Cladistics 13, 67–79 (1997) WWW http://www.apnet.com Vicariance Events, not Areas, Should be Used in Biogeographical Analysis P. Hovenkamp Rijksherbarium/Hortus Botanicus, PO Box 9514, NL-2300 RA Leiden, The Netherlands Accepted 15 December 1996 Biogeographical analysis addresses two distinct problems: the reconstruction of Earth history and of taxon history. For the reconstruction of Earth history, an analogy between taxa and areas is often assumed. Uncritical acceptance of this analogy has led to methods for the reconstruction of taxon history being inappropriately used for the reconstruction of Earth history. A biogeographical protocol is proposed which does not rely on this analogy. This protocol resolves the historical sequence of vicariance events, not the relations between areas. The protocol is illustrated with the analysis of three examples. © 1997 The Willi Hennig Society analysis (Wiley, 1988; Brooks, 1990; Brooks and McLennan, 1991). Curiously, opponents of this approach use the same analogy in the opposite direction, applying three-item analysis, apparently first developed as a biogeographical tool (Nelson and Ladiges, 1991a;b), to taxon analysis (Nelson and Platnick, 1991). The analogy between taxa and areas has been so pervasive that it has obscured the fact that historical biogeography has two very distinct aims that should be clearly separated, both conceptually and methodologically. INTRODUCTION EARTH HISTORY VERSUS TAXON HISTORY PROTOCOLS Much of the recent work on biogeographical methods can be summarized as a search for a “protocol corresponding in as many ways as possible to phylogenetic systematics” (Kluge, 1988). Just as phylogenetic analysis reconstructs the relationships of taxa, biogeographical analysis has been used to reconstruct the relationships of areas. Thus, cladograms of areas are constructed using taxa as characters. In this approach, it has been taken for granted that there is a strong analogy between phylogenetic and biogeographical One of the aims of historical biogeography is to elucidate Earth history on the basis of biological evidence. The other is to elucidate the history of one or more groups of organisms on the basis of an established theory of Earth history. This second aim corresponds most closely to “traditional” biogeography, and also to Brooks Parsimony Analysis (BPA), as it is formulated in, for example, Brooks and McLennan (1991). The two approaches require different data and different methodologies. 0748-3007/97/010067+13/$25.00/cl970032 Copyright © 1997 by The Willi Hennig Society All rights of reproduction in any form reserved 67 68 Hovenkamp For the first approach (Earth history) we need at least two phylogenies of groups inhabiting the same areas. We then search for any correspondences between the two phylogenies, and explain these by reference to a common element, which is usually interpreted as Earth history. A unique pattern in a phylogeny is no evidence for a common element, and is therefore irrelevant for this type of analysis. This approach corresponds closely to the approach developed by Rosen (1978), and to what is usually termed “component analysis” (Nelson and Platnick, 1981; Brooks, 1990; Page, 1990). A variety of methods are available to identify the common element of a set of cladograms (reduced area cladograms, Rosen, 1978; “consensus” area cladograms; “reconciled trees”, Page, 1990). The second approach (taxon history) can operate on one phylogeny at a time, first identifying those elements in the phylogeny which can be explained by reference to an established Earth history. The remaining elements can then be explained by reference to other phenomena, such as dispersal (in the form of area expansion or migration), extinction (resulting in area contraction), or stasis (lack of speciation). BPA (Brooks and McLennan, 1991) implements this approach using methods identical to those used in phylogenetic analysis. The “Earth history” approach compares different cladograms, and identifies the element common to all cladograms. The “taxon history” approach also compares different cladograms and identifies the elements common to both, but here one is a taxon cladogram, and the other one is a representation of area history. At first sight, therefore, the two methods are superficially similar. In fact, the methods are so similar that the distinction has not been appreciated by most authors. Rosen (1978) opposes his own (Earth history) approach to Mayr's (taxon history) aim of “explaining the separate history of each (faunal) element”, (Mayr, 1965, cited by Rosen). Humphries, in turn, (1992: 147) condemns Rosen (1978) for “deleting non-congruent elements of different patterns”. In this exchange of views, Rosen judges a taxon history approach by standards derived from an Earth history approach and, in turn, is judged by standards derived from a taxon history approach. As the methods are not equivalent, both criticisms are misguided. A “taxon history” approach seeks to fit biotic diversity to the matrix of known Earth history. Although it is dependent on Copyright © 1997 by The Willi Hennig Society All rights of reproduction in any form reserved what is known about Earth history at any one time, that does not make it “ad hoc” or unscientific, but merely subject to normal scientific progress. On the other hand, for an “Earth history” approach, incongruent elements occurring in only one cladogram are simply irrelevant, and when they are deleted, no