Hostname: page-component-745bb68f8f-hvd4g Total loading time: 0 Render date: 2025-01-31T05:17:28.578Z Has data issue: false hasContentIssue false

Bomb radiocarbon dating and age estimation of European eel (Anguilla anguilla) of Norway

Published online by Cambridge University Press:  27 January 2025

Allen H Andrews*
Affiliation:
Swedish University of Agricultural Sciences, Department of Aquatic Resources, Lysekil, Sweden Pacific Community (SPC), Oceanic Fisheries Programme, FAME, 98848 Noumea, New Caledonia
Caroline Welte
Affiliation:
ETH Zürich, Laboratory of Ion Beam Physics, Otto-Stern Weg 5 HPK, 8093 Zurich, Switzerland ETH Zürich, Geological Institute, Sonneggstrasse 5, 8092 Zürich, Switzerland
Marina Mihaljevic
Affiliation:
Institute of Marine Research, Ecosystem Acoustics, Austevoll Research Station, Storebø, Norway
Caroline M F Durif
Affiliation:
Institute of Marine Research, Ecosystem Acoustics, Austevoll Research Station, Storebø, Norway
*
Corresponding author: Allen H Andrews; Email: [email protected]
Rights & Permissions [Opens in a new window]

Abstract

Age estimates from bomb 14C dating conflict with a well-recognized age reading protocol (grinding, polishing and staining in the sagittal plane) for otoliths of European eel (Anguilla anguilla). Proper alignment of calculated hatch years for 14C measurements taken from the earliest otolith growth—among the smallest otolith extractions to date for successful 14C analysis due to the advent of gas-AMS—was not achieved using age estimates from an accepted method. The realignment of otolith 14C values to a tropical bomb 14C reference chronology, which is most applicable to the Sargasso Sea as the natal origin of European eel, led to an increase of the original age estimates by 8 to 32 years. A maximum age of approximately 46 years was determined for the European eel specimen with the most massive otolith, of which mass is a reasonable proxy for age and was instrumental in identifying age estimate discrepancies. By extending the otolith mass-to-age relationships from this study to the most massive otoliths available from archived otoliths of Norway, an increase of up to several decades from the original otolith age estimates was discovered, leading to support for a potential lifespan of 70–100 years in the natural environment.

Type
Research Article
Creative Commons
Creative Common License - CCCreative Common License - BY
This is an Open Access article, distributed under the terms of the Creative Commons Attribution licence (https://creativecommons.org/licenses/by/4.0/), which permits unrestricted re-use, distribution and reproduction, provided the original article is properly cited.
Copyright
© The Author(s), 2025. Published by Cambridge University Press on behalf of University of Arizona

Introduction

European eel (Anguilla anguilla) is an ecologically and commercially important species among Anguillid eels for which accurate estimation of age and growth is crucial for successful monitoring of population status and development of proper management strategies (Bevacqua et al. Reference Bevacqua, Melià, Schiavina, Crivelli, De Leo and Gatto2019; De Leo and Gatto Reference De Leo and Gatto1995). It is a critically endangered species that is Red Listed by the IUCN (Pike et al. Reference Pike, Crook and Gollock2020), and yet stock assessment has been extremely challenging due to threat uncertainties and incomplete life history information, with one of the main difficulties being age estimation (ICES 2009a, 2011; OSPAR 2022). Methods exist but have not been validated through ontogeny—a requirement for a proper understanding of population dynamics (Campana Reference Campana2001). Anguilla anguilla is one of 19 species, also known as freshwater eels, that have in common a facultative catadromous life history (Durif et al. Reference Durif, Arts, Bertolini, Cresci, Daverat, Karlsbakk, Koprivnikar, Moland, Olsen, Parzanini, Power, Rohtla, Skiftesvik, Thorstad, Vøllestad and Browman2023). For European eel, spawning occurs in the Sargasso Sea (Schmidt Reference Schmidt1923), although most of its growth phase is spent in coastal and freshwater habitats of northern Africa and throughout Europe after migration across the North Atlantic (Figure 1). Because of this wide geographic distribution, there is an incredible variation in growth and reported lifespan, given they represent one genetic population (Als et al. Reference Als, Hansen, Maes, Castonguay, Riemann, Aarestrup, Munk, Sparholt, Reinhold and Bernatchez2011). Observations from otolith age estimation indicate they grow faster in the southern part of its distribution but live longer and achieve a greater age-at-maturation in the north (Durif et al. Reference Durif, Diserud, Sandlund, Thorstad, Poole, Bergesen, Escobar-Lux, Shema and Vøllestad2020; Vøllestad Reference Vøllestad1992). Estimated life-history parameters also vary according to sex and a choice of habitat that covers marine to freshwater environments (Bertin Reference Bertin1956; Panfili and Ximémès Reference Panfili and Ximénès1994; Panfili et al. Reference Panfili, Boulenger, Musseau and Crivelli2022; Rohtla et al. Reference Rohtla, Daverat, Arts, Browman, Parzanini, Skiftesvik, Thorstad, van der Meeren, Vøllestad and Durif2023).

Figure 1. Map of North Atlantic with surface current patterns relative to the migration path of European eel, with collection locations in Norway (orange stars), and the selected bomb-produced 14C chronology locations from across the North Atlantic and North America (nuclear symbols; see Figure 2). Eggs hatch in the Sargasso Sea and leptocephalus migrate to inshore and continental habitats of northern Africa, throughout Europe, and north to Scandinavia (blue shaded edges). Radiating contours of 10-, 15-, 25-, and 45-mm TL are European eel length limits, within which nothing greater than that length exists in surface water collections and are indicative of the northeasterly migration pattern (Schmidt Reference Schmidt1923). The most applicable bomb 14C reference records are from coral and otoliths in the western North Atlantic (Gulf of Mexico, Caribbean, Bermuda, Antilles) because they represent levels expected for the North Atlantic Gyre (Sargasso Sea) and waters advected as the migration path along the Gulf Stream to locations like Norway. A reliable clam shell record from the North Sea provides insight on 14C levels that are mixed with northern Europe runoff (waters that European eel would cross when migrating to Norway) and is intermediate to the timely 14C records of the Arctic and Laurentian lakes of North America (expected to be similar freshwater 14C records of Norway). Base map was rendered from a classic ocean circulation map produced by American Geographic Society (1943) that remains accurate for general flow patterns with indications of warm tropical (orange) and cooler marginal (green) currents (an otolith 14C record from cool waters of the Labrador Current off Canada provide an example of an attenuated bomb 14C signal for the Northwestern Atlantic; Figure 2).

Age determination is the key to providing feedback on the long-term status of European eel as either recovering or declining, but doubts have been raised on the efficacy of age validation methods (Daverat et al. Reference Daverat, Beaulaton, Poole, Lambert, Wickström, Andersson, Aprahamian, Hizem, Elie, Yalcin-Özdilek and Gumus2012). The accepted manner of age estimation for European eel is from an analysis of otoliths that exposes annuli (periods of fast and slow growth), of which observed growth zone structure may or may not be annual (ICES 2009a, 2011; Moriarty Reference Moriarty1983; Svedäng et al. Reference Svedäng, Wickström, Reizenstein, Holmgren and Florenius1998). Estimates vary according to the methods used to reveal the annuli, which is especially true for older slow-growing eel in the north with lifespan estimates exceeding 50 years (Poole and Reynolds Reference Poole and Reynolds1996, Reference Poole and Reynolds1998)—one well-defined transverse otolith section aged to 55 years exemplifies the potential differences from use of the sagittal plane for age estimation (i.e., See otolith section image shown for a 77.4 cm TL European eel of Ireland on the cover and page 44 of the Otolith Manual from WKAREA 2009; ICES 2009b; Supplemental Material Figure 1). The forms of age validation applied thus far are typically limited to the earliest otolith growth where the otolith margin type can be observed (Panfili and Ximémès Reference Panfili and Ximénès1994) or by tag and return of younger individuals (<12 years; ICES 2009a). There are unique records of individuals that were held captive for 43 years (Palstra et al. Reference Palstra, Jéhannet, Swinkels, Heinsbroek, Lokman, Vesala, Tulonen, Lakka and Saukkonen2020) and over 100 years (Brantevik Eels of Sweden; Wikipedia.org), although it is unknown if such a great lifespan can occur naturally. European eel of Norway are among the oldest specimens for this species (Rohtla et al. Reference Rohtla, Daverat, Arts, Browman, Parzanini, Skiftesvik, Thorstad, van der Meeren, Vøllestad and Durif2023). Recently, European eel—thought to be on average 8 years old based on otolith readings—were re-estimated to an average of 19 years with certain individuals being aged to over 35 years (Durif et al. Reference Durif, Diserud, Sandlund, Thorstad, Poole, Bergesen, Escobar-Lux, Shema and Vøllestad2020). Although the more recently developed otolith processing method revealed more than twice as many annuli, validation of the annual periodicity of growth zone formation remains.

