14 Jun 2021: Le Manach F, Jacquet JL, Bailey M, Jouanneau C, Claire Nouvian and the PLOS ONE Editors (2021) Correction: Small is beautiful, but large is certified: A comparison between fisheries the Marine Stewardship Council (MSC) features in its promotional materials and MSC-certified fisheries. PLOS ONE 16(6): e0253486. https://doi.org/10.1371/journal.pone.0253486 View correction
The Marine Stewardship Council (MSC) sets a standard by which sustainable fisheries can be assessed and eco-certified. It is one of the oldest and most well-known fisheries certifications, and an estimated 15% of global fish catch is MSC-certified. While the MSC is increasingly recognized by decision-makers as an indicator for fishery success, it is also criticized for weak standards and overly-lenient third-party certifiers. This gap between the standard’s reputation and its actual implementation could be a result of how the MSC markets and promotes its brand. Here we classify MSC-certified fisheries by gear type (i.e. active vs. passive) as well as by length of the vessels involved (i.e. large scale vs. small scale; with the division between the two occurring at 12 m in overall length). We compared the MSC-certified fisheries (until 31 December 2017) to 399 photographs the MSC used in promotional materials since 2009. Results show that fisheries involving small-scale vessels and passive gears were disproportionately represented in promotional materials: 64% of promotional photographs were of passive gears, although only 40% of MSC-certified fisheries and 17% of the overall catch were caught by passive gears from 2009–2017. Similarly, 49% of the photographs featured small-scale vessels, although just 20% of MSC-certified fisheries and 7% of the overall MSC-certified catch used small-scale vessels from 2009 to 2017. The MSC disproportionately features photographs of small-scale fisheries although the catch it certifies is overwhelmingly from industrial fisheries.
Citation: Le Manach F, Jacquet JL, Bailey M, Jouanneau C, Nouvian C (2020) Small is beautiful, but large is certified: A comparison between fisheries the Marine Stewardship Council (MSC) features in its promotional materials and MSC-certified fisheries. PLoS ONE 15(5): e0231073. https://doi.org/10.1371/journal.pone.0231073
Editor: David Hyrenbach, Hawaii Pacific University, UNITED STATES
Received: December 11, 2019; Accepted: March 15, 2020; Published: May 4, 2020
Copyright: © 2020 MANACH et al. This is an open access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Data Availability: All data and processing scripts are available from http://dx.doi.org/10.17632/gpynbmn7f9.1. NB: In order to ensure anonymity during the review process, a Dropbox link is provided in the manuscript. It will be replaced with the Mendeley repository, should this manuscript be accepted for publication.
Funding: The authors received no specific funding for this work.
Competing interests: The authors have declared that no competing interests exist.
Operating outside of traditional, state-based governance frameworks for fisheries management, the Marine Stewardship Council (MSC) arose in 1997 as a means for consumers to reform fisheries through their purchasing power . Founded by the (then) largest international consumer goods company (Unilever) and the world's largest environmental NGO (WWF, then known as the World Wildlife Fund), the MSC is a private third-party certification system that sets a global standard by which "the sustainability of a fishery can be assessed regardless of its size, geography or the fishing method used" [2, 3]. Fisheries seeking entry into the program are assessed against the standard by consultants from third-party certifiers (called 'conformity assessment bodies' or 'CABs'; referred to here as 'certifiers'). Fisheries that meet the requirements of the standard are approved by the certifiers and deemed sustainable, and products from these fisheries have the option of using the MSC label (see Table 1 for details on the certification process). Based on the MSC's online database, as of 31 December 2017, 210 fisheries were certified (S1 Table), 76 suspended (i.e. the fishery was certified but then lost the certificate) or withdrawn (i.e. the fishery was certified but then withdrawn from the program), while 44 had failed the MSC’s initial assessment.