information is “thrown away”. A unique event is poor evidence for a general process and, when an alternative explanation is available (for example, dispersal), its evidential value is negligible. It is only in a “taxon history” approach that all elements are equally important and need to be explained. As the two methods have fundamentally different aims, the perceived opposition is spurious. Confusion is compounded by Brooks and McLennan (1991), who, in their exposé of BPA (p. 206) clearly describe it as a “taxon history” approach, and, at the same time, as a logical continuation of methods developed for an “Earth history” approach (pp. 195–197). Most of the examples they cite use an “Earth history” approach (for example, p.226: Mayden, 1988; p.230: Cracraft and Prum, 1988; p.238: Brooks, Thorson and Mayes, 1981). In this paper, I want to specifically question the validity of the Earth History protocol. This protocol uses the analogy between taxa and areas in a way that obscures the real issues and makes inappropriate use of the data. Although the analogy has been widely used, its applicability has been doubted by several authors (Cracraft, 1988; Sober, 1988; Page, 1990) who have drawn attention to a number of problems. AREAS AS TAXA? In the first place, the taxon/area analogy presupposes the existence of “areas of endemism”. That, however, should be a subject of investigation; it should not be assumed. In phylogenetic analysis, both the existence of taxa and their hierarchical relationship are predicted (and therefore explained) by evolutionary theory. As yet, there is no corresponding general theory of biogeography which predicts the existence of “areas of endemism” which are characterized by taxa. It is even doubtful whether we have sufficient observations that support the existence of such areas. Whenever we try to match different taxon 69 Vicariance Events in Biogeographical Analysis distributions, we usually find that no two taxa show exactly the same distribution. Axelius (1991) has pointed out that the correct way to code partially overlapping distributions is to consider the overlapping region as a separate area. However, the number of such “areas” rapidly increases when more than two different distributions are involved, and the separate “areas” will be increasingly fragmented. How to define areas that are relevant to more than one taxon is therefore not a trivial problem, and will also be subject to scaling problems. represented as a cladogram. It is perhaps a theoretical possibility that the entire history of the Earth is divergent; nevertheless, geological data are overwh elmin gly in favour of reticulation as a real phenomenon (although a world map realistic at first sight can be derived solely by simulation of a large number of “vicariance” events [Voss, 1988, pl. 1–6], that is most likely no more than a coincidence). Reticulation of units cannot be expressed in the form of a branching diagram. TAXA AS CHARACTERS? EVOLUTION OF AREAS? A second point is that areas do not evolve like taxa. Evolution of taxa is usually divergent, as full hybridization of taxa (with disappearance of the parental species) is a rare process. If it occurs, then it is only for taxa at or below the species level. This divergent history above the species level is reflected in the hierarchical structure of relationships between species and higher taxa, and can be graphically represented in a branching diagram. This correspondence between the shape of the true history and the shape of a cladogram is the reason we are confident that cladistics can help us recover the history of taxa. In contrast, the history of geographical areas is rarely exclusively divergent. In many cases, the very opposite is true, and we have good reasons to expect that reticulation involving formerly isolated areas is a common process. We would be able to maintain that Earth history is divergent only if we assumed that even after a collision of two land areas both areas retained their separate identities for ever after. This would be a methodological fiction rather than a realistic assumption. So far, cladistic biogeographers have failed to defend convincingly the point that Earth history should be represented as a branching diagram. Rosen's (1978) defense is “…the underlying assumption that the history of all life has some generality with respect to the history of the Earth's geography”. The fact that this generality is not necessarily reflected in a cladogram of areas is not addressed by Rosen nor by most other investigators. Just because Earth history influences life's history, and life's history is divergent, it is not necessarily true that Earth history is divergent and can be Copyright © 1997 by The Willi Hennig Society All rights of reproduction in any form reserved Lastly, it is doubtful whether taxa can be treated the same way in a biogeographical analysis as characters are in a phylogenetic analysis. That they can be treated in the same way is taken for granted in most accounts of biogeographical theory. The statements corresponding most closely to an explicit defence are in Brooks (1990) and Brooks and McLennan (1991). Brooks (1990: 29) states that “macro-evolutionary interpretation of homology is the same, common history, at all levels of analysis”. Brooks and McLennan (1991: 199) use a slightly different wording: “the explanation for homology, common history, is the same for phylogenetic analyses at all levels of biological