One of the most effective methods of determining accurate estimates of age, growth, and lifespan for fishes is bomb radiocarbon (14C) dating of otoliths. This approach to age validation relies on a bomb-produced 14C signal created by thermonuclear testing in the mid-1950s to the early 1960s (Hua et al. Reference Hua, Turnbull, Santos, Rakowski, Ancapichun, De Pol-Holz, Hammer, Lehman, Levin, Miller, Palmer and Turney2022). Because the calcium carbonate (CaCO3) of otoliths is formed mostly from dissolved inorganic carbon (DIC), and therefore environmental levels are reflected in the inert biogenic aragonite, age determination is possible by comparison with regional aquatic 14C reference chronologies (i.e., coral or known-age otolith material). The approach can be used to test the validity of ages from an estimation protocol, or it can provide an independent age estimate when quantifying growth zone structure that is inaccurate or poorly defined (e.g., Andrews and Schofield Reference Andrews and Scofield2021; Andrews et al. Reference Andrews, Smale, Cowley and Chang2018a, Reference Andrews, Humphreys and Sampaga2018b). The use of bomb 14C dating for age validation of fishes has undergone steady refinement and innovation over the last 25–30 years (Andrews et al. Reference Andrews, Barnett, Allman, Moyer and Trowbridge2013, Reference Andrews, Yeman, Welte, Hattendorf, Wacker and Christl2019, Reference Andrews, Daugherty, Wertnik, Welte, Smith, Buckmeier and Riecke2024; Kalish Reference Kalish1993; Shervette et al. Reference Shervette and Rivera Hernandez2023), and the method has led to lifespan revelations and validated life history parameters that contribute to a better understanding of North Atlantic fisheries (e.g., Andrews et al. Reference Andrews, Pacicco, Allman, Falterman, Lang and Golet2020; Dwyer et al. Reference Dwyer, Treble and Campana2016; Friess and Sedberry Reference Freiss and Sedberry2011; Kalish et al. Reference Kalish, Nydal, Nedreaas, Burr and Eine2001; Neilson and Campana Reference Neilson and Campana2008).

European eel exhibits a migratory life history in the North Atlantic that would complicate otolith 14C composition because uptake is derived from the environment at the time and location of the fish through ontogeny. They begin life in the warm waters of the Sargasso Sea in the North Atlantic after adults migrate from continental habitats to spawn. Eggs hatch and the leptocephali (so-called eel larvae) and glass eel (juvenile stage) drift within the Sargasso Sea and Gulf Stream for the first 1–2 years of life to continental waters, within which they will spend most of their growth phase (Bohemmeau et al. Reference Bonhommeau, Castonguay, Sabatié and Le Pape2010; Lecomte-Finger Reference Lecomte-Finiger1992, Reference Lecomte-Finiger1994; Tesch Reference Tesch2003). Thus, it is expected that the 14C content of core material formed in the first 1–2 years of life would be representative of tropical to subtropical marine environments of the North Atlantic. Material deposited in the following years is likely to represent recruitment to the inshore marine environment and onward to freshwater habitat, depending on the individual and location (Limburg et al. Reference Limburg, Wickström, Svedäng, Elfman and Kristiansson2003; Rohtla et al. Reference Rohtla, Daverat, Arts, Browman, Parzanini, Skiftesvik, Thorstad, van der Meeren, Vøllestad and Durif2023). Hence, 14C measurements from the earliest otolith growth must consider potential changes in the environmental 14C levels during the migration period.

In this study, assays of 14C levels were made from the earliest growth of the very small otoliths (3–10 mg) of European eel of Norway, with the aim of applying bomb 14C dating to test estimates of age by alignment of measured values to a range of applicable bomb-produced 14C reference chronologies. Ten previously aged European eel otoliths were selected from collections made in southern and central Norway (Nedstrand and Sunnmøre) to measure 14C levels within the first 1–2 years of otolith growth (core extraction of ∼100–200 µg CaCO3), which was possible with the advent of gas-AMS (Synal et al Reference Synal, Stocker and Suter2007; Wacker et al. Reference Wacker, Fahrni, Hajdas, Molnar, Synal, Szidat and Zhang2013a, Reference Wacker, Fülöp, Hajdas, Molnár and Rethemeyer2013b). Estimated ages from counting annuli were 8–29 years for these specimens with corresponding hatch years spanning 1983–2005. The premise for this sample series was that if the age estimates were accurate, then the otolith core 14C measurements would align with a reference chronology for the post-peak decline of bomb-produced 14C, as defined at a minimum by atmospheric 14C levels, and by coral and known-age otoliths of North Atlantic tropical seas. Because initial observations of otolith mass as a potential proxy for age provided an indication that age estimates were inconsistent and may not be accurate for some or all of the individuals, otolith mass was considered further as a tool in age estimate refinement on the basis of measured 14C values and the potential years of reference chronology alignment.

Material and methods

Otoliths of European eel were considered from various collection locations across southern and central Norway that were previously aged using a standardized age reading protocol (grinding, polishing and staining in the sagittal plane; Durif et al. Reference Durif, Diserud, Sandlund, Thorstad, Poole, Bergesen, Escobar-Lux, Shema and Vøllestad2020). Two regions were selected (Sunnmøre and Nedstrand, Norway) with a range of ages and otolith masses to cover what may be an indication of age estimate inconsistency—the relationship for otolith mass to estimated age was poorly aligned because some younger fish had larger otoliths than older specimens by a considerable margin. The selected specimens had age estimates of 8 to 29 years, coupled with otolith masses that covered 3 to 10 mg because it is often a reasonable proxy for age (e.g., Andrews and Scofield Reference Andrews and Scofield2021; Andrews et al. Reference Andrews, Smale, Cowley and Chang2018a; Pacheco et al. Reference Pacheco, Bustamante and Araya2021), to potentially reveal deficiencies in the age reading protocol (Table 1). In addition, the approach to bomb 14C dating was to select a series of age estimates within a narrow collection period to trace the bomb 14C signal back through time, thereby attributing the increases of otolith 14C levels between individuals to progressively older hatch years. Hence, the selected collection years of 2012–2013 led to calculated hatch years of 1983–2005. Given the original age estimates are accurate, the measured 14C values from the earliest otolith growth (core) were expected to be related to the post-peak bomb 14C decline, with the earliest years being the most elevated because the fish were alive near the peak of bomb-produced 14C in aquatic environments—see measured 14C alignments in Andrews and Scofield (Reference Andrews and Scofield2021) and Hupfeld et al. (Reference Hupfeld, Lackmann, Andrews, Welte and Jones2023).

Table 1. European eel data for fish and otoliths used in this study that were collected in 2012–13 from Sunnmøre and Nedstrand, Norway, with estimated age from growth zone counting in sagittal otolith sections, readability score, measured 14C from otolith cores, and alternate age scenarios based on 14C reference records. Age from atmospheric chronology (Atm) are minimum ages and bold values are older than the original age estimates by at least the number of years in parenthesis. Data for EE009A/B are successive core extractions on same otolith specimen. The F14C values listed had a measurement error of ±12–16‰ from sample masses of ∼100–170 μg CaCO3 that generated 12–20 μg C. The number of years added from original age (+yrs) and hatch year (hyr) are provided to show shifts in age based on alignments of measured 14C values to each reference chronology

NR = Sample was not recovered from foil packet. † Coring included younger material that diluted the measurement (F14C much lower than expected and visually confirmed). ‡ The core sample (9A) cannot be younger than the second core sample (9B) that has a minimum age of 25 years due to 14C level.

