Skip to main content
Wiley Open Access Collection logoLink to Wiley Open Access Collection
. 2026 Aug 30;40(5):e70380. doi: 10.1111/cobi.70380

On the need for accurate IUCN data and transparent methods: Response to Lin et al. (2025)

Monica V Biondo 1,✉, Ricardo Calado 2
PMCID: PMC13613546  PMID: 42669927

INTRODUCTION

The article “Extent of Threats to Marine Fish from the Online Aquarium Trade in the United States” by Lin et al. (2025) addresses a relevant topic in the marine aquarium trade, a multimillion dollars industry that has in the European Union and the United States two of its main importing markets in terms of value (Biondo et al., 2024). We commend the authors for addressing the conservation implications of this trade, but we identified several factual inaccuracies in their reporting of species’ conservation statuses and data sources that may significantly affect the conclusions they drew.

ERRORS IN IUCN RED LIST CLASSIFICATION

Lin et al. report that 45 marine fish species sold online are of conservation concern, including four species listed as endangered (Pterapogon kauderni, Elacatinus prochilos, Gobiodon citrinus, and Amphiprion clarkii), 16 as vulnerable, and 33 as having decreasing population trends. We found multiple inconsistencies between the conservation statuses listed by Lin et al. and those reported in the International Union for Conservation of Nature (IUCN) Red List (IUCN, 2025). The errors identified are not restricted to obscure, rarely traded species but actually apply to some iconic, routinely traded species (Biondo & Burki, 2019; Biondo et al., 2024). For example, A. clarkii, reported by Lin et al. as being endangered, was assessed globally and officially by the IUCN as of least concern. The IUCN reported it as being endangered only in the Persian Gulf. Similarly, G. citrinus was globally assessed as being of least concern and endangered only in the Persian Gulf. Elacatinus prochilos was globally assessed as being vulnerable and was considered endangered only in the Gulf of Mexico. Of the four reef fish species reported by Lin et al. as being endangered, only P. kauderni is indeed listed as globally endangered on the IUCN Red List. A complete list of these discrepancies as reported by Lin et al. and corrections based on the IUCN Red List (accessed 28 October 2025) are in Table 1.

TABLE 1.

Species available for sale, their conservation status as provided by Lin et al. (2025), and corrections and additional information based on the International Union for Conservation of Nature (IUCN) Red List as of 28 October 2025.

Lin et al.‐reported status Corrections
Species Source Global conservation status Population status Last global assessment
Acanthurus chronixis a Wild Vulnerable Vulnerable Unknown 3 May 2010
Acanthurus sohal a Wild Vulnerable Least concern (vulnerable in the Persian Gulf, assessed 4 November 2013) Stable 4 May 2010
Zebrasoma xanthurum a Wild Vulnerable Least concern (vulnerable in the Persian Gulf, assessed 3 November 2013) Stable 7 May 2010
Pterapogon kauderni a Both Endangered Endangered Decreasing 1 March 2007
Ophioblennius steindachneri a Wild Vulnerable Least concern Stable 27 May 2007
Coryphopterus personatus a Wild Vulnerable Vulnerable Unknown 22 March 2011
Elacatinus figaro a Cultured Vulnerable Vulnerable Decreasing 6 April 2022
Elacatinus prochilos a Wild Endangered Vulnerable (endangered in the Gulf of Mexico, assessed 10 January 2014) Unknown 01 March 2010
Gobiodon citrinus a Wild Endangered Least concern (endangered in the Persian Gulf, assessed 3 November 2013) Unknown 28 June 2018
Oxymonacanthus longirostris a Wild Vulnerable Vulnerable Decreasing 5 July 2015
Lachnolaimus maximus a Cultured Vulnerable Vulnerable Decreasing 4 February 2009
Coris aygula a Wild Vulnerable Least concern Unknown 12 April 2008
Halichoeres marginatus a Wild Vulnerable Least concern (vulnerable in Persian Gulf, assessed 5 November 2013) Unknown 25 March 2009
Holacanthus clarionensis a Cultured Vulnerable Vulnerable Stable (CITES App. II) 10 October 2009
Amblyglyphidodon ternatensis a Wild Vulnerable Vulnerable Decreasing 15 Novembre 2010
Amphiprion clarkii a Both Endangered Least concern (endangered in the Persian Gulf, assessed 5 November 2013) Unknown 03 February 2021
Amphiprion mccullochi a Cultured Vulnerable Vulnerable Decreasing 1 August 2021
Chrysiptera hemicyanea a Both Vulnerable Vulnerable Decreasing 1 August 2021
Chrysiptera parasema a Wild Vulnerable Least concern Decreasing 23 September 2021
Dascyllus trimaculatus a Wild Vulnerable Least concern (vulnerable in the Persian Gulf, assessed 5 November 2013) Unknown 23 September 2021
a

