Results
Of the 214 specimens measured in this study, only 46 had directly measurable SLs, which ranged from 58.8 mm to 221.2 mm (Table S4). Morphometric analyses of those 46 specimens showed that each of the six morphological parameters tested increased with SL (Figure 2). Following regression analyses, Orbit Diameter, Vertebrae Width and Jaw Length were discounted as predictors of SL as the R 2 was lower than 80%, the F -statistics were relatively low and the residual error was relatively high (Table 2), indicating that these parameters poorly explained the variability in SL. Although Trunk Length R 2 was higher than 80%, a relatively high F -statistic and relatively low residual error, the sample size was much smaller than that of the other parameters ( n < 20). Therefore, Trunk Length was also discounted as a predictor of SL. Head Length and Head Height demonstrated the highest R 2 values, highest F -statistics, and the lowest residual error, indicating that these two parameters best explain the variability in SL (Table 2). Therefore, coefficients from linear regressions using the predictor parameters Head Length (Slope = 2.92, Intercept = 4.28) and Head Height (Slope = 2.12, Intercept = 10.11) were inserted into Equation 1 to estimate SL for incomplete specimens. In specimens where both Head Length and Head Height were available, the mean of the individual SL estimates from both Head Length and Head Height was used as the final estimate of SL.
Of the 54 samples analysed geochemically, 26 were associated with specimens of fish where SL was directly measured and 28 where SL was estimated from direct measurements of Head Length, Head Height or a mean of both. Forty-seven samples were from specimens of H. lewesiensis, with the remaining 7 either unassigned to species or assigned to other species.
Measured 𝛿 18 O values ranged from -1.9 to -3.6‰, which equated to seawater temperature estimates of 19.5 to 27.1°C respectively (Table 3). For H. lewesiensis, a significant inverse relationship between SL and estimated seawater temperatures is recorded ( r (45) = -.35, p = .015), indicating that sizes are smaller at higher estimated temperatures (Figure 3). There were insufficient specimens to test this relationship in other Hoplopteryx species separately. For the whole Hoplopteryx spp. dataset ( n = 54), SL was inversely correlated to estimated temperature, but this relationship was not significant ( r (52) = -.13, p = .34).
Measured 𝛿 13 C values ranged from 1.3 to 4.2‰ across the 54 samples, (Table 3). There was a strong, significant negative correlation between SL and 𝛿 13 C in both H. lewesiensis ( r (45) = -.54, p = <.001) and in Hoplopteryx spp. ( r (52) = -.45, p = <.001) (Figure 4). Notably, there was no significant correlation between 𝛿 13 C and 𝛿 18 O in the chalk matrix samples ( R 2 = <.01) (Figure S2), suggesting the two palaeoenvironmental proxies are independent of each other. Furthermore, the lack of correlation between carbon and oxygen isotope values is an indicator of weak pore fluid-rock interaction, and therefore minimal diagenetic alteration to isotopic signatures (Huber et al., 2024).
Body size and seawater temperature
By combining morphometric measurements of fossil specimens with geochemical analysis of their surrounding chalk matrix, our study provides the first test of the size-temperature relationship in an extinct member of the extant and commercially important deep-sea fish family Trachichthyidae. We found a significant positive correlation between the Standard Length of individuals of the species Hoplopteryx lewesiensis, which is the most common trachichthyid species from the Upper Cretaceous British Chalk Group, and the 𝛿 18 O values of the chalk matrix surrounding each specimen. When 𝛿 18 O values were converted to estimates of seawater temperature, following a well-established approach and using standard assumptions, our results show a significant negative correlation between the Standard Length of H. lewesiensis and seawater temperature; i.e. body size decreased with increasing seawater palaeotemperature.
These results are consistent with studies of similarly sized extant fish, which show that higher temperatures have led to smaller body size (Audzijonyte et al., 2020). They provide further support for the prediction that marine animals in general, and fish in particular, will decline in body size with current and future ocean warming owing to reduction in dissolved oxygen concentrations (e.g. Sheridan and Bickford, 2011; Cheung et al., 2013). Although it is possible that the Trachichthyidae may have evolved greater resilience to temperature change since the Late Cretaceous, given the limited data available for living slimeheads (Clark et al., 2000; Thresher et al., 2007) , our results provide an insight into how current climate warming may impact the body sizes of living members of this family.
We did not find a significant relationship between estimated seawater temperature and body size in our genus-level analysis, which we attribute to the confounding effect of inter-species variation in body size in the different Hoplopteryx species (Patterson, 1964). Furthermore, a number of specimens within our genus-level database were unable to be assigned to individual species, and it is possible that they may represent juveniles rather than adults (see discussion below). For those specimens that were assigned to other species, (e.g. to H. simus, H. macrocanthus ), there were insufficient numbers to undertake robust species-level statistical analyses.