Annuli based age determination

Prior to processing, otoliths were weighed using a microbalance (Metler Toledo) to the nearest 0.001 mg. Either one of the two sagittal otoliths were prepared by grinding, etching, and staining, and age reading according to the described protocol (ICES 2009a, 2009b, 2011). The year-0 band was assigned as the first winter after the oceanic migration marking the beginning of the continental life stage. None of the otoliths had clear and regularly spaced annuli. Most presented numerous tight rings, unevenly spaced, which sometimes joined in a “bundle” or fused into one large annulus on the other side of the otolith. It was assumed that some of the marks forming a bundle represented false checks, caused for example by thermal stress outside of the typical winter annuli formation. Thus, one bundle represented one year. An age estimate was assigned but it was apparent that errors could be linked to (1) bundles and possible false checks and (2) outer rings that were not considered as they were not entirely embedded in the resin and polished (see sample EE009).

Micromilling

The core of the remaining whole sagittal otolith from each pair (one was aged previously) was extracted with a New Wave micromilling machine for 14C analysis. Otoliths were prepared for milling by mounting them in Cytoseal 60 (Richard Allen Scientific Company) on glass microscope slides with the distal surface facing upward (sulcus side down). Because the distal surface shows mass accretion through ontogeny in transverse sections, and this external surface was hand ground (600 grit carbide wet-dry sandpaper) to a thickness that was just shy of the plane (sagittal) that is usually used for age reading. This approach effectively conserved the nuclear region for extraction of the earliest growth with the micromill. Core material, estimated as the first 1–2 years of growth, was determined using existing information on otolith size with age as shown in otolith sections for the selected specimens, as well as other well-illustrated references (e.g., ICES 2009a, 2009b, 2011; Durif et al. Reference Durif, Diserud, Sandlund, Thorstad, Poole, Bergesen, Escobar-Lux, Shema and Vøllestad2020). Otoliths from a migrating elver were measured as approximately 500 × 600 × 300 μm (width, height, depth; ICES 2009a, 2009b, 2011), dimensions that would yield just enough material for gas-AMS technology with reasonable precision (∼150 μg CaCO3). Once the otolith thickness reached a dimension that indicated the earliest growth was exposed, a 300 μm carbide spherical cutting bur (Brasseler USA) was used to mill the core region, which was verified microscopically after the extraction. The mill extractions were three passes of a 5-point surface scan to a depth of 100 μm on each pass. Each extraction is targeted within the first 1–2 years of growth. An additional extraction was performed on the largest otolith to sample growth years 3–4 by running two 100 μm deep passes along a 6-point scan that skirted the edge of the first core. The target mass for each extraction was approximately 100–200 μg of CaCO3. Each small pile of colloidal powder that was generated from each extraction was hand collected and placed in foil envelopes to be sent to ETH Zürich for 14C analysis with gas-AMS.

Gas-AMS

Radiocarbon analysis of otolith calcium carbonate samples was performed by gas-AMS using the Mini Carbon Dating System (MICADAS) at the Laboratory of Ion Beam Physics, ETH Zürich, Switzerland (Synal et al. Reference Synal, Stocker and Suter2007). Samples were dissolved in phosphoric acid in the septum-sealed vials (Labco UK, Exetainer® 4.5 mL round-bottom borosilicate vials) under helium and CO2 is released from the carbonates. In contrast to conventional graphite AMS analysis, where the liberated CO2 is reduced to graphite and measurements are performed on solid targets (e.g., Wacker et al. Reference Wacker, Fülöp, Hajdas, Molnár and Rethemeyer2013b), the CO2 gas is concentrated by means of a zeolite trap and transferred with a helium gas carrier into a syringe in the gas interface system (Wacker Reference Wacker, Fahrni, Hajdas, Molnar, Synal, Szidat and Zhang2013a). The gas sample is further diluted with helium and fed into the gas ion source of the AMS. A major advantage of the gas-AMS technique is, besides it being cost-effective and fast, that sample sizes required for the analysis are significantly smaller. Solid-AMS analysis typically requires 1 mg of CaCO3 compared to less than 100 ug CaCO3 needed for a gas analysis. With this approach, otolith carbonate samples were 10–20 times smaller compared to previous studies. Fossil and modern reference materials (IAEA-C1; Rozanski Reference Rozanski1991) and an in-house coral standard (CSTD, nominal F14C value 0.9447 ± 0.0002, G. Dos Santos, pers. comm.) were analyzed in concert with the samples. Data evaluation was performed with the “Beautiful AMS Tool of Switzerland” software (BATS), an analysis routine that functions as a reliable data reduction tool (Wacker et al. Reference Wacker, Christl and Synal2010). Radiocarbon data are reported as Fraction Modern (F14C) according to Reimer et al. (Reference Reimer, Brown and Reimer2004).

Reference 14C chronologies and age alignments

Five chronologies were selected to align the measured 14C values from European eel otolith cores to the potential years of the otolith core formation. These chronologies ranged from atmospheric and freshwater records to locations across the North Atlantic that would function as a proxy for 14C levels on the migration route used by European eel to reach Norway from the Sargasso Sea (Figure 1). The Northern Hemisphere atmospheric bomb 14C record (NH1) describes the uptake and transport of bomb-produced 14C throughout the Northern Hemisphere at latitudes greater than 40°N (Hua et al. Reference Hua, Turnbull, Santos, Rakowski, Ancapichun, De Pol-Holz, Hammer, Lehman, Levin, Miller, Palmer and Turney2022). This temporal reference represents the most recent date that an elevated bomb 14C level can be sequestered by an otolith that formed in an aquatic environment at northern latitudes. Alignment of measured otolith 14C values from a recently collected fish with this chronology provides an absolute minimum age limit (Figure 2).

Figure 2. Selected bomb-produced 14C chronologies from across the North Atlantic and the northern freshwater hydrosphere that are applicable to otolith formation during the migrational early life history of European eel. The atmospheric chronology for the Northern Hemisphere (NH1)—a composite of 14C measurements from regions greater than 40°N latitude (Hua et al. Reference Hua, Turnbull, Santos, Rakowski, Ancapichun, De Pol-Holz, Hammer, Lehman, Levin, Miller, Palmer and Turney2022)—provides an absolute minimum age for the alignment of otolith 14C values from recent capture years. The tropical North Atlantic chronology is considered the most reliable temporal reference for the earliest growth of European eel because it is a composite of 14C references that would reflect the mean 14C levels in the mixed layer of the Sargasso Sea, the known natal grounds for this species (Andrews et al. Reference Andrews, Barnett, Allman, Moyer and Trowbridge2013, Reference Andrews, Pacicco, Allman, Falterman, Lang and Golet2020, Barnett et al. Reference Barnett, Thornton, Allman, Chanton and Patterson2018, Shervette et al. 2023). The North America Lakes freshwater chronology, established from otoliths of Arctic and Laurentian fishes (Campana et al. Reference Campana, Casselman and Jones2008; Casselman et al. Reference Casselman, Jones and Campana2019; Lackmann et al. Reference Lackmann, Andrews, Butler, Bielak-Lackmann and Clark2019), is the best available proxy for the freshwaters of Norway. An intermediate record from the North Sea—established by an Arctica islandica clam shell in the mixed German Bight (Scourse et al. Reference Scourse, Wannamaker, Weidman, Heinemeier, Reimer, Butler, Witbaard and Richardson2012)—provides a proxy for a mixed 14C signal of North Atlantic waters that European eel would cross during migration to Norway. For a contrast in bomb 14C signal strength, a northwestern Atlantic otolith chronology (Campana et al. Reference Campana, Casselman and Jones2008) shows the strong attenuation effects of mixed deep waters that are 14C-deficient.

A series of otolith 14C measurements from fishes of Arctic and Laurentian lakes of North America (Campana et al. Reference Campana, Casselman and Jones2008; Casselman et al. Reference Casselman, Jones and Campana2019; Lackmann et al. Reference Lackmann, Andrews, Butler, Bielak-Lackmann and Clark2019) was used as a proxy for freshwater 14C levels in Norway. European eel used in this study eventually reached the freshwaters of Norway and would sequester to the otolith a similar near-atmospheric 14C signal. There are no known water or fish otolith measurements of 14C from freshwaters of Norway, but the 14C records of North America should represent the precipitation 14C signal (rain to river) across the well-mixed atmosphere of the Northern Hemisphere (Figure 2).

