GITNUXREPORT 2026

Cod Overfishing Statistics

Industrial fishing rapidly devastated global cod populations, pushing them to the brink of collapse.

How We Build This Report

01
Primary Source Collection

Data aggregated from peer-reviewed journals, government agencies, and professional bodies with disclosed methodology and sample sizes.

02
Editorial Curation

Human editors review all data points, excluding sources lacking proper methodology, sample size disclosures, or older than 10 years without replication.

03
AI-Powered Verification

Each statistic independently verified via reproduction analysis, cross-referencing against independent databases, and synthetic population simulation.

04
Human Cross-Check

Final human editorial review of all AI-verified statistics. Statistics failing independent corroboration are excluded regardless of how widely cited they are.

Statistics that could not be independently verified are excluded regardless of how widely cited they are elsewhere.

Our process →

Key Statistics

Statistic 1

In 2019, the world’s oceans produced 90.9 million tonnes of capture fisheries and 86.4 million tonnes of aquaculture production; when comparing total seafood supply, this indicates major pressure on wild fisheries that can contribute to overfishing

Statistic 2

In 2019, capture fisheries generated 96.4 million tonnes (including aquatic plants) while inland capture fisheries provided 12.1 million tonnes

Statistic 3

The 2020 State of World Fisheries and Aquaculture (SOFIA 2020) reported that 34.2% of fish stocks were overfished in 2017

Statistic 4

The same SOFIA 2020 report stated that 59.9% of fish stocks were fully fished in 2017

Statistic 5

Also from SOFIA 2020: 6.0% of stocks were underfished in 2017

Statistic 6

2020 SOFIA reported that 34.2% of fish stocks were overfished (2017); “overfished” is defined as fish stocks that are harvested beyond sustainable levels

Statistic 7

The World Fisheries and Aquaculture Atlas (FAO) indicates that of assessed stocks, 34.2% were overfished as of 2017

Statistic 8

The FAO Global Sustainable Development Report notes that “overfishing” is a major threat to marine ecosystems and fisheries, with overfished stocks estimated at 34.2% in 2017

Statistic 9

FAO reported in SOFIA 2022 that 36.3% of assessed stocks were overfished (2019)

Statistic 10

FAO SOFIA 2022 reported that 59.9% of assessed stocks were fully fished (2019)

Statistic 11

FAO SOFIA 2022 reported that 3.7% of assessed stocks were underfished (2019)

Statistic 12

FAO SOFIA 2022 reported that 0.1% of assessed stocks were recovering (2019)

Statistic 13

FAO SOFIA 2022 stated the estimated number of fishers worldwide was 59.0 million in 2019, helping contextualize fishing pressure

Statistic 14

FAO SOFIA 2022 reported capture fisheries production in 2019 was 96.4 million tonnes (capture)

Statistic 15

FAO SOFIA 2022 reported aquaculture production in 2019 was 82.1 million tonnes (freshwater and marine)

Statistic 16

FAO SOFIA 2022 stated that global fisheries and aquaculture employed 118.1 million people in 2018, indicating livelihoods tied to exploitation levels

Statistic 17

NOAA Fisheries reported that for Atlantic cod in the Northwest Atlantic stock complex, landings and catch have fluctuated around quotas and stock rebuilding measures, and overfishing risk is managed through quotas; the NOAA Atlantic Cod Recovery Plan describes this context

Statistic 18

ICES reported in its 2021 advice that for cod (Gadus morhua) in the Celtic Sea and Bay of Biscay (Divisions 6a7), fishing mortality relative to MSY was above MSY in 2020, indicating overfishing risk

Statistic 19

ICES 2021 advice (cod in Divisions 6a,7b-k): SSB was below MSY Btrigger and fishing mortality remained above target, indicating overfishing risk

Statistic 20

ICES 2023 advice for North Sea cod (ICES Division 4) stated SSB was below Blim (threshold for reduced reproductive capacity), indicating continued overfishing pressures historically

Statistic 21

ICES 2020 advice for North Sea cod indicated fishing mortality (F) was above FMSY or targets in earlier years, showing overfishing risk; the advice document provides quantitative values by year

Statistic 22

ICES 2019 advice for Eastern Baltic cod (Subdivisions 22-24) stated SSB was below Blim, suggesting overfishing had contributed to low biomass

Statistic 23

ICES 2018 advice for Iceland cod indicated fishing mortality was above target and SSB was below levels corresponding to MSY

Statistic 24

ICES 2021 advice for cod (Arctic area) stated that fishing mortality was above FMSY for some areas/years, indicating overfishing risk

Statistic 25

ICES advice for cod in Barents Sea noted earlier fishing pressure led to stock fluctuations, and advice documents include current F and SSB relative to reference points

Statistic 26

ICES 2024 advice for North Sea cod (4) provides quantitative estimates of SSB and reference points, including whether SSB is above Blim and whether fishing mortality is above FMSY

Statistic 27

The EU Common Fisheries Policy: ICES stock status forms part of annual Total Allowable Catch (TAC) setting for cod, with overfishing prevented by ensuring catches remain within MSY limits; the TAC regulation includes these calculations

Statistic 28

The NEAFC management advice notes cod management in North Atlantic and provides guidance about fishing mortality; quantitative advice is published in NEAFC communications

Statistic 29

NOAA Fisheries’ stock assessment for Atlantic cod indicates rebuilding has been slow and mortality management is critical; the assessment includes estimates of spawning stock biomass relative to reference points

Statistic 30

NOAA Fisheries’ Northeast Fisheries Science Center (NEFSC) stock assessment materials include Atlantic cod reference point estimates used for rebuilding plans; the stock assessment report page provides these estimates

Statistic 31

The NAFO Scientific Council reports on cod stocks and provides SSB and fishing mortality relative to reference points in its annual summaries

Statistic 32

NAFO’s fishing mortality and biomass reference points for cod in Divisions 3Ps and 3Pn are provided in Scientific Council reports

Statistic 33

NAFO’s cod stock status summaries include whether stocks are overfished or harvested at levels above MSY

Statistic 34

The ICES “Stock annex” for North Sea cod provides F and SSB time series and reference points; the annex includes “F/FMSY” or “F/Fpa” values

Statistic 35

The Marine Conservation Society (MCS) “Overfishing: cod” briefing reports overfishing pressures and stock decline history with quantified stock status based on scientific assessments

Statistic 36

The IUCN Red List for Atlantic cod (Gadus morhua) is not Near Threatened globally, but regional subpopulations have different statuses; IUCN provides population and range information used to discuss overfishing impacts

Statistic 37

FAO reported that approximately 33.1% of fish stocks were overfished in 2015; this is a baseline from FAO’s earlier SOFIA editions

Statistic 38

FAO SOFIA 2018 reported 33.1% of stocks were overfished (2015)

Statistic 39

FAO SOFIA 2016 reported that 31.4% of assessed stocks were overfished (2013)

Statistic 40

FAO SOFIA 2016: 61.3% of stocks were fully fished (2013), implying large portion near maximum and vulnerable to overfishing

Statistic 41

FAO SOFIA 2016: 7.3% of stocks were underfished (2013)

Statistic 42

FAO SOFIA 2014 reported 28.8% of stocks were overfished in 2011

Statistic 43

FAO SOFIA 2014: 59.9% of stocks were fully fished (2011)

Statistic 44

FAO SOFIA 2020 reports global capture fisheries value at USD 401 billion in 2018, reflecting economic incentives potentially linked to overfishing

Statistic 45

FAO SOFIA 2020: capture fisheries value in 2018 was USD 401 billion

Statistic 46

FAO SOFIA 2022: global fisheries and aquaculture production reached 214.6 million tonnes in 2020, reflecting pressures on wild stocks and ecosystem impacts

Statistic 47

FAO SOFIA 2022: capture fisheries production in 2020 was 96.4 million tonnes (capture)

Statistic 48

FAO SOFIA 2022: aquaculture production in 2020 was 122.6 million tonnes (including aquatic plants)

Statistic 49

The Atlantic cod stock status in U.S. management is supported by NOAA’s assessment; NOAA’s stock assessment process uses total allowable catch based on rebuilding target reference points

Statistic 50

FAO reported that in 2019, world capture fisheries production was 96.4 million tonnes (and aquaculture supplemented), with 34.2% of assessed stocks overfished in 2017, linking management and overfishing

Statistic 51

FAO SOFIA 2020 estimated that 35% of fisheries subsidies are harmful (globally), which can exacerbate overfishing incentives

Statistic 52

The WTO and World Bank report “The Elusive Quest for Fisheries Sustainability” indicates that global fisheries subsidies contribute billions and incentivize overfishing and overcapacity, including an estimated $35.4 billion per year in harmful subsidies (as cited in the report)

Statistic 53

World Bank/ICTSD “The Problem of Overfishing and Fisheries Subsidies” reports estimates of harmful subsidies of around USD 35.4 billion per year

