INTRODUCTION
Wild fisheries catch is declining, and much hope is pinned on the aquaculture industry to meet growing seafood demand (
1). However, many of the fish species that are produced and considered desirable by people in high-income countries, for example, Atlantic salmon, are carnivorous [approximately 63 million tonnes in 2020 (
2)] and need to be fed with other fish. To meet fish nutrition requirements, aquatic feeds often contain fishmeal and fish oil (FMFO) ingredients (
3). In 2022, the State of World Fisheries and Aquaculture report found that 86% of FM and 73% of FO were directed toward aquaculture. Meanwhile, the global supply of FMFO has plateaued as the demand, and consequently the price, of FMFO have grown (
4).
FMFO can be produced using whole fish and/or fish processing waste (e.g., heads and tails from canning operations). However, to date, a large proportion of raw materials for FM (66%) and FO (47%) still originate from wild capture, small pelagic fisheries (
5)—the so-called forage fisheries (
6). This practice is controversial for three main reasons. First, capturing fish to produce aquaculture feed threatens marine ecosystems by, for instance, increasing demand for fishing on wild fish populations that could exacerbate overfishing (
6,
7). Second, diverting wild fish from human consumption to fed aquaculture undermines human food and nutrition security of low-income people all over the world (
8–
10). Third, the globalization of FMFO trade has resulted in lower traceability of aquatic feed inputs (
11). This points to an important question raised by Naylor
et al. (
11): “How should forage fish resources be allocated among competing uses: to the highest economic value (e.g., ranched bluefin tuna), to feeding the largest number of people, or to conserving natural ecosystems (
11)?”
FMFO are critical to the fed aquaculture sector due to their unique nutrient profile, palatability (which enhances appetite and thus growth) (
12), and high protein content, which are required to grow fish to market size (
13). Fishmeal is particularly rich in protein, with a much higher protein to meal ratio compared to plant-based alternatives (
14). Moreover, plant-based proteins, such as soybean meal, may contain antinutritional factors that negatively affect the intestinal microbiota and immunity of carnivorous aquaculture species, further limiting the ability to fully replace fishmeal with vegetable proteins (
15). Aquaculture species can also have higher lipid requirements than terrestrial farm animals. This explains why fish oil, which contains high levels of key lipid classes including omega-3 long-chain polyunsaturated fatty acids [eicosapentaenoic acid (EPA) and docosahexaenoic acid (DHA)], is essential for the growth and nutrition of fish and must be included in a fish’s diet as they cannot synthesize these fatty acids themselves (
4,
16).
The need for key nutrients in aquatic feeds has diverted millions of tonnes of nutritious fish away from countries with high rates of nutrition insecurity (
8,
17,
18). FMFO factories have been shown to compete with nearby communities for fish access, resulting in increased fish prices and depletion of fish stocks (
5,
19)—stocks that are in turn diverted toward farmed fish meant for luxury markets (
20). Farmed Atlantic salmon, for example, is a major consumer of FMFO and substantial contributor to the expansion of the global aquatic products trade (
5). This is of particular concern given that small pelagic fishes are a vital source of affordable nutrition in many coastal emerging economies, such as those in West Africa and Southeast Asia (
21). Notably, one study found that if Peruvian anchovy (
Engraulis ringens), the largest fishery by weight in the world, were directed toward direct human consumption rather than FMFO production, then it could eradicate severe malnutrition in children globally (
9).
While studies have addressed the efficacy of using whole fish for FMFO production and how this production should be prioritized (
7,
8,
21,
22), there has been limited research on the production landscape, for example, where FMFO factories are located, which species of fish the factories are consuming, and factory ownership. This type of information is critical chiefly because of the implications for local and regional food (in)security mentioned above. It is also relevant because factories can have notable localized environmental effects on the communities in which they are located (
19,
23,
24). For example, they may contribute to air and water pollution. The cooking and drying of fish during FMFO production generates substantial emissions of particulate matter, nitrogen oxides, sulfur oxides, and hydrogen sulfides, as well as high odor levels from excess trimethylamines (
25). One recent report by the Changing Markets Foundation documented numerous accounts of pollution and environmental degradation in Peru’s FMFO industry, including untreated wastewater dumping and decreased air quality (
26). Understanding the spatial distribution of factories helps to identify hotspots where these impacts are most pronounced, allowing for targeted mitigation and management strategies.
In addition, as fish stocks shift due to climate change, the geographic location of factories within a country or region will influence their ability to continue operating, with impacts on local economies. Temperature-driven shifts in fish stocks have already been seen in West Africa (
27), where FMFO factories are located up and down the coast. Mapping the factory locations provides a baseline for understanding how these shifts in fish stocks might affect the industry and local communities over time.