The most applicable 14C reference chronology for hatch year otolith material of European eel is from tropical coral and otoliths covering the marine 14C signal for North Atlantic waters, such as the natal origin of European eel, the Sargasso Sea. This collection of 14C records covers a vast area ranging from western Gulf of Mexico and Caribbean Sea to Bermuda (Andrews et al Reference Andrews, Barnett, Allman, Moyer and Trowbridge2013; Barnett et al. Reference Barnett, Thornton, Allman, Chanton and Patterson2018; Shervette et al. Reference Shervette, Overly and Rivera Hernandez2021) and yet it provides a very consistent reference chronology that has become the 14C reservoir by crossing the atmospheric 14C record in the early 2000s (Figure 2). An intermediate chronology from a long-lived clam shell (Arctica islandica; Scourse et al. Reference Scourse, Wannamaker, Weidman, Heinemeier, Reimer, Butler, Witbaard and Richardson2012) of the North Sea was selected as a good proxy for a mixed 14C signal—tropical marine waters advected north by the Gulf Stream to mix with freshwater influxes from Europe—as migrating European eel approach Norway (Figures 1, 2).

Hatch years were initially determined as the difference between capture year and the estimated age from annuli counting in the otolith sections. These hatch years were combined with the measured 14C value from otolith core material and were plotted with the series of applicable bomb 14C reference chronologies (Figure 3). Each hatch year was adjusted by +1 year to cover the mean year of formation for a more accurate alignment (2-year core) and all ages and collection dates were treated as years. When hatch years did not align with a given 14C chronology, the year of formation was shifted by the number of years required to align with each reference curve. These shifts in time, rounded to nearest year, led to revised hatch years and ages that were used to provide insight on the age reading of European eel otoliths. In addition, otolith mass can function as a proxy for age and was used as a guide in making decisions about greater age scenarios relative to the applicable 14C reference chronologies.

Figure 3. Alignments of 14C data from European eel (Anguilla anguilla) otoliths relative to the collection years (X with sample ID) that are projected back to hatch year scenarios (green dashed arrows) as determined by: 1) the original otolith section age estimations (open circles); 2) the minimum 14C age from an alignment with the atmospheric 14C chronology (blue triangles); 3) the most applicable 14C age from an alignment with the tropical seas chronology on the post-peak decline (orange diamonds); and 4) an extended 14C age (old age scenario) from an alignment with the 14C rise and peak period (blue squares). The grey circle connected to some data points is the second core from EE009 A/B (see Figure 5), the most massive otolith in the study and likely the oldest, as evidenced by the elevated 14C levels noted in Sargasso Sea DIC measurements (Nydal et al. Reference Nydal, Gulliksen, Löveseth and Skogseth1984). The freshwater and mixed 14C chronologies are from North Sea and North America lakes as possible elevated alignment chronologies that depend on where this fish was during the otolith core formation period. The tropical seas chronology (Tropical North Atlantic) is also represented by the data from coral and otoliths (small yellow circles) to provide a visual on the variance associated with this 14C record.

Results

Calcium carbonate samples were successfully extracted from the otoliths of European eel, which may be the smallest ever used in bomb 14C dating. Otolith core material that was extracted with a micromilling machine was 100–170 µg from whole otoliths that weighed 3.24–10.47 mg (Table 1). The initial comparison of otolith mass to estimated age revealed differences in otolith mass-growth through time and a poor correlation among individuals (Figure 4). These differences were further highlighted with the corresponding 14C measurements and reference chronology inferences and alignments.

Figure 4. Plots of European eel (Anguilla anguilla) age estimates versus otolith mass for the otoliths used in this study that provided an opportunity to investigate relationships for three age estimation scenarios (original age = annuli counting; decline age = alignment of 14C values to the post-peak decline; rise-decline age = an extension of the two most massive otoliths to the upper 14C rise and peak period). Because otolith mass is often a reasonably good proxy for age, these comparisons can provide insight on what age estimates are more likely to be accurate in the absence of known age otoliths. The original age estimates (open circles) provided the poorest fit with large inconsistencies in otolith mass accretion rates and an unrealistic intercept. Alignment of the otolith 14C values to the post-peak decline led to ages that made otolith mass a better proxy for age, but the best fit was when the two most massive otoliths were shifted to upper bomb 14C rise and intermediate peak positions (Figure 3).

Radiocarbon measurements for European eel were successful for eight of the 10 specimens because two samples were not successfully recovered from the foil envelopes (Table 1). The measured F14C values were 1.091–1.177 and followed a generally increasing pattern with increasing otolith mass and age (as hatch year decreases (increasing age) within the last few decades, the bomb-produced 14C values should increase systematically toward peak values); however, the calculated hatch years for the otolith measurements led to a mix of within and outside the absolute minimum age for hatch years set by the atmospheric reference chronology (Figure 3).

Minimum age from bomb 14C

The hatch years from annuli estimates for three specimens resided well outside the atmospheric 14C chronology (Figure 3). Therefore, ages must have been underestimated by at least 5 to 11 years (EE001 = 11 cf. 16 years, EE005 = 8 cf. 19 years, EE009A = 14 cf. 21 years) from the otolith core measurements and by at least 16 years for the second core (EE009B = 14 cf. 25 years; Table 1). The age of 25 years for EE009B, being the most elevated value of the EE009A/B measurement pair, trumps the minimum age of 21 years for EE009A because the core cannot be younger than a sample extracted from more recently formed material. Furthermore, these ages are strictly the minimum age for each fish from the alignment of each year of formation with the atmospheric 14C chronology. The true age of each specimen is likely older than determined by this limitation because only freshwater aquatic habitats tend to be nearly in synch with the atmosphere due to timely aquatic deposition via precipitation (e.g., Figure 2).

The other four otolith core 14C values were within the range of possible 14C values as prescribed by the various reference chronologies (Figure 3). One specimen had a 14C value that aligned with the atmospheric reference at an age of 17 years (EE003), but this fish is likely older for reasons stated previously. Two fish were aged in their mid-20s with calculated hatch years later than the minimum age set by the atmospheric 14C reference (EE006 = 24 cf. 21 years, EE007 = 27 cf. 22 years; Table 1). One measurement (EE004), however, was suspected to be contaminated because the 14C value was considerably lower than expected relative to the other sample findings (Table 1). Upon inspection of the cored otolith and referring to laboratory notes, this sample most likely included a significant amount of mass from other parts of the otolith that were formed more recently (cracks formed during milling with missing micro-pieces mixed into the sample). Inclusion of material away from the core would reduce the apparent core 14C value, as indicated by being the lowest 14C value (F14C = 1.091), because of the decrease of environmental 14C over the lifespan of the fish. Hence, this sample was deemed unreliable and is not considered further.

Bomb 14C age

Annuli-based age estimates provided a range of formation years that were either reasonable or unreasonable in terms of the limits set by bomb-produced 14C (Table 1). The earliest otolith growth was expected to be formed primarily from DIC of the tropical waters of the Sargasso Sea through to the northern extent of the Gulf Stream near the North Sea (Figure 1). Hence, the most applicable temporal reference for measured 14C values from European eel otolith cores is the tropical coral and otolith chronology that covers much of the marine mixed-layer 14C signal for the North Atlantic but must also consider the North Sea reference chronology as a mix of oceanic and continental freshwater sources (Figures 2, 3). Beginning with the smallest otolith (EE001, 3.24 mg) at a minimum age of 16 years from alignment to the atmospheric chronology, a realignment of the measured 14C values to the tropical chronology leads to an age of 23 years and a hatch year of 1990 (Figure 3). This is an increase of 12 years from the annuli count estimate of 11 years. Following this approach, EE003 and EE005 are the next most massive otoliths (4.80 and 6.00 mg) with minimum ages from alignment to the atmospheric chronology of 17 and 19 years, respectively. While the annuli-based year of formation for EE003 aligns with the atmospheric 14C record, the actual age would be 8 years older for an age of 25 years and a hatch year of 1987 based on the tropical North Atlantic chronology. For EE005 the original age estimate of 8 years was underaged by at least 11 years according to the atmospheric record and would have been 27 years old by aligning with the tropical 14C chronology, an increase of 19 years for a hatch year of 1986.