Body size and 𝛿 13 C
A significant negative correlation between the Standard Length and the δ 13 C values of the surrounding chalk matrix was found for both the genus Hoplopteryx and for the species H. lewesiensis, with the smallest fish being associated with the most positive δ 13 C values. The interpretation of these results is not straightforward because there are many interacting biotic and abiotic factors which can affect the 𝛿 13 C signature of marine carbonates such as chalk. The primary controls on 𝛿 13 C in chalk are widely considered to be primary productivity and burial of organic matter in seafloor sediments (Jarvis et al., 2002, 2006; Mitchell et al., 1996). Carbon isotope fractionation during marine photosynthesis leads to organic matter enriched in 12 C and the remaining carbon pool in the surrounding water, from which marine organisms precipitate their skeletal carbonates and, therefore becomes relatively enriched in 13 C (Jarvis et al., 2002). The burial of this 13 C-depleted organic matter in seafloor sediments further enhances this process by removing relatively more 12 C from the system. Thus, during times of enhanced productivity and/or greater burial of organic matter, the 𝛿 13 C of marine carbonates is expected to be more positive (e.g. Mitchell et al., 1996). Our results, therefore, indicate that Hoplopteryx became smaller with an increase in productivity and/or burial of organic matter.
Interpreting these results in terms of changes in productivity is problematic. Although we have no direct evidence of the diet of Hoplopteryx, it might be expected that greater primary productivity would have increased available food supply at higher trophic levels, which in turn would lead to an increase in Hoplopteryx body size (e.g. Mora et al., 2013 and references therein) . Unless, perhaps, Hoplopteryx was adapted to more oligotrophic conditions, which have been inferred for the offshore environments of the UK chalk seas (Püttmann and Mutterlose, 2021), and higher productivity caused a negative impact on body size. Our results are easier to interpret, however, if burial of organic matter is the most significant factor controlling the 𝛿 13 C of the bulk chalk. Increasing organic matter burial could be achieved by increasing the area of seafloor available, for example at times of higher global sea-level (Mitchell et al., 1996), or by reducing the dissolved oxygen content at or near the seafloor, enhancing preservation potential (Jarvis et al., 2002). The latter could explain why Hoplopteryx size decreases as 𝛿 13 C increases, as reduced oxygen availability is known to limit fish growth and size (e.g. Cheung et al., 2013; Pörtner and Knust, 2007; Sheridan and Bickford, 2011).
Standard Length increases through ontogeny and in some fish, there is also a substantial size difference between the two sexes. It is, unfortunately, often impossible to determine either the sex or ontogenetic stage of a fossilised individual, unless ontogenetic differences or sexual dimorphism are clearly recorded in the preserved skeletal tissues. Here we consider the extent to which either factor could have biased these results.
In extant Trachichthyidae, there is evidence of sexual dimorphism in some species, but not all (D’onghia et al., 1998; Dunn and Forman, 2011; Elliott et al., 1995; Shimizu, 1977). Even in species where it may occur, the size difference between sexes is relatively small (D’onghia et al., 1998; Elliott et al., 1995; Tracey, 1999). Determining the sex of a fossil fish from partial skeletal remains is challenging at best and, in common with nearly all palaeontological studies, we were not able to do this for our specimens. We note, however, that the size distribution of our dataset is unimodal (Figs. S3 and S4), and so even if Hoplopteryx is shown to have size-related sexual dimorphism, it is unlikely to have biased our data or caused the significant correlations between Standard Length and chalk 𝛿 18 O values/seawater temperature or chalk 𝛿 13 C values.
The possible impact of ontogeny on our results is more difficult to determine, as methods to determine ontogeny in fish from skeletal remains are limited. Biological age determination using otoliths is the most reliable method of age determination in fishes (Khan et al., 2013). However, otoliths have not been reported from any British Chalk Group fish taxon, probably owing to early diagenetic loss of aragonite (Friedman et al., 2016), so we could not use this technique. Instead, we attempted to assess the biological age of individual specimens by counting the circuli and annuli preserved in their scales. Unfortunately, very few individuals ( n = 11) preserved visible, measurable circuli, and therefore the correlation between size and age was inconclusive. An alternative approach may be to use computed tomography to image the scales (Thomson and McCune, 1984), but this was not possible during our study. In the absence of ontogenetic data, we therefore assume that the randomly selected subset of individuals chosen for geochemical analysis all represent adults.
