ANN. MISSOURI BOT. GARD. 91: 159?185. 2004. GEOGRAPHICAL DIVERSIFICATION OF TRIBES EPILOBIEAE, GONGYLOCARPEAE, AND ONAGREAE (ONAGRACEAE) IN NORTH AMERICA, BASED ON PARSIMONY ANALYSIS OF ENDEMICITY AND TRACK COMPATIBILITY ANALYSIS1 Liliana Katinas,2 Jorge V. Crisci,2 Warren L. Wagner,3 and Peter C. Hoch4 ABSTRACT Tribes Epilobieae, Gongylocarpeae, and Onagreae, a monophyletic branch in the family Onagraceae, comprise genera endemic to or having their major basal radiation in the Madrean Floristic Region of southwestern North America. Parsimony analysis of endemicity (PAE) and panbiogeography (track compatibility analysis) were performed in order to seek an historical explanation for the patterns of high diversity and endemicity for the group in this region. Twenty- one areas of endemism are delimited, based on previous biogeographic schemes and presence of endemic plant and animal taxa. Based on distributional data on 173 species, a strict consensus PAE cladogram shows four main groups of areas: northern North America, the central Mexican areas, western North America, and eastern North America. Track compatibility analysis resulted in two strongly supported generalized tracks: one includes eastern North America, and the other western North America. PAE and panbiogeographical analyses of the distributional patterns of these taxa suggest a close relationship of eastern and western North America, with both areas more related to the Neotropics than to the Palearctic, and a rather weak association between northern North America and Asia. The discovery of two tracks in eastern and western North America for Epilobieae, Gongylocarpeae, and Onagreae reveal little relationship of North America with Asia or other continents. These tribes display a distinct but contemporaneous biogeographical history that differs from those of the Holarctic. These eastern and western tracks show that ancestral biotas existed on each side of North America, with the species of each track sharing a common history. Key words: biogeography, endemicity, Madrean, Onagraceae, panbiogeography. Recent developments in biogeography have highlighted the importance of the spatial distribu- tion of organisms as a direct subject of analysis (Craw et al., 1999; Crisci, 2001; Crisci et al., 2000, 2003). The Onagraceae, a moderate-sized, sharply defined, homogeneous family, have been intensively studied (Raven, 1979, 1988; Hoch et al., 1993; Levin et al., 2003, 2004) and thus constitute an excellent group within which to develop such bio- geographic studies. 1 The authors thank the Consejo Nacional de Investigaciones Cient??ficas y Te?cnicas (CONICET, Argentina), Missouri Botanical Garden, and Smithsonian Institution for generous support of this project; primary support for this project came from the Smithsonian Institution Andrew W. Mellon Fellowships in Structure and Evolution of Terrestrial Eco- systems program. We also thank Peter Raven for setting the stage for this analysis through his long study of the Onagraceae, and for his encouragement of this project. We thank Alice Tangerini for preparing the excellent graphics in the figures, Denise Mix for her great help in preparation of the figures and for logistic support for the project, and Tom Hollowell for assistance with the ArcMap base map for the figures. We also thank Matt Lavin, Jun Wen, and an anonymous reviewer for useful comments. 2 Divisio?n Plantas Vasculares, Museo de La Plata, Paseo del Bosque s/n, 1900 La Plata, Argentina. katinas@ museo.fcnym.unlp.edu.ar, jcrisci@netverk.com.ar. 3 Department of Systematic Biology, Botany, MRC 166, Smithsonian Institution, P.O. Box 37012, Washington, D.C. 20013-7012, U.S.A. wagner.warren@nmnh.si.edu. 4 Missouri Botanical Garden, P.O. Box 299, St. Louis, Missouri 63166-0299, U.S.A. peter.hoch@mobot.org. The family Onagraceae includes six monogeneric tribes?Circaeeae, Fuchsieae, Gongylocarpeae, Hauyeae, Jussiaeeae, and Lopezieae?and two larger, more diverse tribes, Epilobieae and Ona- greae (Raven, 1979; Hoch et al., 1993; Levin et al., 2003). Tribes Epilobieae, Gongylocarpeae, and On- agreae, which form a monophyletic branch in the family (Levin et al., 2003), are biogeographically distinct because almost all 11 genera in these tribes are endemic to or have had their major basal ra- 160 Annals of the Missouri Botanical Garden diation in western North America. A primary con- centration of genera exists in the Madrean Floristic Region (Takhtajan, 1986), comprising the south- western United States and northern Mexico. This is an area of great geological and climatological com- plexity with a rich and highly characteristic biota (Axelrod, 1958; Axelrod & Raven, 1985; Takhta- jan, 1986). Gongylocarpus, until recently included in the Onagreae, and Xylonagra (Onagreae) are endemic to western North America, and Camissonia, Clark- ia, and Gayophytum (all Onagreae) have the great majority of their taxa in the region, especially in the California Floristic Province (Raven & Axelrod, 1978); each of the latter three genera also has one or two species in temperate South America. The remaining genera of Onagreae (Calylophus, Gaura, Oenothera, Stenosiphon) have centers of diversity further east in North America, although Gaura ex- tends into central Mexico and Oenothera into Cen- tral and South America. One exception to the pre- dominantly North American nature of these tribes is Chamerion (the fireweeds), a genus of Epilobieae with six of its eight species and one of two sections endemic in Europe and Asia. Tribe Epilobieae def- initely has a north temperate origin, with a distri- bution pattern that suggests a more complex history of diversification (Raven, 1976; Baum et al., 1994). All seven sections of Epilobium (including the for- mer segregate genera Boisduvalia and Zauschneria) occur in or are restricted to the Madrean Region, with the large section Epilobium diversified on all other continents except Antarctica. In order to seek the historical explanations that led to the high diversity and endemicity of Epilo- bieae, Gongylocarpeae, and Onagreae in North America, we will analyze the patterns of distribu- tion of species of these tribes native to North Amer- ica (for a list of species and references, see Table 1). A focus on patterns of distribution requires con- ceptual and methodological tools that allow com- parisons to be made in a meaningful and informa- tive way. Two modern approaches that allow this kind of analysis are parsimony analysis of ende- micity and track compatibility analysis (panbi- ogeography) (Morrone & Crisci, 1990, 1995; Crisci et al., 2000, 2003). MATERIALS AND METHODS AREAS OF ENDEMISM An area of endemism is defined as an area of nonrandom distributional congruence among differ- ent taxa. It is identified by the congruent distri- butional boundaries of two or more species, where congruence does not demand complete agreement on those limits at all possible scales of mapping, but relatively extensive sympatry is a prerequisite (Platnick, 1991). Areas of endemism used in this analysis are de- fined primarily by Takhtajan (1986) and Thorne (1993) and validated by other biogeographical stud- ies (i.e., Dice, 1943; Rzedowski, 1978; Brown et al., 1979, 1998; McLaughlin, 1989, 1992; Ayala et al., 1993; Escalante Pliego et al., 1993; Fa & Mo- rales, 1993; Li & Adair, 1994; Liebherr, 1994a, b; Morrone et al., 1999; Marshall & Liebherr, 2000; Morrone, 2001). Because the focus of this study is on a major plant lineage that has diversified in arid North America, we have used small, closely defined areas within the Madrean area. Some taxa within this lineage have distributions that extend beyond the North American regions. For these we used the more broadly defined Neotropical, East Palearctic, and West Palearctic regions, since they fall outside of our area of focus in North America. Africa and Australia were not included because native North American species of these three tribes occur in these areas only as exotics. Table 2 lists the areas of endemism alphabetically, with taxa of the three target tribes endemic to each area. Full descrip- tions of each area of endemism, including sample plant and animal taxa endemic to each, are provid- ed in Appendix 1. The areas are illustrated in Fig- ure 1. In some regions, the area delineations provided by Takhtajan (1986) and Thorne (1993) proved somewhat vague or difficult to interpret, and in those cases we used additional resources to deter- mine the boundaries. For example, we used the geographical subdivisions found in The Jepson Manual (Hickman, 1993) to more precisely delin- eate the five regions in California (CAL, GBA, MOJ, SON, and VAN; see Table 2 for area acro- nyms). Similarly, we used the vegetational areas de- scribed in Correll and Johnston (1970) to establish the boundaries of the regions in Texas (APP, ATL, CHI, NAP, and TAM). Additional sources used for specific areas are referenced in the area descrip- tion. In this way, distributional records could be placed more precisely in the appropriate area of endemicity. TAXA ANALYZED The primary data for this analysis are the distri- butions of 173 native species of Onagraceae tribes Epilobieae, Gongylocarpeae, and Onagreae inhab- iting North America (Canada, Mexico, United States; Table 1). The distributional data were taken Volume 91, Number 1 2004 161Katinas et al. Geographical Diversification Table 1. List of species included in this analysis and source of distributional data (see text for details regarding unpublished data). Gongylocarpus is listed here in tribe Onagreae; only recently (Levin et al., 2003) it was transferred to tribe Gongylocarpeae. The number of each species corresponds with column numbers in the data matrix (Table 3). Names of taxa are those currently in use, based on recent revisions. Two of the