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Several weeks ago, a brief review of Wignall's comment appeared here. For those on the net who don't receive the circulars from IGCP 335 (Biotic Recoveries from Mass Extinction) led by Dr. Douglas H. Erwin and Prof. Erle G. Kauffman, we have decided to retype Wignall's original piece as it appeared in the Fourth Circular, followed by our (Erle Kauffman and Peter Harries) response to it which will appear in the Fifth Circular. DO REFUGIA REALLY EXIST? by Paul Wignall, University of Leeds The recent meeting of Project 335 at Plymouth highlighted the rather varied and generally vague use of the term refugia. In reality refugia (in the sense used at Plymouth) probably do not exist. In the context of mass extinctions, a refugium is considered a place that remains habitable whilst all around is uninhabitable. Populations of species which disappear from everywhere else in the world remain as lucky survivors on their refuge. Why? Presumably because their local environment is somewhow immured from the global perturbations. Just how this could come about is never explained. Most taxa are in fact Lazarus taxa because we haven't yet found them, the refugia are therefore intrinsically hypothetical. Essentially refuge/Lazarus taxa are a product of inadequate sampling. But consider what happens when we collect this missing taxa in some previously sampled part of the world. Do we call this area the refuge? What happens when they are collected from a second area, does that become another refuge? In fact, refugia are impossible to prove, because with further testing (collecting), they gradually cease to exist. Refugia are just an indirect admittal of an inadequate database for which we already have the far more useful concept of Lazarus taxa - a term which has no connotations of hypothetical paradise. Many of the supposed refugia taxa proposed recently have been discovered in China - an area that has only been well known to western paleontologists for a decade or so. Thus the refugia taxa are new to us and in many cases that is the only reason for calling them such. But, consider how we would perceive such fossils if they had been discovered neraly two centuries ago at the time that many of the familiar British fossils were first being found. Such fossils would be familiar to us, they would probably feature in textbooks and generally there would be no tendency to consider them unusual or at all special. Thus refugia as geographic entities do not exist. Most references to such areas rely on the circular reasoning that the area is a refugium because it contains refuge species. I would suggest that a refuge can only exist in an environmental sense. For example, if an anoxic event wipes out shallow-marine faunas whilst leaving the deep ocean untouched then the deep ocean abyssal zone becomes a refuge for that particular event. In order to define a refuge environment we must be able to demonstrate two things: i) the taxa in that environment show preferential survival during mass extinction. ii) there must be independent sedimentary/geochemical criteria for defining a refuge environment. The presence of so-called refuge species has no diagnostic value. Thus, in summary, there is no validity to the concept of geographic refugia, but, within anygiven region, there could be an environmental refuge. Defining such environments is fundamental to our understanding of mass extinctions and their aftermath. YOU CAN'T HIDE FROM REFUGIA: A REPLY TO WIGNALL Paul Wignall's comment on refugia in the last IGCP 335 newsletter is not well argued, without data, and misrepresents the sense of the discussion at the Plymouth meeting. Whereas none of us would debate that some Lazarus Taxa are artifacts of inadequate sampling, especially among rare species, others have held up under the rigors of even the most highly resolved, cm-scale stratigraphic data, and the focused efforts of numerous international scientists, e.g., across the Frasnian-Famennian, Cenomanian-Turonian, and Cretaceous-Tertiary boundary intervals. Without evidence to the contrary, there remains a high probability that effective refugia existed for these Lazarus Taxa. Wignall's separation of geographic from environmental and ecologic aspects of refugia or protected habitats is artificial: clearly these are interrelated aspects of all habitats; geography strongly influences local environments, the nature and diversity of habitats, and biological response to them. To further state that all refugia are "hypothetical paradises" which cannot be defined by their constituent organisms, ignores the facts of biology and paleobiology, as well as widely utilized concepts of refugia and refugia species. Many modern refugia are documented and well-studied, including specific deep-sea habitats, reef caves and other cryptic sites, cold artesian springs and bogs with periglacial biotas in more temperate climate zones, isolated valleys with tropical microclimates within arid and/or temperate mountain ranges, mountain-top microhabitats with Pleistocene-style climates and biotas, situated well south (or north) of the present glacial margin, and many others. We further imagine that cryptic sclerosponges, deep-sea monoplacophorans, stalked crinoids and hexactinellids, coelocanths, and Austral marsupials would be surprised to learn that their survival in these isolated and/or secondary habitats were not evidence of refugia. Pervasive negativism is not the way to unravel the the complex phenomena of survival and recovery from mass extinction: rather it is an excuse not to look for answers and test hypotheses with comprehensive data sets. In an attempt to be more objective in this debate, and avoid semantic arguments, we broadly define the nature and scope of refugia and refugia species below, culled from diverse published literature and the advice of numerous colleagues, and request your constructive comments to help us arrive at a generally acceptable set of concepts for IGCP 335 studies. In making this proposal, we assume that there were protected habitats for fossil taxa, as there are for modern refugia species, to which (a) organisms could migrate, by design or chance, (b) in which they have been stranded by long-term environmental changes around them, or emigration of their primary habitats, or (c) which they marginally occupied during background