Conclusion
Our study is the first to demonstrate a significant relationship between seawater palaeotemperature and the body size of an extinct species of Trachichthyidae. We show a significant negative correlation between estimated seawater temperature, inferred from oxygen isotope analysis, and body size in the Late Cretaceous species Hoplopteryx lewesiensis from the British Chalk Group . Additionally, a significant negative correlation was found between Hoplopteryx body size and carbon isotope values (𝛿 13 C) of the surrounding chalk, indicating that other abiotic factors also influenced body size in this group of fish through the Late Cretaceous. Our study demonstrates the importance of utilising the fossil record as an alternative source of data to test the size-temperature relationship in marine animals such as deep-sea fish.
LITERATURE CITED
Ahti, P.A., Kuparinen, A. and Uusi-Heikkilä, S. (2020), “Size does matter — the eco-evolutionary effects of changing body size in fish”, Environmental Reviews, NRC Research Press, Vol. 28 No. 3, pp. 311–324, doi: 10.1139/er-2019-0076.Anderson, T.F. and Arthur, M.A. (1983), “Stable Isotopes of Oxygen and Carbon and their Application to Sedimentologic and Paleoenvironmental Problems”, in Arthur, M.A., Anderson, T.F., Kaplan, I.R., Veizer, J. and Land, L.S. (Eds.), Stable Isotopes in Sedimentary Geology, Vol. 10, SEPM Society for Sedimentary Geology, doi: 10.2110/scn.83.01.0000.Atkinson, D. (1994), “Temperature and Organism Size—A Biological Law for Ectotherms?”, edited by Begon, M. and Fitter, A.H. Advances in Ecological Research, Vol. 25, pp. 1–58, doi: 10.1016/S0065-2504(08)60212-3.Audzijonyte, A., Richards, S.A., Stuart-Smith, R.D., Pecl, G., Edgar, G.J., Barrett, N.S., Payne, N., et al. (2020), “Fish body sizes change with temperature but not all species shrink with warming”, Nature Ecology & Evolution, Nature Publishing Group, Vol. 4 No. 6, pp. 809–814, doi: 10.1038/s41559-020-1171-0.Baudron, A.R., Needle, C.L., Rijnsdorp, A.D. and Tara Marshall, C. (2014), “Warming temperatures and smaller body sizes: synchronous changes in growth of North Sea fishes”, Global Change Biology, Vol. 20 No. 4, pp. 1023–1031, doi: 10.1111/gcb.12514.Bell, F.G., Culshaw, M.G. and Cripps, J.C. (1999), “A review of selected engineering geological characteristics of English Chalk”, Engineering Geology, Vol. 54 No. 3–4, pp. 237–269, doi: 10.1016/S0013-7952(99)00043-5.Berg, L.S. (1958), “XII. Klasse Teleostomi”, System Der Rezenten Und Fossilien Fischartigen Und Fische / Classification of Fishes Both Recent and Fossil [Translated by H. Kirchhoff], VEB Deutscher Verlag der Wissenschaften, Berlin, Germany, p. 241.Bergmann, C. (1847), “About the relationships between heat conservation and body size of animals.”, Goett Stud, Vol. 1, pp. 595–708.Brand, W.A., Coplen, T.B., Vogl, J., Rosner, M. and Prohaska, T. (2014), “Assessment of international reference materials for isotope-ratio analysis (IUPAC Technical Report)”, Pure and Applied Chemistry, De Gruyter, Vol. 86 No. 3, pp. 425–467, doi: 10.1515/pac-2013-1023.Bulman, C. and Koslow, J. (1992), “Diet and food consumption of a deep-sea fish orange roughy Hoplostethus atlanticus (Pisces Trachichthyidae), off southeastern Australia”, Marine Ecology Progress Series, Vol. 82, pp. 115–129, doi: 10.3354/meps082115.Cheung, W.W.L., Sarmiento, J.L., Dunne, J., Frölicher, T.L., Lam, V.W.Y., Deng Palomares, M.L., Watson, R., et al. (2013), “Shrinking of fishes exacerbates impacts of global ocean changes on marine ecosystems”, Nature Climate Change, Nature Publishing Group, Vol. 3 No. 3, pp. 254–258, doi: 10.1038/nclimate1691.Clark, M.R., Anderson, O.F., Chris Francis, R.I.C. and Tracey, D.M. (2000), “The effects of commercial exploitation on orange roughy ( Hoplostethus atlanticus ) from the continental slope of