Following this trend of using the tropical reference chronology to reassess age, the three most massive otoliths that also had the most elevated F14C values were revised to ages of 33 to 37 years with hatch years of 1975–1980 (Table 1). These ages are 10–19 years older than the original age estimates. For EE009A/B, the 14C value for the second sample core rises above the tropical 14C reference and is estimated to be 2 years more recent than the first otolith core. The timing for this measurement aligns with a combination of the freshwater proxy for 14C (North America lakes) and the levels expected for the North Sea (Figure 3), as expected if this individual had moved into the coastal waterways of Norway by this time in the formation of the otolith. This elevated F14C value provides support for the alignment of the first otolith core with the tropical North Atlantic chronology because placement in time with the North Sea or freshwater proxy is limited and leads to a less plausible alignment to, or outside, the atmospheric chronology.

The alignment of the three most massive otoliths focused on the post-peak 14C decline but because of their proximity to peak 14C levels during this period, the measurements could have formed further back in time and still agree with the tropical 14C chronology. By comparing otolith mass to age there is support for greater ages to EE007 and EE009 because mass becomes a better proxy for age (Figure 4). Hence, the most massive otolith may be associated with the late rise of bomb 14C, prior to reaching peak levels, by assuming only the first 2–3 years of growth were sampled. Alignment to the bomb-produced 14C rise increases the age of EE009A to 46 years with a hatch year of 1968, which consequently places the elevated second core in 1970 and near peak levels, possibly representing uptake of 14C from a combination of the tropical seas and mixed North Sea waters while in transit to the northeast (Figure 3). Consideration of historic 14C measurements made in DIC from the Sargasso Sea during the peak period (Nydal et al. Reference Nydal, Gulliksen, Löveseth and Skogseth1984) might explain some of the slightly elevated 14C level of the second measurement, relative to the more averaged chronology that is derived from coral and otolith samples, but it seems more likely that the elevated levels reflect a mix of the 14C chronologies to the northeast and its arrival in the freshwaters of Norway (Figure 3). It is important to note that DIC measurements are typically much more variable than coral and otolith samples (months or even a year of accretionary growth) because each DIC measurement is instantaneous. For EE007, the hatch year alignment is not as well defined because the measured 14C value from the core is similar to peak bomb 14C levels, but an estimated hatch year of 1971 was applied in this case (toward the top of the rise period, although it could be a few years younger) for an age of 42 years (Figure 3). These alignments are an increase of 15 and 32 years to the original age estimates (Table 1).

The successive 14C measurements made for the most massive otolith (EE009 at 10.47 mg) exemplify the successful process used to extract core material from European eel otoliths. The first extraction (Core 1) targeted the first two years of growth and the second (Core 2) targeted a few more years beyond the core (Figure 5A). Based on the original counting to 14 years (marked), Core 1 extracted the first year of growth and Core 2 covered most of years 2–3 based on an overlay of the cutting paths (Figure 5B). However, because the first two growth zones are tightly coupled and not originally counted separately, it is possible that Core 1 sampled years 1–2 and Core 2 sampled years 3–4. Alignments were similar for the other single-extraction otolith cores by being within what is interpreted here as the first 2 years of growth.

Figure 5. Sagittal otolith sections from the European eel (EE009) with the most massive otolith (10.47 mg) showing (A) the core extractions and (B) the growth zone counting marked to attain the original age estimate of 14 years. The otolith core was extracted twice (A) with core 1 centered on the first 2 years of growth and core 2 as a concentric extraction to remove years 3 and 4. The overlay (B) shows how this specimen and the other otoliths were verified by tracing a microscopic view of the extraction area on the aged otoliths. An older age reading scenario that may account for the much greater age of 46 years is indicated with the white arrow extending from the nucleus to the edge, along which there are numerous finer increments that are currently considered subannual.

Discussion

Bomb 14C dating of European eel otoliths has revealed that an accepted otolith age reading protocol can significantly underestimate true age. The temporal constraints that are set by environmental 14C reference chronologies indicate the age of some individuals was older by at least 5–11 years and by up to a few decades when aligned with the most applicable bomb 14C chronology. Because the natal origin of European eel is the Sargasso Sea, use of the coral-otolith 14C reference for the tropical North Atlantic was the most trustworthy for the alignment of measured 14C values from otolith cores because of the shared water mass sources (Figure 1). Discrepancies in how age was determined were highlighted by changes in the otolith mass-to-age relationship as estimates of age increased with the more applicable 14C reference alignments. Because otolith mass usually functions as a reasonable proxy for age (e.g., Andrews and Scofield Reference Andrews and Scofield2021; Andrews et al. Reference Andrews, Smale, Cowley and Chang2018a; Pacheco et al. Reference Pacheco, Bustamante and Araya2021), it was evident that there were problems with the accepted age estimates because otolith mass-to-age provided a poor correlation. Once minimum ages were determined from the atmospheric 14C chronology, and then further projected to the tropical seas 14C record, the otolith mass-to-age relationship improved and supported ages approaching 50 years (Figure 4).

The specimen with the greatest age estimate discrepancy was for the European eel with the greatest otolith mass at 10.47 mg. Age was initially estimated to be 14 years from what appears to be a well-defined age reading protocol, but 14C levels indicated the fish was much older. The otolith for this fish was successively sampled (two core extractions) to investigate changes in 14C uptake through the early years of growth. From otolith section image overlays, the first core was likely the first 1–2 years of growth and the second core (a ring around the first core) was material that may have formed during ages 3–4, given early ring counts are accurate—one closely set ring to the first was considered year-2 but may have been part of the first ring (Figure 5). The 14C levels measured for this sample pair revealed a pattern that may reflect a habitat transition or a longer lifespan. Because the core 14C value was lower than the second core (F14C = 1.138 cf. 1.177), the increase in 14C could represent movement from tropical marine (Sargasso Sea and Gulf Stream) to freshwater influenced habitats of the eastern North Atlantic, like the North Sea, or rivers and streams of Norway (e.g., Arctic-Laurentian freshwater habitats of North America by proxy). For this scenario, alignment of sample EE009A with the post-peak 14C decline of tropical seas leads to placement of the elevated sample EE009B on a date that reflects a mix of North Sea and freshwater habitat 14C levels (Figure 3), as expected with a 1–2-year migration to Norway. This alignment leads to an age of 33 years, which is 19 years older than the original age estimate.

While it is known that this species begins life in the Sargasso Sea and would continue to sequester 14C levels representative of the North Atlantic tropical seas through to northern latitudes of the North Atlantic, the formation time and location within the sampled otolith was not known. Hence, the estimated age may have incorporated levels that are represented by the North Sea chronology during the latter formation period of the core sample. However, the successive measurements made on the largest otolith provided important insight by limiting the alignment of the core to the tropical North Atlantic chronology by placement of the second core as a mix of the freshwater and North Sea chronologies. This observation provides support for the age of recruits, as they reach Scandinavian habitats by crossing the greatest distance traveled, is a few years old in order to complete the migration from the Sargasso Sea (Bonhommeau et al. Reference Bonhommeau, Castonguay, Sabatié and Le Pape2010; Kettle and Haines Reference Kettle and Haines2006; Lecomte-Finiger Reference Lecomte-Finiger1992).

The long-lifespan interpretation for the largest otolith, however, is equally viable and places the hatch year on the upper rise of bomb-produced 14C in 1968 for an age of 46 years (Figure 3). This leads to placement of the second measurement in 1970 near peak 14C levels. While this elevated value is above the range of peak 14C values from the tropical chronology, it can be explained by either the measurement uncertainty (±12–16‰) or more elevated 14C levels during this time that are unaccounted for from the gyre waters of the Sargasso Sea (Nydal et al. Reference Nydal, Gulliksen, Löveseth and Skogseth1984). In addition, otolith mass provides better support for the older age interpretation because this otolith would have been the oldest, as opposed to second oldest based on an alignment to the post-peak decline. The age of 46 years for the most massive otolith, and a marginally greater age of 42 years for the next most massive otolith (EE007) as having formed during the peak period, significantly improved the otolith mass-to-age relationship (Figure 4). This finding is more in line with what was expected and may be an indication that otolith mass can function as an effective proxy for European eel age.