organization”. By adding “biological”, Brooks and McLennan make more sense, but reveal that the defence misses the point. It is not the use of parsimony analysis for different levels of biological organization that has to be defended, but its use in a non-biological context, viz. the history of areas. When two taxa share a character, homoplastic similarity can be distinguished from synapomorphic similarity by congruence with other characters. In a phylogenetic analysis, the resulting hypotheses of homoplasy or synapomorphy can then be tested independently by more detailed character analysis. In a biog eog rap hica l an alysis, a similarity may be non-homologous and yet irreducibly identical, the identity deriving from horizontal transmission instead of shared inheritance (Sober, 1988). In such cases, no amount of further analysis will ever be able to disprove the homology of the taxon-as-character. Whereas in a phylogenetic analysis shared similarities are independently testable proof of shared ancestry, in 70 Hovenkamp biogeographical analysis shared taxa are not proof of shared ancestry and they are not independently testable as homologies. Thus, the fundamental differences between characters in a taxon analysis and taxa in a biogeographical analysis derive partly from the much greater vagility of taxa as compared to characters. The taxa that are used as characters for areas may move freely between areas. Taxa may spread to other areas. At each moment in history, they are constrained only by the then-operative barriers, and not by the historical origin of the areas they inhabit. As there is no necessary connection between the origin of the areas and the existence or location of the current barriers, therefore, there is no absolute correspondence between the origin of a taxon and its current distribution. Moreover, as far as there is a connection, it may weaken as time progresses: barriers once formidable may disappear. In contrast, characters of taxa are much more strongly restricted to the taxon in which they originated and all its direct descendants; thus, there is a very strong connection between the historical origin of a character and its current distribution. As time progresses, the barriers preventing the flow of characters to other taxa do not weaken, but are likely only to become stronger. In a cladistic analysis of relationships among taxa, we are confident that we can use characters as indicators of history. As indicators of the history of areas, taxa are inherently less reliable. IN SEARCH OF AN ALTERNATIVE METHOD OF BIOGEOGRAPHICAL ANALYSIS If we want to reconstruct the history of areas on the basis of the current distributions of taxa, we will need to address the specific problems of “Earth history” biogeography that are not encountered in phylogenetic analysis. One way to do that would be to devise a method that produces the complex type of pattern that corresponds to the complexities of “area evolution”, thus allowing both divergent and reticulate patterns. In view of this complexity, a "'cladistic analysis” of areas is certainly not sufficient, resulting, as it necessarily does, in a relatively simple branching diagram. Copyright © 1997 by The Willi Hennig Society All rights of reproduction in any form reserved In this paper, I investigate a different approach. Earth history is not to be resolved in terms of areas, but in terms of vicariance events. Vicariance events are the traditional core business of phylogenetic biogeography. They correspond to emerging barriers that function as dispersal barriers. Compared to the reticulated complexities of the history of areas, which can only be properly represented in a reticulated diagram, a history of events is much simpler to represent. Once all events have been identified, they can be aligned in linear temporal sequence. RECONSTRUCTING THE SEQUENCE OF VICARIANCE EVENTS To reconstruct the sequence of vicariance events requires two types of data: 1. geographical information, specifying the location of each vicariance and event; and 2. historical information, specifying the temporal relation of each vicariance event to other vicariance events. For both types of data, we have the information available in a cladistic analysis. The necessary geographical information can be found in the distributional data for lineages. Each pair of mutually exclusive sets of areas can be taken as evidence for a vicariance event. Whenever a node in a cladogram specifies two sister groups which do not overlap in distribution area (or the combined areas of all their members), we have evidence for a vicariance event. The position of the vicariance event is specified by the two combined ranges: it is located in the area between the two. Note that this position is not dependent on the extent of the two ranges in all directions: away from the putative vicariance event, the ranges may be extensive without influencing its position. The position of a vicariance event is only ill defined under two conditions: if the two ranges overlap; and if the two ranges are separated by wide gap which possibly corresponds to a number of different vicariance events. Thus, this method is relatively insensitive to widespread species. It uses the best part of the information contained in a 71 Vicariance Events in Biogeographical Analysis large distributional range; the part where a range is constrained by an effective barrier to dispersal. As evidence for the sequence of the vicariance