names, Oenothera deserticola and O. purpusii, subsequently have been revised due to a nomenclatural problem (Wagner, 2004): Oenothera purpusii in the sense used here will become O. deserticola, and the current O. deserticola will take a new name. Taxa Source of information TRIBE ONAGREAE Camissonia Link Raven (1962, 1969) 1. C. andina (Nutt.) P. H. Raven 2. C. arenaria (A. Nelson) P. H. Raven 3. C. boothii (Douglas) P. H. Raven 4. C. breviflora (Torr. & A. Gray) P. H. Raven 5. C. brevipes (A. Gray) P. H. Raven 6. C. californica (Nutt. ex Torr. & A. Gray) P. H. Raven 7. C. campestris (Greene) P. H. Raven 8. C. cardiophylla (Torr.) P. H. Raven 9. C. chamaenerioides (A. Gray) P. H. Raven 10. C. cheiranthifolia (Hornem. ex Spreng.) Raim. 11. C. claviformis (Torr. & Fre?m.) P. H. Raven 12. C. confusa P. H. Raven 13. C. contorta (Douglas) Kearney 14. C. eastwoodiae (Munz) P. H. Raven 15. C. graciliflora (Hook. & Arn.) P. H. Raven 16. C. guadalupensis (S. Watson) P. H. Raven 17. C. hilgardii (Greene) P. H. Raven 18. C. hirtella (Greene) P. H. Raven 19. C. ignota (Jeps.) P. H. Raven 20. C. intermedia P. H. Raven 21. C. kernensis (Munz) P. H. Raven 22. C. lacustris P. H. Raven 23. C. lewisii P. H. Raven 24. C. minor (A. Nelson) P. H. Raven 25. C. multijuga (S. Watson) P. H. Raven 26. C. ovata (Nutt. ex Torr. & A. Gray) P. H. Raven 27. C. pallida (Abrams) P. H. Raven 28. C. palmeri (S. Watson) P. H. Raven 29. C. parvula (Nutt. ex Torr. & A. Gray) P. H. Raven 30. C. pterosperma (S. Watson) P. H. Raven 31. C. pubens (S. Watson) P. H. Raven 32. C. pusilla P. H. Raven 33. C. pygmaea (Douglas) P. H. Raven 34. C. refracta (S. Watson) P. H. Raven 35. C. robusta P. H. Raven 36. C. scapoidea (Torr. & A. Gray) P. H. Raven 37. C. strigulosa (Fisch. & C. A. Mey.) P. H. Raven 38. C. subacaulis (Pursh) P. H. Raven 39. C. tanacetifolia (Torr. & A. Gray) P. H. Raven 40. C. walkeri (A. Nelson) P. H. Raven Calylophus Spach Towner (1977) 41. C. berlandieri Spach 42. C. hartwegii (Benth.) P. H. Raven 43. C. lavandulifolius (Torr. & A. Gray) P. H. Raven 44. C. serrulatus (Nutt.) P. H. Raven 45. C. toumeyi (Small) Towner 46. C. tubicula (A. Gray) P. H. Raven Clarkia Pursh Lewis & Lewis (1955, except in *) 47. C. amoena (Lehm.) A. Nelson & J. F. Macbr. 162 Annals of the Missouri Botanical Garden Table 1. Continued. Taxa Source of information 48. C. biloba (Durand) A. Nelson & J. F. Macbr. 49. C. concinna (Fisch. & C. A. Mey.) Greene 50. C. cylindrica (Jeps.) F. H. Lewis & M. R. Lewis 51. C. dudleyana (Abrams) J. F. Macbr. 52. C. epilobioides (Nutt. ex Torr. & A. Gray) A. Nelson & Macbr. 53. C. gracilis (Piper) A. Nelson & J. F. Macbr. 54. *C. heterandra (Torr.) F. H. Lewis & P. H. Raven 55. C. lassenensis (Eastw.) F. H. Lewis & M. R. Lewis 56. C. modesta Jeps. 57. *C. mosquini E. Small 58. C. pulchella Pursh 59. C. purpurea (Curtis) A. Nelson & J. F. Macbr. 60. C. rhomboidea Douglas 61. *C. rostrata W. S. Davis 62. C. speciosa F. H. Lewis & M. R. Lewis 63. *C. tembloriensis Vasek 64. C. unguiculata Lindl. Lewis (1993) Lewis (1993) Lewis (1993) Lewis (1993) 65. C. xantiana A. Gray Gaura L. Raven & Gregory (1972) 66. G. angustifolia Michx. 67. G. biennis L. 68. G. boquillensis P. H. Raven & D. P. Greg. 69. G. brachycarpa Small 70. G. calcicola P. H. Raven & D. P. Greg. 71. G. coccinea Pursh 72. G. drummondii (Spach) Torr. & A. Gray 73. G. filipes Spach 74. G. hexandra Ortega 75. G. longiflora Spach 76. G. mckelveyae (Munz) P. H. Raven & D. P. Greg. 77. G. mutabilis Cav. 78. G. neomexicana Wooton 79. G. parviflora Douglas ex Lehm. 80. G. sinuata Nutt. ex Ser. 81. G. suffulta Engelm. ex A. Gray 82. G. villosa Torr. Gayophytum A. Juss. Lewis & Szweykowski (1964) 83. G. decipiens F. H. Lewis & Szweykowski 84. G. diffusum Torr. & A. Gray 85. G. heterozygum F. H. Lewis & Szweykowski 86. G. humile A. Juss. 87. G. racemosum Torr. & A. Gray 88. G. ramosissimum Torr. & A. Gray Gongylocarpus Cham. & Schltdl. (transferred to Gongylocarpeae; Levin et al., 2003) 89. G. rubricaulis Schltdl. & Cham. Carlquist & Raven (1966) Oenothera L. 90. O. albicaulis Pursh 91. O. biennis L. 92. O. brachycarpa A. Gray 93. O. caespitosa Nutt. W. L. Wagner (unpublished data) Dietrich et al. (1997) W. L. Wagner (unpublished data) Wagner et al. (1985) 94. O. californica (S. Watson) S. Watson 95. O. cavernae Munz 96. O. cordata J. W. Loudon W. L. Wagner (unpublished data) Wagner et al. (1985) Dietrich & Wagner (1988) 97. O. coronopifolia Torr. & A. Gray 98. O. deltoides Torr. & Fre?m. W. L. Wagner (unpublished data) W. L. Wagner (unpublished data) Volume 91, Number 1 2004 163Katinas et al. Geographical Diversification Table 1. Continued. Taxa Source of information 99. O. deserticola (Loes.) Munz 100. O. dissecta A. Gray ex S. Watson 101. O. drummondii Hook. 102. O. elata Kunth 103. O. epilobiifolia Kunth 104. O. falfurriae W. Dietr. & W. L. Wagner 105. O. flava (A. Nelson) Garrett 106. O. fruticosa L. 107. O. grandiflora L?He?r. Wagner (2004, unpublished data) Wagner (1984) Dietrich & Wagner (1988) Dietrich et al. (1997) W. L. Wagner (unpublished data) Dietrich & Wagner (1988) W. L. Wagner (unpublished data) Straley (1977) Dietrich et al. (1997) 108. O. grandis (Britton) Smyth 109. O. heterophylla Spach 110. O. howardii (A. Nelson) W. L. Wagner 111. O. humifusa Nutt. 112. O. jamesii Torrey & A. Gray Dietrich & Wagner (1988) Dietrich & Wagner (1988) W. L. Wagner (unpublished data) Dietrich & Wagner (1988) Dietrich et al. (1997) 113. O. kunthiana (Spach) Munz 114. O. laciniata Hill 115. O. latifolia (Rydb.) Munz 116. O. linifolia Nutt. 117. O. longissima Rydb. 118. O. macrocarpa Nutt. 119. O. macrosceles A. Gray 120. O. mexicana Spach 121. O. nuttallii Sweet 122. O. nutans G. F. Atk. & Bartlett W. L. Wagner (unpublished data) Dietrich & Wagner (1988) W. L. Wagner (unpublished data) Straley (1977) Dietrich et al. (1997) W. L. Wagner (unpublished data) Dietrich et al. (1985) Dietrich & Wagner (1988) W. L. Wagner (unpublished data) Dietrich et al. (1997) 123. O. oakesiana (A. Gray) J. W. Robbins ex S. Watson & J. M. Coulter 124. O. pallida Lindl. 125. O. parviflora L. 126. O. pennellii Munz 127. O. perennis L. 128. O. pilosella Raf. 129. O. primiveris A. Gray 130. O. pubescens Willd. ex Spreng. 131. O. purpusii Munz Dietrich et al. (1997) W. L. Wagner (unpublished data) W. L. Wagner (unpublished data) W. L. Wagner (unpublished data) Straley (1977) Straley (1977) Wagner (1986, unpublished data) Dietrich & Wagner (1988) Wagner (2004, unpublished data) 132. O. rhombipetala Nutt. ex Torr. & A. Gray 133. O. rosea L?He?r. ex Aiton 134. O. spachiana Torr. & A. Gray 135. O. speciosa Nutt. 136. O. tetraptera Cav. 137. O. triloba Nutt. Dietrich & Wagner (1988) W. L. Wagner (unpublished data) Straley (1977) W. L. Wagner (unpublished data) W. L. Wagner (unpublished data) W. L. Wagner (unpublished data) 138. O. tubifera Ser. 139. O. villosa Thunb. W. L. Wagner (unpublished data) W. L. Wagner (unpublished data) Stenosiphon Spach 140. S. linifolius (Nutt.) Heynh. Great Plains Flora Assoc. (1986) TRIBE EPILOBIEAE Chamerion (Raf.) Raf. Hoch (1993) 141. C. angustifolium L. 142. C. latifolium L. Mosquin (1966) Small (1968) Epilobium L. Hoch (1986, 1993, unpublished (see text)) 143. E. anagallidifolium Lam. 144. E. arcticum Sam. 145. E. brachycarpum C. Presl 146. E. canum (Greene) P. H. Raven 147. E. ciliatum Raf. 148. E. clavatum Hausskn. 164 Annals of the Missouri Botanical Garden Table 1. Continued. Taxa Source of information 149. E. coloratum Spreng. 150. E. davuricum Fisch. ex Hornem. 151. E. densiflorum (Lindl.) Hoch & P. H. Raven Raven & Moore (1965) 152. E. denticulatum Ruiz & Pav. 153. E. foliosum (Nutt. ex Torr. & A. Gray) Suksd. 154. E. glaberrimum Barbey 155. E. halleanum Hausskn. 156. E. hornemannii Rchb. 157. E. lactiflorum Hausskn. 158. E. leptocarpum Hausskn. 159. E. leptophyllum Raf. 160. E. luteum Pursh 161. E. minutum Lindl. ex Lehm. 162. E. mirabile Trel. 163. E. nevadense Munz 164. E. obcordatum A. Gray 165. E. oregonense Hausskn. 166. E. pallidum (Eastw.) Hoch & P. H. Raven Raven & Moore (1965) 167. E. palustre L. 168. E. pygmaeum (Speg.) Hoch & P. H. Raven Raven & Moore (1965) 169. E. saximontanum Hausskn. 170. E. smithii H. Le?v. 171. E. strictum Muhl. 172. E. suffruticosum Nutt. 173. E. torreyi (S. Watson) Hoch & P. H. Raven Raven & Moore (1965) from recent or unpublished taxonomic revisions, supplemented with specimen label data from the herbaria at MO and US (Table 3). Distribution re- cords for Epilobium derive from nearly 100,000 specimens from more than 100 herbaria consulted in preparation for a revision (Hoch et al., unpub- lished); these records served as the basis for Epi- lobium treatments in The Jepson Manual (Hoch, 1993), the Flora of the Great Plains (Hoch, 1986), and other recent floras. Records for several sections of Oenothera for which taxonomic revisions are not yet published (cited in Table 1 as ??Wagner, unpub- lished data??) are derived from several sources. All unpublished Oenothera distributions except for those of section Anogra are based on approximately 4500 collections from more than 100 herbaria bor- rowed for those revisions. For the 10 species of section Anogra, distributions derive from some 250 collections at US and MO, supplemented by addi- tional collections examined for The Jepson Manual project (Wagner, 1993). We have excluded from our distributional analysis specimens that were culti- vated and/or appear far outside the established range in human-disturbed habitats. Species that oc- cur only in one area of endemism are not infor- mative in a Parsimony Analysis of Endemicity (PAE) regarding area relationships and therefore are excluded from the analysis. However, they pro- vide support for the delimitation of areas of ende- mism and are listed in Table 2. For example, the monotypic genus Xylonagra is endemic to Central Baja