1 Uplands, Lowlands, and Climate: Taphonomic Megabiases and the Apparent Rise of a Xeromorphic

1 Uplands, Lowlands, and Climate: Taphonomic Megabiases and the Apparent Rise of a Xeromorphic

Manuscript File 1 1 Uplands, lowlands, and climate: Taphonomic megabiases and the apparent rise of a xeromorphic, 2 drought-tolerant flora during the Pennsylvanian-Permian transition 3 4 William A. DiMichelea*, Arden R. Bashforthb, Howard J. Falcon-Langc, and Spencer G. Lucasd 5 6 a*Department of Paleobiology, National Museum of Natural History, Smithsonian Institution, 7 Washington, DC 20560 USA, [email protected], corresponding author; bNatural History Museum 8 of Denmark, University of Copenhagen, Øster Voldgade 5-7, 1350 Copenhagen K, Denmark, 9 [email protected]; cDepartment of Earth Sciences, Royal Holloway, University of London, 10 Egham, Surrey TW20 0EX, UK, [email protected]; dNew Mexico Museum of 11 Natural History and Science, Albuquerque, NM 87104, USA, [email protected] 12 13 ABSTRACT – The Late Mississippian and Pennsylvanian have been referred to as the Coal Age 14 due to enormous paleotropical peat accumulations (coal beds). Numerous fossil floras have been 15 collected from these coals, and their associated seatearth paleosols and roof shales, over more 16 than two centuries, leading to the inference of vast swampy wetlands covering the Pangean 17 tropics during the Pennsylvanian. In contrast, the Permian tropics are characterized as more arid, 18 with sparser and more heterogeneous vegetation than inferred for the Pennsylvanian. In the 19 tropics, the Pennsylvanian to Permian transition has been described as a changeover from a 20 pteridophyte-dominated “Paleophytic flora”, to a seed-plant dominated “Mesophytic flora”. This 21 view notwithstanding, floras dominated by xeromorphic seed plants also are well known from 22 the Pennsylvanian tropics. Some authors have characterized these plants as being occupants of 23 uplands, , subsequently transported into basinal-lowland, preservational environments. In this 2 24 model, uplands are well drained, causing areas of drought under otherwise everwet climates. In 25 this paper, we present an alternative interpretation: that the apparent transition in Pennsylvanian- 26 Permian tropical vegetation reflects two types of megabias. First is a taphonomic megabias, 27 strongly favoring the vegetation of humid climates over that of seasonally dry climates. 28 Accordingly, tropical-plant preservational potential fluctuated in concert with Late Paleozoic Ice 29 Age glacial-interglacial oscillations, and contemporaneous sea-level and climatic changes. 30 Second is an analytical megabias, strongly favoring the discovery and collection of the wetland 31 biome from Pennsylvanian strata, overlooking the less frequently and more poorly preserved 32 drought-tolerant biome. By Permian times, vast wetlands, and their fossil record, had largely 33 disappeared from central Pangea (although continuing in Cathaysia), making drought-tolerant 34 vegetation more “visible” to searchers, without changing its preservational circumstances. We 35 demonstrate that the upland model is untenable, being inconsistent with the principles of plant 36 biogeography and with geological aspects of the fossil record. 37 38 Key words: wetland; dryland; Paleophytic; Mesophytic; late Paleozoic 39 3 40 1. Introduction 41 42 Contra negantem principia non est disputandum (Against one who denies the principles, there 43 can be no debate). -- Arthur Schopenhauer, Eristische Dialektik (1831) 44 45 It has long been recognized that the Pennsylvanian wetland flora of Pangea’s 46 Euramerican tropical latitudes differed significantly from the drought-tolerant, xeromorphic flora 47 that later typified those tropical regions during the early Permian. This change in the most 48 commonly found types of plant fossils has been attributed, we believe correctly, to a long-term 49 drying trend in the tropics, which began at the end of the Early Pennsylvanian and continued, in 50 a long-wavelength, oscillatory manner, into the Permian (e.g., McKee and Crosby, 1975; Cecil et 51 al., 1985; Joeckel, 1995; Roscher and Schneider, 2006; Schneider et al., 2006; Schneider and 52 Romer, 2010; Rosenau et al., 2013; DiMichele et al. 2011; Opluštil et al., 2013a; Martino, 2017). 53 For many years, there has been a sense that these long-term climatic changes were accompanied 54 by the rise of a distinctive kind of vegetation, the so-called Mesophytic Flora (e.g. Gothan, 1912; 55 Gothan and Gimm, 1930; von Bülow, 1942; Fredericksen, 1972; DiMichele et al., 2008; Cleal 56 and Cascales‐ Miñana, 2014) that typified the Permian, an emergence that could be used as a 57 biostratigraphic guide. The line of reasoning is that even if the exact Pennsylvanian-Permian 58 boundary were fuzzy in terms of lithological and biotic composition, one could discern the 59 difference between these time periods by the on-average compositional aspects of their floras. 60 This argument can be found in discussions about the age of floras dominated by more 61 xeromorphic elements, such as conifers, callipterids, Taeniopteris, and others (e.g., Fredericksen, 62 1972; Bode comments following Gillespie et al., in Barlow, 1975; Wagner and Lyons, 1997; 4 63 DiMichele et al., 2008; van Hoof et al., 2013), which differ greatly from the wetland floras found 64 in association with coal beds, primarily from partings, roof-shales, seat-earths, and fossils from 65 the coal beds themselves (palynomorphs and coal-balls). 