) and scientific survey (abundance) data, or may revise an assessment to include new time-series of data or adopt an improved method of analysis. This can result in substantial changes to the trends in spawning stock biomass and rate of exploitation, causing changes to the historical values in the UK indicator series. On the basis of new evidence, ICES may also provide advice in relation to reference points for stocks for which the assessments were previously considered unreliable, or stop providing such advice for stocks for which the assessments or reference points are no longer considered reliable.

All stock data are derived from ICES advice and stock assessment working group reports.

Table B2i. Fish species and stocks included in this indicator

Species

List of Species

List of Species

Black-bellied anglerfish (Lophius budegassa)

Norway lobster (Nephrops norvegicus)

Blue whiting (Micromesistius poutasso)

Plaice (Pleuronectes platessa)

Cod (Gadus morhua

Pollack (Pollachius pollachius)

Haddock (Melanogrammus aeglefinus

Roundnose grenadier (Coryphaenoides rupestris)

Hake (Merluccius merluccius)

Saithe (Pollachius virens)

Herring (Clupea harengus)

Sole (Solea solea)

Horse mackerel (Trachurus trachurus)

Sprat (Sprattus sprattus)

Ling (Molva molva)

Spurdog (Squalus acanthias)

Mackerel (Scomber scombrus)

White anglerfish (Lophius piscatorius)

Megrim (Lepidorhombus whiffiagonis)

Whiting (Merlangius merlangus)

Stocks

Anglerfish (Lophius budegassaLophius piscatorius) in subareas 4 and 6. and Division 3.a (North Sea. Rockall and West of Scotland. Skagerrak and Kattegat)
Black-bellied anglerfish (Lophius budegassa) in divisions 7.b-k. 8.a-b. and 8.d (west and southwest of Ireland. Bay of Biscay)
Cod (Gadus morhua) in Subarea 4. Division 7.d. and Subdivision 20 (North Sea. eastern English Channel. Skagerrak)
Cod (Gadus morhua) in Division 6.a (West of Scotland)
Cod (Gadus morhua) in Division 6.b (Rockall)
Cod (Gadus morhua) in Division 7.a (Irish Sea)
Cod (Gadus morhua) in divisions 7.e-k (western English Channel and southern Celtic Seas)
Spurdog (Squalus acanthias) in subareas 1-10. 12 and 14 (the Northeast Atlantic and adjacent waters)
Haddock (Melanogrammus aeglefinus) in Subarea 4. Division 6.a. and Subdivision 20 (North Sea. West of Scotland. Skagerrak)
Haddock (Melanogrammus aeglefinus) in Division 6.b (Rockall)
Haddock (Melanogrammus aeglefinus) in Division 7.a (Irish Sea)
Haddock (Melanogrammus aeglefinus) in divisions 7.b-k (southern Celtic Seas and English Channel)
Herring (Clupea harengus) in subareas 1. 2. 5 and divisions 4.a and 14.a. Norwegian spring-spawning herring (the Northeast Atlantic and Arctic Ocean)
Herring (Clupea harengus) in Subarea 4 and divisions 3.a and 7.d. autumn spawners (North Sea. Skagerrak and Kattegat. eastern English Channel)
Herring (Clupea harengus) in divisions 6.a and 7.b-c (West of Scotland. West of Ireland)
Herring (Clupea harengus) in divisions 7.a South of 52°30’N, 7.g–h, and 7.j–k (Irish Sea, Celtic Sea, and southwest of Ireland)
Herring (Clupea harengus) in Division 7.a North of 52°30’N (Irish Sea)
Hake (Merluccius merluccius) in subareas 4. 6. and 7. and divisions 3.a. 8.a-b. and 8.d. Northern stock (Greater North Sea. Celtic Seas. and the northern Bay of Biscay)
Horse mackerel (Trachurus trachurus) in Subarea 8 and divisions 2.a. 4.a. 5.b. 6.a. 7.a-c.e-k (the Northeast Atlantic)
Megrim (Lepidorhombus spp.) in divisions 4.a and 6.a (northern North Sea. West of Scotland)
Megrim (Lepidorhombus spp.) in Division 6.b (Rockall)
Ling (Molva molva) in subareas 6-9. 12. and 14. and divisions 3.a and 4.a (Northeast Atlantic and Arctic Ocean)
Mackerel (Scomber scombrus) in subareas 1-8 and 14 and Division 9.a (the Northeast Atlantic and adjacent waters)
Megrim (Lepidorhombus whiffiagonis) in divisions 7.b-k. 8.a-b. and 8.d (west and southwest of Ireland. Bay of Biscay)
White anglerfish (Lophius piscatorius) in Subarea 7 and divisions 8.a-b and 8.d (Celtic Seas. Bay of Biscay)
Norway lobster (Nephrops norvegicus) in Division 6.a. Functional Unit 11 (West of Scotland. North Minch)
Norway lobster (Nephrops norvegicus) in Division 6.a. Functional Unit 12 (West of Scotland. South Minch)
Norway lobster (Nephrops norvegicus) in Division 6.a. Functional Unit 13 (West of Scotland. the Firth of Clyde and Sound of Jura)
Norway lobster (Nephrops norvegicus) in Division 7.a. Functional Unit 14 (Irish Sea. East)
Norway lobster (Nephrops norvegicus) in Division 7.a. Functional Unit 15 (Irish Sea. West)
Norway lobster (Nephrops norvegicus) in divisions 7.b-c and 7.j-k. Functional Unit 16 (west and southwest of Ireland. Porcupine Bank)
Norway lobster (Nephrops norvegicus) in divisions 4.b and 4.c. Functional Unit 5 (central and southern North Sea. Botney Cut-Silver Pit)
Norway lobster (Nephrops norvegicus) in Division 4.b. Functional Unit 6 (central North Sea. Farn Deeps)
Norway lobster (Nephrops norvegicus) in Division 4.a. Functional Unit 7 (northern North Sea. Fladen Ground)
Norway lobster (Nephrops norvegicus) in Division 4.b. Functional Unit 8 (central North Sea. Firth of Forth)
Norway lobster (Nephrops norvegicus) in Division 4.b. Functional Unit 9 (central North Sea. Moray Firth)
Plaice (Pleuronectes platessa) in Subarea 4 (North Sea) and Subdivision 20 (Skagerrak)
Plaice (Pleuronectes platessa) in Division 7.a (Irish Sea)
Plaice (Pleuronectes platessa) in Division 7.d (eastern English Channel)
Plaice (Pleuronectes platessa) in Division 7.e (western English Channel)
Plaice (Pleuronectes platessa) in divisions 7.f and 7.g (Bristol Channel. Celtic Sea)
Saithe (Pollachius virens) in subareas 4. 6 and Division 3.a (North Sea. Rockall and West of Scotland. Skagerrak and Kattegat)
Pollack (Pollachius pollachius) in subareas 6-7 (Celtic Seas and the English Channel)
Roundnose grenadier (Coryphaenoides rupestris) in subareas 6-7 and divisions 5.b and 12.b (Celtic Seas and the English Channel. Faroes grounds. and western Hatton Bank)
Sole (Solea solea) in Subarea 4 (North Sea)
Sole (Solea solea) in Division 7.a (Irish Sea)
Sole (Solea solea) in Division 7.d (eastern English Channel)
Sole (Solea solea) in Division 7.e (western English Channel)
Sole (Solea solea) in divisions 7.f and 7.g (Bristol Channel. Celtic Sea)
Sprat (Sprattus sprattus) in Subarea 4 (North Sea)
Sprat (Sprattus sprattus) in Subarea 6 and divisions 7.a-c and 7.f-k (West of Scotland. southern Celtic Seas)
Blue whiting (Micromesistius poutassou) in subareas 1-9. 12. and 14 (Northeast Atlantic and adjacent waters)
Whiting (Merlangius merlangus) in Subarea 4 and Division 7.d (North Sea and eastern English Channel)
Whiting (Merlangius merlangus) in Division 6.a (West of Scotland)
Whiting (Merlangius merlangus) in Division 6.b (Rockall)
Whiting (Merlangius merlangus) in Division 7.a (Irish Sea)
Whiting (Merlangius merlangus) in divisions 7.b-c and 7.e-k (southern Celtic Seas and eastern English Channel)