Due to its leading position on the labeled seafood market, the MSC has been widely studied by scholars. Some studies note the MSC’s positive impact, especially by i) the empowerment of small island developing states to gain greater sovereign control over fisheries and increase generation of wealth [10–13]; ii) their rigorous standards/processes and strong market intake as a means to achieve sustainability and increase public awareness [5, 14–20]; and iii) the creation of economic value and other benefits [e.g. improved governance, reputational benefits etc.; 12, 19]. Another body of work is critical of the MSC. These papers have focused on i) outcomes favoring large-scale, independent and internationally-oriented fisheries [1, 21–27], ii) certification of overexploitation of overfished stocks [28, 29], iii) certification of invasive species [30, 31], iv) certification of key species for marine ecosystems [e.g. krill destined for natural supplements and fishmeal, sometimes fished in sensitive areas of the world with relatively minimal anthropogenic impacts, such as the Southern Ocean; 22]; and v) the subjectivity, inconsistency, and leniency of third-party certifiers and adjudicators [7, 32].
Globally, the MSC is the most visible eco-label for seafood, and smaller consumer-facing programs such as Seafood Watch now largely promote the MSC . The number of MSC-certified fisheries in a country is also now included in the Convention on Biological Diversity (CBD) as an indicator for CBD Target 4 ["Governments, businesses and stakeholders at all levels have taken steps to achieve or have implemented plans for sustainable consumption"; 34] and Target 6, which aims to have all fisheries "within safe ecological limits" by 2020 . According to the MSC, 15% of the world's catch was already certified in 2019 , and it publicly announced its aim to have one third of the world's fish catch certified or in assessment by 2030 . According to the MSC, the number of products with the MSC label displayed to consumers has increased 34-fold between 2008 and 2019, reaching 40,000 products . This label is not the only visual item that the MSC uses to promote itself—it also uses a wide range of visuals in its promotional materials, including in annual reports and other media of public communication such as Facebook. As with agricultural production, there is a widespread perception that ‘small is beautiful’ [37–40], which led us to question whether the MSC was accurately representing its certified fisheries in its promotional materials. Here we compare the fisheries the MSC used in its promotional materials (i.e. in documents such as financial reports, and on Facebook) to MSC-certified fisheries.
2. Materials and methods
To compare promotional materials with on-water certifications, we created two datasets that included 1) all photographs showcasing fisheries that were used in public reports published by the MSC and on Facebook since 2009, and 2) all fisheries (by catch, gear type, and scale) that have been MSC-certified until 31 December 2017.
The vessels involved in the MSC-certified fisheries were classified as either 'small scale' or 'large scale'. We used the European definition of 'small-scale, coastal fisheries': "fishing vessels of an overall length of less than 12 m and not using towed fishing gear" [i.e. bottom trawls & dredges; 41, 42]. Vessels longer that 12 m or using towed fishing gears were deemed 'large scale'.
We categorized gears in the photographs as either 'active' or 'passive' (Table 2), a distinction that is used by a wide range of fisheries actors around the world, such as the United Nations, the European Commission, national administrations (e.g. the National Oceanic and Atmospheric Administration in the USA), environmental NGOs, and fishers' representatives. 'Passive' (or 'static' gears) are often seen as a proxy for small-scale vessels , although this is not always true (e.g. many longline or pot-and-trap vessels are 'large scale' according to the definition used here, i.e. larger than 12 m). ‘Passive' gears and small-scale vessels are often considered to have less of an environmental footprint (e.g. little physical impact on marine habitats, low fuel consumption) and are often promoted as the most sustainable practices by fisheries scientists [e.g. 44, 45], environmental NGOs [e.g. 46], and small-scale fishers' representatives [e.g. 47].
Using these two datasets, we were able to compare the gear types (i.e. 'active' vs. 'passive') and vessel lengths (i.e. 'large scale' vs. 'small scale') of MSC-certified fisheries (in terms of both catch and number) with the fisheries represented in the MSC's promotional materials.
3.1. Promotional materials
The 399 photographs analyzed in this paper show 95 unique MSC-certified fisheries (314 photographs) as well as a number of non-identified fisheries (85 photographs). Among the 95 MSC-certified fisheries, 57 were pictured only once or twice, and 13 over five times.
Gear-wise, fisheries involving active gears only represented 32% of the photographs, whereas fisheries involving passive gears accounted for 64% of all photographs. The remaining 4% consisted in a small set of photographs showing undetermined gears (Fig 1).
Fisheries involving large-scale and small-scale vessels were featured almost equally in the MSC's promotional materials, with 47% of photographs showing fisheries involving large-scale vessels, and 49% of photographs showing fisheries involving small-scale vessels (Fig 1). The remaining 4% correspond to photographs showing an undetermined scale. Overall, the MSC tends to use only a few fisheries involving small-scale vessels, but advertises each of them more often than fisheries involving large-scale vessels.