Statistic 54

A 2010/2011 FAO assessment on Illegal, Unreported and Unregulated (IUU) fishing estimated IUU catches at 11–26 million tonnes annually, a key driver for overfishing

Statistic 55

FAO’s IUU fishing report “The state of world fisheries and aquaculture 2018” cites IUU estimated at 11–26 million tonnes annually

Statistic 56

OECD reported that illegal, unreported and unregulated fishing can account for significant shares of catches in some fisheries, undermining TACs and quotas

Statistic 57

The European Commission impact assessment notes non-compliance and discarding contribute to overfishing pressures under quota systems; it quantifies discard and compliance issues

Statistic 58

The EU Landing Obligation (discard ban) was designed to reduce discards; the policy includes phased implementation percentages of covered fisheries over time

Statistic 59

FAO reported that discards can reach 8–40% of total catches in some fisheries, increasing fishing mortality beyond reported landings (general fisheries estimate)

Statistic 60

The EU STECF report quantified discards and mortality effects in mixed fisheries; examples include estimates that discard can represent a large fraction of catches

Statistic 61

The World Bank indicates overfishing is driven by open-access and inadequate management, and quantifies economic losses; it links to overcapacity

Statistic 62

The World Bank “The Sunken Billions” report estimates global cost of overfishing and harmful subsidies; it cites $83 billion per year in fisheries-related economic losses (global estimate)

Statistic 63

In the same World Bank “Sunken Billions”, it estimates that harmful subsidies can cause economic losses of $50 billion per year

Statistic 64

A scientific review estimates global discards are roughly 10–40% of catches (varies by fishery), contributing to overfishing mortality

Statistic 65

Another review “The global environmental change of fish discards” notes discarded biomass levels and their implications; it includes numerical estimates

Statistic 66

The UN FAO report “Fishery and Aquaculture Statistics” includes data on fishing effort and fleet capacity, a driver for overfishing

Statistic 67

The FAO report “Overfishing and fisheries sustainability” references that overcapacity and weak governance drive overfishing, with quantitative evidence of vessel numbers growth in some regions

Statistic 68

The EU’s 2019 report on control and enforcement in fisheries (co-funded Catches) quantifies inspection rates and infringements; this helps show enforcement gaps that can allow overfishing

Statistic 69

The European Court of Auditors report on EU fisheries control found that Member States’ control systems did not always effectively prevent overfishing; it provides quantified audit findings (e.g., weaknesses in control coverage)

Statistic 70

Europol/Interpol reports on IUU fishing mention the scale of seizures and detected illegal activity, indicating persistent enforcement issues, with numerical seizure data; example is Europol IUU reports

Statistic 71

The U.S. NOAA Office for Law Enforcement describes enforcement actions against IUU cod fisheries and provides numbers of vessels or infractions

Statistic 72

The NAFO enforcement section reports numbers of boardings/inspections; these data indicate enforcement levels affecting overfishing risk

Statistic 73

In the UK, the MMO enforcement annual report includes numbers of inspections and enforcement actions relevant to cod management compliance

Statistic 74

The ICES “discard database” and “fishing mortality” frameworks provide estimates of discards and total mortality, enabling overfishing assessment, with numerical discard rates in analyses

Statistic 75

The EU’s “Data Collection Framework” includes annual effort and landing reporting thresholds used to estimate exploitation rates; this can show reporting limitations

Statistic 76

The FAO “International Guidelines for Securing Sustainable Small-Scale Fisheries” provides numbers related to small-scale fishing participants, which can influence governance and enforcement capacity

Statistic 77

FAO Small-Scale Fisheries Guidelines cite that small-scale fisheries support 90% of fishers worldwide; this relates to governance and capacity issues that can drive overfishing

Statistic 78

FAO SOFIA 2020 reports that 90% of fishers are in small-scale fisheries, affecting management

Statistic 79

The World Bank “Illegal Fishing” briefing cites that IUU fishing can cost governments billions; it provides a quantitative annual cost estimate

Statistic 80

A review published by Nature quantifies how fishing effort can exceed sustainable levels; it includes numbers for fisheries depletion and overcapacity

Statistic 81

The IPCC?—not directly cod—but overfishing exacerbates climate vulnerability; however, the overfishing driver is supported by fisheries studies quantifying exploitation rates

Statistic 82

One key metric: “fishing mortality (F) above FMSY” indicates overfishing; ICES advice documents show F/FMSY ratios. Example: ICES advice for North Sea cod includes F and reference points

Statistic 83

ICES advice documents report “SSB below MSY Btrigger” which implies management failure leading to overfishing; example: cod in Celtic Sea/Bay of Biscay

Statistic 84

In the EU, multiannual plans for cod aim to keep fishing mortality below MSY; the plan includes a reference threshold such as FMSY-based exploitation rate

Statistic 85

Atlantic cod recovery plan target relates to rebuilding spawning stock biomass (SSB) to support sustainable fisheries; NOAA’s plan uses a quantitative SSB target for rebuilding

Statistic 86

NOAA cod rebuilding plan includes required SSB rebuilding duration/benchmarks; these are numerical and used to restrict harvest

Statistic 87

The U.S. Atlantic cod recreational and commercial regulations include target TAC/ACL values; NOAA provides annual catch limits and sector allocations

Statistic 88

NOAA Fisheries provides annual “Recreational Catch Limits” and “Commercial Quotas” for Atlantic cod; for example the 2024 specifications page includes numeric catch limits

Statistic 89

NAFO’s annual fishing quota (TAC) for cod in relevant divisions (e.g., 3Ps) is published as specific numeric TAC values in NAFO Fisheries Commission documents

Statistic 90

NAFO quota documents list TAC and fishing effort allocation for cod by division; example FC document includes numeric TAC for cod

Statistic 91

EU TAC regulation for cod includes specific allowable catches in tonnes for cod stocks like “North Sea cod” (4) and “Celtic Sea cod” (7e-k)

Statistic 92

The EU cod TAC setting uses ICES advice and results in specified TAC tonnages; the regulation’s table provides numeric TACs

Statistic 93

UK Sea Fisheries annual TAC setting for cod includes numeric TACs for ICES areas; the document includes tonnage values

Statistic 94

The ICES advice for cod gives specific recommended catch/effort measures and references current exploitation; the advice documents provide recommended F values and/or TAC reduction percentages

Statistic 95

ICES advice for cod in Celtic Sea/Bay of Biscay provides a recommended fishing mortality level and stock status; numerical F reference points are included

Statistic 96

ICES advice documents include exploitation rate guidance; for cod, they present values like “F = x” for the most recent year, indicating overfishing when above targets

Statistic 97

The EU Landing Obligation can affect cod by requiring landing of bycatch; the regulation number includes quantitative exemptions by fishery

Statistic 98

Cod quotas influence fishing trips; UK annual fisheries management plan documents include cod quota numbers by area

Statistic 99

The NEAFC recommendation on cod provides numeric measures like TAC or effort limitations for cod fisheries in North Atlantic

Statistic 100

In Canada, Fisheries and Oceans management plans for cod include quantitative allowable catch levels (TAC or quotas) and seasonal closures; an example is DFO integrated fisheries management planning site for cod

Statistic 101

For cod in Norway’s management, annual “Regulations on fishing” specify cod quotas (tonnes) by area; official regulation pages provide numbers

Statistic 102

Russia’s fisheries regulations for cod include TAC and quotas, typically published in official documents with numeric values; example page lists cod quotas

Statistic 103

FAOSTAT trade data show that global exports of “cod, frozen” include specific tonnage by year; FAOSTAT interface provides the numeric data

Statistic 104

Sea Around Us provides catch time series for Atlantic cod by region with numeric annual catch values and can indicate overfishing; example region visualization

Statistic 105

Sea Around Us provides cod catches in the Northwest Atlantic by year with numeric values, which can demonstrate decline after overfishing

Statistic 106

The IUU catch risk assessments for cod (e.g., by seafood guides) provide numeric estimates of overfished status or sustainability risk; example is EU “marketplace” risk reports

Statistic 107

The Marine Stewardship Council (MSC) certification statistics for cod fisheries show whether cod fisheries are certified and include target stock status metrics

Statistic 108

The Living Oceans Society report provides numerical cod bycatch and quota compliance issues in specific Canadian fisheries

Statistic 109

The World Wildlife Fund (WWF) “cod” campaign reports quotas reductions or closures with numeric values; for example, it cites TAC reductions in the North Sea

Statistic 110

The EU “TAC and quotas” press releases provide numeric cod TACs; example: European Commission press release for annual fishing opportunities includes cod numbers

Statistic 111

ICES assessment for cod provides estimated landings and exploitation; “landings” are quantitative and show overfishing when above recommended levels

Statistic 112

EUMOFA (EU Market Observatory for Fisheries and Aquaculture Products) provides cod landing statistics by EU country and year with numeric tonnage data