the Chatham Rise, New Zealand, from 1979 to 1997”, Fisheries Research, Vol. 45 No. 3, pp. 217–238, doi: 10.1016/S0165-7836(99)00121-6.Cohen, K.M., Finney, S.C., Gibbard, P.L. and Fan, J.X. (2013), “The ICS International Chronostratigraphic Chart”, International Commission on Stratigraphy.Coplen, T.B. (2011), “Guidelines and recommended terms for expression of stable-isotope-ratio and gas-ratio measurement results”, Rapid Communications in Mass Spectrometry, Vol. 25 No. 17, pp. 2538–2560, doi: 10.1002/rcm.5129.Daufresne, M., Lengfellner, K. and Sommer, U. (2009), “Global warming benefits the small in aquatic ecosystems”, Proceedings of the National Academy of Sciences, Proceedings of the National Academy of Sciences, Vol. 106 No. 31, pp. 12788–12793, doi: 10.1073/pnas.0902080106.D’onghia, G., Tursi, A., Marano, C.A. and Basanisi, M. (1998), “Life History Traits of Hoplostethus Mediterraneus (Pisces: Beryciformes) From the North-Western Ionian Sea (Mediterranean Sea)”, Journal of the Marine Biological Association of the United Kingdom, Vol. 78 No. 1, pp. 321–339, doi: 10.1017/S002531540004011X.Dunn, M.R. and Forman, J.S. (2011), “Hypotheses of Spatial Stock Structure in Orange Roughy Hoplostethus atlanticus Inferred from Diet, Feeding, Condition, and Reproductive Activity.”, PLoS ONE, Vol. 6 No. 11, p. e26704, doi: 10.1371/journal.pone.0026704.Elliott, N.G., Haskard, K. and Koslow, J.A. (1995), “Morphometric analysis of orange roughy (Hoplostethus atlanticus) off the continental slope of southern Australia”, Journal of Fish Biology, Vol. 46 No. 2, pp. 202–220, doi: 10.1111/j.1095-8649.1995.tb05962.x.Engelman, R.K. (2023), “A Devonian Fish Tale: A New Method of Body Length Estimation Suggests Much Smaller Sizes for Dunkleosteus terrelli (Placodermi: Arthrodira)”, Diversity, Multidisciplinary Digital Publishing Institute, Vol. 15 No. 3, p. 318, doi: 10.3390/d15030318.Fabricius, I. (2007), “Chalk: composition, diagenesis and physical properties”, Bulletin of The Geological Society of Denmark, Vol. 55, pp. 97–128.Forster, J., Hirst, A.G. and Atkinson, D. (2012), “Warming-induced reductions in body size are greater in aquatic than terrestrial species”, Proceedings of the National Academy of Sciences, Proceedings of the National Academy of Sciences, Vol. 109 No. 47, pp. 19310–19314, doi: 10.1073/pnas.1210460109.Friedman, M., Beckett, H.T., Close, R.A. and Johanson, Z. (2016), “The English Chalk and London Clay: two remarkable British bony fish Lagerstätten”, Geological Society, London, Special Publications, The Geological Society of London, Vol. 430 No. 1, pp. 165–200, doi: 10.1144/SP430.18.Genner, M.J., Sims, D.W., Southward, A.J., Budd, G.C., Masterson, P., Mchugh, M., Rendle, P., et al. (2010), “Body size-dependent responses of a marine fish assemblage to climate change and fishing over a century-long scale”, Global Change Biology, Vol. 16 No. 2, pp. 517–527, doi: 10.1111/j.1365-2486.2009.02027.x.Grouard, S., Perdikaris, S., Espindola Rodrigues, N.E. and Quitmyer, I.R. (2019), “Size estimation of pre-Columbian Caribbean fish”, International Journal of Osteoarchaeology, Vol. 29 No. 3, pp. 452–468, doi: 10.1002/oa.2782.Huber, S.J., Schlidt, V., Seitz, H.-M., Kniest, J.F., Raddatz, J., Marschall, H.R. and Voigt, S. (2024), “Assessment of Chalk as an Archive for the Lithium Isotope Composition of Seawater”, Geochemistry, Geophysics, Geosystems, Vol. 25 No. 2, p. e2023GC011150, doi: 10.1029/2023GC011150.Jablonski, D. (2004), “Extinction: past and present”, Nature, Nature Publishing Group, Vol. 427 No. 6975, pp. 589–589, doi: 10.1038/427589a.James, F.C. (1970), “Geographic Size Variation in Birds and Its Relationship to Climate”, Ecology, Vol. 51 No. 3, pp. 365–390, doi: 10.2307/1935374.Jarvis, I., Gale, A.S., Jenkyns, H.C. and Pearce, M.A. (2006), “Secular variation in Late