With the aquaculture sector projected to expand, demand for FMFO will continue (
2). For example, between 2000 and 2021, the fed aquaculture industry doubled its intake of fishmeal (
2). Moreover, between 2021 and 2022, fed aquaculture production continued to outpace nonfed aquaculture production, reflecting the rapid and sustained growth of the sector (
5). To address sustainability, equity, and conservation concerns associated with this industry, it is essential to develop robust policies for its effective governance and management. Having an accurate and comprehensive spatial database of FMFO factories is important to understand the development of this industry as well as support the monitoring of factories’ activities, including compliance with environmental and labor standards. This is particularly important in contexts where fisheries governance is weak. To support these efforts, this study maps the distribution of FMFO factories, providing a critical first step in assessing the industry’s global footprint.
DISCUSSION
Key findings
Through the collection of the data reported in this paper, we generated a map detailing known FMFO factory locations for 63 countries globally. We also gathered information on the raw materials used as inputs, i.e., whole fish or by-products, by these factories for FMFO production. Our database and findings provide a valuable foundation to understand the industry’s spatial distribution and to identify data gaps. Our results can be used in further studies on the trade of marine ingredients and provide vital information for analyses into the environmental, social, and economic impacts of FMFO factories, with a view to inform the implementation of effective policies in support of responsible FMFO production and use.
We were surprised to find that most factories are using fishery and/or aquaculture by-products as raw material for the production of FMFO rather than whole fish. However, as mentioned previously when considering production quantity, a larger proportion of FMFO still originates from whole fish. This is an important consideration for policymakers trying to better manage the FMFO industry. When fish by-products are converted into FMFO in a transparent and well-regulated manner, it can represent an efficient waste-management strategy (
5,
29,
30). For example, the European Fishmeal and Fish Oil Producers (EFFOP) advocate for the use of fish by-products in member FMFO production to reduce waste and increase recycling, as up to 60% of a fresh fish may be discarded during filleting (
31). However, it is critical to ensure that this process does not inadvertently incentivize unsustainable fishing practices. In contrast, the use of whole fish to produce FMFO can raise concerns, particularly when these fish are species that are typically consumed by local communities or play an important role in nutrition security (
32). The impacts of FMFO production depend heavily on local contexts, including the extent to which communities rely on fish for food or livelihoods, the availability of fisheries data, and the health and management of local stocks.
Our findings also show that the number of FMFO factories in a given country is not an indicator of FMFO production. Factories vary in their production capacities based on the technologies they use. For instance, European countries—including Norway, Denmark, and Ireland—have few factories, but these achieve high production levels. Although FM and FO are coproducts, we found high variability across country-level FM:FO ratios. This variability may stem from several factors. It could be the result of differences in the costs and equipment used for producing FO in a given country. It is likely also dependent on the lipid content of raw materials used, with some species being higher in oil content than others. Some have also posited that environmental conditions, notably temperature, may influence fatty acid content in fish, leading to differences in the yield and quality of oil extracted (
33). Recent work on freshwater fish shows that phylogenetic factors strongly influence their fatty acid composition and omega-3 content and that the response of EPA and DHA content in fish to temperature variations may be species specific (
33). The refining processes used to produce fish oil can further influence the amount of oil that is extracted from fish and its quality (
34).
Study limitations
We acknowledge that despite our best efforts to compile data from official statistics, industry representatives, and available literature, there are gaps in coverage. Several major producing countries, most importantly, China, are not well represented. Reasons for these data gaps include the language used in web-based searches, a lack of national reporting, and the limited online presence of FMFO production companies. In Senegal, some reports suggest that seven FMFO factories are operational, but only two factories were located in Senegal and included. This discrepancy may result from limitations in data accessibility, differences in definitions of “operational” factories, or delays in updates to publicly available sources. Countries with well-established regulatory frameworks and/or regularly updated databases—such as Norway, Peru, or Mauritania—have more readily accessible data and are therefore better represented. Conversely, regions where data-sharing practices are less formalized or where this information is not consistently documented may be underrepresented. Most of our data collection efforts relied on information published by organizations such as IFFO and MarinTrust, membership to which requires considerable fees and proof of capacity for membership.
In addition, this study focused on FMFO producers/factories rather than aquatic feed companies. This is an important distinction because aquaculture species are typically not fed FMFO directly. Rather, FMFO are two key ingredients included in compound aquatic feeds formulated by feed companies (
35). Feed producers are an important link between the FMFO producers and aquaculture farms but were not included in this study due to time and resource availability.
Next steps
Collecting these data was both time and resource intensive. While we made concerted efforts to reach out to experts in various regions to verify and supplement the data, we were limited in the time and resources available to identify and engage with a broader range of experts or to allow for extended response times. This limitation underscores the need for ongoing collaboration with regional stakeholders and experts to refine and expand the database, ensuring more comprehensive and equitable coverage across all regions.
Given the dynamic nature of the sector, it is important to regularly update this database to maintain its relevance and accuracy. Better data availability is crucial for understanding the footprint of the FMFO industry and assessing its impacts at local, regional, and global scales. We therefore urge all major FMFO-producing countries to officially report information on the following:
1) Location: Precise geographical coordinates or addresses of operational factories.
2) Year in operation: To track historical trends and identify newly established or closing factories.