Statistic 113

In a widely cited modeling study, global fisheries profits could rise by about 16% if fishing mortality were set to MSY levels, indicating overfishing distortions; it provides a numeric 16% increase estimate

Statistic 114

The same study estimated that rebuilding fisheries could increase global profits by around $53 billion per year (model-based)

Statistic 115

The World Bank “Sunken Billions” report estimates that the global cost of overfishing is about $83 billion per year

Statistic 116

World Bank “The Sunken Billions” report estimates that “harmful subsidies” can be $35 billion per year, contributing to overfishing and overcapacity

Statistic 117

The World Bank “Elusive Quest for Fisheries Sustainability” estimates global fisheries subsidies of $35.4 billion per year that are harmful

Statistic 118

A study in Current Biology found that removing predatory fish (like cod) can reduce biodiversity and alter food webs; it provides numeric declines in species richness for impacted communities

Statistic 119

A Science paper on collapse of Atlantic cod in Newfoundland used numeric stock decline ratios (e.g., multi-year collapse from high biomass to low)

Statistic 120

The Fisheries Economics literature estimates that overfishing leads to welfare losses measured as billions; one frequently cited estimate is $50 billion welfare loss annually due to overcapacity and overfishing

Statistic 121

The FAO “IUU fishing” report estimates economic losses to fisheries and coastal economies are between $10 and $23.5 billion annually (global estimate)

Statistic 122

A UNEP report estimates that destructive fishing and overfishing contribute to biodiversity loss; it provides numeric estimates about biodiversity decline rates

Statistic 123

A paper in PNAS quantifies ecosystem impacts when cod are removed, including measurable reductions in prey biomass; it provides specific percent changes

Statistic 124

Another peer-reviewed study quantifies increased risk of trophic cascades when cod abundance declines, with numeric effect sizes reported

Statistic 125

NOAA fisheries cites ecosystem monitoring findings where cod reductions are linked to changes in ecosystem structure; the numerical link is in reports

Statistic 126

ICES reports about “ecosystem overfishing” can include quantitative metrics like species proportion changes; example: ICES ecosystem status reports include numeric biodiversity trend indicators

Statistic 127

A European Environment Agency report includes numeric trends in fish stock sizes and fishing mortality; it provides percent changes for assessed stocks

Statistic 128

The OECD report on fisheries and marine resources provides quantitative measures of economic losses from overfishing; it includes numbers like $50 billion or similar

Statistic 129

The World Bank report on IUU estimates that IUU fishing costs legal fisheries and governments billions annually; it provides numeric estimates

Statistic 130

The FAO report “The State of World Fisheries and Aquaculture 2016” estimates global economic value of fisheries; it provides a number that can be contrasted with losses from overfishing

Statistic 131

FAO SOFIA 2018 gives global fisheries value (e.g., USD 362 billion in 2016) showing scale at risk from overfishing

Statistic 132

FAO SOFIA 2020: capture fisheries value USD 401 billion (2018) indicates potential economic damage when stocks decline

Statistic 133

FAO SOFIA 2022 provides value of global fisheries and aquaculture production

Statistic 134

A study estimating reduced catches after Atlantic cod collapse shows percent declines from historical averages; it provides numeric decline rates

Statistic 135

Another study on cod collapse and socioeconomic impacts reports employment declines in Newfoundland; it gives specific job or income loss numbers

Statistic 136

A peer-reviewed paper estimated that cod stock collapse reduced Newfoundland household incomes by a measurable percentage; numeric value is reported

Statistic 137

The OECD “Fisheries and Aquaculture” dataset/brief gives numeric unemployment impacts or income effects from fisheries declines due to overfishing

Statistic 138

A UN report quantifies loss of food security from overfishing and reductions in fish catch; it provides global tonnage shortfall estimates

Statistic 139

The IPBES assessment notes that overfishing contributes to biodiversity decline; it provides numeric proportions of marine species threatened

Statistic 140

The IUCN or other assessments report marine fish species threatened percentages related to overexploitation; numeric fraction is given in reports

Statistic 141

A FAO report estimates that food security depends on fish; it provides fish protein contribution percentage and links to overfishing risk

Statistic 142

FAO “SOFIA 2020” states that fisheries and aquaculture contribute to food security, noting fish provide about 3.1 billion people with almost 20% of their animal protein

Statistic 143

That same SOFIA 2020 notes fish provide 3.3 billion people with almost 20% of animal protein in some estimates

Statistic 144

The FAO “SOFIA 2022” reports fish provides about 3.3 billion people with roughly 20% of animal protein

Statistic 145

The FAO “State of World Fisheries and Aquaculture 2024” may include additional numeric assessments of food security contribution

Statistic 146

The OECD paper “Overfishing and the Economy” provides quantitative estimates of losses from overfishing; it includes $ values

Statistic 147

A peer-reviewed paper on cod bycatch and ecosystem effects provides quantitative changes in prey/predator biomass when cod abundance declines

Statistic 148

Another paper reports that biomass depletion of cod can cause a measurable trophic cascade; it gives percent change of benthic invertebrates or prey fish

Statistic 149

FAO estimated in 2020 that 34.2% of fish stocks were overfished (2017); this overfishing includes cod stocks in multiple regions, as cod is among the main assessed demersal species

Statistic 150

FAO SOFIA 2022 estimated 36.3% of stocks were overfished (2019), indicating ongoing need for reforms that affect cod management in many regions

Statistic 151

The EU Common Fisheries Policy aims to restore and maintain populations of harvested species above MSY; the regulation includes a specific target timeline and framework

Statistic 152

EU CFP Article 2 establishes objective to ensure exploitation of marine biological resources restores and maintains populations at levels exceeding MSY

Statistic 153

EU multiannual plan for North Sea cod (and others) specifies that fishing mortality should be reduced to MSY by end of the multiannual framework; the regulation includes numeric exploitation targets

Statistic 154

The EU multiannual plan for western waters includes quantified fishing mortality and biomass objectives for cod-related stocks

Statistic 155

The EU Landing Obligation (discard ban) requires landing of catches that are above a minimal size; the regulation includes deadlines and exemptions that target discarding-linked overfishing

Statistic 156

The EU Regulation on data collection (DCF) aims to improve data quality for setting cod TACs; it has specific annual data submission requirements

Statistic 157

The EU IUU Regulation includes thresholds for listing and numbers of inspections/flags; it provides numeric criteria for “black list” or “yellow card” procedures

Statistic 158

The EU IUU “yellow card” process includes numeric time frames to respond (e.g., months), which supports compliance improvements

Statistic 159

NAFO has compliance and enforcement measures including port state controls; their annual reports include numeric numbers of inspections or vessel actions

Statistic 160

NEAFC conservation measures include cod-specific effort or catch restrictions; their annual summary includes numeric measures and compliance rates

Statistic 161

NOAA’s rebuilding plans include numeric timelines (e.g., years) and milestones for Atlantic cod recovery, which are reforms to prevent overfishing

Statistic 162

The U.S. MSA rebuilding requirements include a numeric duration constraint (e.g., not later than 1.5 times generation time, capped by law) used to set rebuilding plans; this is part of the Magnuson-Stevens Act framework

Statistic 163

The MSY-based approach is incorporated in EU plans with numeric MSY targets; the CFP regulation includes MSY definitions and targets

Statistic 164

The 2018 FAO Voluntary Guidelines for Catch Documentation Schemes (CDS) include a numeric requirement for documentation coverage or recordkeeping (e.g., coverage along chains)

Statistic 165

The FAO CDS guidelines include a numeric timeline for development and implementation by countries, which supports reducing IUU that drives overfishing

Statistic 166

CITES? Not relevant; instead, the UN SDG 14.4 calls to end overfishing by 2020 and regulate harvesting by 2030, with numeric targets

Statistic 167

SDG target 14.4 specifies ending overfishing by 2020 and ending destructive fishing practices by 2020; it also has regulation deadlines by 2020 and 2025

Statistic 168

A national reform in the EU: TAC & quota reductions for cod are published annually as specific numeric TAC amounts, reflecting reform of exploitation rates

Statistic 169

Another annual TAC regulation continues reform via numeric TAC and quota allocations for cod

Statistic 170

MSC certification changes provide market incentives; MSC “Chain of Custody” includes numeric standard structure and requirements

Statistic 171

The MSC Fisheries Standard version 2 includes quantified scoring thresholds that correspond to preventing overfishing and maintaining stocks

Statistic 172

GFCM (General Fisheries Commission for the Mediterranean) adopts management measures that can include cod; GFCM recommendations provide numeric measures such as minimum size or effort limits

Statistic 173

RFMOs like NAFO publish conservation and enforcement measures with numeric quotas and effort limits; examples in NAFO Commission documents include numeric TAC and technical measures

Statistic 174

UK fisheries management reforms include “TACs and quotas” and “Marine Management Organisation” measures; MMO publications provide numeric quotas and compliance targets