Cretaceous carbon isotopes: a new δ13C carbonate reference curve for the Cenomanian–Campanian (99.6–70.6 Ma)”, Geological Magazine, Vol. 143 No. 5, pp. 561–608, doi: 10.1017/S0016756806002421.Jarvis, I., Mabrouk, A., Moody, R.T.J. and de Cabrera, S. (2002), “Late Cretaceous (Campanian) carbon isotope events, sea-level change and correlation of the Tethyan and Boreal realms”, Palaeogeography, Palaeoclimatology, Palaeoecology, Vol. 188 No. 3, pp. 215–248, doi: 10.1016/S0031-0182(02)00578-3.Jenkyns, H.C., Gale, A.S. and Corfield, R.M. (1994), “Carbon- and oxygen-isotope stratigraphy of the English Chalk and Italian Scaglia and its palaeoclimatic significance”, Geological Magazine, Vol. 131 No. 1, pp. 1–34, doi: 10.1017/S0016756800010451.Khan, S., Afzal Khan, M. and Miyan, K. (2013), “Precision of age determination from otoliths, opercular bones, scales and vertebrae in the threatened freshwater snakehead, Channa punctata (Bloch, 1793)”, Journal of Applied Ichthyology, Vol. 29 No. 4, pp. 757–761, doi: 10.1111/jai.12225.Kim, S.-T., Coplen, T.B. and Horita, J. (2015), “Normalization of stable isotope data for carbonate minerals: Implementation of IUPAC guidelines”, Geochimica et Cosmochimica Acta, Vol. 158, pp. 276–289, doi: 10.1016/j.gca.2015.02.011.Lorance, P., Uiblein, F. and Latrouite, D. (2002), “Habitat, behaviour and colour patterns of orange roughy Hoplostethus atlanticus (Pisces: Trachichthyidae) in the Bay of Biscay”, Journal of the Marine Biological Association of the United Kingdom, Cambridge University Press, Vol. 82 No. 2, pp. 321–331, doi: 10.1017/S0025315402005519.Mace, P.M., Fenaughty, J.M., Coburn, R.P. and Doonan, I.J. (1990), “Growth and productivity of orange roughy (Hoplostethus atlanticus) on the North Chatham Rise”, New Zealand Journal of Marine and Freshwater Research, Vol. 24 No. 1, pp. 105–119.Madurell, T. and Cartes, J.E. (2005), “Temporal changes in feeding habits and daily rations of Hoplostethus mediterraneus in the bathyal Ionian Sea (eastern Mediterranean)”, Marine Biology, Vol. 146 No. 5, pp. 951–962, doi: 10.1007/s00227-004-1502-8.Millien, V., Kathleen Lyons, S., Olson, L., Smith, F.A., Wilson, A.B. and Yom-Tov, Y. (2006), “Ecotypic variation in the context of global climate change: revisiting the rules”, Ecology Letters, Vol. 9 No. 7, pp. 853–869, doi: 10.1111/j.1461-0248.2006.00928.x.Mitchell, S., Paul, C. and Gale, A. (1996), “Carbon isotopes and sequence stratigraphy”, Geological Society, London, Special Publications, Vol. 104, pp. 11–24, doi: 10.1144/GSL.SP.1996.104.01.02.Mora, C., Wei, C.-L., Rollo, A., Amaro, T., Baco, A.R., Billett, D., Bopp, L., et al. (2013), “Biotic and Human Vulnerability to Projected Changes in Ocean Biogeochemistry over the 21st Century”, PLOS Biology, Public Library of Science, Vol. 11 No. 10, p. e1001682, doi: 10.1371/journal.pbio.1001682.Nelson, J.S., Grande, T.C. and Wilson, M.V.H. (2016), Fishes of the World, Fifth Edition., John Wiley & Sons.Patterson, C. (1964), “A Review of Mesozoic Acanthopterygian Fishes, with Special Reference to Those of the English Chalk”, Philosophical Transactions of the Royal Society of London. Series B, Biological Sciences, The Royal Society, Vol. 247 No. 739, pp. 213–482.Paul, D., Skrzypek, G. and Fórizs, I. (2007), “Normalization of measured stable isotopic compositions to isotope reference scales – a review”, Rapid Communications in Mass Spectrometry, Vol. 21 No. 18, pp. 3006–3014, doi: 10.1002/rcm.3185.Peters, R.H. (1983), The Ecological Implications of Body Size, Cambridge University Press, Cambridge, UK.Pörtner, H.O. and Knust, R. (2007), “Climate change affects marine fishes through the oxygen limitation of thermal tolerance”, Science (New York, N.Y.), Vol. 315 No. 5808, pp. 95–97, doi: 10.1126/science.1135471.Püttmann, T. and Mutterlose, J. (2021), “Paleoecology of Late