We also note that African fisheries were showcased in at least 37 photographs (i.e. 9%). However—besides the South African hake trawl fishery (the only MSC-certified African fishery; featured 14 times)—all other photographs represent uncertified and even never-assessed fisheries, mostly in Madagascar and Gambia (10 photographs each). Overall, fisheries that have never been certified accounted for at least 7% of all photographs we examined.
3.2. MSC-certified fisheries
The overall reference catch for the 210 fisheries certified as of 31 December 2017 amounted to 11.6 million tonnes, out of which 9.8 and 10.7 million tonnes originate from fisheries using active gears and operating large-scale vessels, respectively (Table 4). The 76 fisheries that are no longer MSC-certified represent an aggregate reference catch of 1.3 million tonnes.
In terms of catch of MSC-certified fisheries, active gears—i.e. bottom trawls and dredges (including Scottish/Danish seines), pelagic trawls, and purse seines—accounted for 83% of the MSC-certified catch since 2009 (i.e. the period covered by the analysis of the promotional materials), while passive gears (including entangling nets, longlines, pots & traps, and hand-operated gears) only represented 17% of the catch (Fig 2A). Over the same time-period, vessels smaller than 12 m in overall length and not operating bottom trawls or dredges—i.e. 'small scale vessels' according to the EU definition [41, 42]—only accounted for 7% of the MSC-certified catch, the other 93% being caught by large-scale vessels (Fig 2B). Noteworthy, the proportion of fisheries involving small-scale vessels in the total MSC-certified catch has steeply declined over time, from almost 70% in late 2000 to an average of 8% since 2009.
Evolution of MSC-certified catch by gear (A: in catch; C: in number) and scale (B: in catch; D: in number), 2000–2017. The 'Passive gears' category in panels A and C includes entangling nets, longlines and other hooks & lines, pots & traps, and other hand-operated gears (e.g. beach seines, hand rakes).
In terms of number of MSC-certified fisheries (i.e. all fisheries having the same weight regardless of their catch), active gears accounted for 60% of the MSC-certified fisheries since 2009, while passive gears represented 40% of the fisheries (Fig 2C); over the same time-period, small-scale vessels accounted for 20% of the MSC-certified fisheries, the other 80% being caught by large-scale vessels (Fig 2D).
The majority of MSC-certified fisheries use active fishing gear and large-scale vessels (in either North America or Europe), which stands in stark contrast with how the MSC visually represents itself in promotional materials. Passive gears are 3.7 times (in catch; 64% vs. 17%) and 1.6 times (in number; 64% vs. 40%) more prevalent in promotional materials than are actually certified; and fisheries involving small-scale vessels 6.9 times (in catch; 49% vs. 7%) and 2.4 times (in number; 49% vs. 20%). Fisheries involving passive gears and/or small-scale vessels are therefore overrepresented in promotional materials compared to the fisheries that are actually MSC-certified, and the MSC often uses photographs of fisheries that have never been certified.
However, our results also show that the photographs used by the MSC to illustrate specific fisheries are consistent with the text: they correspond to the fisheries the MSC describes in the text, e.g. octopus fishers in Madagascar to correctly illustrate small-scale fisheries in developing countries; a large trawler to correctly illustrate the Alaska pollock fishery etc. In other words, the use of photographs of small-scale fisheries are often used alongside text about the need to increase the number of certified small-scale fisheries, especially from lower income countries. The issue we have identified is that the visual representation chosen for reports and on Facebook mostly showcase small-scale, passive fisheries, whereas mostly large-scale, active fisheries are MSC-certified.
Because sustainability is increasingly focused on climate change, we also note that fisheries involving large-scale vessels and using active gears (i.e. the majority of MSC-certified fisheries) almost always consume more fuel per unit of catch, compared to fisheries involving small-scale vessels and using passive gears [45, 52]. Research suggests that, for large-scale vessels, the most fuel-efficient fisheries are those targeting small pelagics with purse seines, and the least fuel-efficient fisheries are bottom trawlers and pot-fishing crustaceans [53, 54]. Not only does the MSC disproportionately use photographs of small-scale fisheries relative to the seafood that bears its logo, but a substantial number of the photographs feature hand-operated gears (54 photographs, i.e. 14%), which involve the least amount of fossil fuel. In contrast, hand-operated gears only accounted for 0.3% of the MSC-certified catch since 2009.