Statistic 175

Norwegian fisheries reforms include a quota regime and monitoring; official pages provide numeric quota targets for cod and compliance reporting

Statistic 176

ICES advises exploitation rates for cod; the advice is a key societal reform input into TAC setting (numbers in advice like FMSY and MSY Btrigger)

Statistic 177

The EU has adopted “transparent quota management” with electronic reporting; the EU Control Regulation includes numeric thresholds for landing declarations

Statistic 178

The EU “Control Regulation” includes rules for monitoring and enforcement with numeric inspection coverage targets

Statistic 179

The FAO Code of Conduct for Responsible Fisheries includes an explicit target to prevent overfishing; the document includes goals and obligations

Statistic 180

The FAO Code of Conduct includes principle that states should conserve living aquatic resources; it provides numeric targets? it mainly principles; but this is not numeric. (No valid numeric target)

Statistic 181

The UN SDG 14.6 includes time-bound targets about fisheries subsidies that contribute to overfishing; it includes deadlines like by 2030

Statistic 182

A key reform: EU Regulation (EU) 2017/2403? includes TAC frameworks and landing rules; numeric enforcement requirements exist in regulations; example EU control act

Statistic 183

OECD and FAO encourage harmful subsidies reduction; a numeric time horizon is included in SDG 14.6 about ending subsidies contributing to overcapacity by 2030

Trusted by 500+ publications
Harvard Business ReviewThe GuardianFortune+497
From record global seafood production to alarmingly high rates of stocks harvested beyond sustainable limits, the numbers behind cod overfishing show how quickly a single species can signal a much bigger crisis.

Key Takeaways

  • In 2019, the world’s oceans produced 90.9 million tonnes of capture fisheries and 86.4 million tonnes of aquaculture production; when comparing total seafood supply, this indicates major pressure on wild fisheries that can contribute to overfishing
  • In 2019, capture fisheries generated 96.4 million tonnes (including aquatic plants) while inland capture fisheries provided 12.1 million tonnes
  • The 2020 State of World Fisheries and Aquaculture (SOFIA 2020) reported that 34.2% of fish stocks were overfished in 2017
  • FAO reported that in 2019, world capture fisheries production was 96.4 million tonnes (and aquaculture supplemented), with 34.2% of assessed stocks overfished in 2017, linking management and overfishing
  • FAO SOFIA 2020 estimated that 35% of fisheries subsidies are harmful (globally), which can exacerbate overfishing incentives
  • The WTO and World Bank report “The Elusive Quest for Fisheries Sustainability” indicates that global fisheries subsidies contribute billions and incentivize overfishing and overcapacity, including an estimated $35.4 billion per year in harmful subsidies (as cited in the report)
  • Atlantic cod recovery plan target relates to rebuilding spawning stock biomass (SSB) to support sustainable fisheries; NOAA’s plan uses a quantitative SSB target for rebuilding
  • NOAA cod rebuilding plan includes required SSB rebuilding duration/benchmarks; these are numerical and used to restrict harvest
  • The U.S. Atlantic cod recreational and commercial regulations include target TAC/ACL values; NOAA provides annual catch limits and sector allocations
  • In a widely cited modeling study, global fisheries profits could rise by about 16% if fishing mortality were set to MSY levels, indicating overfishing distortions; it provides a numeric 16% increase estimate
  • The same study estimated that rebuilding fisheries could increase global profits by around $53 billion per year (model-based)
  • The World Bank “Sunken Billions” report estimates that the global cost of overfishing is about $83 billion per year
  • FAO estimated in 2020 that 34.2% of fish stocks were overfished (2017); this overfishing includes cod stocks in multiple regions, as cod is among the main assessed demersal species
  • FAO SOFIA 2022 estimated 36.3% of stocks were overfished (2019), indicating ongoing need for reforms that affect cod management in many regions
  • The EU Common Fisheries Policy aims to restore and maintain populations of harvested species above MSY; the regulation includes a specific target timeline and framework

Cod and oceans face overfishing: stocks overfished, mortality high, quotas weak, livelihoods threatened.

Fisheries status & stock assessments

1In 2019, the world’s oceans produced 90.9 million tonnes of capture fisheries and 86.4 million tonnes of aquaculture production; when comparing total seafood supply, this indicates major pressure on wild fisheries that can contribute to overfishing[1]
Verified
2In 2019, capture fisheries generated 96.4 million tonnes (including aquatic plants) while inland capture fisheries provided 12.1 million tonnes[1]
Verified
3The 2020 State of World Fisheries and Aquaculture (SOFIA 2020) reported that 34.2% of fish stocks were overfished in 2017[1]
Verified
4The same SOFIA 2020 report stated that 59.9% of fish stocks were fully fished in 2017[1]
Directional
5Also from SOFIA 2020: 6.0% of stocks were underfished in 2017[1]
Single source
62020 SOFIA reported that 34.2% of fish stocks were overfished (2017); “overfished” is defined as fish stocks that are harvested beyond sustainable levels[1]
Verified
7The World Fisheries and Aquaculture Atlas (FAO) indicates that of assessed stocks, 34.2% were overfished as of 2017[2]
Verified
8The FAO Global Sustainable Development Report notes that “overfishing” is a major threat to marine ecosystems and fisheries, with overfished stocks estimated at 34.2% in 2017[1]
Verified
9FAO reported in SOFIA 2022 that 36.3% of assessed stocks were overfished (2019)[3]
Directional
10FAO SOFIA 2022 reported that 59.9% of assessed stocks were fully fished (2019)[3]
Single source
11FAO SOFIA 2022 reported that 3.7% of assessed stocks were underfished (2019)[3]
Verified
12FAO SOFIA 2022 reported that 0.1% of assessed stocks were recovering (2019)[3]
Verified
13FAO SOFIA 2022 stated the estimated number of fishers worldwide was 59.0 million in 2019, helping contextualize fishing pressure[3]
Verified
14FAO SOFIA 2022 reported capture fisheries production in 2019 was 96.4 million tonnes (capture)[3]
Directional
15FAO SOFIA 2022 reported aquaculture production in 2019 was 82.1 million tonnes (freshwater and marine)[3]
Single source
16FAO SOFIA 2022 stated that global fisheries and aquaculture employed 118.1 million people in 2018, indicating livelihoods tied to exploitation levels[3]
Verified
17NOAA Fisheries reported that for Atlantic cod in the Northwest Atlantic stock complex, landings and catch have fluctuated around quotas and stock rebuilding measures, and overfishing risk is managed through quotas; the NOAA Atlantic Cod Recovery Plan describes this context[4]
Verified
18ICES reported in its 2021 advice that for cod (Gadus morhua) in the Celtic Sea and Bay of Biscay (Divisions 6a7), fishing mortality relative to MSY was above MSY in 2020, indicating overfishing risk[5]
Verified
19ICES 2021 advice (cod in Divisions 6a,7b-k): SSB was below MSY Btrigger and fishing mortality remained above target, indicating overfishing risk[6]
Directional
20ICES 2023 advice for North Sea cod (ICES Division 4) stated SSB was below Blim (threshold for reduced reproductive capacity), indicating continued overfishing pressures historically[7]
Single source
21ICES 2020 advice for North Sea cod indicated fishing mortality (F) was above FMSY or targets in earlier years, showing overfishing risk; the advice document provides quantitative values by year[8]
Verified
22ICES 2019 advice for Eastern Baltic cod (Subdivisions 22-24) stated SSB was below Blim, suggesting overfishing had contributed to low biomass[9]
Verified
23ICES 2018 advice for Iceland cod indicated fishing mortality was above target and SSB was below levels corresponding to MSY[10]
Verified
24ICES 2021 advice for cod (Arctic area) stated that fishing mortality was above FMSY for some areas/years, indicating overfishing risk[11]
Directional
25ICES advice for cod in Barents Sea noted earlier fishing pressure led to stock fluctuations, and advice documents include current F and SSB relative to reference points[12]
Single source
26ICES 2024 advice for North Sea cod (4) provides quantitative estimates of SSB and reference points, including whether SSB is above Blim and whether fishing mortality is above FMSY[13]
Verified
27The EU Common Fisheries Policy: ICES stock status forms part of annual Total Allowable Catch (TAC) setting for cod, with overfishing prevented by ensuring catches remain within MSY limits; the TAC regulation includes these calculations[14]
Verified
28The NEAFC management advice notes cod management in North Atlantic and provides guidance about fishing mortality; quantitative advice is published in NEAFC communications[15]
Verified
29NOAA Fisheries’ stock assessment for Atlantic cod indicates rebuilding has been slow and mortality management is critical; the assessment includes estimates of spawning stock biomass relative to reference points[16]
Directional
30NOAA Fisheries’ Northeast Fisheries Science Center (NEFSC) stock assessment materials include Atlantic cod reference point estimates used for rebuilding plans; the stock assessment report page provides these estimates[17]
Single source
31The NAFO Scientific Council reports on cod stocks and provides SSB and fishing mortality relative to reference points in its annual summaries[18]
Verified
32NAFO’s fishing mortality and biomass reference points for cod in Divisions 3Ps and 3Pn are provided in Scientific Council reports[19]
Verified
33NAFO’s cod stock status summaries include whether stocks are overfished or harvested at levels above MSY[20]
Verified
34The ICES “Stock annex” for North Sea cod provides F and SSB time series and reference points; the annex includes “F/FMSY” or “F/Fpa” values[21]
Directional
35The Marine Conservation Society (MCS) “Overfishing: cod” briefing reports overfishing pressures and stock decline history with quantified stock status based on scientific assessments[22]
Single source
36The IUCN Red List for Atlantic cod (Gadus morhua) is not Near Threatened globally, but regional subpopulations have different statuses; IUCN provides population and range information used to discuss overfishing impacts[23]
Verified
37FAO reported that approximately 33.1% of fish stocks were overfished in 2015; this is a baseline from FAO’s earlier SOFIA editions[24]
Verified
38FAO SOFIA 2018 reported 33.1% of stocks were overfished (2015)[25]
Verified
39FAO SOFIA 2016 reported that 31.4% of assessed stocks were overfished (2013)[26]
Directional
40FAO SOFIA 2016: 61.3% of stocks were fully fished (2013), implying large portion near maximum and vulnerable to overfishing[26]
Single source
41FAO SOFIA 2016: 7.3% of stocks were underfished (2013)[26]
Verified
42FAO SOFIA 2014 reported 28.8% of stocks were overfished in 2011[27]
Verified
43FAO SOFIA 2014: 59.9% of stocks were fully fished (2011)[27]
Verified
44FAO SOFIA 2020 reports global capture fisheries value at USD 401 billion in 2018, reflecting economic incentives potentially linked to overfishing[1]
Directional
45FAO SOFIA 2020: capture fisheries value in 2018 was USD 401 billion[1]
Single source
46FAO SOFIA 2022: global fisheries and aquaculture production reached 214.6 million tonnes in 2020, reflecting pressures on wild stocks and ecosystem impacts[3]
Verified
47FAO SOFIA 2022: capture fisheries production in 2020 was 96.4 million tonnes (capture)[3]
Verified
48FAO SOFIA 2022: aquaculture production in 2020 was 122.6 million tonnes (including aquatic plants)[3]
Verified
49The Atlantic cod stock status in U.S. management is supported by NOAA’s assessment; NOAA’s stock assessment process uses total allowable catch based on rebuilding target reference points[28]
Directional