California and thus is used to circumscribe the Sonoran (SON) region. Although almost all of the genera of Epilobieae, Gongylocarpeae, and Onagreae are endemic to or have had their major basal radiation in the Mad- rean Floristic Region of southwestern North Amer- ica, many species of these tribes, especially in Epi- lobium and Oenothera, occur outside of North America. If native North American species also have a native distribution outside of North America, those distributions are included in the data matrix in the appropriate area (NE, WP, or EP). However, if a species occurs as a native only outside of North America, it has been excluded from this analysis. These excluded taxa include in Epilobieae 6 Eur- asian species of Chamerion and 125 species of Epi- lobium (large groups endemic to South America, Eurasia, and Australasia), and in Onagreae, 1 spe- cies each of Camissonia (C. dentata), Clarkia (C. tenella), and Gayophytum (G. micranthum), and 39 species of Oenothera, virtually all endemic to South America. In Epilobium and Oenothera, we have ex- cluded 9 species (E. billardierianum and E. ko- Volume 91, Number 1 2004 165Katinas et al. Geographical Diversification Table 2. Alphabetical list of areas of endemism used in this analysis, and taxa of tribes Epilobieae, Gongylocarpeae, and Onagreae (Onagraceae) endemic to specific individual areas (see Table 1 for sources of distributional data). See Appendix 1 for full descriptions of the areas and references; numbers in parentheses refer to Appendix 1. Acronym/Area of endemism Endemic taxa APP/Appalachian (3) Gaura demareei P. H. Raven & D. P. Greg.; Oenothera argillicola Mack. ARC/Arctic (1) ? ATL/Atlantic and Gulf Coastal (4) Gaura lindheimeri Engelm. & A. Gray; Oenothera clelandii W. Dietr., P. H. Raven & W. L. Wagner, O. curtissii Small CAL/Californian (9) Camissonia benitensis P. H. Raven, C. bistorta (Nutt. ex Torr. & A. Gray) P. H. Raven, C. hardhamiae P. H. Raven, C. integrifolia P. H. Raven; C. luciae P. H. Raven, C. micrantha (Hornem. ex Spreng.) P. H. Raven; Clarkia affinis F. H. Lewis & M. R. Lewis, C. borealis E. Small, C. bottae (Spach) F. H. Lewis & M. R. Lewis, C. breweri (A. Gray) Greene, C. davyi (Jepson) F. H. Lewis & M. R. Lewis, C. deli- cata (Abrams) A. Nelson & J. F. Macbride, C. franciscana F. H. Lewis & P. H. Raven, C. imbricata F. H. Lewis & M. R. Lewis, C. joloensis D. R. Parn., C. lewisii P. H. Raven & D. R. Parn., C. pros- trata F. H. Lewis & M. R. Lewis, C. rubicunda (Lindl.) F. H. Lewis & M. R. Lewis, C. similis F. H. Lewis & W. R. Ernst; Epilobium cleistogamum (Curran) P. Hoch & P. H. Raven; Gayophytum oligo- spermum F. H. Lewis & Szweyk. CAN/Canadian (2) ? CHI/Chihuahuan (12) Gaura macrocarpa Rothr.; Oenothera havardii S. Watson, O. neomexi- cana (Small) Munz, O. organensis Munz, O. platanorum P. H. Raven & D. R. Parn., O. riskindii W. L. Wagner, O. texensis P. H. Raven & D. R. Parn. EP/East Palearctic (20) ? (some endemics, but outside of North American study group) GBA/Great Basin (8) Camissonia atwoodii Cronquist, C. confertiflora (P. H. Raven) P. H. Ra- ven, C. exilis (P. H. Raven) P. H. Raven, C. gouldii P. H. Raven, C. heterocroma (S. Watson) P. H. Raven, C. megalantha (Munz) P. H. Raven, C. nevadensis (Kellogg) P. H. Raven, C. parryi (S. Watson) P. H. Raven, C. speculicola (P. H. Raven) P. H. Raven MAS/Mexican Altiplano (16) ? MOJ/Mojavean (10) Camissonia munzii (P. H. Raven) P. H. Raven NAP/North American Prairies (5) Gaura triangulata Buckl.; Oenothera canescens Torr. & Fre?m., O. coryi W. L. Wagner, O. engelmannii (Small) Munz, O. harringtonii W. L. Wagner, Stockh. & W. M. Klein NE/Neotropical (19) ? (some endemics, but outside of North American study group) ROC/Rocky Mountain (7) Oenothera acutissima W. L. Wagner, O. psammophila (A. Nelson & J. F. Macbr.) W. L. Wagner, Stockh. & W. M. Klein SMO/Sierra Madre Occidental (14) Epilobium maysillesii Munz; Oenothera maysillesii Munz, O. tamrae W. Dietr. & W. L. Wagner SMR/Sierra Madre Oriental (17) Oenothera muelleri Munz, O. stubbei W. Dietr., P. H. Raven & W. L. Wagner SMS/Sierra Madre del Sur (18) ? SON/Sonoran (11) Camissonia angelorum (S. Watson) P. H. Raven, C. crassifolia (Greene) P. H. Raven, C. proavita P. H. Raven, C. sceptrostigma (Brandegee) P. H. Raven; Gongylocarpus fruticulosus (Benth.) K. Brandegee; Oen- othera arizonica (Munz) W. L. Wagner, O. brandegeei (Munz) P. H. Raven, O. breedlovei W. Dietr. & W. L. Wagner, O. wigginsii W. M. Klein; Xylonagra arborea (Kellogg) J. D. Smith & J. N. Rose TAM/Tamaulipan (13) ? TMV/Trans-Mexican Volcanic Belt (15) ? VAN/Vancouverian (6) Camissonia sierrae P. H. Raven; Clarkia arcuata (Kellogg) A. Nelson & J. F. Macbr., C. australis E. Small, C. exilis F. H. Lewis & Vasek, C. lingulata F. H. Lewis & M. R. Lewis, C. mildrediae (Heller) F. H. Lewis & M. R. Lewis, C. springvillensis Vasek, C. stellata Mosquin, C. virgata Greene, C. williamsonii (Durand & Hilg.) F. H. Lewis & M. R. Lewis; Epilobium howellii P. Hoch, E. nivium T. S. Brandegee, E. oreganum Greene, E. rigidum Hausskn., E. septentrionale (D. D. Keck) Bowman & P. Hoch, E. siskiyouense (Munz) P. Hoch & P. H. Raven; Gayophytum eriospermum Coville; Oenothera wolfii (Munz) P. H. Raven, O. xylocarpa Coville WP/West Palearctic (21) ? (some endemics, but outside of North American study group) 166 Annals of the Missouri Botanical Garden Figure 1. Areas of endemism as delimited for the historical biogeographic analysis and used to code the distri- butional data for each species. The areas were drawn in Photoshop 7.0 by Alice Tangerini on a base map from ArcMap 8.2 (ESRI) with a North American Lambert conformal conic projection. The floristic regions are based primarily on Takhtajan (1986) and Thorne (1993), with other modifications as described in the text. marovianum from Australasia and E. hirsutum, E. montanum, E. obscurum, and E. parviflorum from Eurasia, O. glazioviana, a hybrid of recent origin in Europe, and O. mollissima and O. stricta from South America) because all of them clearly have been introduced into North America in historical time. PARSIMONY ANALYSIS OF ENDEMICITY (PAE) Parsimony analysis of endemicity or PAE (Ro- sen, 1988; Rosen & Smith, 1988) is an historical biogeographical approach that seeks to identify the distributional pattern of organisms. It classifies lo- calities, quadrats, or areas (which are analogous to taxa) by their shared taxa (which are analogous to characters) according to the most parsimonious so- lution resulting in a hierarchical classification of the geographic units (Morrone & Crisci, 1995; Cris- ci et al., 2000, 2003). Rosen (1988) originally pro- posed the method using localities as study units. Craw (1988) and Cracraft (1991) presented a vari- ation of the method using areas of endemism as study units to identify the hierarchical information contained in the geographical distribution of organ- Volume 91, Number 1 2004 167Katinas et al. Geographical Diversification isms to establish area relationships. Indeed, Mc- Laughlin (1992) suggested that areas are actually arranged in a natural hierarchy. The variation of the methodology proposed by Craw (1988) and Cracraft (1991) using areas of en- demism included taxonomic information in the ma- trix by adding columns for higher taxonomic cate- gories or phylogenetic information. Thus, the resulting matrix consisted of areas 3 species dis- tributions plus generic distributions. However, as Crisci et al. (2000) observed, adding phylogenetic or taxonomic information to the matrix is a misuse of Brooks parsimony analysis (Brooks et al., 2001), which is a technique that does not utilize phylo- genetic data specifically. Therefore, we use areas of endemism as our units of study and species distri- butions as the characters of those areas, but ex- clude the information on supraspecific taxa. PAE cladograms represent nested sets of areas in which terminal dichotomies represent two areas between which the most recent biotic interchange has occurred (Morrone & Crisci, 1995). Craw (1988) suggested that ??character?? reversions in the cladogram could be interpreted biogeographically as extinctions, and parallelisms as dispersions. This analysis was carried out using PAUP*, vers. 4.0b10 (Swofford, 2001), applying the branch-and-bound and deltran options. If more than one tree results from the analysis, a strict consensus tree is con- structed. As proposed by Rosen (1988), the clad- ogram was rooted with a hypothetical area coded with all zeros. The bootstrap method (Felsenstein, 1985) was employed to evaluate the reliability of the estimates; 100 replicates were performed. We used the software MacClade 4.0 (Maddison & Mad- dison, 2000) to generate the data matrix and as a tool to analyze the taxa distribution on the tree(s). PANBIOGEOGRAPHY (COMPATIBILITY TRACK METHOD) Croizat (1958) postulated that geographic barri- ers evolve together with biotas. The panbiogeo- graphic approach (Croizat, 1958, 1981) consists of plotting distributions of taxa on maps and connect- ing their separate distributional areas together with lines called individual tracks. When individual tracks coincide, the resulting summary lines are considered generalized tracks, which indicate the pre-existence of ancestral biotas that became frag- mented by tectonic and/or climatic changes. At the same time, generalized tracks provide spatial cri- teria for biogeographic homology (Grehan, 1988a, b; Morrone & Crisci, 1995). When two or more gen- eralized tracks intersect, that area is called a node. Nodes are dynamic biogeographic boundaries where remnant fragments of different ancestral bi- otas come into contact. Nodes are biogeographically interesting because they are composite regions that represent an intersection of different biogeograph- ical and ecological histories. Analytical developments by McAllister