Our analysis solely focused on reports published by the MSC as well as photographs used to promote the label on its international Facebook page, but further anecdotal evidence suggest that the same trend exists with other media. One such example is the MSC's fisheries portal (https://fisheries.msc.org), on which all documentation related to assessments and certifications can be found. On this portal, the only fisheries in the 'in focus' section (a visual carrousel showcasing MSC-certified fisheries) between May 2017 to March 2020 have been three small-scale ones using passive gears: the 'South Australia Lakes and Coorong pipi' fishery (hand-operated gears), the 'Normandy and Jersey lobster' fishery (pots & traps), and the 'Mexico Baja California red rock lobster' fishery (pots & traps). All together, these three fisheries account for 0.02% of the overall 2009–2017 MSC-certified catch. The overall catch of hand-operated gears and pots & traps—the two gears used by the three fisheries 'in focus'—accounted for 3% of the MSC-certified catch over the same time-period. As highlighted above, these small-scale, passive gear fisheries do not generate much revenue for the MSC through royalties, but they do appeal to the consumers' idealization of fisheries and appear to be consistently used by the MSC to promote its brand.
The MSC has relied on fisheries involving large-scale and/or active, higher impact fishing gears to rapidly oversee the certification of a significant part of the world's fisheries and thus become the front-line player in the sustainable seafood market. We believe that, should the MSC want to reach its target to have 30% of the World's catch either certified or in assessment by 2030, it would need to keep certifying large, industrial fisheries operating active gears. Incidentally, this would also allow the MSC to draw in higher revenues, given that a fishery such as the Western Asturias octopus fishery—which catches around 40 tonnes annually —does not generate as many royalties for the MSC as the Alaska pollock fisheries, which catch around 1.5 million tonnes annually [56, 57].
Based on our findings, it appears that the MSC strongly appeals to the idealization of fisheries by consumers and policy-makers by promoting fisheries involving small-scale gears and passive gears in much higher proportions than in reality, as is the case in other sectors such as agriculture [37–39]. The MSC may be trying to appeal to the needs and desires of its consumers, providing them with the symbolic satisfaction of not having harmed the environment . This strategy is already known in other food-production sectors, such as cattle farming, where consumers subconsciously perceive farms as places of "harmony and kindness" .
However, there is a credible risk of misunderstanding for those who scroll quickly through their documents and websites, which may explain to some extent the positive public image of the MSC. The MSC reports that 86% of consumers who know the MSC label currently trust it , however the risks to consumer trust associated with misleading advertising should not be ignored . To maintain trust with the public, the MSC could be proactive and careful to report in a high-profile and even visual way the percentage of product coming from large-scale versus small-scale fisheries so as to ensure accurate communication to casual readers.
While the vast majority of MSC-certified catch comes from large-scale fisheries, the MSC’s communication strategy focuses on small-scale, lower impact fisheries. We hypothesize that this discrepancy between MSC-certified fisheries and what the MSC advertises aims to ‘green’ its image with consumers. We further posit that this discrepancy might be the reason behind a perceived gap between its ‘supporters’—including policy-makers—and other stakeholders that have gradually disengaged or become critical of the MSC (e.g., coalitions such as On The Hook or Make Stewardship Count). ‘Small is beautiful’ and the MSC favors representations of pastoral fisheries in its promotional materials, but large-scale, active fisheries represent the majority of MSC-certified fisheries.
S1 Text. Description of the process used to produce a time-series of the MSC-certified catch.
S1 Table. Summary of the MSC-certified fisheries, as of 31 December 2017 (ordered by certification date within each status category).
We gratefully acknowledge Rainer Froese and Laurenne Schiller for their insightful comments and edits on various drafts of the manuscript, as well as the insightful comments and suggestions from anonymous reviewers.
- 1. Foley P. National government responses to Marine Stewardship Council (MSC) fisheries certification: insights from Atlantic Canada. New Political Economy. 2013;18(2):284–307.