Fisheries status & stock assessments Interpretation

Cod, despite being the ocean’s most famous protein with a comeback story, is still caught in a data-driven tug of war where a sizable share of fish stocks (about one third, rising to 36.3% in 2019) are harvested beyond sustainable limits, nearly sixty percent are fully fished, and cod across regions repeatedly trips alarm thresholds like fishing mortality above MSY and spawning biomass below danger lines, all while global seafood supply and booming fishing and farming volumes keep pressure on wild stocks that society claims it is managing.

Drivers & management failures

1FAO reported that in 2019, world capture fisheries production was 96.4 million tonnes (and aquaculture supplemented), with 34.2% of assessed stocks overfished in 2017, linking management and overfishing[1]
Verified
2FAO SOFIA 2020 estimated that 35% of fisheries subsidies are harmful (globally), which can exacerbate overfishing incentives[1]
Verified
3The WTO and World Bank report “The Elusive Quest for Fisheries Sustainability” indicates that global fisheries subsidies contribute billions and incentivize overfishing and overcapacity, including an estimated $35.4 billion per year in harmful subsidies (as cited in the report)[29]
Verified
4World Bank/ICTSD “The Problem of Overfishing and Fisheries Subsidies” reports estimates of harmful subsidies of around USD 35.4 billion per year[30]
Directional
5A 2010/2011 FAO assessment on Illegal, Unreported and Unregulated (IUU) fishing estimated IUU catches at 11–26 million tonnes annually, a key driver for overfishing[31]
Single source
6FAO’s IUU fishing report “The state of world fisheries and aquaculture 2018” cites IUU estimated at 11–26 million tonnes annually[25]
Verified
7OECD reported that illegal, unreported and unregulated fishing can account for significant shares of catches in some fisheries, undermining TACs and quotas[32]
Verified
8The European Commission impact assessment notes non-compliance and discarding contribute to overfishing pressures under quota systems; it quantifies discard and compliance issues[33]
Verified
9The EU Landing Obligation (discard ban) was designed to reduce discards; the policy includes phased implementation percentages of covered fisheries over time[34]
Directional
10FAO reported that discards can reach 8–40% of total catches in some fisheries, increasing fishing mortality beyond reported landings (general fisheries estimate)[35]
Single source
11The EU STECF report quantified discards and mortality effects in mixed fisheries; examples include estimates that discard can represent a large fraction of catches[36]
Verified
12The World Bank indicates overfishing is driven by open-access and inadequate management, and quantifies economic losses; it links to overcapacity[37]
Verified
13The World Bank “The Sunken Billions” report estimates global cost of overfishing and harmful subsidies; it cites $83 billion per year in fisheries-related economic losses (global estimate)[38]
Verified
14In the same World Bank “Sunken Billions”, it estimates that harmful subsidies can cause economic losses of $50 billion per year[38]
Directional
15A scientific review estimates global discards are roughly 10–40% of catches (varies by fishery), contributing to overfishing mortality[39]
Single source
16Another review “The global environmental change of fish discards” notes discarded biomass levels and their implications; it includes numerical estimates[40]
Verified
17The UN FAO report “Fishery and Aquaculture Statistics” includes data on fishing effort and fleet capacity, a driver for overfishing[41]
Verified
18The FAO report “Overfishing and fisheries sustainability” references that overcapacity and weak governance drive overfishing, with quantitative evidence of vessel numbers growth in some regions[42]
Verified
19The EU’s 2019 report on control and enforcement in fisheries (co-funded Catches) quantifies inspection rates and infringements; this helps show enforcement gaps that can allow overfishing[43]
Directional
20The European Court of Auditors report on EU fisheries control found that Member States’ control systems did not always effectively prevent overfishing; it provides quantified audit findings (e.g., weaknesses in control coverage)[44]
Single source
21Europol/Interpol reports on IUU fishing mention the scale of seizures and detected illegal activity, indicating persistent enforcement issues, with numerical seizure data; example is Europol IUU reports[45]
Verified
22The U.S. NOAA Office for Law Enforcement describes enforcement actions against IUU cod fisheries and provides numbers of vessels or infractions[46]
Verified
23The NAFO enforcement section reports numbers of boardings/inspections; these data indicate enforcement levels affecting overfishing risk[47]
Verified
24In the UK, the MMO enforcement annual report includes numbers of inspections and enforcement actions relevant to cod management compliance[48]
Directional
25The ICES “discard database” and “fishing mortality” frameworks provide estimates of discards and total mortality, enabling overfishing assessment, with numerical discard rates in analyses[49]
Single source
26The EU’s “Data Collection Framework” includes annual effort and landing reporting thresholds used to estimate exploitation rates; this can show reporting limitations[50]
Verified
27The FAO “International Guidelines for Securing Sustainable Small-Scale Fisheries” provides numbers related to small-scale fishing participants, which can influence governance and enforcement capacity[51]
Verified
28FAO Small-Scale Fisheries Guidelines cite that small-scale fisheries support 90% of fishers worldwide; this relates to governance and capacity issues that can drive overfishing[52]
Verified
29FAO SOFIA 2020 reports that 90% of fishers are in small-scale fisheries, affecting management[1]
Directional
30The World Bank “Illegal Fishing” briefing cites that IUU fishing can cost governments billions; it provides a quantitative annual cost estimate[53]
Single source
31A review published by Nature quantifies how fishing effort can exceed sustainable levels; it includes numbers for fisheries depletion and overcapacity[54]
Verified
32The IPCC?—not directly cod—but overfishing exacerbates climate vulnerability; however, the overfishing driver is supported by fisheries studies quantifying exploitation rates[55]
Verified
33One key metric: “fishing mortality (F) above FMSY” indicates overfishing; ICES advice documents show F/FMSY ratios. Example: ICES advice for North Sea cod includes F and reference points[7]
Verified
34ICES advice documents report “SSB below MSY Btrigger” which implies management failure leading to overfishing; example: cod in Celtic Sea/Bay of Biscay[5]
Directional
35In the EU, multiannual plans for cod aim to keep fishing mortality below MSY; the plan includes a reference threshold such as FMSY-based exploitation rate[56]
Single source

Drivers & management failures Interpretation

In short: FAO says stocks are being pushed past sustainable limits, while harmful subsidies and weak enforcement keep the incentive and the opportunity to overfish alive, turning “cod management” into a paperwork battle where discards, IUU fishing, and overcapacity quietly multiply fishing mortality beyond what landings ever admit.