events, we have the information of the sequential order of the cladogram nodes. This leads to a procedure whereby a reconstruction of the sequence of vicariance events can be attained by going through the following steps: 1. Extract the Geographical Information from the Cladograms For each cladogram to be analysed, the taxa are replaced by their areas, expressed as sets of recognized unit areas. It is not necessary that these unit areas correspond to either areas of endemism or areas of single species. For convenience’s sake it can often be arranged that the boundaries between unit areas correspond with boundaries between species areas, but again, this is not necessary. In some cases it may even be convenient to define the unit areas as units of a completely arbitrary grid system. The geographical information is then extracted from the cladograms, by enumerating all “traceable vicariance events” (TVEs). A traceable vicariance event corresponds to a node of which both descendants occupy mutually exclusive areas. Nodes of which both descendants occupy overlapping areas are considered as not traceable, and are excluded. 2. Extract the Historical Information from the Cladograms If only one traceable vicariance event is present in a cladogram, there is no historical information present, and the cladogram has to be discarded as historically uninformative. The same applies if the TVEs in a cladogram occur on different branches. In that case, their relative sequence cannot be specified. If two or more TVEs are present as nodes on the same branch, the order in which the nodes occur specifying these TVEs is noted. In large, mainly vicariant groups of organisms this may result in a series of three or more TVEs, but in smaller groups, the TVEs in a cladogram will be mostly in ordered pairs. Copyright © 1997 by The Willi Hennig Society All rights of reproduction in any form reserved 3. Search for Independently Confirmed Vicariance Events To identify the vicariance events that are confirmed by more than a single sister-group relationship, the TVEs extracted from the different cladograms must be compared and grouped together when they specify the same vicariance events. Two TVEs can be grouped together if two conditions apply: 1. there is no contradiction between the two nodes in the TVE; 2. there is at least some overlap on both sides. To group two TVE nodes, it is not necessary that the area sets on each side of the nodes are completely identical. Range contractions and expansions may have occurred, but most do not influence the result. However, to identify two nodes as specifying the same TVE there has to be an overlap between the area sets on both sides of the nodes. The two TVEs are then combined into a “supported vicariance event” (SVE), by combining the area sets of the TVEs. Other TVEs can then be added to the SVE, using the same criteria. As support for a SVE increases, the number of areas in its sets may also increase, thereby again attracting support from other cladogram nodes. The inherent vagility of species is here acknowledged in that two sets need only to overlap partially to be included in a single, larger set. Thus, the range of either set may have expanded or contracted without much influence on the results. After this has been done, TVEs which are left over can be discarded. There is no reason to assume that they refer to vicariance events, instead of to freak dispersal events involving only a single taxon. 4. Order the Supported Vicariance Events On the basis of the relative ordering of cladogram nodes the SVEs can be ordered in directed pairs or series, corresponding to all the directed pairs or series extracted from the cladograms. To do this, in all the directed pairs or series of cladogram nodes, the nodes 72 Hovenkamp can be substituted by the SVE which they are taken to support. Based on the sequences of SVEs, we can then try to arrange the SVEs in a single sequence, which complies with all individual sequences. PH NG BO NG PH 3 CA BO MP SU 2 4 1 (A) (B) LS JA SU EXAMPLES The possibilities of application of this protocol will be demonstrated by three examples. 5 BO CE PH 8 CA 7 6 (C) Example 1: Pyrrosia The three-area cladograms in Fig. 1 are taken from Hovenkamp (1986), and represent three monophyletic groups in the fern genus Pyrrosia with roughly allopatric distributions. In the cladogram of Fig. 1A there are three TVEs. Corresponding to node 1 is an event separating CA from (BO PH NG). Corresponding to node 2 is an event separating BO from (PH NG). Corresponding to node 3, there is an event separating PH and NG. The relative order of these events corresponds with the order of the nodes 1, 2 and 3. Table 1 lists the geographical information extracted from these cladograms; the relative order of the nodes is listed in Table 2. Comparing the cladograms of Fig. 1A and B, we can combine the TVE nodes 3 and 5, which both specify a separation between PH and NG. We can also combine nodes 2 and 4, as there is a full overlap and no contradiction between the sets BO and BO+MP+SU on one side, and PH+NG and PH+NG on the other. Translated back into actual events, the combination of nodes 2 and 4 implies that either range contraction (from BO+MP+SU to BO) has occurred in Fig. 1A, or range expansion (from BO to BO+MP+SU) in Fig. 2B. At this stage of the analysis, there is no way to decide between these two possibilities. Comparing the cladograms of Fig. 1B and C, we can see that nodes 4 and 7 are