- 2. MSC. MSC fisheries certification requirements and guidance. Version 2.0. London (UK): Marine Stewardship Council (MSC), 2014. Available from: http://bit.ly/38vui64
- 3. MSC. What is sustainable fishing? 2019 [14/02/2019]. Available from: http://bit.ly/2Pqf0GX
- 4. MSC. Get certified! Your guide to the MSC fishery assessment process. London (UK): Marine Stewardship Council (MSC), 2015. Available from: http://bit.ly/2E8oNMS
- 5. Brown S, Agnew DJ, Martin W. On the road to fisheries certification: the value of the Objections Procedure in achieving the MSC sustainability standard. Fisheries Research. 2016;182:136–48.
- 6. WWF. WWF retrospective on Indian Ocean tuna harvest control rules. Hamburg (Germany): World Wide Fund for Nature (WWF), 2016. Available from: http://bit.ly/2USpyVc
- 7. Christian C, Ainley D, Bailey M, Dayton P, Hocevar P, LeVine M, et al. A review of formal objections to Marine Stewardship Council fisheries certifications. Biological Conservation. 2013;161:10–7.
- 8. MSCI. Ecolabel licensing system—MSCI licensing fee structure. London (UK): Marine Stewardship Council International (MSCI), 2016. Available from: http://bit.ly/2UP4bnu
- 9. MSC. Working together for thriving oceans—The MSC Annual Report 2018–19. London (UK): Marine Stewardship Council (MSC), 2019. Available from: https://bit.ly/3axR5i2
- 10. Adolf S, Bush SR, Vellema S. Reinserting state agency in global value chains: the case of MSC certified skipjack tuna. Fisheries Research. 2016;182:79–87.
- 11. Yeeting AD, Bush SR, Ram-Bidesi V, Bailey M. Implications of new economic policy instruments for tuna management in the Western and Central Pacific. Marine Policy. 2016;63:45–52.
- 12. Carlson A, Palmer C. A qualitative meta-synthesis of the benefits of eco-labeling in developing countries. Ecological Economics. 2016;127:129–45.
- 13. Pérez-Ramírez M, Lluch-Cota S, Lasta M. MSC certification in Argentina: stakeholders’ perceptions and lessons learned. Marine Policy. 2012;36(5):1182–7.
- 14. Bellchambers LM, Gaughan DJ, Wise BS, Jackson G, Fletcher WJ. Adopting Marine Stewardship Council certification of Western Australian fisheries at a jurisdictional level: the benefits and challenges. Fisheries Research. 2016;183:609–16.
- 15. Cummins A. The Marine Stewardship Council: a multi-stakeholder approach to sustainable fishing. Corporate Social Responsibility and Environmental Management. 2004;11(2):85–94.
- 16. Field JG, Attwood CG, Jarre A, Sink K, Atkinson LJ, Petersen S. Cooperation between scientists, NGOs and industry in support of sustainable fisheries: the South African hake Merluccius spp. trawl fishery experience. Journal of Fish Biology. 2013;83(4):1019–34. pmid:24090560
- 17. Gutiérrez NL, Valencia SR, Branch TA, Agnew DJ, Baum JK, Bianchi PL, et al. Eco-label conveys reliable information on fish stock health to seafood consumers. PLOS ONE. 2012;7(8):e43765. pmid:22928029
- 18. Martin SM, Cambridge TA, Grieve C, Nimmo FM, Agnew DJ. An evaluation of environmental changes within fisheries involved in the Marine Stewardship Council certification scheme. Reviews in Fisheries Science. 2012;20(2):61–9.
- 19. Lallemand P, Bergh M, Hansen M, Purves M. Estimating the economic benefits of MSC certification for the South African hake trawl fishery. Fisheries Research. 2016;182:98–115.
- 20. Wakamatsu M, Wakamatsu H. The certification of small-scale fisheries. Marine Policy. 2017;77:97–103.
- 21. Moreno G, Herrera M, Morón J. To FAD or not to FAD: a challenge to the Marine Stewardship Council and its Conformity Assessment Bodies on the use of Units of Assessment and Units of Certification for industrial purse seine tuna fisheries. Marine Policy. 2016;73:100–7.
- 22. Jacquet JL, Pauly D, Ainley D, Holt S, Dayton PK, Jackson JBC. Seafood stewardship in crisis. Nature. 2010;467(7311):28–9. pmid:20811437
- 23. Borland ME, Bailey M. A tale of two standards: a case study of the Fair Trade USA certified Maluku handline yellowfin tuna (Thunnus albacares) fishery. Marine Policy. 2019;100:353–60.