et al. (1986), Page (1987), Connor (1988), Craw (1989), and Henderson (1990, 1991) used graph theory to provide objective and quantitative methods for drawing and comparing tracks, including the com- patibility track method applied here. This method was developed by Craw (1988, 1989), based on the concept of distributional compatibility (Connor, 1988; Craw, 1989). Individual tracks are treated as biogeographic hypotheses of relationship among lo- calities or distribution areas. Two or more individ- ual tracks are regarded as being compatible only if they result in the same pairwise comparison or if one track is a subset of the other. This method is analogous to character compatibility (Meacham, 1984). However, in the track compatibility method, nonoverlapping tracks are incompatible, whereas they would be compatible under the original taxo- nomic concept. The compatibility track method ba- sically consists of constructing a matrix (areas vs. taxa), where each taxon is scored as present (1) or absent (0) in each area, and applying compatibility analysis software to find the largest clique(s) of compatible tracks. The method involves finding a simple form of spanning tree linking localities or distribution areas. The tree is constructed from the largest clique of compatible distributions in a dis- tributional compatibility matrix and is based on the original concept of compatibility (nonoverlapping tracks are also considered compatible). Therefore, using a restricted concept of compatibility (only in- dividual tracks that are either included within or replicated by one another are compatible) the tree (5 clique) could contain more than one generalized track. In this case, multiple generalized tracks (groups) found in one clique will be formed only by areas that are exclusive of each generalized track. If more than one largest clique or several cliques of considerable size are found, then a hypothesis of existence of several generalized tracks linking the localities or distribution areas in more than one way can be considered (areas can be members of more than one generalized track at the same time). Al- ternatively, the intersection (i.e., those individual tracks common to all the largest cliques) can also be identified as a generalized track (Craw, 1990). For more details and other applications of this method see Craw (1988, 1989), Morrone and Crisci 168 Annals of the Missouri Botanical Garden Ta bl e 3. D at a m at ri x (g eo gr ap hi ca l ar ea s vs . in di vi du al ta xa of O na gr ac ea e) fo r th e co m pa ti bi li ty tr ac k an al ys is an d pa rs im on y an al ys is of en de m ic it y. O U T 5 O ut gr ou p; ot he r ar ea ac ro ny m s ar e as li st ed in Ta bl e 2 an d A pp en di x 1. Ta xo n nu m be r co rr es po nd s to th os e fo un d in Ta bl e 1. A bs en ce 5 0; pr es en ce 5 1. 10 20 30 40 50 60 70 80 90 O U T A R C C A N A P P A T L N A P 00 00 00 00 00 00 00 00 00 00 00 01 00 00 00 00 00 00 00 00 00 00 00 00 00 10 01 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 01 01 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 11 01 00 00 00 11 01 00 00 00 11 11 01 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 01 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 10 10 00 00 01 10 10 00 00 00 10 11 00 00 00 00 00 00 00 00 00 00 10 00 00 00 00 01 10 11 00 11 01 10 11 00 11 11 00 10 01 11 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 10 00 00 00 00 10 00 00 00 00 11 01 00 11 01 V A N R O C G B A C A L M O J SO N 10 10 00 10 01 10 11 00 00 00 10 11 10 00 10 01 10 11 10 01 00 10 11 01 10 01 10 11 01 11 10 10 10 11 10 00 11 00 10 00 10 01 00 00 00 11 10 11 01 11 10 00 00 00 00 11 00 01 01 11 11 01 01 01 01 00 01 00 00 10 00 01 10 11 11 11 10 01 11 00 10 00 10 11 01 00 10 00 10 00 11 11 00 01 10 01 10 01 01 11 11 11 01 01 11 10 01 10 10 00 01 01 00 00 01 00 01 10 10 00 00 00 00 11 11 01 11 00 00 00 01 10 00 00 00 00 00 00 11 11 00 10 00 00 00 00 11 10 00 00 10 11 11 11 11 00 10 00 01 01 00 10 10 01 01 11 11 11 10 11 00 00 00 00 00 01 00 00 00 11 11 11 10 00 00 00 00 00 00 00 00 00 00 00 00 11 11 10 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 10 00 00 01 10 10 01 00 00 10 00 00 00 00 00 10 00 00 00 10 10 01 00 10 10 00 11 11 11 00 00 11 01 11 01 00 11 11 11 01 00 11 11 10 00 00 00 00 00 01 00 10 00 01 01 C H I TA M SM O T M V M A S SM R 00 00 00 00 10 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 11 11 11 00 00 11 11 01 00 00 00 00 10 00 00 00 00 00 00 00 01 00 00 00 00 01 00 01 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 01 01 00 00 00 01 11 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 11 01 00 11 11 11 00 11 00 11 10 01 00 10 10 11 01 00 10 10 11 01 00 10 00 10 01 00 10 00 11 00 00 00 01 11 00 00 00 10 00 00 00 00 10 00 00 00 00 10 00 00 00 00 10 00 00 00 00 00 SM S N E W P E P 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 01 00 00 00 00 00 00 00 00 00 00 00 00 11 00 00 10 00 00 01 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 01 00 10 00 00 00 00 00 00 00 00 00 00 Volume 91, Number 1 2004 169Katinas et al. Geographical Diversification Ta bl e 3. C on ti nu ed . 1 00 11 0 12 0 13 0 14 0 15 0 16 0 17 0 17 3 O U T A R C C A N A P P A T L N A P 00 00 00 00 00 00 00 00 00 00 10 00 00 00 00 10 00 01 00 00 10 00 01 00 00 10 10 00 10 00 00 00 00 00 00 00 00 00 00 00 00 00 01 00 00 01 01 01 11 10 10 01 01 11 10 01 01 11 01 11 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 01 01 01 01 01 11 01 01 01 01 01 11 11 01 00 00 00 00 00 00 00 00 00 00 00 00 10 10 11 00 11 10 10 11 00 01 10 10 11 00 10 01 10 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 10 01 01 11 10 11 00 11 11 00 10 01 01 10 10 11 00 00 00 00 00 11 11 00 10 01 11 11 10 10 11 10 00 10 10 10 10 00 00 10 10 10 00 10 10 10 00 00 00 00 00 00 00 01 11 11 00 00 01 10 10 00 00 00 00 10 00 00 00 00 10 00 00 11 10 10 00 00 00 00 00 00 00 00 10 10 00 00 00 10 10 00 00 00 10 00 00 00 00 10 00 00 00 00 11 10 00 0 00 0 10 0 10 0 10 0 00 0 V A N R O C G B A C A L M O J SO N 00 00 00 01 00 00 10 00 10 00 00 11 10 11 00 00 01 00 01 00 00 11 10 11 00 01 11 00 01 00 01 00 10 00 00 01 00 10 00 00 01 00 10 00 01 01 00 10 00 00 00 00 10 00 01 11 00 10 00 00 00 00 00 00 00 00 00 10 10 00 00 00 10 10 00 00 00 00 00 00 00 00 00 10 00 00 10 00 00 00 00 01 00 00 00 10 01 00 00 01 00 01 00 00 11 00 00 00 00 00 00 00 00 00 11 00 01 00 00 11 00 00 00 00 10 00 00 00 00 10 00 00 00 00 10 00 00 00 00 00 00 00 00 00 00 00 10 00 10 00 11 10 11 11 00 11 10 11 11 01 11 10 11 11 00 11 10 11 11 00 10 00 11 10 00 00 00 11 10 00 10 11 11 11 11 10 11 11 11 11 10 01 11 10 10 10 11 11 10 10 00 00 00 00 00 10 11 00 00 00 11 01 11 11 11 11 01 10 11 11 10 11 11 11 10 10 00 11 11 00 00 10 00 00 00 00 00 00 00 00 00 1 01 1 01 1 00 1 00 0 00 0 C H I TA M SM O T M V M A S SM R 01 10 00 10 01 01 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 11 00 00 00 00 10 01 00 10 00 00 10 01 00 01 00 01 00 10 00 00 00 00 00 00 00 01 10 10 00 00 01 10 00 00 00 01 11 00 01 10 01 11 00 00 10 00 10 00 00 00 00 10 00 00 00 01 10 00 00 00 00 10 00 00 00 00 01 01 00 11 00 00 01 00 01 00 00 00 00 01 00 00 00 00 01 00 00 00 00 01 00 00 00 00 01 01 10 10 10 11 00 10 11 10 00 00 10 01 01 00 10 10 01 01 00 10 10 01 01 00 10 10 01 01 00 10 00 11 10 00 00 00 00 00 00 00 00 00 10 00 00 00 00 10 00 00 00 00 10 00 00 00 00 10 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 01 00 00 00 00 01 00 00 00 00 00 00 00 00 00 00 00 00 00 10 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 0 00 0 00 0 00 0 00 0 00 0 SM S N E W P E P 00 00 00 00 00 00 00 00 00 10 00 00 00 00 00 00 00 00 00 00 01 10 00 00 00 01 10 00 00 00 00 00 00 00 00 00 00 00 00 00 00 10 00 00 00 10 11 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 01 00 00 00 00 01 00 00 00 00 00 00 00 00 00 00 10 10 01 00 00 00 10 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 00 10 00 00 00 00 10 10 11 11 00 00 01 11 11 00 10 01 01 00 00 00 00 01 00 00 00 00 00 00 01 10 00 00 00 01 10 00 00 00 00 00 00 00 00 00 00 00 00 00 00 10 00 00 00 00 10 00 00 0 00 0 00 0 00 0 170 Annals of the Missouri Botanical Garden (1990, 1995), Craw et al. (1999), and Crisci et al. (2000, 2003). In this analysis we use the same areas of ende- mism and the same data matrix (Table 3) that we used in the PAE analysis. The analysis of the data matrix of 21 areas of endemism versus individual tracks of 173 taxa (Table 3) was carried out with SECANT 2.2 (Salisbury, 1999). SECANT identifies all groups of cladistically compatible characters. Individual tracks were treated here as binary char- acters ordered with absence as the ??ancestral?? state for each (5 outgroup with all zeros), and presence as state 1. RESULTS PARSIMONY ANALYSIS OF ENDEMICITY The analysis of the data matrix (Table 3) with PAUP*4.0b10 generated four area cladograms (Fig. 2) with 377 steps, consistency index (CI) 5 0.459, and retention index (RI) 5 0.619, which differed in the relationships among most Mexican areas SMO, TMV, MAS, SMR, SMS; in the relationship of the Neotropical area (NE) either with the Mexi- can areas (Fig. 2B?D) or with the eastern North American areas APP, ATL, NAP, CHI, and TAM (Fig. 2A); in the relationship of APP, ATL, NAP, CHI, and TAM either with the Mexican areas (Fig. 2A?B) or with the western areas VAN, CAL, ROC, GBA, SON, and MOJ (Fig. 2C?D); and in the re- lationship of Tamaulipas (TAM) either with Chi- huahua (CHI) (Fig. 2C?D), or with APP, ATL, NAP, and CHI (Fig. 2A?B). The strict consensus of the four trees (Fig. 3) shows the following area relationships: (1) ((Arctic, Canadian) West Palearctic, East Palearctic) forms the basalmost lineage, sister to the remaining areas; (2) (((Appalachian, Atlantic) North American Prai- ries) Chihuahuan, Tamaulipas); (3) ((((Vancouveri- an, Californian) (Rocky Mountains, Great Basin)) Sonoran) Mojavean); (4) ((Mexican Altiplano, Sierra