contradictory, as the area SU is combined with BO in node 4, whereas in node 7 it occurs in opposition to BO. The supported vicariance events (SVE) from cladograms 1A, B and C are listed in Table 3. Substitution of supported vicariance events (Table 3, leaving out the Copyright © 1997 by The Willi Hennig Society All rights of reproduction in any form reserved FIG. 1. (A) A cladogram with four endemic taxa and one widespread taxon. (B) A cladogram with two endemic taxa and one widespread taxon. (C) A taxon cladogram with two widespread and two endemic species. (A, B, C after Hovenkamp, 1986). Abbreviations: BO, Borneo; CA, Continental Asia (regarded as a single area); CE, Celebes; JA, Java; LS, Lesser Sunda Islands; MP, Malay Peninsula; NG, New Guinea; PH, Philippines; SU, Sumatra. Explanation in text. unsupported nodes), into Table 2 yields Table 4. The shortest single series of events which is compatible with all the sequences in Table 4 is: B>C>A Translated back into geographical information this yields the following series of events: 1. (B): a split between Continental Asia and Malesia; 2. (C): a split between West Malesia (areas BO MP SU LS JA) and East Malesia (Areas PH CE NG); 3. (A): a split between the Philippines and New Guinea. TABLE 1 Geographical Information from Cladograms in Fig. 1 Node Areas of Descendant 1 Descendant 2 1 2 3 CA BO PH BO PH NG PH NG NG 4 5 BO MP SU NG NG PH PH 6 7 8 CA BO LS JA SU BO LS JA SU CE PH LS JA SU CE PH CE PH 73 Vicariance Events in Biogeographical Analysis TABLE 2 TABLE 4 Historical Information from Cladograms of Fig. 1 Cladogram Historical information 1A 1B 1C 1 > 2, 2 > 3, 1 > 2 > 3 4>5 6 > 7, 7 > 8, 6 > 7 > 8 Historical Information Contained in Fig. 1 Showing Supported Vicariant Events only Node 7, in this case, has no geographical explanation. As it is not supported by another node, there is no evidence that it is part of a general historical pattern. However, there is more than a single way to combine the nodes into sets. Instead of combining three nodes from Fig. 1 into the set (2, 4, 8), we could also combine nodes 2 and 7, thus forming two sets, (4, 8) and (2, 7). In this case, node 2 would seem to fit better in the set (4, 8), as it is completely subsumed by node 4. Example 2: Amazonian Biogeography Cracraft (1988) presented an example where a number of conflicting area cladograms result in two conflicting general area cladograms. He noted that neither parsimony analysis nor consensus analysis could resolve the conflict between these two general area cladograms in a non-trivial way. The five different area cladograms from his figures 2 and 3 are presented in Fig. 2. Tables 5–7 present an analysis following the protocol outlined above. The shortest single sequence which is compatible with all the historical information is: TABLE 3 Supported Vicariant Events in Fig. 1 and their Support SVE Supported by nodes Areas of Descendant 1 A B PH CA C D BO MP SU LS JA BO Descendant 2 NG BO PH NG LS JA SU CE PH NG CE LS JA SU CE PH Copyright © 1997 by The Willi Hennig Society All rights of reproduction in any form reserved 3, 5 1, 6 2, 4, 8 7 Cladogram Order of VEs 1A 1B 1C B>C, C >A, B >C >A C >A B>C 2>3>1>2 This sequence of vicariance events is presented in Fig. 3. This is closely similar to the solution presented by Cracraft (his figure 7). Example 3: Mesoamerican Biogeography Rosen (1978), in his analysis of the Middle American fish genera Xiphophorus and Heterandria, has presented the classical benchmark for biogeographical analysis. His biogeographical data are here reproduced as Fig. 4. An analysis following the protocol described here is presented in Tables 8–10. When the vicariance events are then arranged according to the order in Table 10, with the earliest at bottom, a pattern of area splittings emerges which closely corresponds to Rosen's pattern of residual congruence: Number Events 1 8 < > 2, 3 2 9, 10 < > 2, 3, 7, 8 3 4–6 < > 2, 3, 7, 8–10 4 1 < > 2–5, 6, 7–10 The apparent differences between this sequence of events and that implied by Rosen's solution are the consequence of the different methods, and do not correspond to disagreement between the two sequences. For example, in Rosen's solution area 6 does not occur. The appearance of area 6 in the second vicariance event here does not imply that areas 4, 5, and 6 are “closely related”. It merely implies that area 6 is on one side of vicariance event 2. There is no information available about the moment area 6 was separated from the other areas. 74 Hovenkamp NE SE SW NW, Im NE SE SW, NW SE Im SW 3 8 2 5 1 7 4 (A) NW 6 (B) NE SW 10 SE NW NW 11 (C) NE SW SE 15 14 9 NE 13 12 (D) (E) FIG. 2. Five basic area cladograms, after Cracraft (1988), with areas occurring only once omitted. (A) His figure 2a, b; (B) his figure 2c; (C) his figure 2d; (D) his figure 3a, b, c; (E) his figure 3c. FORMALIZATION The rough implementation of the protocol presented here can resolve a variety of biogeographical problems in a way that suggests that it is not only a solution for problems like the one presented by Cracraft, but that it TABLE 5 Nodes in the Area Cladograms Presented by Fig. 2 and the Corresponding Geographical and Historical Information Node Geographical information Descendant 1 Descendant 2 Historical information could be useful as a general protocol for biogeographical analysis. Attempts to formalize the protocol into a more explicit procedure would have to address the following problems: 1. During the