Taking the findings of this study one step further, it is possible to estimate the maximum age of European eel in Norway. An examination of otolith archives for Norway revealed that otoliths can attain masses that are nearly 3 times greater than the largest otolith of this study (10 mg cf. 28 mg). By applying the older age scenarios for otolith mass-to-age, it is possible to speculate that European eel in Norway may reach a 70- to 100-year lifespan, considerably older than an estimate of 34 years from annuli counting in the 28 mg otolith. Clearly, this series of estimates is based on a few data points and should be considered with caution, but it is suggested that these otolith mass-to-age relationships be used to design a follow up study to further explore 14C in European eel otoliths. The temporal alignment of additional European eel otolith measurements to bomb 14C chronologies, with further investigation of how otoliths are interpreted for age estimation, should lead to better age-at-length estimates that provide a validated basis for accurate life history parameters and population longevity.

Conclusions

European eel of Norway are longer lived than previously estimated using an accepted age reading protocol. The offset of hatch years for 14C values measured in the earliest otolith growth from bomb-produced 14C chronologies provide compelling temporal constraints on the actual age. Age estimation from otoliths should be revisited to discover patterns of otolith growth that might correct for the discrepancies exhibited here. Specifically, it is recommended that transverse sections be investigated for increment structure that may not be present in the sagittal plane, as well as comparisons with other methods, like burnt and cracked otoliths. It is also recommended that a follow up study be conducted using bomb 14C dating on otoliths from Norway and other regions, using otolith mass as guidance in the experimental design, to further investigate the development of a validated age estimation method. Overall, if otolith mass can be considered a reasonable proxy for age and the ages generated from the bomb 14C alignments in this study are nearly accurate, then the lifespan of European eel may approach 100 years in the natural environment.

Supplementary material

To view supplementary material for this article, please visit https://doi.org/10.1017/RDC.2024.134.

Acknowledgments

Thank you to Negar Haghipour (AMS sample processing) along with Lukas Wacker, Marcus Christl, and Arno Synal (project support) from the Laboratory of Ion Beam Physics at ETH Zürich. Thanks to Russell Poole (Fisheries Ecosystems Advisory Services, Marine Institute, Newport, Ireland) for providing access to otolith age estimates and masses for European eel of Ireland. This work was supported in part for A.H. Andrews under the August T. Larsson Guest Researcher Programme at Sveriges Lantbruksuniversitet (Swedish University of Agricultural Sciences). This study was funded by the Norwegian Research Council (MAREEL; grant/award number: 280658) and by the Institute of Marine Research’s Coastal Ecosystems Program.