Cretaceous Coccolithophores: Insights From the Shallow-Marine Record”, Paleoceanography and Paleoclimatology, Vol. 36 No. 3, p. e2020PA004161, doi: 10.1029/2020PA004161.van Rijn, I., Buba, Y., DeLong, J., Kiflawi, M. and Belmaker, J. (2017), “Large but uneven reduction in fish size across species in relation to changing sea temperatures”, Global Change Biology, Vol. 23 No. 9, pp. 3667–3674, doi: 10.1111/gcb.13688.Santrock, J., Studley, S.A. and Hayes, J.M. (1985), “Isotopic analyses based on the mass spectrum of carbon dioxide”, Analytical Chemistry, Vol. 57 No. 7, pp. 1444–1448, doi: 10.1021/ac00284a060.Sheridan, J.A. and Bickford, D. (2011), “Shrinking body size as an ecological response to climate change”, Nature Climate Change, Nature Publishing Group, Vol. 1 No. 8, pp. 401–406, doi: 10.1038/nclimate1259.Shimizu, T. (1977), “Comparative Morphology Of The Expanded Epipleural And Its Associated Structures In Four Species Of The Trachichthyidae.”, Jap. J. Ichthyol, Vol. 23 No. 4, pp. 192–198.Thomson, K.S. and McCune, A.R. (1984), “Scale Structure as Evidence of Growth Patterns in Fossil Semionotid Fishes”, Journal of Vertebrate Paleontology, [Society of Vertebrate Paleontology, Taylor & Francis, Ltd.], Vol. 4 No. 3, pp. 422–429.Thresher, R.E., Koslow, J.A., Morison, A.K. and Smith, D.C. (2007), “Depth-mediated reversal of the effects of climate change on long-term growth rates of exploited marine fish”, Proceedings of the National Academy of Sciences, Proceedings of the National Academy of Sciences, Vol. 104 No. 18, pp. 7461–7465, doi: 10.1073/pnas.0610546104.Todd, C.D., Hughes, S.L., Marshall, C.T., MacLEAN, J.C., Lonergan, M.E. and Biuw, E.M. (2008), “Detrimental effects of recent ocean surface warming on growth condition of Atlantic salmon”, Global Change Biology, Vol. 14 No. 5, pp. 958–970, doi: 10.1111/j.1365-2486.2007.01522.x.Tracey. (1999), “Background and review of ageing orange roughy (Hoplostethus atlanticus, Trachichthyidae) from New Zealand and elsewhere”.Wefer, G. and Berger, W.H. (1991), “Isotope paleontology: growth and composition of extant calcareous species”, Marine Geology, Vol. 100 No. 1, pp. 207–248, doi: 10.1016/0025-3227(91)90234-U.Wilkin, J. (2021), Introduction to the Principles of δ18O, δ13C, and 87Sr/86Sr in the Palaeosciences., preprint, PaleorXiv, doi: 10.31233/osf.io/kn7cw.
TABLES
Table 1: Definitions of the seven morphological parameters measured in this study .
| Head Length | Length from the tip of the snout to the anterior of the operculum |
| Head Height | Length from the most dorsal to the most ventral point of the head, perpendicular to head length |
| Jaw Length | Length from the most anterior to the most posterior point of the visible jawbone(s) |
| Orbit Diameter | Length of the eye socket from the most anterior to the most posterior point |
| Trunk Length | Length from the most anterior point behind the head, to the point just before any preserved a-l fin rays |
| Vertebrae Width | Length of the most anterior visible vertebra, from its most anterior to most posterior point |
| Standard Length (SL) | Length from the tip of the snout to the base of the tail |
Table 2: Results of regression analyses of each morphological parameter.
| Head Length | 39 | 0.89 | 294.4 | 13.69 on 38 df. |
| Head Height | 33 | 0.85 | 185.8 | 14.53 on 32 df. |
| Trunk Length | 15 | 0.91 | 142.3 | 13.28 on 14 df. |
| Vertebrae Width | 32 | 0.78 | 110.3 | 18.94 on 31 df. |
| Jaw Length | 35 | 0.74 | 96.35 | 18.54 on 34 df. |
| Orbit Diameter | 31 | 0.61 | 46.23 | 23.70 on 30 df. |
Table 3: Geochemical and Standard Length (SL) data collected from Hoplopteryx spp. specimens at the Natural History Museum, UK. Estimated SL are in bold. Italicised SL are the mean of two measurements. Minimum and maximum estimated or measured SL are listed where applicable.