- 24. Bailey M, Bush S, Oosterveer P, Larastiti L. Fishers, Fair Trade, and finding middle ground. Fisheries Research. 2016;182:59–68.
- 25. Bellchambers LM, Fisher EA, Harry AV, Travaille KL. Identifying and mitigating potential risks for Marine Stewardship Council assessment and certification. Fisheries Research. 2016;182:7–17.
- 26. Pristupa AO, Lamers M, Amelung B. Private informational governance in Post-Soviet waters: implications of the Marine Stewardship Council certification in the Russian Barents Sea region. Fisheries Research. 2016;182:128–35.
- 27. Selden RL, Valencia SR, Larsen AE, Cornejo-Donoso J, Wasserman AA. Evaluating seafood eco-labeling as a mechanism to reduce collateral impacts of fisheries in an ecosystem-based fisheries management context. Marine Policy. 2016;64(Supplement C):102–15.
- 28. Froese R, Proelss A. Evaluation and legal assessment of certified seafood. Marine Policy. 2012;36(6):1284–9.
- 29. Opitz S, Hoffmann J, Quaas M, Matz-Lück N, Binohlan C, Froese R. Assessment of MSC-certified fish stocks in the Northeast Atlantic. Marine Policy. 2016;71:10–4.
- 30. Kourantidou M, Kaiser BA. Sustainable seafood certifications are inadequate to challenges of ecosystem change. ICES Journal of Marine Science. 2019:1–9.
- 31. Galil BS, Genovesi P, Ojaveer H, Quílez-Badia G, Occhipinti A. Mislabeled: eco-labeling an invasive alien shellfish fishery. Biological Invasions. 2013;15(11):2363–5.
- 32. Ward TJ. Barriers to biodiversity conservation in marine fishery certification. Fish and Fisheries. 2008;9(2):169–77.
- 33. Seafood Watch. Benchmarking equivalency draft results assessed against the Seafood Watch Fisheries Criteria. Monterey, CA (USA): Monterey Bay Aquarium, 2013.
- 34. MSC. MSC an official biodiversity indicator partner for a second Aichi Target. 2019. Available from: http://bit.ly/2VF4e4X
- 35. Convention on Biological Diversity. Conference of the Parties to the Convention on Biological Diversity, thirteenth meeting, Cancun (Mexico), 4–17 December 2016. Agenda item 19—Decision adopted by the Conference of the Parties to the Convention on Biological Diversity—XIII/28. indicators for the strategic plan for biodiversity 2011–2020 and the Aichi biodiversity targets. Montreal (Canada): Secretariat of the Convention on Biological Diversity (CBD), 2016. Available from: https://www.cbd.int/doc/decisions/cop-13/cop-13-dec-28-en.pdf
- 36. MSC. Teeming with life—A summary of the Marine Stewardship Council’s Strategic Plan, 2017–2020. London (UK): Marine Stewardship Council (MSC), 2017. Available from: http://bit.ly/2XBDOOW
- 37. Amos C, Pentina I, Hawkins TG, Davis N. “Natural” labeling and consumers’ sentimental pastoral notion. Journal of Product & Brand Management. 2014;23(4/5):268–81.
- 38. Mondelaers K, Verbeke W, Van Huylenbroeck G. Importance of health and environment as quality traits in the buying decision of organic products. British Food Journal. 2009;111(10):1120–39.
- 39. Sörqvist P, Haga A, Holmgren M, Hansla A. An eco-label effect in the built environment: performance and comfort effects of labeling a light source environmentally friendly. Journal of Environmental Psychology. 2015;42:123–7.
- 40. Schumacher EF. Small is beautiful: a study of ecomonics as if people mattered. London (UK): Blond & Briggs; 1973.
- 41. European Union. Council Regulation (EC) No 1198/2006 of 27 July 2006 on the European Fisheries Fund. Official Journal L. 2006;223:1–44.
- 42. European Parliament, Council of the EU. Regulation (EU) No 508/2014 of the European Parliament and of the Council of 15 May 2014 on the European Maritime and Fisheries Fund and repealing Council Regulations (EC) No 2328/2003, (EC) No 861/2006, (EC) No 1198/2006 and (EC) No 791/2007 and Regulation (EU) No 1255/2011 of the European Parliament and of the Council. Official Journal L. 2014;149:1–66.