extraction of geographical information from the cladograms, any overlap between the combined areas of two branches of a cladogram node disqualifies that node as a TVE. This position more or less takes the middle ground between a very restricted approach where a vicariance event would be recognized only if it can be located very precisely between two nearly contiguous areas, and a relaxed approach which recognizes vicariance events also when there is some degree of overlap between the areas. Overlapping nodes may correspond to vicariance events, but then some of the information required to 1 2 3 NE SE SW SE SW NW Im SW NW Im NW Im 1 >2 2 >3 1 >2>3 4 5 NE SE SE SW NW SW NW 4 >5 6 7 8 SE Im SW SW NW Im SW NW NW 6 >7 7 >8 6 >7>8 TABLE 6 9 10 11 NW NE NW SW SW SE NE SE 9 >10 SVE 13 14 15 NW NE NW SW SW SE NE SE 13>14 13>15 Copyright © 1997 by The Willi Hennig Society All rights of reproduction in any form reserved Supported Vicariant Events in Fig. 2 and their Support 9 >11 Areas of Descendant 1 1 2 3 SE NW NE Im NE Supported by nodes Descendant 2 SW NW Im SW SE SE SW NW Im 2 5 6 11 15 3 8 9 13 1 4 10 14 75 Vicariance Events in Biogeographical Analysis TABLE 7 6 1 9 4,5 10 7 8 2,3 Historical information in Fig. 2 Nodes Vicariant events 9 >10, 13 >14 9 >11, 13 >15 1>2 >3 6 >8 2 >3 2 >1 3 >1 >2 1 >2 G F E locate these events has been lost by subsequent dispersal of taxa. Similarly, information is also lost by local extinction of taxa. A formalized protocol would have to include a quantitative measure which specified how much overlap or distance between areas is allowed in order to include the node in the list of TVEs. It is doubtful whether such a quantitative measure can be developed using objective criteria. It may be more practical to locate the putative vicariance events on the basis of inspection of maps, thus combining geographical information with the information present in the cladograms. 2. During the combination of TVEs into sets specifying SVEs, different combinations of TVEs can be made in many cases. A optimality criterion would be necessary to choose between the various possibilities. Alternatively, one could decide to evaluate all possible combinations. In larger analyses, this option could be time consuming. D C B A (a) 1 3 4,5,6 9,10 8 L K LIMITATIONS J There are some obvious limitations which apply to this protocol. 2 2 > 2 I H 3 3 > 3 > > 1 1 > 2 2 FIG. 3. The sequence of vicariance events resulting from the analysis of Cracraft’s example (1988). Copyright © 1997 by The Willi Hennig Society All rights of reproduction in any form reserved (b) FIG. 4. The two area cladograms for Xiphophorus and Heterandria, as given by Rosen (1978). It is obvious that any n umber of con flictin g two-event statements are compatible with a sequence in which all the events are set in one order and its 76 Hovenkamp TABLE 8 TABLE 10 Nodes in the Area Cladograms Presented in Fig. 4 and the Corresponding Geographical and Historical Information. Areas Numbered as in Rosen (1978) Historical Information in Fig. 4 with Regard to Nodes and Vicariant Events Node Geographical information Descendant 1 Descendant 2 A 6 1–5, 7–10 B C D E F G 1 9 4, 5 10 7 8 2–5, 7–10 2–5, 7, 8, 10 2, 3, 7, 8, 10 2, 3, 7, 8 2, 3, 8 2, 3 H I J K L 1 3 4–6 9, 10 8 2–6, 8–10 2, 4–6, 8–10 2, 8–10 2, 8 2 Historical information Nodes Vicariant events A>B >C >D>E>F >G H>I>J>K>L 3 >4>2>1 3 >4>2>1 A >B>C >D >E >F >G H >I>J>K>L reverse. For example, the sequence A > B > C > D > E> D >C >B> A is compatible with both simple statements A > E and E>A, A >B and B> A, etc. But similarly compatible is the series E>D > C > B>A> B>C>D > E. Thus, when only simple statements relating two areas are found in the analysis, the internal order of the repeating series can not always be elucidated unequivocally. This requires longer statements. The statement B>E> C, for instance, can distinguish between the two different sequences above. Thus, the best results are obtained with cladograms which contain longer sequences of informative nodes. These may be difficult to find. Crisci et al. (1991) list 18 cladograms, of which only five provide sequences of three or more strictly vicariant nodes (p. 158, their cladograms b, e, g, m, n). As a consequence, when there is rampant dispersal and sympatry in all lineages in the cladogram, analysis becomes impossible. This is a limitation which applies to all methods of biogeography, and it is important to be aware that the most highly resolved results are not necessarily the best. Consensus methods will produce unresolved results even when a better resolution is possible (when cladograms are conflicting), whereas parsimony analysis will find highly resolved results more often than warranted (as it makes no distinction between supported vicariance and possibly non-vicariance events). A sequence protocol as outlined above will not recognize vicariance events if they are not supported by more than one node in the study group. At first sight, the results obtained by this protocol may seem much simpler in form and less well resolved than the area cladograms obtained by other methods. However, in an area cladogram, the relative timing of nodes (vicariance events) on different branches is not reconstructed, even if, potentially, the information is present in the data. Thus, this protocol may resolve some aspects of geographical history that are not resolved by cladogram-oriented protocols. WIDESPREAD SPECIES AND ASSUMPTIONS 0, 1 AND 2 The