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Volumn 285, Issue 5432, 1999, Pages 1386-1390

Fossil plants and global warming at the Triassic-Jurassic boundary

Author keywords

[No Author keywords available]

Indexed keywords

CARBON DIOXIDE;

EID: 0033609999     PISSN: 00368075     EISSN: None     Source Type: Journal    
DOI: 10.1126/science.285.5432.1386     Document Type: Article
Times cited : (576)

References (45)
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    • D. J. Beerling and W. G. Chaloner, Ann. Bot. 71, 431 (1992); D. J. Beerling, W. G. Chaloner, B. Huntley, J. A. Pearson, M. J. Tooley, Proc. R. Soc. London. B Biol. Sci. 251, 133 (1993); J. Van der Burgh, J. Visscher, H. Dilcher, W. M. Kurschner, Science 260, 1788 (1993); P. K. Van de Water, S. W. Leavitt, J. L. Betancourt, ibid. 264, 239 (1994); J. C. McElwain, Philos. Trans. R. Soc. London B 353, 83 (1998).
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    • D. J. Beerling and W. G. Chaloner, Ann. Bot. 71, 431 (1992); D. J. Beerling, W. G. Chaloner, B. Huntley, J. A. Pearson, M. J. Tooley, Proc. R. Soc. London. B Biol. Sci. 251, 133 (1993); J. Van der Burgh, J. Visscher, H. Dilcher, W. M. Kurschner, Science 260, 1788 (1993); P. K. Van de Water, S. W. Leavitt, J. L. Betancourt, ibid. 264, 239 (1994); J. C. McElwain, Philos. Trans. R. Soc. London B 353, 83 (1998).
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    • note
    • Primary SD and SI data (Table 1) were normalized according to x̄ - x, where x̄ is the genus mean for all beds or localities in either Greenland or Sweden and x is the genus mean per bed or locality. Normalized data were then corrected for any shifts in floral composition between individual beds by multiplying by the percentage composition of that genus at each of the beds or localities in Sweden and Greenland. These procedures were repeated for all individual genera to calculate an artificially genus-weighted trend. Mean genus-weighted SD and SI trends were calculated for both sites and removed from the normalized data to provide detrended stomatal records, which were independent of any floral composition changes between individual beds or localities.
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    • 2) where ΔT is the difference in mean global surface air temperature. The estimates will be somewhat dependent on the responses of the thermohaline circulation [E. Barrera et al., Geology 25, 715 (1997)].
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    • 2) where ΔT is the difference in mean global surface air temperature. The estimates will be somewhat dependent on the responses of the thermohaline circulation [E. Barrera et al., Geology 25, 715 (1997)].
    • (1997) Geology , vol.25 , pp. 715
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    • 2 [J. L. Sarmiento and J. R. Toggweiler, Nature 308, 621 (1984)]. Isotopic evidence supports a reduction in oceanic productivity at the T-J boundary (8); however, the data are equivocal because of potential diagenetic effects (8, 9).
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    • -1) and close to daily maximum temperatures are reached. This approach was used to estimate relative maximum leaf size during the period of study (Fig. 3).
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    • The threshold for thermal damage of nonsucculent leaves (45° to 52°C) is a highly conserved characteristic across a wide range of extant taxa [W. Larcher, in Ecophysiology of Photosynthesis, E. D. Schultze and M. M. Caldwell, Eds. (Springer-Verlag, Berlin, 1994), pp. 261-277; Y. Gauslaa, Holarct. Ecol. 7, 1 (1984)], implying little evolutionary change through time.
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    • A review of fossil Ginkgoalean leaves revealed that species with the most dissected leaves, characterized by multidichotomies 0.5 to 2 mm wide, are restricted to Late Triassic to early Middle Jurassic facies [T. Kimura, G. Naito, T. Ohana, Bull. Natl. Sci. Mus. Tokyo 9, 91 (1983)].
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    • The cause of T-J floral turnover has traditionally been attributed to a sedimentary hiatus (3). However, this hypothesis is unsupported by sedimentological evidence [G. Dam and F. Surlyk, Geology 20, 749 (1992); Spec. Publ. Int. Assoc. Sedimentol. 18, 4189 (1993)], which identifies no major facies changes or unconformities between the T-J strata in Greenland. Furthermore, the absence of the upper Rhaetian Ricciisporites-Polypodisporites acme zone [W. M. L. Schuurman, Rev. Palaeobot. Palynol. 23, 159 (1977)] in Greenland (10) and Sweden (11), which has also been tentatively interpreted as evidence of a hiatus at both localities, is questionable, as acme zones are generally considered of only local use, owing to the effects of ecological, environmental, and postdepositional processes on relative pollen abundances.
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    • The cause of T-J floral turnover has traditionally been attributed to a sedimentary hiatus (3). However, this hypothesis is unsupported by sedimentological evidence [G. Dam and F. Surlyk, Geology 20, 749 (1992); Spec. Publ. Int. Assoc. Sedimentol. 18, 4189 (1993)], which identifies no major facies changes or unconformities between the T-J strata in Greenland. Furthermore, the absence of the upper Rhaetian Ricciisporites-Polypodisporites acme zone [W. M. L. Schuurman, Rev. Palaeobot. Palynol. 23, 159 (1977)] in Greenland (10) and Sweden (11), which has also been tentatively interpreted as evidence of a hiatus at both localities, is questionable, as acme zones are generally considered of only local use, owing to the effects of ecological, environmental, and postdepositional processes on relative pollen abundances.
    • (1993) Spec. Publ. Int. Assoc. Sedimentol. , vol.18 , pp. 4189
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    • The cause of T-J floral turnover has traditionally been attributed to a sedimentary hiatus (3). However, this hypothesis is unsupported by sedimentological evidence [G. Dam and F. Surlyk, Geology 20, 749 (1992); Spec. Publ. Int. Assoc. Sedimentol. 18, 4189 (1993)], which identifies no major facies changes or unconformities between the T-J strata in Greenland. Furthermore, the absence of the upper Rhaetian Ricciisporites-Polypodisporites acme zone [W. M. L. Schuurman, Rev. Palaeobot. Palynol. 23, 159 (1977)] in Greenland (10) and Sweden (11), which has also been tentatively interpreted as evidence of a hiatus at both localities, is questionable, as acme zones are generally considered of only local use, owing to the effects of ecological, environmental, and postdepositional processes on relative pollen abundances.
    • (1977) Rev. Palaeobot. Palynol. , vol.23 , pp. 159
    • Schuurman, W.M.L.1
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    • note
    • std)] - 1} × 1000 where unk the ratio of unknown to sample and std is the ratio of the pee dee belemnite standard.
  • 45
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    • note
    • 13C. We gratefully acknowledge funding from the Natural Environment Research Council, UK (GR9/02930), and through Royal Society Research Fellow and Equipment grants to D.J.B.


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