Madre Oriental) Sierra Madre Occidental, Trans- Mexican Volcanic Belt, Sierra Madre del Sur); and (5) the Neotropical as one single branch. The last four branches (2?5) constitute a polytomy. Thus, the strict consensus cladogram generated by PAUP*4.0b10 shows four main groups (Fig. 4): northern North America, eastern North America, western North America, and the central Mexican areas. The percentage of 100 bootstrap replicates dem- onstrates that strength of support for nodes varies considerably. Many branches have less than 50% support, but others, particularly in eastern and western North America, have stronger support. The most strongly supported branches in order are: 99% (APP?ATL), 98% (VAN?CAL), 96% (VAN, CAL, ROC, GBA), 79% (ROC?GBA), 78% (APP, ATL, NAP, CHI, TAM), 62% (VAN, CAL, ROC, GBA, SON, MOJ), 61% (APP, ATL, NAP), and 60% (ARC, CAN, WP, EP). The weakness and strength of bootstrap values may reflect the strong concen- tration of taxa in northern Mexico and southwestern United States, and lower concentration in areas more distant from that area. PANBIOGEOGRAPHY (COMPATIBILITY TRACK METHOD) Applying the SECANT 2.2 program to the data matrix (Table 3) resulted in 4 largest cliques, each with 51 individual tracks. The intersection (those 49 individual tracks common to the 4 largest cliques) is considered as the fifth large clique. These 5 cliques contain a total of 11 generalized tracks. The first clique contains 2 generalized tracks, the second clique contains 2, the third clique contains 3, the fourth clique contains 2, and the intersection contains 2 generalized tracks. Since many of these tracks in different cliques are the same, the 11 generalized tracks can be reduced to 3 generalized tracks: 2 strongly supported (??East??/green and ??West??/purple in Fig. 5), and 1 weakly supported (??South??/orange in Fig. 5). The northern regions (ARC, CAN, EP, and WP) and two areas in Mexico (SMO and TMV) are not part of these supported generalized tracks, and are shown as white in Figure 5. The first (??East??) strong generalized track in- cludes eastern North American areas (ATL, APP, CHI, NAP, TAM), and is strongly supported by 17 individual tracks from taxa in 3 genera, namely, Calylophus berlandieri (taxon 41); Gaura biennis (67), G. brachycarpa (69), G. filipes (73), G. longi- flora (75), G. sinuata (80), and G. suffulta (81); and Oenothera cordata (96), O. falfurriae (104), O. grandiflora (107), O. grandis (108), O. heterophylla (109), O. linifolia (116), O. mexicana (120), O. nu- tans (122), O. spachiana (134), and O. speciosa (135). The second (??West??) strong generalized track in- cludes the western North American areas (CAL, GBA, MOJ, ROC, SON, VAN), and is supported by 31 individual tracks from taxa in 4 genera, namely, Camissonia boothii (taxon 3), C. campestris (7), C. graciliflora (15), C. lacustris (22), C. ovata (26), and C. pubens (26); all species of Clarkia (47?65) ex- cept for C. epilobioides (52), C. pulchella (58), and C. purpurea (59); Gayophytum decipiens (83) and G. heterozygum (85); and Epilobium clavatum (148), E. Volume 91, Number 1 2004 171Katinas et al. Geographical Diversification Figure 2. Four most parsimonious cladograms (A?D) resulting from the parsimony analysis of endemicity (PAE) analysis after applying PAUP* vers. 4.0b10. Trees are 377 steps, CI 5 0.459, and RI 5 0.619. Area acronyms correspond to those in Figure 1 and Table 2. 172 Annals of the Missouri Botanical Garden Figure 3. Strict consensus cladogram of the four cladograms obtained in the parsimony analysis of endemicity (PAE). Bootstrap support values are shown above the branches. Area acronyms correspond to those in Figure 1 and Table 2. Volume 91, Number 1 2004 173Katinas et al. Geographical Diversification Figure 4. Strict consensus cladogram of the four cladograms obtained in the parsimony analysis of endemicity superimposed onto the map with the areas of endemism. The tree branches delineate four main groups of areas: northern (ARC, CAN, EP, WP), eastern North America (APP, ATL, NAP, CHI, TAM), western North America (VAN, CAL, ROC, GBA, SON, MOJ), and southern North America (SMO, TMV, MAS, SMR, SMS). Areas correspond to those in Figure 1 and Table 2. densiflorum (151), E. glaberrimum (154), E. minu- tum (161), E. oregonense (165), E. pallidum (166), and E. torreyi (173). The third (??South??) generalized track includes some of the Mexican areas (MAS, SMR, SMS) and the Neotropical area (NE), with support from only 2 individual tracks, of Oenothera deserticola (taxon 99) and O. epilobiifolia (103). The South general- ized track is considerably weaker than the previous two, since it is supported by many fewer individual tracks. The Neotropical area is supported as part of the East generalized track by Oenothera lacinia- ta (taxon 114). The Trans-Mexican Volcanic Belt (TMV) is supported as part of the South generalized track by Oenothera kunthiana (taxon 113). Several Mexican areas (SMS, TMV, MAS) are supported as part of the East generalized track by Gaura drum- mondii (taxon 72) and Oenothera jamesii (112). As noted above, the Sierra Madre Occidental (SMO) does not form part of any generalized track. 174 Annals of the Missouri Botanical Garden Figure 5. Distributional patterns after applying track compatibility analysis: a strongly supported Eastern gener- alized track including APP, ATL, CHI, NAP, and TAM, shown in green; a strongly supported Western generalized track, including CAL, GBA, MOJ, ROC, SON, and VAN, shown in purple; and a weakly supported Mexican and Neotropic generalized track including MAS, NE, SMR, and SMS, shown in orange. The areas ARC, CAN, SMO, and TMV, shown in white, and the two non-North American areas EP and WP, do not form part of any generalized track. Area acronyms correspond to those in Figure 1 and Table 2. These data weakly support the Neotropical area (NE) as a panbiogeographic node in the distribu- tional history of Onagreae, Gongylocarpeae, and Epilobieae, since there is some support for its in- clusion in both the East and South generalized tracks. The program SECANT 2.2 also found 9 cliques each with 50 individual tracks. The analysis of these 9 cliques resulted in the same generalized tracks that we found among the five largest cliques, with the exception of one generalized track found in only one of the 9 cliques. This additional track includes the areas CHI and TAM, supported by Gaura boquillensis (taxon 68), Oenothera macros- celes (119), and O. pennellii (126). Most of the genera of Epilobieae and Onagreae support at least one of the generalized tracks found in this analysis, i.e., Calylophus, Gaura, and Oen- othera belong to the East track, and Camissonia, Clarkia, Gayophytum, and Epilobium to the West track. Several other genera, including Chamerion (Epilobieae; two species), Gongylocarpus (Gongy- Volume 91, Number 1 2004 175Katinas et al. Geographical Diversification locarpeae; two species), and Stenosiphon (Ona- greae; one species) do not form part of any gener- alized track. DISCUSSION The historical biogeography of North America has long been a focus of botanists attempting to find general patterns of relationships within North America and between North America and other continents. The present-day geographical distribu- tion of Epilobieae, Gongylocarpeae, and Onagreae and the biogeographic patterns generated by those distributions may provide clues to understanding the high diversity and endemicity of these three tribes in North America, as well as the history of the areas involved. DISTRIBUTIONAL PATTERNS The application of Parsimony Analysis of En- demicity (PAE) to the species distribution of Epi- lobieae, Gongylocarpeae, and Onagreae delimits four major regions: northern North America; east- ern North America; western North America; and central Mexico (Fig. 4). Three of them (eastern North America, western North America, and central Mexico) are also found in the compatibility track analysis. Comparison of these with the higher re- gional floristic categories in the schemes of Takh- tajan (1986) and Thorne (1993) suggests the follow- ing differences and similarities. (1) Our northern North American region coincides with the Circum- boreal region of Takhtajan and Thorne. (2) Our eastern North American region corresponds to the North American Atlantic region of Takhtajan and Thorne, with the addition of the Tamaulipas (TAM) and Chihuahua (CHI) areas. Miranda and Sharp (1950) proposed such an affinity from distributions of many plant species, and they and Berry (1930) suggested that this shared flora was derived from the Eocene Wilcox flora of the Mississippi Embay- ment. (3) The Rocky Mountain and Madrean re- gions of Takhtajan and Thorne show different affin- ities in our analysis. Their regions proposed close affinities between ROC and VAN, and among CAL, GBA, and the Sonoran Province, whereas our re- sults link VAN with CAL and ROC with GBA. Ra- ven and Axelrod (1978) considered the Vancouver- ian (VAN) and Californian (CAL) areas to be closely related since they share a flora comprising a mix- ture of northern temperate elements and xeric, southern elements, with a very high degree of en- demism. Furthermore, Axelrod and Raven (1985) also considered the Rocky Mountains (ROC) and Great Basin (GBA) areas to be close because Cor- dilleran taxa spread into the western Great Basin largely after 14 m.y. ago as the climate became drier, summer rains decreased, and eastern exotic taxa were eliminated. (4) Our central Mexican areas coincide with the Mexican Highlands Province of Takhtajan and Thorne. The lower level of resolution among the central Mexican areas observed in the consensus PAE cladogram is most likely due to the relatively few species of Epilobieae, Gongylocar- peae, and Onagreae distributed there. The relationships of the