Names link to IUCN Red List entries.

Although Conservation Biology published a correction (14 November 2025), in this correction, Lin et al. primarily provide textual amendments and summary adjustments to the reported results, and several corrected values represent substantial quantitative changes rather than minor discrepancies. Notably, the number of vulnerable species was changed from 16 to 12, and the number of species not recognized as aquarium trade taxa by the IUCN or FishBase nearly tripled (increased from 100 to 282), altering both the severity and nature of the conservation risk narrative. Critically, the correction does not correct Appendix S8, which remains incomplete, listing only a subset of species and lacking accurate conservation status data. This issue is particularly important because many marine ornamental fishes are listed as either not evaluated or data deficient on the IUCN Red List or their assessments are over 10 years old, potentially limiting the reliability of conservation status data. As a result, Appendix S8 continues to hinder replication of analyses and verification of the main findings. Future work would benefit from clearer separation of global versus regional IUCN assessments and greater transparency in how conservation categories are harmonized across databases. Readers should refer to the corrected values in Table 1 when considering policy implications.

METHODOLOGICAL TRANSPARENCY

In their Methods section, Lin et al. provide insufficient detail on how conservation statuses were assessed. In their Appendix S1, the authors say refer “extinction risk, population trend, and use/trade data were obtained from IUCN in November 2023 and updated in August 2025.” Given the errors reported above, our attempts to replicate Lin et al.’s methods and extract data from IUCN yielded very different conclusions about the global conservation status of the species Lin et al. refer to as imperiled (as shown in Table 1). Verification of IUCN Red List conservation status based on direct examination of information in the IUCN Red List (https://www.iucnredlist.org) would likely have prevented this type of mistake.

PROBLEMS WITH DATA INTERPRETATION

Only 20 of the 45 species Lin et al. claimed to be of conservation concern are listed in their Appendix S8 (referred to as Appendix A8 in the text but labeled Appendix S8 in the appendix file). Of the 16 species they identified as vulnerable, seven are currently classified as least concern on the IUCN Red List. The claim that the United States accounts for two‐thirds of the global marine ornamental fish trade is not supported by the cited literature. Published global estimates range from 15 to 30 million fish annually (Biondo & Burki, 2020; Monticini, 2010; Wabnitz et al., 2003). The sources cited for the two‐thirds figure either offer no quantitative data (Sinha et al., 2023) or report U.S. imports of about 10 million fish in 2011 (Rhyne et al., 2012) and an average of 7.5 million for 2008, 2009, and 2011 (Rhyne et al., 2017). Although 10 million imports would represent two‐thirds of the lowest global estimate (15 million), this proportion falls to 33–50% within the broader 20–30 million range supported by most analyses. Thus, the assertion is inconsistent with available data. Additionally, Appendix A4 (S4 in the appendix file) includes no species names, even though 100 traded fish species are absent from both the IUCN Red List and FishBase aquarium trade records.

IMPLICATIONS

Accurate representation of conservation statuses is critical in studies of wildlife trade. Misreporting IUCN categories can distort the perceived level of threat, potentially leading to misinformed conservation priorities, policy decisions, and public perception. A reanalysis of all species found in trade by Lin et al. based on verified IUCN Red List conservation status data is essential to ensure that Lin et al.’s conclusions regarding the marine aquarium trade are realistic and to ensure transparent and reproducible methods are used to address this important marine conservation topic.