66 Kerp (1996, 2000) and later DiMichele et al. (2008) argued that these terms had 67 significant problems, noting that there was a major conceptual change between their original 68 definitions and subsequent use. In essence, the terms had moved from representing 69 stratigraphically-diagnostic floras to representing distinct biomes. With that shift, although the 70 new concept filled a clear need, it also conflicted with the original sense of the terms, which 71 were now largely incongruent. 72 Before going further in our exploration of this matter, some terms that we use in this 73 paper must be defined. We broadly demarcate the different regions of equatorial (or, 74 interchangeably, tropical) Pangea into its western, central, and eastern parts. The areas 75 envisioned do not have formal, latitudinal boundaries, and are outlined both spatially, and in 76 terms of prevailing aspects of their environment, particularly climate. Western equatorial Pangea 77 is considered to stretch from the Panthalassan coast line, present-day western United States and 78 northern Mexico, into the regions of the western Midcontinent, approximately West Texas, and 79 western portions of Kansas, Nebraska, and Iowa. Central equatorial Pangea encompasses those 80 regions characterized by extensive coal-bearing strata, located in a string of basins from North- 81 Central Texas, eastern parts of Oklahoma, Kansas, Nebraska, and Iowa (the Midcontinent region 82 of the U.S.), through the eastern U.S. (Illinois and Appalachian basins), the Maritime basins of 83 eastern Canada, the Variscan regions of Europe, and into the Donets Basin of the Ukraine. 84 Eastern equatorial Pangea includes regions of the Middle East, southern Russia, and China. 5 85 We also employ various terms to describe assemblages of plants, both alone and in their 86 environmental context. The terminology is somewhat hierarchical, reflecting the fact that 87 ecological terminology is notoriously non-quantitative, conceptual, and often scaled to the 88 problem being addressed. The term “vegetation” is used in a very general sense, and refers to the 89 plants growing in an area of unspecified size, with possible consideration of their physiognomy, 90 or relative abundances. A “biome” means an assemblage of plants with particular physiognomic 91 characteristics, associated with certain soil and climatic conditions. The term has broad 92 taxonomic implications, mainly at higher taxonomic levels, such as arborescent lycopsids, 93 conifers, tree ferns, or callipterids. By “habitat”, we refer to the physical-environmental, abiotic 94 variables that predominate in an organism’s site of growth. Although not scale-free, the concept 95 of habitat does depend on the size of the organisms in question. There may be a variety of 96 different habitats and microhabitats (differentiated inexactly by spatial scale) within a biome, and 97 they may harbor quantitatively different proportions of species from place to place, and differ 98 compositionally from one another. The concept of “niche” is frequently used side-by-side with 99 habitat, and captures the multidimensional life-history strategy of an organism. Thus, a niche 100 includes biotic interactions and the physical environment in which an organism lives. A “flora” 101 is taxonomically specific, but non-quantitative, and refers to the plant taxa, at the finest 102 resolution possible, for a particular area, or within a biome. A “species pool” refers to the suite of 103 species in a particular geographic area that potentially could colonize any portion of that region, 104 even if the plants might not be able to survive under the particular local conditions at any given 105 moment; in other words, these are the species for which there is no dispersal limitation. A 106 “community” is an assemblage of species living under a common set of physical and climatic 107 conditions, and is characterized quantitatively by a particular dominance-diversity profile. We 6 108 use “ecosystem” to include both plants and animals in an expanded version of the community 109 concept, recognizing both internal factors such as nutrient cycling, soil chemistry and 110 microbiome, organism

View Full Text

Details

  • File Type
    pdf
  • Upload Time
    -
  • Content Languages
    English
  • Upload User
    Anonymous/Not logged-in
  • File Pages
    137 Page
  • File Size
    -

Download

Channel Download Status
Express Download Enable

Copyright

We respect the copyrights and intellectual property rights of all users. All uploaded documents are either original works of the uploader or authorized works of the rightful owners.

  • Not to be reproduced or distributed without explicit permission.
  • Not used for commercial purposes outside of approved use cases.
  • Not used to infringe on the rights of the original creators.
  • If you believe any content infringes your copyright, please contact us immediately.

Support

For help with questions, suggestions, or problems, please contact us