conditions, collectively allowing at least limited populations to survive the rigors of mass extinction. These refugia taxa would thus be available to return to former primary habitats (or post-extinction variations of these) and thus to partially seed the recovery of ecosystems following biotic crises. The origins of the concept of a refuge are relevant, and rooted in human history. Refuge (from the Latin refugium) means to flee, and seek shelter and protection from danger and distress; a refuge (or refugium) is a shelter or protection from danger, distress, and calamity; any place where one is out of the way of danger. The meaning of refuge or refugium seems obvious, and it is also relevant that dictionary definitions, from which the above was culled, implies migration from an organisms' primary habitat to a new or secondary habitat, even over a short distance. We present below, to focus discussion, a broad paleobiologic/biologic definition of refugia from our paper recently submitted to the research volume stemming from the IGCP 335 Plymouth, UK, meeting in September, 1994. Refugia are very small (e.g. reef cavities, artesian springs) to very large (e.g., the deep ocean) protected habitats which (a) have been isolated or left-behind by long-term deterioraton or shifts in once-prominent Earth environments (e.g., glacial retreat), (b) to which organisms have emigrated from primary habitats during times of severe environmental stress, and/or (c) to which local species populations have adapted, and ultimately become restricted, at the margins of their primary species range. Primary habitation of refugia by surviving species populations commonly results from environmental deterioration and/or competitive displacement in their original preferred habitat. Refugia effectively protect species from the severe environmental perturbations that lead to a significant decline in biomass, mass death, and mass extinction of taxa in more perturbed primary habitats. The character of these refugia may vary among organisms and different mass extinction events, depending on the nature of forcing mechanisms and their environmental feedback loops. Many refugia taxa probably retain their ability to reoccupy primary habitats from which they have been environmentally and/or biologically displaced, as Immigrant Survivors, as those environments stabilize or themselves immigrate back into the area of the refugium; refugia species may thus comprise Lazarus Taxa. Their ability to do this, however, may decline as the evolutionary time in the refugium lengthens. Two types of refugia species have been recognized in the biostratigraphic record of mass extinctions: Short- and Long-term Refugia Species (or taxa, clades). Short-term Refugia Species are those taxa which were forced into refugia habitats they did not previously occupy, or which they sparsely occupied as small populations at the margins of their adaptive range, by highly stressful environmental conditions during regional biological crises or mass extinctions. As post-crisis environmental conditions normalize, these taxa may rapidly return to occupy their primary habitats, through active or passive dispersion, usually without having undergone speciation. They thus become short-term Lazarus Taxa or early immigrant survivors. Stratigraphically, short-term refugia taxa have relatively continuous biostratigraphic ranges, though with diminishing abundance and dispersion, into early phases of a mass extinction interval, at which time they essentially disappear from the fossil record or have very rare scattered occurrences (possibly representing immigration episodes during short, less stressful environmental intervals), during the major interval of environmental decline. After a geologically short interval of non- occurrence, they then return abundantly as immigrant Lazarus Taxa within the survival and early recovery intervals. Long-term Refugia Species comprise those taxa which have been displaced from their primary habitat (usually through biological competition or long-term emigration or destruction of their primary habitat) long before the onset of stressed environments associated with biodiversity crises and mass extinction. These refugia taxa may further have evolved new taxa and adapted to their refugia habitats, while still retaining their dispersal potential. If the original displacing mechanism or competitor no longer exists after the crisis event, or their prior habitat re-develops in a region, these long-term refugia taxa may expand their range to include their original or related niches, either as the same species (in slowly evolving lineages) or as new, phylogenetically related species with similar habitat requirements. Conceivably, long-term refugia species could have evolved characteristics that would allow them to occupy a different primary habitat after a mass extinction than that which they originally inhabited. Stratigraphically, these long-term refugia taxa become rare or disappear from the fossil record in their primary habitats before the first perturbations associated with mass extinction intervals. After long stratigraphic intervals of non-occurrence, they reappear as late immigrants, or long-term Lazarus Taxa, during ecosystem recovery. Some workers have a more expanded view of refugia species, suggesting that the term also applies to species whose populations are greatly reduced and temporarily restricted to within a small portion of their original primary habitat by a short-term environmental crisis, and which may subsequently reoccupy much of their original prime ecospace as environmental conditions ameliorate. Because this example does not involve significant migration of either the habitat (away from the refugium), or of the main surviving species population(s) (away from the perturbation) to new or marginal habitats (i.e. refugia) that are more protected from these perturbations, it does not strictly fit the original definition of a refugium species (or population). We have termed these types of survivors "stranded populations." We invite your comments on these concepts in future IGCP 335 newsletters. Erle G. Kauffman, Department of Geological Sciences, University of Colorado, Boulder, CO 80309-0250, and Peter J. Harries, Department of Geology, University of South Florida, Tampa, FL 33620-5200, U. S. A.
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