- 43. Bjordal Å. The use of technical measures in responsible fisheries: regulation of fishing gears. In: Cochrane KL, editor. A fishery manager's guidebook—Management measures and their application. Fisheries Technical Paper. 424. Rome (Italy): Food and Agriculture Organization of the United Nations (FAO); 2002.
- 44. Chuenpagdee R, Morgan LE, Maxwell SM, Norse EA, Pauly D. Shifting gears: assessing collateral impacts of fishing methods in US waters. Frontiers in Ecology and the Environment. 2003;10(1):517–24.
- 45. Jacquet JL, Pauly D. Funding priorities: big barriers to small-scale fisheries. Conservation Biology. 2008;22(4):832–5. pmid:18637910
- 46. Dittel MA, Absil C, Verbeek M. Reducing the footprint—Moving towards low impact fisheries. Brussels (Belgium): Seas at Risk, 2010. Available from: https://seas-at-risk.org/images/pdf/archive/ReducingFootprintBrochureUK4_final_1.pdf
- 47. LIFE Platform. Declaration and Mission Statement. Brussels (Belgium): Low Impact Fishers of Europe (LIFE), 2012. Available from: http://lifeplatform.eu/our-mission/
- 48. MSC. Annual report 2013–14. London (UK): Marine Stewardship Council (MSC), 2014. Available from: http://bit.ly/2YCZcFf
- 49. MSC. Sustainable seafood: the first 20 years—A history of the Marine Stewardship Council. London (UK): Marine Stewardship Council (MSC) and The Press Association, 2017. Available from: http://20-years.msc.org/
- 50. MSC. Global Impacts Report 2017–1997–2017: a 20th anniversary review of the Marine Stewardship Council program and the progress and improvements made by MSC certified fisheries around the world. London (UK): Marine Stewardship Council (MSC), 2017. Available from: http://bit.ly/2GEpzDv
- 51. MSC. The MSC at 20. Wild. Certified. Sustainable—Annual Report 2016–17. London (UK): Marine Stewardship Council (MSC), 2017. Available from: http://bit.ly/2Vm0mFS
- 52. Suuronen P, Chopin F, Glass C, Løkkeborg S, Matsushita Y, Queirolo D, et al. Low impact and fuel efficient fishing—Looking beyond the horizon. Fisheries Research. 2012;119–120:135–46.
- 53. Parker RWR, Tyedmers PH. Fuel consumption of global fishing fleets: current understanding and knowledge gaps. Fish and Fisheries. 2015;16(4):684–96.
- 54. Hilborn R, Banobi J, Hall SJ, Pucylowski T, Walsworth TE. The environmental cost of animal source foods. Frontiers in Ecology and the Environment. 2018;16(6):329–35.
- 55. González González AF, Macho Rivero G, De Novoa J, García Silva M. Public certification report—Western Asturias octopus traps fishery of artisanal Cofradias. Neuilly-sur-Seine (France): Bureau Veritas, 2016. Available from: http://bit.ly/2YFcUaQ
- 56. Bowen D, Rice J, Trumble RJ. MSC 2nd annual surveillance report—Remote surveillance for Alaska pollock fishery—Bering Sea-Aleutian Islands. St Petersburg, FL (USA): MRAG Americas, 2017. Available from: http://bit.ly/2IRWDJI
- 57. Bowen D, Rice J, Trumble RJ. MSC 2nd annual surveillance report—Remote surveillance for Alaska pollock fishery—Gulf of Alaska. St Petersburg, FL (USA): MRAG Americas, 2017. Available from: http://bit.ly/2vgPU3Q
- 58. Cadet A, Cathelat B. À propos de l'image du consommateur. Les Cahiers de la publicité. 1966;16:141–5.
- 59. Monbiot G. It's time to wean ourselves off the fairytale version of farming. The Guardian. 2015 29 May 2015.
- 60. MSC. Seafood consumers put sustainability before price and brand. London (UK): Marine Stewardship Council (MSC, 2017. Available from: http://bit.ly/2Uun22d
- 61. Kirchhoff S. Green business and blue angels. Environmental Resource Economics. 2000;15(4):403–20.