References

Als, TD, Hansen, MM, Maes, GE, Castonguay, M, Riemann, L, Aarestrup, K, Munk, P, Sparholt, H, Reinhold, H and Bernatchez, L (2011) All roads lead to home: Panmixia of European eel in the Sargasso Sea. Molecular Ecology 20, 13331346.CrossRefGoogle ScholarPubMed
American Geographical Society (1943) Ocean Currents and Sea Ice. Atlas of World Maps. United States Army Service Forces, Army Specialized Training Division. Army Service Forces Manual M-101. (Public Domain, United States Federal Government)Google Scholar
Andrews, AH and Scofield, TR (2021) Early overcounting in otoliths – a case study of age and growth for gindai (Pristipomoides zonatus) using bomb 14C dating. Fisheries and Aquatic Sciences 24, 5362.CrossRefGoogle Scholar
Andrews, AH, Barnett, BK, Allman, RJ, Moyer, RP, Trowbridge, HD (2013) Great longevity of speckled hind (Epinephelus drummondhayi), a deep-water grouper, with novel use of postbomb radiocarbon dating in the Gulf of Mexico. Canadian Journal of Fisheries and Aquatic Sciences 70(8), 11311140.CrossRefGoogle Scholar
Andrews, AH, Smale, MJ, Cowley, PD and Chang, N (2018a) Fifty-five-year longevity for the largest member of the family Sparidae: the endemic red steenbras Petrus rupestris from South Africa. African Journal of Marine Science 40, 343353.CrossRefGoogle Scholar
Andrews, AH, Humphreys, RL and Sampaga, JD (2018b) Blue marlin (Makaira nigricans) longevity estimates confirmed with bomb radiocarbon dating. Canadian Journal of Fisheries and Aquatic Sciences 75, 1725.CrossRefGoogle Scholar
Andrews, AH, Yeman, C, Welte, C, Hattendorf, B, Wacker, L and Christl, M (2019) Laser ablation accelerator mass spectrometry reveals complete bomb 14C signal in an otolith with confirmation of 60-year longevity for red snapper (Lutjanus campechanus). Marine and Freshwater Research 70, 17681780.CrossRefGoogle Scholar
Andrews, AH, Pacicco, A, Allman, R, Falterman, BJ, Lang, ET and Golet, W (2020) Age validation of yellowfin (Thunnus albacares) and bigeye (Thunnus obesus) tuna of the northwestern Atlantic Ocean. Canadian Journal of Fisheries and Aquatic Sciences 77, 637643.CrossRefGoogle Scholar
Andrews, AH, Daugherty, DJ, Wertnik, M, Welte, C, Smith, NG, Buckmeier, DL and Riecke, D (2024) Alligator Gar as a centenarian species—Extending lifespan estimates using bomb radiocarbon and Laser Ablation–Accelerator Mass Spectrometry. Marine and Freshwater Research 75, MF24024. doi: 10.1071/MF24024 CrossRefGoogle Scholar
Barnett, BK, Thornton, L, Allman, R, Chanton, JP and Patterson, WF (2018) Linear decline in red snapper (Lutjanus campechanus) otolith Δ14C extends the utility of the bomb radiocarbon chronometer for fish age validation in the Northern Gulf of Mexico. ICES Journal of Marine Science 75, 16641671.CrossRefGoogle Scholar
Bertin, L (1956) Eels, A Biological Study. London: Cleaver-Hume Press.Google Scholar
Bevacqua, D, Melià, P, Schiavina, M, Crivelli, AJ, De Leo, GA and Gatto, M (2019) A demographic model for the conservation and management of the European eel: An application to a Mediterranean coastal lagoon. ICES Journal of Marine Science 76, 21642178.Google Scholar
Bonhommeau, S, Castonguay, M, Sabatié, Rivot E and Le Pape, O (2010) The duration of migration of Atlantic Anguilla larvae. Fish and Fisheries 11, 289306.CrossRefGoogle Scholar
Campana, SE (2001) Accuracy, precision and quality control in age determination, including a review of the use and abuse of age validation methods. Journal of Fisheries Biology 59, 197242.CrossRefGoogle Scholar
Campana, SE, Casselman, JM and Jones, CM (2008) Bomb radiocarbon chronologies in the Arctic, with implications for the age validation of lake trout (Salvelinus namaycush) and other Arctic species. Canadian Journal of Fisheries and Aquatic Sciences 65, 733743.CrossRefGoogle Scholar
Casselman, JM, Jones, CM and Campana, SE (2019) Bomb radiocarbon age validation for the long-lived, unexploited Arctic fish species Coregonus clupeaformis . Marine and Freshwater Research 70, 17811788. doi: 10.1071/MF18354 CrossRefGoogle Scholar
Daverat, F, Beaulaton, L, Poole, R, Lambert, P, Wickström, H, Andersson, J, Aprahamian, M, Hizem, B, Elie, P, Yalcin-Özdilek, S and Gumus, A (2012) One century of eel growth: Changes and implications. Ecology of Freshwater Fish 21, 325–36.CrossRefGoogle Scholar
De Leo, GA and Gatto, M (1995) A size and age-structured model of the European eel (Anguilla anguilla). Canadian Journal of Fisheries and Aquatic Sciences 52, 13511367.CrossRefGoogle Scholar
Durif, CMF, Diserud, OH, Sandlund, OT, Thorstad, EB, Poole, R, Bergesen, K, Escobar-Lux, RH, Shema, S and Vøllestad, LA (2020) Age of European silver eels during a period of declining abundance in Norway. Ecology and Evolution 10, 48014815.CrossRefGoogle ScholarPubMed
Durif, CMF, Arts, M, Bertolini, F, Cresci, A, Daverat, F, Karlsbakk, E, Koprivnikar, J, Moland, E, Olsen, EM, Parzanini, C, Power, M, Rohtla, M, Skiftesvik, AB, Thorstad, E, Vøllestad, LA and Browman, HI (2023) The evolving story of catadromy in the European eel (Anguilla anguilla). ICES Journal of Marine Science 80, 22532265.CrossRefGoogle Scholar
Dwyer, KS, Treble, MA and Campana, SE (2016) Age and growth of Greenland Halibut (Reinhardtius hippoglossoides) in the Northwest Atlantic: A changing perception based on bomb radiocarbon analyses. Fisheries Research 179, 342350.CrossRefGoogle Scholar
Freiss, C and Sedberry, GR (2011) Age, growth, and spawning season of red bream (Beryx decadactylus) off the southeastern United States. Fishery Bulletin 109, 2033.Google Scholar
Hua, Q, Turnbull, JC, Santos, GM, Rakowski, AZ, Ancapichun, S, De Pol-Holz, R, Hammer, S, Lehman, SJ, Levin, I, Miller, JB, Palmer, JG and Turney, CSM (2022) Atmospheric radiocarbon for the period 1950–2019. Radiocarbon 64, 723745.CrossRefGoogle Scholar
Hupfeld, RN, Lackmann, AR, Andrews, AH, Welte, C and Jones, G (2023) Bomb radiocarbon dating reveals 40-year lifespan of Shovelnose Sturgeon (Scaphirhynchus platorynchus)—Implications for stock assessments of long-lived, primitive fishes. Fisheries Management and Ecology 30, 423435.CrossRefGoogle Scholar
ICES (2009a) Workshop on Age Reading of European and American Eel (WKAREA), 20–24 April 2009, Bordeaux, France. ICES CM 2009/ACOM:48. 66 p. https://doi.org/10.17895/ices.pub.19280528 CrossRefGoogle Scholar
ICES (2009b) Annex 4: Manual for the Ageing of Atlantic Eel. Workshop on Age Reading of European and American Eel (WKAREA), 20–24 April 2009, Bordeaux, France. ICES CM 2009. 57 p. https://doi.org/10.17895/ices.pub.19280528 CrossRefGoogle Scholar
ICES (2011) Report of the Workshop on Age Reading of European and American Eel (WKAREA2), 22–24 March 2011, Bordeaux, France. ICES CM 2011/ACOM:43. 35 p. https://doi.org/10.17895/ices.pub.19280858 CrossRefGoogle Scholar
Kalish, JM (1993) Pre- and post-bomb radiocarbon in fish otoliths. Earth and Planetary Science Letters 114, 549554.CrossRefGoogle Scholar
Kalish, JM, Nydal, R, Nedreaas, KH, Burr, GS and Eine, GL (2001) A time history of pre- and post-bomb radiocarbon in the Barents Sea derived from Arcto-Norwegian cod otoliths. Radiocarbon 43, 843855.CrossRefGoogle Scholar
Kettle, AJ and Haines, K (2006) How does the European eel (Anguilla anguilla) retain its population structure during its larval migration across the North Atlantic Ocean? Canadian Journal of Fisheries and Aquatic Sciences 63, 90106.CrossRefGoogle Scholar
Lackmann, AR, Andrews, AH, Butler, MG, Bielak-Lackmann, ES and Clark, ME (2019) Bigmouth Buffalo Ictiobus cyprinellus sets freshwater teleost record as improved age analysis reveals centenarian longevity. Communications Biology 2, Article #197 https://doi.org/10.1038/s42003-019-0452-0 CrossRefGoogle Scholar
Lecomte-Finiger, R (1992) Growth history and age at recruitment of European glass eels (Anguilla anguilla) as revealed by otolith microstructure. Marine Biology 114, 205210.CrossRefGoogle Scholar
Lecomte-Finiger, R (1994) The early life of the European eel. Nature 370, 424.CrossRefGoogle Scholar
Limburg, KE, Wickström, H, Svedäng, H, Elfman, M and Kristiansson, P (2003) Do stocked freshwater eels migrate? Evidence from the Baltic suggests “Yes”. American Fisheries Society Symposium 33, 275284.Google Scholar
Moriarty, C (1983) Age determination and growth rate of eels, Anguilla anguilla (L). Journal of Fish Biology 23, 257264.CrossRefGoogle Scholar
Neilson, JD and Campana, SE (2008) A validated description of age and growth of western Atlantic bluefin tuna (Thunnus thynnus). Canadian Journal of Fisheries and Aquatic Sciences 65, 15231527.CrossRefGoogle Scholar
Nydal, R, Gulliksen, S, Löveseth, K and Skogseth, FH (1984) Bomb 14C in the ocean surface 1966–1981. Radiocarbon 26, 745.CrossRefGoogle Scholar
Pacheco, C, Bustamante, C and Araya, M (2021) Mass-effect: Understanding the relationship between age and otolith weight in fishes. Fish and Fisheries 22, 623633.CrossRefGoogle Scholar
Palstra, AP, Jéhannet, P, Swinkels, W, Heinsbroek, LTN, Lokman, PM, Vesala, S, Tulonen, T, Lakka, T and Saukkonen, S (2020) First observations of a spontaneously matured female European eel (Anguilla anguilla). Scientific Reports 10, 2339.CrossRefGoogle ScholarPubMed
Panfili, J and Ximénès, MC (1994) Évaluation de l’âge et de la croissance de l’anguille européenne (Anguilla anguilla L.) en milieu continental: Méthodologies, validation, application en Méditerranée et comparaisons en Europe. Bulletin Francais De La Pêche Et De La Pisciculture 335, 4366.CrossRefGoogle Scholar
Panfili, J, Boulenger, C, Musseau, C and Crivelli, AJ (2022) Extreme variability in European eel growth revealed by an extended mark and recapture experiment in southern France and implications for management. Canadian Journal of Fisheries and Aquatic Sciences 79, 631641.CrossRefGoogle Scholar
Pike, C, Crook, V and Gollock, M (2020) Anguilla anguilla. The IUCN Red List of Threatened Species 2020, e.T60344A152845178. https://doi.org/10.2305/IUCN.UK.20202.RLTS.T60344A152845178.en CrossRefGoogle Scholar
Poole, WR and Reynolds, JD (1996) Growth rate and age at migration of Anguilla anguilla . Journal of Fish Biology 48, 633642.Google Scholar
Poole, WR and Reynolds, JD (1998) Variability on growth rate in European eel Anguilla anguilla (L.) in a western Irish catchment. Biology and Environment: Proceedings of the Royal Irish Academy 98B, 141145.Google Scholar
Reimer, PJ, Brown, TA and Reimer, RW (2004) Discussion: Reporting and calibration of post-bomb 14C data. Radiocarbon 46, 12991304.Google Scholar
Rohtla, M, Daverat, F, Arts, MT, Browman, HI, Parzanini, C, Skiftesvik, AB, Thorstad, EB, van der Meeren, T, Vøllestad, LA and Durif, CMF (2023) Habitat use and growth of yellow-stage European eel in coastal and freshwater ecosystems in Norway. Canadian Journal of Fisheries and Aquatic Sciences 80, 1426.CrossRefGoogle Scholar
Rozanski, K (1991) Consultants group meeting on 14C reference materials for radiocarbon laboratories. 18–20 February 1991, Vienna, Austria. Internal Report, IAEA, Vienna.Google Scholar
Schmidt, J (1923) IV. The breeding places of the eel. Philosophical Transactions of the Royal Society London B – Biological Sciences 211, 179208.Google Scholar
Scourse, JD, Wannamaker, AD, Weidman, C, Heinemeier, J, Reimer, PJ, Butler, PG, Witbaard, R, Richardson, CA (2012) The marine radiocarbon bomb pulse across the temperate North Atlantic: A compilation of Δ14C time histories from Arctica islandica growth increments. Radiocarbon 54, 165186.CrossRefGoogle Scholar
Shervette, VR, Overly, KE and Rivera Hernandez, JM (2021) Radiocarbon in otoliths of tropical marine fishes: Reference Δ14C chronology for north Caribbean waters. PloS ONE 16, e0251442.CrossRefGoogle ScholarPubMed
Shervette, VR, Rivera Hernandez, JM (2023) Queen triggerfish Balistes vetula: Validation of otolith-based age, growth, and longevity estimates via application of bomb radiocarbon. PLoS ONE 17, e0262281.Google Scholar
Svedäng, H, Wickström, H, Reizenstein, M, Holmgren, K and Florenius, P (1998) Accuracy and precision in eel age estimation, using otoliths of known and unknown age. Journal of Fish Biology 53, 456464.Google Scholar
Synal, H-A, Stocker, M and Suter, M (2007) MICADAS: A new compact radiocarbon AMS system. Nuclear Instruments and Methods in Physics Research Section B: Beam Interactions with Materials and Atoms 259, 713.CrossRefGoogle Scholar
Tesch, FW (2003) The Eel. Oxford: Blackwell Publishing, 408 p.CrossRefGoogle Scholar
Vøllestad, LA (1992) Geographic-variation in age and length at metamorphosis of maturing European Eel—Environmental-effects and phenotypic plasticity. Journal of Animal Ecology 61, 4148.CrossRefGoogle Scholar
Wacker, L, Christl, H and Synal, H-A (2010) Bats: A new tool for AMS data reduction. Nuclear Instruments and Methods in Physics Research B 268, 376379.CrossRefGoogle Scholar
Wacker, L, Fahrni, SM, Hajdas, I, Molnar, M, Synal, H-A, Szidat, S and Zhang, YL (2013a) A versatile gas interface for routine radiocarbon analysis with a gas ion source. Nuclear Instruments and Methods in Physics Research B 294, 315319.CrossRefGoogle Scholar
Wacker, L, Fülöp, R-H, Hajdas, I, Molnár, M and Rethemeyer, J (2013b) A novel approach to process carbonate samples for radiocarbon measurements with helium carrier gas. Nuclear Instruments and Methods in Physics Research B 294, 214217.CrossRefGoogle Scholar
Figure 0