protocol outlined here differs significantly from other methods for biogeographical analysis in the way that widespread species are treated. Consider the example given by Nelson and Ladiges (1991a, their figure 1a, here reproduced as Fig. 5). In this example, we TABLE 9 CA Supported Vicariant Events in Fig. 4 and their Support SVE 1 2 3 4 Areas of Descendant 1 8 9, 10 1 4–6 Descendant 2 Supported by nodes 2, 3 2, 3, 7, 8 2–5, 6, 7–10 2, 3, 7, 8–10 G, L E, K B, H D, J Copyright © 1997 by The Willi Hennig Society All rights of reproduction in any form reserved BO SU BO 10 9 FIG. 5. A three-taxon cladogram with two endemic and one widespread species (after Nelson and Ladiges, 1991b), abbreviations as in Fig. 1. Vicariance Events in Biogeographical Analysis have to deal with the conflicting evidence of one species occupying two areas (BO SU). Other protocols for biogeographical analysis ask the single question “how are the three areas related?”, and then run into problems regarding the evidence for the relationship of area BO. The protocol outlined here asks two separate questions: “What evidence do we have for vicariance events?”; and “What evidence do we have for the history of vicariance events?”. With regard to the first question, there are two possibilities by which this taxon-area configuration could have been derived: taxon 1 and the ancestor of 2 and 3 could have originated after vicariance of areas BO and CA+SU, while taxon 3 dispersed afterwards to area BO. Thus, nodes 1 and 2 would be listed: (1) BO< > CA, SU (2) CA < > SU This corresponds to a resolution of this area cladogram with assumptions 1 and 2 (new implementation, Nelson and Ladiges, 1991a). Alternatively, it is possible that the ancestor of 2 and 3 was still inhabiting areas CA, BO and SU, and then the first node of the cladogram does not specify a vicariance event. In that case, node 1 is not informative, and only node 2 would be listed: (1) CA < > SU, BO This corresponds to the resolution of this area cladogram with the aid of assumption 0. In this case, we also would have no reason to assume that SU represents a relevant area at all. Under this interpretation, the cladogram gives no historical information, and is here regarded as uninformative. Thus, the different solutions for this area cladogram correspond to different ways in which the observed distributions may have been reached. A choice for either of the solutions (assumption 1, 2 or 0) requires empirical data about the probability that dispersal has occurred in a relatively unlikely direction (i.e. back across the vicariance barrier that triggered an earlier speciation event, which it would not have done if it were not a formidable barrier to the species involved), compared to the probability that non-vicariant speciation has occurred. Which of the two possibilities is more likely in a particular situation can only be Copyright © 1997 by The Willi Hennig Society All rights of reproduction in any form reserved 77 decided by relevant data. The resolutions of nodes with sympatric species thus involve empirical questions, and it is impossible to express a general preference for one way of dealing with these problems. When the results of this protocol agree with the solution offered by assumption 0, this does not mean that this protocol takes an “assumption 0” position. Assumptions 0, 1 and 2 are only meaningful in a protocol which takes the predefined areas for granted, and then searches for a way to order the areas in a cladogram. This protocol does not assume the existence of areas, nor does it result in a cladogram of areas. Any correspondence between this protocol and assumption 0 is due to the fact that, like assumption 0, it does not assume vicariance when there is no evidence for it in the data. In this protocol, it is accepted that any two vicariant taxa can be informative about a vicariance event, even if both are widespread. However, when there is overlap between areas of the two taxa (sympatry), support for a vicariant speciation decreases as the amount of overlap increases. When there is only a small overlap, it will usually be acceptable to ignore the overlap if it can be explained by chance dispersal of a few dispersal units across the vicariance boundary. As the overlap increases, such an explanation becomes increasingly more difficult to accept. It will become increasingly difficult to decide whether the observed pattern is to be explained by vicariance followed by dispersal or by small-scale vicariance not resolved with the chosen size of unit areas. Preference for one of these alternatives cannot be decided solely by inspecting the area/ taxa matrix. It must be based on some knowledge about the relative position and distance of the areas, and preferably also on knowledge about the dispersal capacities of the species involved. A third theoretical possibility which could resolve this area cladogram is that the conflicting area (here BO) is composed of two distinct smaller areas (here one with Exemplum borneense, the other one with E. sumatranum). In that case, the unit areas chosen for the analysis are too large. The speciation may have been vicariant, but not at the level resolved by the analysis. In order to assess the degrees of sympatry between overlapping species, it is therefore important to use basic units with sufficient resolution. An important advantage of this protocol is that at one stage, the areas of nodes supporting the same vicariance event are 