3) Species processed: Including quantities and whether fish are used whole or as by-products.
4) Total production: Data for FMFO and the species used for each.
5) Conversion rates: Tonnes of fish required to produce FMFO.
6) Disclosure of certifications obtained, e.g., MarinTrust.
7) Information on regulatory compliance.
One mechanism that is well-positioned to provide guidance to countries on fisheries reporting and transparency frameworks is the Fisheries Transparency Initiative (FiTI), an internationally recognized framework on what fisheries information should be published online by governments (
36). For example, FiTI members are required to publish information on the post-harvest sector and fish trade. Section B.1.7 of The FiTI Standard (2017) includes: (i) total quantity of fish and fish products produced, disaggregated by species and fish products; (ii) total quantity of imports of fish and fish products, disaggregated by species and fish products, indicating the country of their origin; and (iii) total quantities of exports of fish and fish products, disaggregated by species and fish products, indicating the country of their destination (
37). Mauritania, a member of FiTI, is a role model in this regard as the Institut Mauritanien de Recherches Océanographiques et des Pêches (IMROP) publishes a list of approved FMFO production sites in their annual report (
38). With improved data transparency in the FMFO industry, we can better understand industry impacts and inform the development of policies to promote more sustainable, responsible, and equitable practices across the supply chain.
Policymakers must consider how factories and the sourcing of fish to support their operations effect community stakeholders, such as local fishers, processers, and consumers as well as the surrounding environment and management of fisheries. This is especially crucial in areas with high factory density, such as coastal towns in Peru. A more comprehensive governance approach will require multiple interconnected elements: (i) cross-sector collaboration, for instance between fisheries management authorities, labor departments, and civil society groups; (ii) effective governance with enforcement mechanisms, including setting and enforcing science-based quotas and robust monitoring systems procedures; (iii) inclusive decision-making processes that meaningfully incorporate local community voices, including fishers and processors, in how marine resources are used and managed; and (iv) clear accountability measures. The Global Roundtable on Marine Ingredients represents a step toward this integration, bringing together industry, NGOs, and other stakeholders to address environmental and social challenges in the FMFO industry (
39).
Future research could build on this data by comparing areas where FMFO factories are performing better or worse environmentally, socially, and/or economically. In addition, more research is needed on the waste and emissions created by these factories and ways to reduce their environmental impacts [see (
40) for an example].
FMFO are limited resources, and although the use of novel feed ingredients is on the rise (
22), they are unlikely to make a major contribution to the industry for years to come. Therefore, it is crucial to support the environmentally sustainable and socially responsible management of the FMFO industry as it stands. Despite concerns regarding the use of whole fish for FMFO production, it remains an effective waste management strategy for fish processing activities via the use of by-products for FMFO production. Policies should be better designed to incentivize by-product rendering for circular food production systems.
Acknowledgments
We thank P. Majluf for providing detailed factory information for Peru and the IFFO: Marine Ingredients Organization for providing country-specific FMFO production data. We also thank P. Henriksson and M. Troell for the very helpful insights and contributions to the final draft of this manuscript. Last, we thank our funding sources, as listed below.
Funding: This work was supported by the Packard Foundation Grant 2023-28472 (to L.A.S. and U.R.S.), Social Sciences and Humanity Council of Canada Partnership Grant 895-2022-1002 (to W.W.L.C. and U.R.S.), Packard Foundation Grant 2022-73546 (to C.C.C.W.), Moore Foundation 8721.01 (C.C.C.W.), and Walton Family Foundation Grant 00104857 (to C.C.C.W.).
Author contributions: Conceptualization: L.A.S., C.C.C.W., W.W.L.C., and U.R.S., Methodology: L.A.S., C.C.C.W., W.W.L.C., and U.R.S. Resources: L.A.S., C.C.C.W., W.W.L.C., D.P., and U.R.S. Funding acquisition: U.R.S. Investigation: L.A.S. and U.R.S. Data curation: L.A.S. Validation: L.A.S., U.R.S., and D.P. Formal analysis: L.A.S. and U.R.S. Project administration: U.R.S. Visualization: L.A.S. Supervision: L.A.S., C.C.C.W., W.W.L.C., D.P., and U.R.S. Writing—original draft: L.A.S. and C.C.C.W. Writing—review and editing: L.A.S., C.C.C.W., W.W.L.C., D.P., and U.R.S.
Competing interests: C.C.C.W. provides scientific support to companies in the seafood sector through the Seafood Business for Ocean Stewardship (SeaBOS) initiative (
https://seabos.org/). None of the SeaBOS members had any role in the study design, analysis, interpretation of data, or conclusions drawn in this paper. All other authors declare that they have no competing interests.
Data and materials availability: All data needed to evaluate the conclusions in the paper are present in the paper and/or the Supplementary Materials. The dataset containing factory information is openly available online Borealis: Canadian Dataverse Repository at
https://doi.org/10.5683/SP3/P0GLZF. Note that the dataset version at the time of publication is version 2.