Madrean and other North American regions to the Neotropical (NE) are particularly complex, which is reflected in the am- biguous position of NE in the four shortest trees (Fig. 2). Indeed, NE could be considered a panbi- ogeographic node in our study. Three species (Gau- ra angustifolia [taxon 66], Oenothera humifusa [111], and O. laciniata [114]) otherwise restricted to the East region reach NE only at the southern tip of Florida, and another eastern species, Epilob- ium coloratum (149), occurs on Hispaniola (in NE), apparently by long-distance dispersal. These taxa provide support for NE as sister to the East region (Fig. 2A). A single species, Gayophytum humile (86), found primarily in the western region (VAN- CAL-ROC-GBA), also occurs in NE, apparently as a result of long-distance dispersal to central Chile and Argentina (Lewis & Szweykowski, 1964). Most of the connections of North American regions with NE, however, are through the Mexican region (Fig. 2B?D), almost always by close adjacent dispersal in western and southern Mexico, extending south to Central and sometimes South America. Recent phylogenetic analysis of Onagraceae (Levin et al., 2003, 2004) suggests the following: (1) the imme- diate sister clade to the Gongylocarpeae 1 Epilo- bieae 1 Onagreae is a branch with Lopezia (Lo- pezieae) and Megacorax (unplaced), both found primarily or exclusively in the central Mexican re- gion, with some Lopezia species extending to NE; and (2) each of the three successive basal clades of the family, namely Fuchsia 1 Circaea, Hauya, and Ludwigia, have primary or exclusive distribu- tions in NE. Circaea, with its circumboreal distri- bution and absence from NE, is a notable excep- tion; however, it forms a strongly supported clade with Fuchsia. A detailed analysis of biogeographi- cal patterns in Onagraceae using phylogenetic in- formation is now in progress. The distributions of numerous species do not co- incide with the major patterns found in the PAE and track compatibility analysis. In general, these inconsistencies can result from one of three types of processes, namely, dispersal, vicariance, or ex- tinction affecting one or few species. The predom- 176 Annals of the Missouri Botanical Garden inant process in our study appears to be short-dis- tance dispersal into geographically contiguous but unrelated areas. This may involve large-scale dis- persal, but more often involves only a few or even one population(s) in the adjacent area. For exam- ple, many species with distributions in the East North American region often extend into the CAN area [North region; e.g., Oenothera biennis (91), O. fruticosa (106), O. parviflora (125)], or into ROC [West region; e.g., Calylophus serrulatus (44), Oen- othera nuttallii (121)], or to the south into the Mex- ican region [e.g., Gaura drummondii (72), Oenoth- era jamesii (112)]. Similarly, some western species reach CAN [Camissonia breviflora (4)] or even ARC [along the southwest coast of Alaska; Epilobium lep- tocarpum (158), E. luteum (160)] in the northern region, or CHI [Camissonia chamaenerioides (9), Epilobium canum (146)] or NAP [Camissonia an- dina (1), C. subacaulis (38), Gayophytum ramosis- simum (88)] in the East region. One particularly clear example of adjacent dispersal concerns Oen- othera primiveris (129); in the West region of primary distribution (GBA, SON, MOJ), most pop- ulations are large-flowered and outcrossing (includ- ing some that are self-incompatible), whereas the populations in CHI (East region) are small-flowered and autogamous (Wagner, unpublished data). Some distributions that seem to represent adja- cent dispersal may in fact have another explana- tion. For example, Oenothera villosa (taxon 139) oc- curs widely in both the western and eastern regions, suggesting adjacent dispersal. However, genome and cytological analysis (Dietrich et al., 1997) of this permanent translocation heterozygote species shows that populations in the western and eastern regions, which currently are treated as subspecies, derived independently from different populations of Oenothera elata (102). Nevertheless, they inter- grade so extensively in the transition area between ROC and NAP that they are best treated as sub- species of a single species. Several taxa may represent examples of long-dis- tance dispersal. For example, Epilobium saximon- tanum (169), found primarily in the western region (ROC, GBA, VAN) with near outliers in the eastern region (NAP, CHI), also occurs in eastern CAN (Newfoundland) and ARC (Ungava Bay, Quebec) in the northern region. This highly disjunct pattern is not found in other species and seems best ex- plained as a case of long-distance dispersal. The distribution of Calylophus lavandulifolius (43) is unusual in several ways: it appears ??bimodal,?? with concentrations of populations in NAP (eastern) and GBA (western) and relatively few populations in in- tervening areas. In addition, the apparently normal distribution in NAP 1 CHI 1 TAM in the eastern region masks a long-distance disjunction between populations in northern CHI and southern TAM. Certain recurring inconsistent distribution pat- terns may represent vicariance events. One pattern [found in Clarkia pulchella (58) and three Epilob- ium?E. hornemannii (156), E. lactiflorum (157), and E. saximontanum (169)] concerns the occur- rence of outlier populations of western taxa (in ROC and VAN) in the Black Hills of South Dakota in NAP (East region). The Black Hills, home to nu- merous disjunct montane and northern taxa (e.g., Asteraceae: Balsamorhiza sagittata; Pinaceae: Pi- nus contorta, P. flexilis; Ranunculaceae: Aconitum columbianum; Van Bruggen, 1976; Great Plains Flora Association, 1986), have become isolated as the climate warmed in postglacial times; the pattern seems best explained as an example of vicariance. Similarly, at least six taxa (Camissonia confusa [12], three Clarkia?C. epilobioides [52], C. purpurea [59], and C. rhomboidea [60], and two Epilobium? E. foliosum [153] and E. glaberrimum [154]) show strongly disjunct distributions from southern Cali- fornia (CAL and/or VAN) to south-central Arizona (SON), mirroring a ??trans-Sonoran Desert?? vicari- ance event described by Axelrod (1979). Finally, the absence of taxa from certain areas in which they may otherwise be anticipated may rep- resent cases of local extinction. These are, however, difficult to prove, and in some cases clearly do not represent extinctions. For example, some species [4 of Camissonia?C. brevipes (5), C. claviformis (11), C. pallida (27), and C. refracta (34) and 2 of Oen- othera?O. californica (94) and O. deltoides (98)] otherwise widespread in the western region are missing in ROC. Yet their absence in ROC cannot be considered extinctions, since all of these are de- sert taxa with southwestern distributions quite dis- tant from the ROC boundaries. On the other hand, many taxa with the CAL 1 VAN (17 taxa) or CAL 1 VAN 1 SON (3 taxa) distribution patterns may have become extinct in the adjacent MOJ area, which has become progressively more extreme in Holocene time, and progressively inhospitable to many species (Axelrod, 1979). The absence of many taxa in the MOJ region may have forced MOJ into the position as the sister group to the rest of the western region, when it may in fact be a more recently derived area (Van Devender & Spaulding, 1979). The establishment of western and eastern North American major regions found by PAE and track compatibility analysis agrees with many previous analyses (e.g., Li, 1952; Croizat, 1965; Graham, 1972; Iltis, 1983; Xiang et al., 1998, 2000; Wen, Volume 91, Number 1 2004 177Katinas et al. Geographical Diversification 1999; Guo & Ricklefs, 2000; Donoghue et al., 2001; Sanmart??n et al., 2001). These analyses have defined the two broad biogeographic units based on the distributions of many taxa, some of which were evaluated in a phylogenetic context. In many of those analyses, however, there exists a relationship of these areas with East Asia. Disjunct North Amer- ican?Asian taxa have been considered as Tertiary relics with former widespread distributions during the Paleogene. This ??Arcto-Tertiary geoflora?? (Wolfe, 1978; Larsen, 1980) resulted from migra- tions between eastern Asia and North America through Beringia or across the north Atlantic. The distributional patterns of Epilobieae, Gongylocar- peae, and Onagreae show a close relationship be- tween eastern and western North America, with both areas more related to the Neotropics than to the Palearctic, and a weak association between northern North America and Asia. Our results do not reject other hypotheses of such continental con- nections. The taxa of Onagraceae chosen for our analysis?the tribes Epilobieae, Gongylocarpeae, and Onagreae?display a biogeographical history that may differ from those of other taxa, but that can coexist at the same time. Our analysis does not disprove the migration of taxa (including Epilo- bieae, Gongylocarpeae, and Onagreae) through the Bering and Atlantic northern land bridges, or through the Panama isthmus. The East and West tracks show that two ancestral biotas existed on both sides of North America, with the species of each track sharing a common distributional history. CORRELATION OF BIOGEOGRAPHIC PATTERN WITH GEOLOGIC AND PALEOCLIMATIC EVIDENCE The geological and climatic processes in the past provide at least partial explanations for the current biogeographical patterns in North America of Epi- lobieae, Gongylocarpeae, and Onagreae. Major his- torical events in this area include orogenic pro- cesses such as the uplifting of the Rocky Mountains, the Sierra Madre, and western Cordil- lera, and the most recent glaciations (summary in Graham, 1999). The uplifting of the Rocky Mountains together with the uplifting of the Sierra Madre Occidental in