Figure 1. Map of North Atlantic with surface current patterns relative to the migration path of European eel, with collection locations in Norway (orange stars), and the selected bomb-produced 14C chronology locations from across the North Atlantic and North America (nuclear symbols; see Figure 2). Eggs hatch in the Sargasso Sea and leptocephalus migrate to inshore and continental habitats of northern Africa, throughout Europe, and north to Scandinavia (blue shaded edges). Radiating contours of 10-, 15-, 25-, and 45-mm TL are European eel length limits, within which nothing greater than that length exists in surface water collections and are indicative of the northeasterly migration pattern (Schmidt 1923). The most applicable bomb 14C reference records are from coral and otoliths in the western North Atlantic (Gulf of Mexico, Caribbean, Bermuda, Antilles) because they represent levels expected for the North Atlantic Gyre (Sargasso Sea) and waters advected as the migration path along the Gulf Stream to locations like Norway. A reliable clam shell record from the North Sea provides insight on 14C levels that are mixed with northern Europe runoff (waters that European eel would cross when migrating to Norway) and is intermediate to the timely 14C records of the Arctic and Laurentian lakes of North America (expected to be similar freshwater 14C records of Norway). Base map was rendered from a classic ocean circulation map produced by American Geographic Society (1943) that remains accurate for general flow patterns with indications of warm tropical (orange) and cooler marginal (green) currents (an otolith 14C record from cool waters of the Labrador Current off Canada provide an example of an attenuated bomb 14C signal for the Northwestern Atlantic; Figure 2).

Figure 1

Table 1. European eel data for fish and otoliths used in this study that were collected in 2012–13 from Sunnmøre and Nedstrand, Norway, with estimated age from growth zone counting in sagittal otolith sections, readability score, measured 14C from otolith cores, and alternate age scenarios based on 14C reference records. Age from atmospheric chronology (Atm) are minimum ages and bold values are older than the original age estimates by at least the number of years in parenthesis. Data for EE009A/B are successive core extractions on same otolith specimen. The F14C values listed had a measurement error of ±12–16‰ from sample masses of ∼100–170 μg CaCO3 that generated 12–20 μg C. The number of years added from original age (+yrs) and hatch year (hyr) are provided to show shifts in age based on alignments of measured 14C values to each reference chronology

Figure 2

Figure 2. Selected bomb-produced 14C chronologies from across the North Atlantic and the northern freshwater hydrosphere that are applicable to otolith formation during the migrational early life history of European eel. The atmospheric chronology for the Northern Hemisphere (NH1)—a composite of 14C measurements from regions greater than 40°N latitude (Hua et al. 2022)—provides an absolute minimum age for the alignment of otolith 14C values from recent capture years. The tropical North Atlantic chronology is considered the most reliable temporal reference for the earliest growth of European eel because it is a composite of 14C references that would reflect the mean 14C levels in the mixed layer of the Sargasso Sea, the known natal grounds for this species (Andrews et al. 2013, 2020, Barnett et al. 2018, Shervette et al. 2023). The North America Lakes freshwater chronology, established from otoliths of Arctic and Laurentian fishes (Campana et al. 2008; Casselman et al. 2019; Lackmann et al. 2019), is the best available proxy for the freshwaters of Norway. An intermediate record from the North Sea—established by an Arctica islandica clam shell in the mixed German Bight (Scourse et al. 2012)—provides a proxy for a mixed 14C signal of North Atlantic waters that European eel would cross during migration to Norway. For a contrast in bomb 14C signal strength, a northwestern Atlantic otolith chronology (Campana et al. 2008) shows the strong attenuation effects of mixed deep waters that are 14C-deficient.

Figure 3

Figure 3. Alignments of 14C data from European eel (Anguilla anguilla) otoliths relative to the collection years (X with sample ID) that are projected back to hatch year scenarios (green dashed arrows) as determined by: 1) the original otolith section age estimations (open circles); 2) the minimum 14C age from an alignment with the atmospheric 14C chronology (blue triangles); 3) the most applicable 14C age from an alignment with the tropical seas chronology on the post-peak decline (orange diamonds); and 4) an extended 14C age (old age scenario) from an alignment with the 14C rise and peak period (blue squares). The grey circle connected to some data points is the second core from EE009 A/B (see Figure 5), the most massive otolith in the study and likely the oldest, as evidenced by the elevated 14C levels noted in Sargasso Sea DIC measurements (Nydal et al. 1984). The freshwater and mixed 14C chronologies are from North Sea and North America lakes as possible elevated alignment chronologies that depend on where this fish was during the otolith core formation period. The tropical seas chronology (Tropical North Atlantic) is also represented by the data from coral and otoliths (small yellow circles) to provide a visual on the variance associated with this 14C record.

Figure 4

Figure 4. Plots of European eel (Anguilla anguilla) age estimates versus otolith mass for the otoliths used in this study that provided an opportunity to investigate relationships for three age estimation scenarios (original age = annuli counting; decline age = alignment of 14C values to the post-peak decline; rise-decline age = an extension of the two most massive otoliths to the upper 14C rise and peak period). Because otolith mass is often a reasonably good proxy for age, these comparisons can provide insight on what age estimates are more likely to be accurate in the absence of known age otoliths. The original age estimates (open circles) provided the poorest fit with large inconsistencies in otolith mass accretion rates and an unrealistic intercept. Alignment of the otolith 14C values to the post-peak decline led to ages that made otolith mass a better proxy for age, but the best fit was when the two most massive otoliths were shifted to upper bomb 14C rise and intermediate peak positions (Figure 3).

Figure 5

Figure 5. Sagittal otolith sections from the European eel (EE009) with the most massive otolith (10.47 mg) showing (A) the core extractions and (B) the growth zone counting marked to attain the original age estimate of 14 years. The otolith core was extracted twice (A) with core 1 centered on the first 2 years of growth and core 2 as a concentric extraction to remove years 3 and 4. The overlay (B) shows how this specimen and the other otoliths were verified by tracing a microscopic view of the extraction area on the aged otoliths. An older age reading scenario that may account for the much greater age of 46 years is indicated with the white arrow extending from the nucleus to the edge, along which there are numerous finer increments that are currently considered subannual.

Supplementary material: File

Andrews et al. supplementary material

Andrews et al. supplementary material
Download Andrews et al. supplementary material(File)
File 158.2 KB