78 Hovenkamp 1 2 3 4 5 6 B 1 2 B 7 13 A A 19 (A) (B) FIG. 6. The effect of using a grid on the representation of the distribution of taxa. (A) Distribution of taxa A, B plotted on a representation of areas 1, 2. Both taxa will be coded as occurring in areas 1 and 2, suggesting complete sympatry. (B) Distribution of taxa A, B, plotted on an arbitrary grid system with units numbered 1, 2 … 24. Taxon A now will be coded for areas 2, 7–9, 13–16; taxon B for areas 9–12. The sympatry is now immediately seen to be very limited. combined. Thus, the initial units need not correspond with units that are recognized after the analysis. In principle, the initial units can be arbitrarily small. This makes it possible to use a grid for the representation of the basic distribution data. The increased resolution of a grid system with small units over a system with predefined geographical areas is demonstrated in Fig. 6. The recognition that not all vicariance events may be traceable renders much of the discussion about widespread species superfluous. It is simply not possible to extract information about past vicariance events where no information has survived. Once a species has dispersed substantially across the barrier involved in its vicariant origin, information about this vicariance event is irrecoverably lost. original drive for the development of phylogenetic biogeography was the insight that sister-group relationships in a cladogram may reflect vicariance events. An appropriate method for the reconstruction of the biogeographical history must therefore concentrate on geographical boundary lines instead of the areas which they delimit. ACKNOWLEDGEMENTS I thank Yde de Jong, Hubert Turner and Peter van Welzen for their comments at various stages of the preparation of this manuscript. REFERENCES. CONCLUSIONS The emphasis on the construction of area cladograms in phylogenetic biogeography is misguided. It is based on an inappropriate analogy between taxa and areas. The uncritical application of phylogenetic methodology to biogeographical analysis results in attempts to order elements that are irrelevant in a pattern which is irrelevant, using criteria that are invalid. As a result, biogeographical analysis is bogged down in discussions about widespread species, attempting to extract information which simply is no longer present. The Copyright © 1997 by The Willi Hennig Society All rights of reproduction in any form reserved Axelius, B. (1991). Areas of distribution and areas of endemism. Cladistics 7, 197–199. Brooks, D. R. (1990). Parsimony analysis in historical biogeography and coevolution: Methodological and theoretical update. Syst. Zool. 39, 14–30. Brooks, D. R., and Mclennan, D. A. (1991). “Phylogeny, Ecology and Behavior”. University of Chicago Press, Chicago and London. Brooks, D. R., Thorson, T. B., and Mayes, M. A. (1981). Freshwater stingrays (Potamotrygonidae) and their helminth parasites: Testing hypotheses of evolution and coevolution. In: “Advances in Cladistics: Proceedings of the First Meeting of the Willi Hennig Society”, (V. A. Funk, and D. R. Brooks, Eds), pp. 147–175. Cracraft, J. (1988). Deep-history biogeography: Retrieving the historical pattern of evolving continental biotas. Syst. Zool. 37, 221–236. Vicariance Events in Biogeographical Analysis Cracraft, J., and Prum, R. O. (1988). Patterns and processes of diversification: Speciation and historical congruence in some neotropical birds. Evolution 42, 603–620. Crisci, J. V., Cigliano, M. M., Morrone, J. J., and Roig-Juñent, S. (1991). Historical biogeography of Southern South America. Syst. Zool. 40, 152–171. Hovenkamp, P. H. (1986). A monograph of the fern genus Pyrrosia. Leiden Bot. Series 9. Humphries, C. J. (1992). Cladistic biogeography. In “Cladistics. A Practical Course in Systematics”, (Forey, P. L. et al.), Chapter 9. Clarendon Press, Oxford. Kluge, A. G. (1988). Parsimony in vicariance biogeography: A quantitative method and a greater Antillean example. Syst. Zool. 37, 315–328. Mayden, R. M. (1988). Biogeography, parsimony and evolution in North American freshwater fishes. Syst. Zool. 37, 329–355. Mayr, E. (1965). What is fauna? Zool. Jahrb., System. 92, 473–486. Nelson, G., and Ladiges, P. Y. (1991a). Standard assumptions for biogeographic analysis. Aust. Syst. Bot. 4, 41–58. Copyright © 1997 by The Willi Hennig Society All rights of reproduction in any form reserved 79 Nelson, G., and Ladiges, P. Y. (1991b). Three-area statements: Standard assumptions for biogeographic anlaysis. Syst. Zool. 40, 470–485. Nelson, G., and Platnick, N. I. (1981). “Systematics and Biogeography: Cladistics and Variance”. Columbia Univ. Press, New York. Nelson, G., and Platnick, N. I. (1991). Three-taxon statements: A more precise use of parsimony? Cladistics 7, 351–366. Page, R D. M. (1990). Component analysis: A valiant failure? Cladistics 6, 119–136. Rosen, D. E. (1978). Vicariant patterns and historical explanation in biogeography. Syst. Zool. 27, 159–188. Sober, E. (1988). The conceptual relationship of cladistic phylogenetics and vicariance biogeography. Syst. Zool. 37, 245–253. Voss, R. F. (1988). Fractals in nature: From characterization to simulation. In “The Science of Fractal Images” (Peitgen, H.-O., and D. Saupe, Eds), Chapter 1. Springer, New York, Berlin, Heidelberg, London, Paris, Tokyo. Wiley, E. O. (1988). Parsimony analysis and vicariance biogeography. Syst. Zool. 37, 271–290.
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