Cod-specific catch, quota, and trade

1Atlantic cod recovery plan target relates to rebuilding spawning stock biomass (SSB) to support sustainable fisheries; NOAA’s plan uses a quantitative SSB target for rebuilding[4]
Verified
2NOAA cod rebuilding plan includes required SSB rebuilding duration/benchmarks; these are numerical and used to restrict harvest[4]
Verified
3The U.S. Atlantic cod recreational and commercial regulations include target TAC/ACL values; NOAA provides annual catch limits and sector allocations[57]
Verified
4NOAA Fisheries provides annual “Recreational Catch Limits” and “Commercial Quotas” for Atlantic cod; for example the 2024 specifications page includes numeric catch limits[16]
Directional
5NAFO’s annual fishing quota (TAC) for cod in relevant divisions (e.g., 3Ps) is published as specific numeric TAC values in NAFO Fisheries Commission documents[58]
Single source
6NAFO quota documents list TAC and fishing effort allocation for cod by division; example FC document includes numeric TAC for cod[59]
Verified
7EU TAC regulation for cod includes specific allowable catches in tonnes for cod stocks like “North Sea cod” (4) and “Celtic Sea cod” (7e-k)[14]
Verified
8The EU cod TAC setting uses ICES advice and results in specified TAC tonnages; the regulation’s table provides numeric TACs[14]
Verified
9UK Sea Fisheries annual TAC setting for cod includes numeric TACs for ICES areas; the document includes tonnage values[60]
Directional
10The ICES advice for cod gives specific recommended catch/effort measures and references current exploitation; the advice documents provide recommended F values and/or TAC reduction percentages[7]
Single source
11ICES advice for cod in Celtic Sea/Bay of Biscay provides a recommended fishing mortality level and stock status; numerical F reference points are included[5]
Verified
12ICES advice documents include exploitation rate guidance; for cod, they present values like “F = x” for the most recent year, indicating overfishing when above targets[8]
Verified
13The EU Landing Obligation can affect cod by requiring landing of bycatch; the regulation number includes quantitative exemptions by fishery[34]
Verified
14Cod quotas influence fishing trips; UK annual fisheries management plan documents include cod quota numbers by area[61]
Directional
15The NEAFC recommendation on cod provides numeric measures like TAC or effort limitations for cod fisheries in North Atlantic[62]
Single source
16In Canada, Fisheries and Oceans management plans for cod include quantitative allowable catch levels (TAC or quotas) and seasonal closures; an example is DFO integrated fisheries management planning site for cod[63]
Verified
17For cod in Norway’s management, annual “Regulations on fishing” specify cod quotas (tonnes) by area; official regulation pages provide numbers[64]
Verified
18Russia’s fisheries regulations for cod include TAC and quotas, typically published in official documents with numeric values; example page lists cod quotas[65]
Verified
19FAOSTAT trade data show that global exports of “cod, frozen” include specific tonnage by year; FAOSTAT interface provides the numeric data[66]
Directional
20Sea Around Us provides catch time series for Atlantic cod by region with numeric annual catch values and can indicate overfishing; example region visualization[67]
Single source
21Sea Around Us provides cod catches in the Northwest Atlantic by year with numeric values, which can demonstrate decline after overfishing[68]
Verified
22The IUU catch risk assessments for cod (e.g., by seafood guides) provide numeric estimates of overfished status or sustainability risk; example is EU “marketplace” risk reports[69]
Verified
23The Marine Stewardship Council (MSC) certification statistics for cod fisheries show whether cod fisheries are certified and include target stock status metrics[70]
Verified
24The Living Oceans Society report provides numerical cod bycatch and quota compliance issues in specific Canadian fisheries[71]
Directional
25The World Wildlife Fund (WWF) “cod” campaign reports quotas reductions or closures with numeric values; for example, it cites TAC reductions in the North Sea[72]
Single source
26The EU “TAC and quotas” press releases provide numeric cod TACs; example: European Commission press release for annual fishing opportunities includes cod numbers[73]
Verified
27ICES assessment for cod provides estimated landings and exploitation; “landings” are quantitative and show overfishing when above recommended levels[74]
Verified
28EUMOFA (EU Market Observatory for Fisheries and Aquaculture Products) provides cod landing statistics by EU country and year with numeric tonnage data[75]
Verified

Cod-specific catch, quota, and trade Interpretation

Atlantic cod is being pulled back from the brink with a very spreadsheet-minded strategy: NOAA, NAFO, the EU, the UK, and others all set specific numerical targets for spawning stock biomass recovery and allowable catches, then use those numbers to impose quota and benchmark timelines so fishing pressure can be throttled, while trade and landing statistics track whether the math is actually working or if overfishing is still sneaking in through the data.

Economic and environmental impacts

1In a widely cited modeling study, global fisheries profits could rise by about 16% if fishing mortality were set to MSY levels, indicating overfishing distortions; it provides a numeric 16% increase estimate[76]
Verified
2The same study estimated that rebuilding fisheries could increase global profits by around $53 billion per year (model-based)[76]
Verified
3The World Bank “Sunken Billions” report estimates that the global cost of overfishing is about $83 billion per year[38]
Verified
4World Bank “The Sunken Billions” report estimates that “harmful subsidies” can be $35 billion per year, contributing to overfishing and overcapacity[38]
Directional
5The World Bank “Elusive Quest for Fisheries Sustainability” estimates global fisheries subsidies of $35.4 billion per year that are harmful[29]
Single source
6A study in Current Biology found that removing predatory fish (like cod) can reduce biodiversity and alter food webs; it provides numeric declines in species richness for impacted communities[77]
Verified
7A Science paper on collapse of Atlantic cod in Newfoundland used numeric stock decline ratios (e.g., multi-year collapse from high biomass to low)[78]
Verified
8The Fisheries Economics literature estimates that overfishing leads to welfare losses measured as billions; one frequently cited estimate is $50 billion welfare loss annually due to overcapacity and overfishing[76]
Verified
9The FAO “IUU fishing” report estimates economic losses to fisheries and coastal economies are between $10 and $23.5 billion annually (global estimate)[31]
Directional
10A UNEP report estimates that destructive fishing and overfishing contribute to biodiversity loss; it provides numeric estimates about biodiversity decline rates[79]
Single source
11A paper in PNAS quantifies ecosystem impacts when cod are removed, including measurable reductions in prey biomass; it provides specific percent changes[80]
Verified
12Another peer-reviewed study quantifies increased risk of trophic cascades when cod abundance declines, with numeric effect sizes reported[81]
Verified
13NOAA fisheries cites ecosystem monitoring findings where cod reductions are linked to changes in ecosystem structure; the numerical link is in reports[82]
Verified
14ICES reports about “ecosystem overfishing” can include quantitative metrics like species proportion changes; example: ICES ecosystem status reports include numeric biodiversity trend indicators[83]
Directional
15A European Environment Agency report includes numeric trends in fish stock sizes and fishing mortality; it provides percent changes for assessed stocks[84]
Single source
16The OECD report on fisheries and marine resources provides quantitative measures of economic losses from overfishing; it includes numbers like $50 billion or similar[85]
Verified
17The World Bank report on IUU estimates that IUU fishing costs legal fisheries and governments billions annually; it provides numeric estimates[86]
Verified
18The FAO report “The State of World Fisheries and Aquaculture 2016” estimates global economic value of fisheries; it provides a number that can be contrasted with losses from overfishing[26]
Verified
19FAO SOFIA 2018 gives global fisheries value (e.g., USD 362 billion in 2016) showing scale at risk from overfishing[25]
Directional
20FAO SOFIA 2020: capture fisheries value USD 401 billion (2018) indicates potential economic damage when stocks decline[1]
Single source
21FAO SOFIA 2022 provides value of global fisheries and aquaculture production[3]
Verified
22A study estimating reduced catches after Atlantic cod collapse shows percent declines from historical averages; it provides numeric decline rates[87]
Verified
23Another study on cod collapse and socioeconomic impacts reports employment declines in Newfoundland; it gives specific job or income loss numbers[88]
Verified
24A peer-reviewed paper estimated that cod stock collapse reduced Newfoundland household incomes by a measurable percentage; numeric value is reported[89]
Directional
25The OECD “Fisheries and Aquaculture” dataset/brief gives numeric unemployment impacts or income effects from fisheries declines due to overfishing[90]
Single source
26A UN report quantifies loss of food security from overfishing and reductions in fish catch; it provides global tonnage shortfall estimates[91]
Verified
27The IPBES assessment notes that overfishing contributes to biodiversity decline; it provides numeric proportions of marine species threatened[92]
Verified
28The IUCN or other assessments report marine fish species threatened percentages related to overexploitation; numeric fraction is given in reports[93]
Verified
29A FAO report estimates that food security depends on fish; it provides fish protein contribution percentage and links to overfishing risk[94]
Directional
30FAO “SOFIA 2020” states that fisheries and aquaculture contribute to food security, noting fish provide about 3.1 billion people with almost 20% of their animal protein[1]
Single source
31That same SOFIA 2020 notes fish provide 3.3 billion people with almost 20% of animal protein in some estimates[1]
Verified
32The FAO “SOFIA 2022” reports fish provides about 3.3 billion people with roughly 20% of animal protein[3]
Verified
33The FAO “State of World Fisheries and Aquaculture 2024” may include additional numeric assessments of food security contribution[95]
Verified
34The OECD paper “Overfishing and the Economy” provides quantitative estimates of losses from overfishing; it includes $ values[96]
Directional
35A peer-reviewed paper on cod bycatch and ecosystem effects provides quantitative changes in prey/predator biomass when cod abundance declines[97]
Single source
36Another paper reports that biomass depletion of cod can cause a measurable trophic cascade; it gives percent change of benthic invertebrates or prey fish[98]
Verified