Source: Centre for Environment, Fisheries and Aquaculture Science (Cefas; see: https://moat.cefas.co.uk/pressures-from-human-activities/commercial-fish-and-shellfish/.)

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Goals and Targets

The UK and England Biodiversity Indicators are currently being assessed alongside the Environment Improvement Plan Targets, and the new Kunming-Montreal Global Biodiversity Framework Targets, when this work has been completed the references to Biodiversity 2020 and the Aichi Global Biodiversity Framework Targets will be updated.

Aichi Targets for which this is a primary indicator

Strategic Goal B. Reduce the direct pressures on biodiversity and promote sustainable use.

Aichi Target 6 iconTarget 6: By 2020, all fish and invertebrate stocks and aquatic plants are managed and harvested sustainably, legally and applying ecosystem based approaches, so that overfishing is avoided, recovery plans and measures are in place for all depleted species, fisheries have no significant adverse impacts on threatened species and vulnerable ecosystems and the impacts of fisheries on stocks, species and ecosystems are within safe ecological limits. 

Aichi Targets for which this is a relevant indicator

Strategic Goal A. Address the underlying causes of biodiversity loss by mainstreaming biodiversity across government and society.

Aichi Target 3 icon

Target 3: By 2020, at the latest, incentives, including subsidies, harmful to biodiversity are eliminated, phased out or reformed in order to minimize or avoid negative impacts, and positive incentives for the conservation and sustainable use of biodiversity are developed and applied, consistent and in harmony with the Convention and other relevant international obligations, taking into account national socio economic conditions.

Aichi Target 4 icon

Target 4: By 2020, at the latest, Governments, business and stakeholders at all levels have taken steps to achieve or have implemented plans for sustainable production and consumption and have kept the impacts of use of natural resources well within safe ecological limits.

Strategic Goal B. Reduce the direct pressures on biodiversity and promote sustainable use.

Aichi Target 7 icon

Target 7: By 2020 areas under agriculture, aquaculture and forestry are managed sustainably, ensuring conservation of biodiversity.

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Full details of this indicator and its supporting data are available here:
https://moat.cefas.co.uk/pressures-from-human-activities/commercial-fish-and-shellfish/fishing-pressure/

https://moat.cefas.co.uk/pressures-from-human-activities/commercial-fish-and-shellfish/reproductive-capacity/

Lynam, C., Allison, C., Ribeiro, J., Campon-Linares, V., Garnacho E. (2022) International (ICES) and national UK fish stocks and shellfish data from 2020 assessment year. https://doi.org/10.14466/CefasDataHub.130

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Downloads

Download the Datasheet and Technical background document from JNCC's Resource Hub.

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Last updated: November 2023

Latest data available:

Percentage of marine fish (quota) stocks of UK interest harvested sustainably – 2020;

Percentage of marine fish (quota) stocks of UK interest with biomass at levels that maintain full reproductive capacity – 2020.

 

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Categories:

UK Biodiversity Indicators 2023

Published: .

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