the early Tertiary remarkably changed the biota of western North America, creating a barrier for floristic exchanges between eastern and western North America. This had two main effects on the flora of western North America: significant extinc- tion of taxa because of the increasingly dry climate, and accelerated speciation and diversification of new taxa (Qian, 2001). Indeed, the area of the southern Rocky Mountains and the Sierra Madre Occidental was an important center for the evolu- tion of the Madro-Tertiary geoflora (Axelrod, 1958). The early diversification of Onagraceae tribe Ona- greae was postulated to have taken place in the Madrean vegetation of western North America (Ra- ven & Axelrod, 1978). Until recently, tribe Gon- gylocarpeae, also endemic to the Madrean region, was considered to be the basal branch of Onagreae (Carlquist & Raven, 1966). Tribe Epilobieae also may have originated in western North America as part of the Madro-Tertiary geoflora (Raven, 1976; Baum et al., 1994), but evidence from fossil pollen is equivocal, and the distribution of Chamerion and its position as sister to Epilobium (Baum et al., 1994) suggest a possible origin in western Eurasia (Raven & Raven, 1976). The strong association of Epilobium to the western track, and the endemism of the near-basal species E. rigidum (Baum et al., 1994; Levin et al., 2004) in the VAN region, sup- port an origin of the genus in western North Amer- ica. The Madro-Tertiary geoflora had already ap- peared on the drier borders of the North American tropics by the Middle Eocene, and probably occu- pied much of the southwestern United States and adjacent Mexico by the close of the Oligocene. It extended its range in all directions in response to the expanding aridity in the succeeding Miocene epoch (Axelrod, 1958; Valliente-Banuet et al., 1998). Major expansion of Onagraceae tribes On- agreae, Gongylocarpeae, and Epilobieae may have occurred during the Miocene and Pliocene (Raven & Axelrod, 1974; Raven & Raven, 1976; Raven, 1979). From the late Oligocene (25 mya) through the Pliocene, new orogeny gave rise to the present western Cordilleran System, including major defor- mation and uplift of the Rocky Mountains, Sierra Nevada, Sierra Madre Occidental, and Sierra Ma- dre Oriental (Axelrod & Raven, 1985; Wing, 1987; Graham, 1993). This resulted in cooler and drier climates that precipitated the development of grass- lands in central North America (Sanmart??n et al., 2001), being thus a third event differentiating the western and the eastern floras. However, Wen (1999) noted that the close biogeographic relation- ship between western and eastern North America suggests that the Cordilleran range was not an ef- fective barrier to exchange between these two flo- ristic regions. In the Quaternary period, the flora of North America experienced late Pleistocene full-glacial conditions (20,000?15,000 yr. b.p.), late-glacial cli- matic amelioration (15,000?10,000 yr. b.p.), and Holocene interglacial conditions of the last 10,000 178 Annals of the Missouri Botanical Garden years (Graham, 1999). The Quaternary can be char- acterized more by changes in the distributions of plant taxa than by the evolution of new genera and species (Delcourt & Delcourt, 1993). 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The eastern Asian and eastern and western North America floristic disjunction: Congruent phylogenetic patterns in seven diverse genera. Molec. Phylogenet. Evol. 10: 178?190. , , , S. R. Manchester & D. J. Craw- ford. 2000. Timing the Eastern Asian?Eastern North American floristic disjunction: Molecular clock corrob- orates paleontological estimates. Molec. Phylogenet. Evol. 15: 462?472. APPENDIX 1. North American areas of endemism used in this analysis; see text for sources and explanation. References for plant endemics generally follow Takhtajan (1986); these are sup- plemented in some areas by Barbour & Christensen (1993), in Canada by Aiken et al. (1999: ^www.mun.ca/biology/ delta/arcticf/&); in California by Hickman (1993), and in Mexico by Rzedowski (1978) and Ramamoorthy et al. (1993). Names were checked against the on-line Flora of North America database (^http://hua.huh.harvard.edu/ FNA&). Endemic animals are arranged in the following or- der: fish, amphibians, reptiles, birds, mammals, inverte- brates; within groups, alphabetical by family. References for animal endemics are as follows: 1Ricketts et al. (1999); 2Mammals of the World (Wilson & Reeder, 1993: ^www.nmnh.si.edu/msw/&); 3Avibase (Lepage, 2003: ^www. bsc-eoc.org/avibase&); 4Amphibian Species of the World (Frost, 2002: ^research.amnh.org/herpetology/amphibia/&); 5Walker?s Mammals of the World (Nowak, 1997: ^www. press.jhu.edu/books/walkerspmammalspofpthepworld/&); 6Fishbase (Froese & Pauly, 2003: ^www.fishbase.org&); 7Rep- tile database (Uetz et al., 2003: ^www.reptile-database. org&); 8entomology (California Academy of Sciences, 2003: ^www.calacademy.org/research/entomology&). 1. Arctic (ARC): includes most of coastal Alaska, north- ern coastal Canada, all of the ice-free Canadian Ar- chipelago, and Greenland. The flora is depauperate in a nearly tree-less region of tundra and polar desert, with fewer than 1000 species of vascular plants. En- demism at the species level is moderate (Aiken et al., 1999), e.g.: Asteraceae: Taraxacum hyparcticum; Brassicaceae: Braya thorild-wulffii, Parrya arctica; Caryophyllaceae: Cerastium regelii, Silene sorensenis; Orobanchaceae: Castilleja arctica; Polemoniaceae: Phlox richardsonii. Endemic fauna include Mammals [Cervidae] Rangifer tarandus pearyi (Peary caribou)1,5; [Leporidae] Lepus arcticus (arctic hare)1,2; [Soricidae] Sorex pribilofensis (Pribiloff Island shrew)1,5. 2. Canadian (CAN): forms a broad band across Canada and Alaska, south of ARC and north of Rocky Moun- tain (ROC) and Appalachian (APP) regions, including extreme northern New England, Michigan, and Min- nesota. Consists primarily of taiga and coniferous bo- real forests, with dominant tree species in Abies, Bet- ula, Larix, Picea, Pinus, and Populus. Some endemic plants include Asteraceae: Aster yukonensis; Boragi- naceae: Cryptantha shakletteana; Brassicaceae: Erys- imum aspermum; Caryophyllaceae: Silene williamsii; Fabaceae: Astragalus ecosmus; Orobanchaceae: Cas- tilleja annua; Polygonaceae: Eriogonum flavum; Por- tulacaceae: Claytonia bostockii; Primulaceae: Doug- lasia gormanii. Endemic fauna include Mammals: [Soricidae] Sorex gaspensis (Gaspe shrew)2,5; Insects: [Lepidoptera] Coenonympha nepisiquit (maritime ring- let butterfly)1. 3. Appalachian (APP): includes a small part of southern Ontario and Quebec, Canada, and most of the eastern United States, excluding the Atlantic and Gulf Coast- al region (ATL) to the south. Extends from central Maine, southern Canada, and Minnesota to central Georgia, central Alabama, the Ozark Plateau and the Quachita Mts. in Missouri and Arkansas, and eastern Texas. In Texas, corresponds to the ??Post Oak Savan- nah?? and ??Blackland Prairies?? areas of Correll and Johnston (1970). Dominant climax vegetation is the eastern deciduous forest, with dominant tree species in Acer, Aesculus, Betula, Fagus, Magnolia, Quercus, and Tilia. Many endemic plant species, including Magnoliaceae: Magnolia fraseri; Menispermaceae: Menispermum canadense; Pinaceae: Abies fraseri; Ranunculaceae: Aconitum reclinatum, Anemone acu- tiloba; Rosaceae: Prunus alleghanensis; Ulmaceae: Ulmus serotina. Endemic fauna include Amphibians: [Plethodontidae] Desmognathus welten (Black Moun- tain salamander)1,4; Reptiles: [Emydidae] Clemmys muhlenbergii (bog turtle)1; Birds: [Emberizidae] Den- droica kirtlandii (Kirkland?s warbler)1,3; Annelids: [Acanthodrilidae] Diplocardia meansi (earthworm)1. 4. Atlantic and Gulf Coastal (ATL): occupies the geolog- ic coastal plain of the Atlantic and Gulf Coast states of the United States, from Massachusetts and New Jersey to Florida and west to south-central Texas. In Texas, corresponds to the ??Pineywoods?? and ??Gulf Prairies and Marshes?? areas of Correll and Johnston (1970). Also extends across the lower Mississippi River valley to southern Missouri and Illinois. Much of the coastal plain is characterized by extensive for- ests of Pinus, replaced in some areas by Carya, Fa- gus, and/or Quercus, and in wetter areas by Taxodium distichum and species of Nyssa and Fraxinus. Endem- ic taxa include Onagraceae (tribe Jussiaeeae): Lud- wigia lanceolata, L. pilosa, L. ravenii, and L. suffru- ticosa, and several hundred species including Annonaceae: Asimina incana; Iridaceae: Iris hexago- na; Lauraceae: Persea palustris; Pinaceae: Pinus el- liottii; Salicaceae: Salix floridana; Simaroubaceae: Leitneria floridana; Taxaceae: Taxus floridana, Torre- ya taxifolia. Endemic fauna include Reptiles [Testu- dinidae] Gopherus polyphemus (gopher tortoise)1; Birds: [Corvidae] Aphelocoma coerulescens coerules- cens (Florida scrub jay)1,3; [Picidae] Picoides borealis 182 Annals of the Missouri Botanical Garden (red-cockaded woodpecker)1,3; Mammals: [Ursidae] Ursus americanus floridanus (Florida black bear)5. 5. North American Prairies (NAP): includes prairies and plains between the eastern deciduous forest of APP on the east, the coniferous forests of ROC on the west and CAN on the north, and the arid semi-deserts of CHI and TAM to the southwest. Corresponds for the most part with the ??Great Plains?? (Great Plains Flora Assoc., 1986), but in Texas also includes the ??Ed- wards Plateau,?? ??Rolling Plains,?? and ??High Plains?? areas of Correll and Johnston (1970). Grasses are dominant in this region, with a rich mix of perennial forbs, and forest trees in some areas near rivers. No endemic families, few endemic genera, and some en- demic species, including the bryophyte Pottiaceae: Aschisma kansanum; and Agavaceae: Yucca rupicola; Brassicaceae: Lesquerella angustifolia; Fabaceae: As- tragalus gracilis, Psoralea cuspidata; Polygonaceae: Eriogonum correllii; Valerianaceae: Valeriana texana. Endemic fauna include Amphibians: [Plethodontidae] Typhlomolge (Eurycea) rathbuni (Texas blind sala- mander)1,4 and T. robusta (Blanco blind salamander)1,4; Birds: [Phasianidae] Tympanuchus cupido (greater prairie chicken)1,3; Mammals: [Canidae] Vulpes velox (swift fox)1,2. 