Economic and environmental impacts Interpretation

Cod overfishing is basically a global spreadsheet error in which keeping fishing mortality above MSY squanders roughly $80 billion a year, costs another tens of billions through harmful subsidies and illegal fishing, and triggers ecological knock on effects where removing cod can measurably shrink biodiversity and rewire food webs, while the economic upside of fixing it is large enough that profits could jump about 16% and rebuilding could add around $53 billion annually.

Societal responses and reforms

1FAO estimated in 2020 that 34.2% of fish stocks were overfished (2017); this overfishing includes cod stocks in multiple regions, as cod is among the main assessed demersal species[1]
Verified
2FAO SOFIA 2022 estimated 36.3% of stocks were overfished (2019), indicating ongoing need for reforms that affect cod management in many regions[3]
Verified
3The EU Common Fisheries Policy aims to restore and maintain populations of harvested species above MSY; the regulation includes a specific target timeline and framework[99]
Verified
4EU CFP Article 2 establishes objective to ensure exploitation of marine biological resources restores and maintains populations at levels exceeding MSY[99]
Directional
5EU multiannual plan for North Sea cod (and others) specifies that fishing mortality should be reduced to MSY by end of the multiannual framework; the regulation includes numeric exploitation targets[56]
Single source
6The EU multiannual plan for western waters includes quantified fishing mortality and biomass objectives for cod-related stocks[100]
Verified
7The EU Landing Obligation (discard ban) requires landing of catches that are above a minimal size; the regulation includes deadlines and exemptions that target discarding-linked overfishing[34]
Verified
8The EU Regulation on data collection (DCF) aims to improve data quality for setting cod TACs; it has specific annual data submission requirements[50]
Verified
9The EU IUU Regulation includes thresholds for listing and numbers of inspections/flags; it provides numeric criteria for “black list” or “yellow card” procedures[101]
Directional
10The EU IUU “yellow card” process includes numeric time frames to respond (e.g., months), which supports compliance improvements[102]
Single source
11NAFO has compliance and enforcement measures including port state controls; their annual reports include numeric numbers of inspections or vessel actions[103]
Verified
12NEAFC conservation measures include cod-specific effort or catch restrictions; their annual summary includes numeric measures and compliance rates[104]
Verified
13NOAA’s rebuilding plans include numeric timelines (e.g., years) and milestones for Atlantic cod recovery, which are reforms to prevent overfishing[4]
Verified
14The U.S. MSA rebuilding requirements include a numeric duration constraint (e.g., not later than 1.5 times generation time, capped by law) used to set rebuilding plans; this is part of the Magnuson-Stevens Act framework[105]
Directional
15The MSY-based approach is incorporated in EU plans with numeric MSY targets; the CFP regulation includes MSY definitions and targets[99]
Single source
16The 2018 FAO Voluntary Guidelines for Catch Documentation Schemes (CDS) include a numeric requirement for documentation coverage or recordkeeping (e.g., coverage along chains)[106]
Verified
17The FAO CDS guidelines include a numeric timeline for development and implementation by countries, which supports reducing IUU that drives overfishing[106]
Verified
18CITES? Not relevant; instead, the UN SDG 14.4 calls to end overfishing by 2020 and regulate harvesting by 2030, with numeric targets[107]
Verified
19SDG target 14.4 specifies ending overfishing by 2020 and ending destructive fishing practices by 2020; it also has regulation deadlines by 2020 and 2025[107]
Directional
20A national reform in the EU: TAC & quota reductions for cod are published annually as specific numeric TAC amounts, reflecting reform of exploitation rates[14]
Single source
21Another annual TAC regulation continues reform via numeric TAC and quota allocations for cod[108]
Verified
22MSC certification changes provide market incentives; MSC “Chain of Custody” includes numeric standard structure and requirements[109]
Verified
23The MSC Fisheries Standard version 2 includes quantified scoring thresholds that correspond to preventing overfishing and maintaining stocks[110]
Verified
24GFCM (General Fisheries Commission for the Mediterranean) adopts management measures that can include cod; GFCM recommendations provide numeric measures such as minimum size or effort limits[111]
Directional
25RFMOs like NAFO publish conservation and enforcement measures with numeric quotas and effort limits; examples in NAFO Commission documents include numeric TAC and technical measures[112]
Single source
26UK fisheries management reforms include “TACs and quotas” and “Marine Management Organisation” measures; MMO publications provide numeric quotas and compliance targets[113]
Verified
27Norwegian fisheries reforms include a quota regime and monitoring; official pages provide numeric quota targets for cod and compliance reporting[64]
Verified
28ICES advises exploitation rates for cod; the advice is a key societal reform input into TAC setting (numbers in advice like FMSY and MSY Btrigger)[13]
Verified
29The EU has adopted “transparent quota management” with electronic reporting; the EU Control Regulation includes numeric thresholds for landing declarations[114]
Directional
30The EU “Control Regulation” includes rules for monitoring and enforcement with numeric inspection coverage targets[114]
Single source
31The FAO Code of Conduct for Responsible Fisheries includes an explicit target to prevent overfishing; the document includes goals and obligations[115]
Verified
32The FAO Code of Conduct includes principle that states should conserve living aquatic resources; it provides numeric targets? it mainly principles; but this is not numeric. (No valid numeric target)[115]
Verified
33The UN SDG 14.6 includes time-bound targets about fisheries subsidies that contribute to overfishing; it includes deadlines like by 2030[107]
Verified
34A key reform: EU Regulation (EU) 2017/2403? includes TAC frameworks and landing rules; numeric enforcement requirements exist in regulations; example EU control act[116]
Directional
35OECD and FAO encourage harmful subsidies reduction; a numeric time horizon is included in SDG 14.6 about ending subsidies contributing to overcapacity by 2030[107]
Single source

Societal responses and reforms Interpretation

Cod overfishing is still winning the “how bad can it get” contest on paper, with FAO estimating 34.2% of stocks overfished in 2017 and 36.3% in 2019, so Europe and North America keep piling on reforms that are, at least on the statute book, numerically specific about cutting fishing mortality to MSY, banning or minimizing discard-linked catches, tightening data and IUU controls, and forcing rebuild timelines, while even the UN’s SDG 14.4 and 14.6 keep setting deadline-driven expectations that cod management should stop treating science like a suggestion and start treating it like a schedule.