| PV OR 36917(a) | lewesiensis | -2.82 | 23.7 | 2.29 | 61.6 | 61.4 | 61.9 |
| PV P 5423 | lewesiensis | -3.3 | 25.9 | 3.02 | 80.6 | 76.45 | 84.7 |
| PV OR 25827 | lewesiensis | -2.93 | 24.2 | 2.09 | 82.2 | 81.4 | 83.1 |
| PV OR 41993 | ? | -1.86 | 19.5 | 2.02 | 83.2 | - | - |
| PV P 10222 | simus | -2.53 | 22.4 | 1.62 | 86.7 | 85.9 | 87.5 |
| PV OR 4012 | lewesiensis | -3.38 | 26.3 | 2.32 | 90.1 | - | - |
| PV P 6464 | lewesiensis | -2.99 | 24.5 | 2.99 | 96 | 92.7 | 99.4 |
| PV OR 4008 | lewesiensis | -3.31 | 25.9 | 2.41 | 107.5 | 107.5 | 107.6 |
| PV OR 4026 | lewesiensis | -3.28 | 25.8 | 2.4 | 113.4 | 111.9 | 114.8 |
| PV OR 33230 | macrocanthus | -2.2 | 21 | 1.91 | 113.5 | - | - |
| PV OR 49038 | lewesiensis | -2.89 | 24 | 2.24 | 113.7 | - | - |
| PV P 1948(d) | lewesiensis | -3.04 | 24.7 | 3.01 | 116.1 | - | - |
| PV OR 25912 | lewesiensis | -3.3 | 25.9 | 1.38 | 117.2 | 105.5 | 129.0 |
| PV P 1948(a) (1) | lewesiensis | -3.12 | 25.1 | 1.93 | 118.6 | 118.0 | 119.1 |
| PV OR 4011 | lewesiensis | -3.22 | 25.5 | 2.28 | 127.2 | - | - |
| PV OR 25863 | lewesiensis | -3.09 | 24.9 | 2.39 | 130.2 | 124.2 | 136.1 |
| PV OR 49041(1) | lewesiensis | -2.97 | 24.4 | 1.58 | 131.9 | - | - |
| PV OR 49888 | lewesiensis | -3.36 | 26.2 | 2.88 | 132 | 118.4 | 145.6 |
| PV OR 49867(1) | lewesiensis | -3.27 | 25.7 | 1.92 | 134.8 | - | - |
| PV P 5420 | lewesiensis | -2.69 | 23.1 | 3.14 | 141 | 137.4 | 144.6 |
| PV P 4842 | lewesiensis | -2.98 | 24.4 | 2.21 | 143.3 | - | - |
| PV OR 4019 | lewesiensis | -2.93 | 24.2 | 1.53 | 146.7 | 142.5 | 151.0 |
| PV OR 4014 | lewesiensis | -2.33 | 21.5 | 1.94 | 149.4 | 148.8 | 150.1 |
| PV OR 4016 | lewesiensis | -2.98 | 24.4 | 2.83 | 151.5 | 149.1 | 154.0 |
| PV OR 49870 | lewesiensis | -3.38 | 26.3 | 2.35 | 151.8 | - | - |
| PV OR 41104 | gephyrognathus | -2.89 | 24 | 4.24 | 158.2 | 145.8 | 170.6 |
| PV OR 25781 | lewesiensis | -2.63 | 22.9 | 3.01 | 158.2 | 157.7 | 158.6 |
| PV OR 4106 | lewesiensis | -2.8 | 23.6 | 2.12 | 158.4 | 149.8 | 167.1 |
| PV OR 25841 | lewesiensis | -3.11 | 25 | 1.91 | 162.4 | - | - |
| PV P 5690 | lewesiensis | -2.85 | 23.8 | 2 | 162.5 | 159.7 | 165.3 |
| PV P 7189 | lewesiensis | -3.56 | 27.1 | 1.92 | 162.5 | 154.3 | 170.7 |
| PV OR 41105(a) | lewesiensis | -2.67 | 23 | 2.03 | 164.2 | 161.0 | 167.5 |
| PV OR 4015 | lewesiensis | -2.24 | 21.2 | 1.93 | 165.8 | 151.8 | 179.8 |
| PV OR 4109 | lewesiensis | -2.86 | 23.9 | 1.3 | 166.8 | - | - |
| PV P 5692 | lewesiensis | -3.24 | 25.6 | 1.71 | 166.9 | 166.0 | 167.8 |
| PV P 73798 | lewesiensis | -3.07 | 24.8 | 2.98 | 167.7 | - | - |
| PV P 5693 | lewesiensis | -3.17 | 25.3 | 1.7 | 169.4 | 158.5 | 180.4 |
| PV P 1948(b) | lewesiensis | -2.69 | 23.1 | 1.75 | 171.1 | 170.9 | 171.4 |
| PV OR 4021a | lewesiensis | -3.32 | 26 | 1.96 | 172.4 | 164.2 | 180.6 |
| PV OR 79 | lewesiensis | -2.37 | 21.7 | 1.98 | 172.4 | 171.4 | 173.4 |
| PV OR 28392 | ? | -3.21 | 25.5 | 1.41 | 177.5 | 166.7 | 188.3 |
| PV OR 49037 | lewesiensis | -2.67 | 23 | 2.02 | 179.9 | 174.2 | 185.5 |
| PV P 5694 | lewesiensis | -2.96 | 24.3 | 1.92 | 180.7 | - | - |