ACKNOWLEDGMENTS

We thank three anonymous reviewers for their constructive feedback and suggestions that helped us clarify and advocate for scientific accuracy and transparency. This work was financially supported by project CITAQUA, Desenvolvimento do Projeto de Reforço do Polo de Aveiro (H4), framed within Measure 10 of Investment TC‐C10‐01—Hub Azul—Rede de Infrastruturas para a Economia Azul, financed by the Recovery and Resilience Plan (PRR), and supported by Fundo Azul of the Portuguese Government. This work was also funded by national funds through FCT (Fundação para a Ciência e a Tecnologia I.P.) under project CESAM‐Centro de Estudos do Ambiente e do Mar (references UID/50017/2025 [https://doi.org/10.54499/UID/50017/2025] and LA/P/0094/2020 [https://doi.org/10.54499/LA/P/0094/2020]).

REFERENCES

  1. Biondo, M. V. , & Burki, R. P. (2019). Monitoring the trade in marine ornamental fishes through the European Trade Control and Expert System TRACES: Challenges and possibilities. Marine Policy, 108, Article 103620. 10.1016/j.marpol.2019.103620 [DOI] [Google Scholar]
  2. Biondo, M. V. , & Burki, R. P. (2020). A systematic review of the ornamental fish trade with emphasis on coral reef fishes—An impossible task. Animals, 10(11), Article 2014. 10.3390/ani10112014 [DOI] [PMC free article] [PubMed] [Google Scholar]
  3. Biondo, M. V. , Burki, R. P. , Aguayo, F. , & Calado, R. (2024). An updated review of the marine ornamental fish trade in the European Union. Animals, 14, Article 1761. 10.3390/ani14121761 [DOI] [PMC free article] [PubMed] [Google Scholar]
  4. International Union for Conservation of Nature (IUCN) . (2025). The IUCN Red List of Threatened Species. Version 2025‐2 . http://www.iucnredlist.org
  5. Lin, B. , Zeng, Y. , To, B. , Holmberg, R. J. , Rhyne, A. L. , Tlusty, M. , & Wilcove, D. S. (2025). Extent of threats to marine fish from the online aquarium trade in the United States. Conservation Biology, 40, Article e70155. 10.1111/cobi.70155 [DOI] [PMC free article] [PubMed] [Google Scholar]
  6. Monticini, P. (2010). The ornamental fish trade. Production and commerce of ornamental fish: Technical‐managerial and legislative aspects (Globefish Research Programme, Vol. 102). Globefish Research Programme, Food and Agriculture Organisation. https://www.fao.org/fishery/en/publications/76531 [Google Scholar]
  7. Rhyne, A. , Tlusty, M. , Schofield, P. , Kaufman, L. , Morris, J. , & Bruckner, A. (2012). Revealing the appetite of the marine aquarium fish trade: The volume and biodiversity of fish imported into the United States. PLoS ONE, 7, Article e35808. 10.1371/journal.pone.0035808 [DOI] [PMC free article] [PubMed] [Google Scholar]
  8. Rhyne, A. L. , Tlusty, M. F. , Szczebak, J. T. , & Holmberg, R. J. (2017). Expanding our understanding of the trade in marine aquarium animals. PeerJ, 5, Article e2949. 10.7717/peerj.2949 [DOI] [PMC free article] [PubMed] [Google Scholar]
  9. Sinha, A. , Pandey, P. K. , & Ghosh, S. (2023). Editorial: Ornamental fishing industry. Frontiers in Marine Science, 10, Article 1245218. 10.3389/fmars.2023.1245218 [DOI] [Google Scholar]
  10. Wabnitz, C. , Taylor, M. , Green, E. , & Razak, T. (2003). From ocean to aquarium. UNEP‐WCM. https://wedocs.unep.org/bitstream/handle/20.500.11822/8341/‐From%20Ocean%20to%20Aquarium,%20The%20Global%20Trade%20in%20Marine%20Orna‐mental%20Species‐20033641.pdf?sequence=3&%3BisAllowed= [Google Scholar]

Articles from Conservation Biology are provided here courtesy of Wiley

RESOURCES