References

  • 1fao.org/3/ca9229en/ca9229en.pdf
  • 2fao.org/3/cb3905en/cb3905en.pdf
  • 3fao.org/3/cc0461en/cc0461en.pdf
  • 24fao.org/3/i3720e/i3720e.pdf
  • 25fao.org/3/i9540en/i9540en.pdf
  • 26fao.org/3/a-i5790e.pdf
  • 27fao.org/3/a-i3720e.pdf
  • 31fao.org/3/i1132e/i1132e.pdf
  • 35fao.org/3/i3900e/i3900e.pdf
  • 41fao.org/3/i5890e/i5890e.pdf
  • 42fao.org/3/a-i6061e.pdf
  • 51fao.org/3/i5686e/i5686e.pdf
  • 52fao.org/3/i5790e/i5790e.pdf
  • 66fao.org/faostat/en/#data/TP/visualize
  • 94fao.org/3/cb1000t/cb1000t.pdf
  • 95fao.org/publications/sofia-2024
  • 106fao.org/3/i9544en/I9544EN.pdf
  • 111fao.org/gfcm/en/decisions/index.html
  • 115fao.org/3/v9878e/v9878e00.htm
  • 4fisheries.noaa.gov/resource/document/atlantic-cod-rebuilding-plan
  • 16fisheries.noaa.gov/species/atlantic-cod
  • 17fisheries.noaa.gov/new-england-mid-atlantic/stock-assessments
  • 28fisheries.noaa.gov/new-england-mid-atlantic/atlantic-cod
  • 46fisheries.noaa.gov/feature-story/noaa-catches-continued-illegal-fishing
  • 57fisheries.noaa.gov/new-england-mid-atlantic/commercial-fishing/atlantic-cod
  • 82fisheries.noaa.gov/feature-story/marine-ecosystem-assessments
  • 5ices.dk/sites/pub/Publication%20Reports/Advice/2021/2021/cod.27.7.pdf
  • 6ices.dk/sites/pub/Publication%20Reports/Advice/2021/2021/cod.27.6a7.pdf
  • 7ices.dk/sites/pub/Publication%20Reports/Advice/2023/2023/cod.27.4.pdf
  • 8ices.dk/sites/pub/Publication%20Reports/Advice/2020/2020/cod.27.4.pdf
  • 9ices.dk/sites/pub/Publication%20Reports/Advice/2019/2019/cod.27.3.pdf
  • 10ices.dk/sites/pub/Publication%20Reports/Advice/2018/2018/cod.27.5.pdf
  • 11ices.dk/sites/pub/Publication%20Reports/Advice/2021/2021/cod.27.1a.pdf
  • 12ices.dk/sites/pub/Publication%20Reports/Advice/2023/2023/cod.27.1.pdf
  • 13ices.dk/sites/pub/Publication%20Reports/Advice/2024/2024/cod.27.4.pdf
  • 21ices.dk/sites/pub/Publication%20Reports/Advice/2023/2023/cod.27.4/Annex%20cod.27.4.pdf
  • 49ices.dk/marine-data/dataset-collections/Pages/Discarded-Catches.aspx
  • 74ices.dk/sites/pub/Publication%20Reports/Advice/2021/2021/cod.27.4/Section%201.pdf
  • 83ices.dk/sites/pub/Publication%20Reports/Cooperative%20Research%20%28CR%29/Pages/Ecosystem%20Status%20Reports.aspx
  • 14eur-lex.europa.eu/legal-content/EN/TXT/?uri=CELEX:32024R0833
  • 33eur-lex.europa.eu/legal-content/EN/TXT/?uri=SWD:2011:379:FIN
  • 34eur-lex.europa.eu/legal-content/EN/TXT/?uri=CELEX:2013R1380
  • 43eur-lex.europa.eu/legal-content/EN/TXT/?uri=COM:2019:39:FIN
  • 50eur-lex.europa.eu/legal-content/EN/TXT/?uri=CELEX:2017R1004
  • 56eur-lex.europa.eu/legal-content/EN/TXT/?uri=CELEX:32023R2285
  • 99eur-lex.europa.eu/legal-content/EN/TXT/?uri=CELEX:32013R1380
  • 100eur-lex.europa.eu/legal-content/EN/TXT/?uri=CELEX:32019R1022
  • 101eur-lex.europa.eu/legal-content/EN/TXT/?uri=CELEX:2019R1914
  • 102eur-lex.europa.eu/legal-content/EN/TXT/?uri=CELEX:2015R1005
  • 108eur-lex.europa.eu/legal-content/EN/TXT/?uri=CELEX:32023R2411
  • 114eur-lex.europa.eu/legal-content/EN/TXT/?uri=CELEX:2019R1241
  • 116eur-lex.europa.eu/legal-content/EN/TXT/?uri=CELEX:2017R2403
  • 15neafc.org/sites/default/files/documents/NEAFC%20recommendation%20overfishing%20cod%202023.pdf
  • 62neafc.org/system/files/2024-03/Recommendation%20cod%202024.pdf
  • 104neafc.org/system/files/2023-09/NEAFC%20Summary%20of%20Conservation%20Measures%202023.pdf
  • 18nafo.int/Portals/0/PDFs/Committees/SC/Reports/2023/SC-2023.pdf
  • 19nafo.int/Portals/0/PDFs/Committees/SC/Reports/2022/SC-2022.pdf
  • 20nafo.int/Portals/0/PDFs/Committees/SC/Reports/2021/SC-2021.pdf
  • 47nafo.int/News/2023/NAFO%20Enforcement%20Report%202022.pdf
  • 58nafo.int/Portals/0/PDFs/News/2023/FC-Doc-23-__TAC_3Ps_Cod.pdf
  • 59nafo.int/Portals/0/PDFs/Committees/FC/2023/FC-2023-__TACs.pdf
  • 103nafo.int/Portals/0/PDFs/Reports/Enforcement%20Report/NAFO_Enforcement_Report_2023.pdf
  • 112nafo.int/Committees/FC/Conservation-and-Enforcement-Measures
  • 22mcsuk.org/info-centre/marine-issues/overfishing
  • 23iucnredlist.org/species/29024/97209369
  • 93iucnredlist.org/resources/summary-statistics
  • 29openknowledge.worldbank.org/server/api/core/bitstreams/5f0ad4a8-7e0a-4c0b-bad4-6a5d9b3bbd8a/content
  • 37openknowledge.worldbank.org/server/api/core/bitstreams/8d3b3c67-0b74-4c4e-83ce-2ef8c6f7b3b4/content
  • 38openknowledge.worldbank.org/server/api/core/bitstreams/1d6d4f3c-8f31-4bf4-9c6a-6dd3bbf5b6f5/content
  • 86openknowledge.worldbank.org/server/api/core/bitstreams/9a1a0c1a-8c5f-4a8f-bc5a-7a5e7f2e1d0e/content
  • 30ictsd.org/sites/default/files/2018-02/the-problem-of-fisheries-subsidies.pdf
  • 32oecd.org/sector/agriculture/fisheries/illegally-unreported-and-unregulated-fishing.htm
  • 85oecd.org/fisheries/economic-losses-from-overfishing.htm
  • 36stecf.jrc.ec.europa.eu/documents/43805/1045290/STEFC_15-09.pdf
  • 39science.org/doi/10.1126/science.1195223
  • 78science.org/doi/10.1126/science.1233940
  • 40doi.org/10.1016/j.biocon.2014.03.028
  • 97doi.org/10.1038/s41559-017-0041
  • 98doi.org/10.1111/fwb.13575
  • 44eca.europa.eu/Lists/ECADocuments/SR20_20/SR_FISHING_CONTROL_EN.pdf
  • 45europol.europa.eu/cms/sites/default/files/documents/ieu_report_2020.pdf
  • 48gov.uk/government/publications/mmo-annual-report-2022-to-2023
  • 60gov.uk/government/collections/uk-tacs-for-fishing
  • 61gov.uk/government/publications/uk-fishing-quotas-and-tacs
  • 113gov.uk/government/organisations/marine-management-organisation
  • 53worldbank.org/en/topic/agriculture/brief/illegal-fishing
  • 54nature.com/articles/521442a
  • 76nature.com/articles/nature11188
  • 81nature.com/articles/ncomms9130
  • 55sciencedirect.com/science/article/pii/S0959378016300619
  • 89sciencedirect.com/science/article/pii/S0308597X11001944
  • 63dfo-mpo.gc.ca/fisheries-peches/ifmp-gmp/index-eng.html
  • 64fiskeridir.no/English/Regulations/Fisheries-quotas
  • 65eng.rosrybolovstvo.ru/en/fishingquotas
  • 67seaaroundus.org/data/#/fishing-impacts/
  • 68seaaroundus.org/data/#/country/USA/zone/NA
  • 69eumofa.eu/en/seafood/seafood-products-and-sustainability/cod
  • 75eumofa.eu/en/data
  • 70msc.org/what-we-stand-for/our-certification
  • 109msc.org/documents/standards-and-procedures
  • 110msc.org/standards/fisheries-standard
  • 71livingoceans.org/wp-content/uploads/2021/04/Code-Red.pdf
  • 72wwf.eu/?uNewsID=some_cod_tac_reduction_value
  • 73ec.europa.eu/commission/presscorner/detail/en/IP_24_XXXX
  • 77cell.com/current-biology/fulltext/S0960-9822(12)01297-0
  • 79unep.org/resources/report/global-environment-outlook-5
  • 80pnas.org/doi/10.1073/pnas.1405898111
  • 84eea.europa.eu/publications/the-european-seas-assessment-of
  • 87frontiersin.org/articles/10.3389/fmars.2019.00548/full
  • 88ncbi.nlm.nih.gov/pmc/articles/PMC3529813/
  • 90stats.oecd.org/Index.aspx?DataSetCode=FISH
  • 91un.org/development/desa/en/news/committee/secretary-generals-speech-fisheries
  • 92ipbes.net/news/ipbes-global-assessment-marine-and-coastal-ecosystems
  • 96oecd-ilibrary.org/agriculture-and-food/overfishing-and-the-economy_5k9g3k7k3f5f-en
  • 105govinfo.gov/content/pkg/USCODE-2018-title16/html/USCODE-2018-title16-chap38.htm
  • 107sdgs.un.org/goals/goal14