| PV P 5688 | lewesiensis | -3.12 | 25.1 | 1.71 | 180.9 | 178.5 | 183.3 |
| PV P 4297 | sp | -2.97 | 24.4 | 1.98 | 184.2 | 177.5 | 190.9 |
| PV P 5689 | lewesiensis | -3.21 | 25.5 | 1.73 | 185.6 | 181.3 | 190.0 |
| PV P 51289 | lewesiensis | -2.83 | 23.8 | 1.96 | 190.2 | - | - |
| PV OR 49862 | lewesiensis | -2.77 | 23.5 | 1.96 | 195.8 | 176.9 | 214.7 |
| PV P 5687 | lewesiensis | -3.3 | 25.9 | 1.62 | 198.0 | 196.09 | 199.95 |
| PV P 9909 | lewesiensis | -2.75 | 23.4 | 1.27 | 204.1 | - | - |
| PV OR 49863 | lewesiensis | -2.53 | 22.4 | 1.47 | 205.6 | 188.4 | 222.9 |
| PV OR 35712 | lewesiensis | -2.91 | 24.1 | 2.1 | 208.3 | 208.2 | 208.5 |
| PV OR 49043 | lewesiensis | -2.53 | 22.4 | 1.63 | 221.2 | 220.6 | 221.8 |
| PV OR 4239 | ? | -3.17 | 25.3 | 1.93 | 222.8 | 197.5 | 248.1 |
FIGURE LEGENDS
Figure 1: Hoplopteryx lewesiensis specimen (NHMUK PV P 51289) labelled with the seven morphological parameters measured in this study (definitions in Table 1).
Figure 2: The relationship between Standard Length (SL) and each morphometric parameter in Hoplopteryx spp. Each dot represents one specimen. Colours represent different morphological parameters, as shown in the key. A regression line (y~x) has been fitted to each parameter dataset. Sample sizes are shown on the plot.
Figure 3: The relationship between 𝛿 18 O-derived seawater temperature estimates and Standard Length (SL) in (A) Hoplopteryx spp. and (B) Hoplopteryx lewesiensis . Estimated points show a mean from Head Length and Head Height SL estimates. Measured points either show the true SL measurement or a mean of two repeats. The error bars on estimated SL points show the smallest and largest estimates. No error bars are shown on measured SL points as the smallest and largest values of repeat measurements were smaller than the size of the symbol. Sample sizes are shown on each plot. A regression line (y~x) is added to each plot and the grey-shaded areas represent a 95% confidence interval.
Figure 4: The relationship between 𝛿 13 C and Standard Length (SL) in (A) Hoplopteryx spp. and (B) Hoplopteryx lewesiensis . Estimated points show a mean from Head Length and Head Height SL estimates. Measured points either show the true SL measurement or a mean of two repeats. The error bars on estimated SL points show the smallest and largest estimates. No error bars are shown on measured SL points as the smallest and largest values of repeat measurements were smaller than the size of the symbol. Sample sizes are shown on each plot. A regression line (y~x) is added to each plot and the grey-shaded areas represent a 95% confidence interval.
DATA ACCESSIBILITY STATEMENT
The authors confirm that the data supporting the findings of this study are available within the article and its Supporting Information.
COMPETING INTERESTS STATEMENT
None declared.
AUTHOR CONTRIBUTIONS SECTION
Conceptualization: ALL;
Data Curation: CVG, ELB;
Formal Analysis: CVG, JCSB;
Funding Acquisition: RJT;
Investigation: CVG, JCSB;
Methodology: ALL;
Writing – Original Draft Preparation: CG;
Writing – Review & Editing: ALL