6. Vancouverian (VAN): extends as a coastal strip from Kodiak Island in Alaska to coastal British Columbia, widening in Washington and Oregon to include the Cascade, Olympic, and Coast Ranges, extending into California through the Klamath and Northern Coast ranges in the west and through the southern Cascades into the Sierra Nevada to its terminus in southern California. In California, VAN corresponds to the NW, CW, CaR, and SN regions of The Jepson Manual (Hickman, 1993). Conifers dominate the climax veg- etation, along with some broad-leaved species of Acer, Alnus, Cornus, Fraxinus, Populus, and Quercus. There are endemic genera and some 500 to 600 endemic species, including Apiaceae: Lomatium bradshawii; Asteraceae: Aster paludicola, Erigeron cervinus, Se- necio clarkianus; Iridaceae: Iris bracteata; Sarraceni- aceae: Darlingtonia californica; Taxodiaceae: Sequoia sempervirens, Sequoiadendron giganteum. Endemic fauna include Fishes: [Catostomidae] Catostomus rim- iculus (Jenny Creek sucker)1,6; [Cyprinidae] Gila bi- color bicolor (Tui chub)1,6; Amphibians: [Dicampto- dontidae] Dicamptodon ensatus (Pacific giant salamander)1,4; Birds: [Strigidae] Strix occidentalis caurina (northern spotted owl)1,3; Insects: [Lepidop- tera] Colias behrii (Sierra sulfur butterfly)1. 7. Rocky Mountain (ROC): includes the Rocky Moun- tains and associated inland ranges from northern Brit- ish Columbia and southwestern Yukon to central Oregon, south-central Idaho, extreme northeastern Utah, and north-central New Mexico, bounded on the west by VAN and GBA and on the east by CAN and NAP. In the extreme south, ROC borders the deserts of CHI. Also includes some associated outlier ranges, especially extending to the east and south of the main cordillera. Vegetation is zoned vertically, with Pinus ponderosa dominant in the lowest zones, and species of Abies, Juniperus, Picea, Pinus, Populus, and Pseu- dotsuga dominant at higher zones. Some endemic plant species include Apiaceae: Angelica ampla, Lomatium tuberosum; Brassicaceae: Draba grayana; Fabaceae: Astragalus arrectus; Orobanchaceae: Cas- tilleja christii; Plantaginaceae: Penstemon elegantulus; Polemoniaceae: Phlox colubrina. Endemic fauna in- clude Fishes: [Cyprinidae] Gila cypha (humpback chub)1,6; [Salmonidae] Oncorhynchus clarki lewisi (westslope cutthroat trout)1,6; Mammals: [Mustelidae] Mustela negripes (black-footed ferret)1,2,5; [Sciuridae] Cynomys leucurus (white-tailed prairie dog)1,2. 8. Great Basin (GBA): bounded on the west by the Cas- cade-Sierra Nevada axis (VAN), on the east by ROC, and on the south by the desert regions of MOJ, SON, and CHI. In California, the boundaries correspond to those of the MP and SNE (including the White and Inyo Mountains) regions of The Jepson Manual (Hick- man, 1993). Includes the Snake River Plains of southern Idaho and most of the Colorado Plateau, and consists of many north-south trending mountain rang- es separated by broad, alkaline basins without exter- nal drainage, with much of the area above 1300 m. Characterized by diversity of species of Artemisia, Chenopodiaceae, and at higher elevations by some combination of species of Acer, Populus, Quercus, Juniperus, and Pinus. The region has numerous en- demic species, including Asteraceae: Chaetadelpha wheeleri, Erigeron mancus; Loasaceae: Mentzelia packardiae; Papaveraceae: Canbya aurea; Plantagi- naceae: Penstemon compactus; Primulaceae: Primula maguirei. Endemic fauna include Fishes: [Cyprini- dae] Ptychocheilus lucius (Colorado pikeminnow)1,6; Mammals [Heteromyidae] Microdipodops pallidus (pale kangaroo mouse)1,2. 9. Californian (CAL): occupies a large part of the state of California, including the Central Valley, the Coast Ranges from the San Francisco region south into northwestern Baja California Norte, Mexico, and the Transverse Ranges of southern California. Bounded on the northwest, north, and east by VAN, and on the southeast by MOJ and SON (Raven & Axelrod, 1978). Corresponds to the GV, CW, and SW regions of The Jepson Manual (Hickman, 1993). The vegetation varies altitudinally, from treeless grassland in lower areas to chapparal and mixed forests of Aesculus, Pla- tanus, Populus, Quercus, Salix, and conifers at higher levels. Numerous endemic plant genera and species include Asteraceae: Erigeron sanctarum; Fagaceae: Quercus douglasii; Ophioglossaceae: Ophioglossum californicum; Papaveraceae: the genus Romneya; Po- lygonaceae: the genus Hollisteria. Endemic fauna in- clude Fishes: [Cyprinidae] Gilia bicolor mojavensis (Mohave Tui chub)1,6; Reptiles: [Colubridae] Masti- cophis flagellum ruddocki (San Joaquin whipsnake)1,7; Mammals: [Canidae] Urocyon littoralis (Island gray fox)1,2; [Heteromyidae] Dipodomys ingens (giant kan- garoo rat)1,2, D. venustus (narrow-faced kangaroo rat)1,2; Perognathus inornatus (San Joaquin pocket mouse)1,2; Insects [Lepidoptera, Pieridae] Euphydryas editha quino (Quino checkerspot butterfly)1. 10. Mojavean (MOJ): small but complex region borders VAN and CAL on west, GBA on north, and SON on south and east. Includes Death Valley, adjacent desert ranges, and large desert region of southeastern Cali- fornia, to base of Transverse ranges, corresponding to DMoj region of The Jepson Manual (Hickman, 1993). Extends to east through southern Nevada and north- western Arizona to extreme southwestern Utah (MacMahon, 2000). Predominately shrubby desert dominated by endemic Joshua-tree Yucca brevifolia (Agavaceae), with saltbush (Atriplex) scrub character- istic of alkaline basins. Other characteristic species Volume 91, Number 1 2004 183Katinas et al. Geographical Diversification include Agavaceae: Yucca schidigera; Asteraceae: Ambrosia dumosa; Cactaceae: Echinocactus polyce- phalus, Ferocactus achantoides; and Zygophyllaceae: Larrea divaricata subsp. tridentata. Some endemic plants include Agavaceae: Yucca brevifolia; Astera- ceae: Amphipappus fremontii; Caryophyllaceae: Sco- pulophila rixfordii; Cactaceae: Opuntia chlorotica; Plantaginaceae: Penstemon calcareus; Polygonaceae: Gilmania luteola. Endemic fauna include Reptiles: [Phrynosomatidae] Uma scoparia (Mojave fringe-toed lizard)1,7; Mammals: [Muridae] Microtus californicus scirpensis (Amargosa vole)1; [Sciuridae] Spermophilus mohavensis (Mojave ground squirrel)1,2; Insects: [Or- thoptera, Stenopelmatidae] Ammopelmatus kelsoensis (Kelso Dunes jerusalem cricket)1,8. 11. Sonoran (SON): ranges from the southern border of the MOJ in southeastern California, south throughout Baja California, Mexico, east through most of south- western Arizona, and southeast through Sonora, Mex- ico. Very characteristic plants of the region include columnar cacti such as Carnegiea gigantea (saguaro) and Pachycereus pringlei (Cactaceae), trees such as Yucca valida (Agavaceae), Cercidium floridum, and C. microphyllum (Cercidiphyllaceae), and shrubs such as Acacia greggii (Fabaceae), Krameria grayi (Krameri- aceae), and Larrea divaricata subsp. tridentata (Zyg- ophyllaceae). Endemic plant taxa include Onagraceae (tribe Lopezieae): Lopezia clavata, and species in var- ious other families, including Agavaceae: Agave au- rea; Cactaceae: Opuntia rosarica; Fabaceae: Acacia brandegeana, A. goldmanii, Errazurizia benthami; Fouquieriaceae: Fouquieria columnaris; Lamiaceae: Hyptis laniflora; Sapindaceae: Aesculus parryi; Sapo- taceae: Sideroxylon peninsulare. Endemic fauna in- clude Birds: [Emberizidae] Aimophila carpalis (ru- fous-winged sparrow)1,3; [Hydrobatidae] Oceanodroma macarodactyla (Guadalupe storm petrol, possibly ex- tinct)1,3; Insects: [Coleoptera, Carabidae] Calathus peropacus (ground beetle; Liebherr, 1991b), Pelma- tellus parallelus (ground beetle)1,8; [Hymenoptera, An- thophoridae] Agapanthinus (digger bees; Ayala et al., 1993). 12. Chihuahuan (CHI): borders SON and SMO on west, GBA and ROC on north, NAP and TAM on east, and MAS on south. Extends from eastern Arizona and central New Mexico through trans-Pecos Texas and south into Mexico, including most of Chihuahua and Coahuila, eastern Durango, and northern Zacatecas. Cooler desert than the Sonoran Desert, dominated by shrubby Larrea divaricata subsp. tridentata and spe- cies of Acacia, Agave, Dalea, Ephedra, Flourensia, Fouqueria, and Jatropha, among others. Trees, mainly species of Yucca and Opuntia, are found only along larger streambeds. Endemic plant species include As- teraceae: Ambrosia johnstoniorum, Flaveria anomala, Gaillardia gypsophila; Chenopodiaceae: Meiomeria stellata; Fabaceae: Dalea filiciformis; Hydrophylla- ceae: Phacelia gypsogenia. Endemic fauna include Fishes: [Cyprinidae] Campostoma ornatum (Mexican stoneroller)1,6, Notropis chihuahua (Chihuahua shin- er)1,6; Reptiles: [Teiidae] Cnemidophorus tigris vari- olosus)1,7; Insects [Coleoptera, Carabidae] Agonum ex- timum (ground beetle; Liebherr, 1991a). 13. Tamaulipan (TAM): ranges from southeastern Texas to western Coahuila and most of Nuevo Leo?n and Ta- maulipas in Mexico, excluding southern parts of these states. Bounded on west by CHI and SMR and on north in southern Texas by complex interface with NAP, APP, and ATL. In Texas, corresponds to ??South Texas Plains?? area of Correll and Johnston (1970). Characterized mostly by thornscrubs or mesquite- grasslands, moister than CHI desert to the west. Veg- etation is largely open shrub- and grasslands with Acacia, Aloysia, Celtis, Condalia, Prosopis, Ziziphus, and other spiny species. Endemic plant species in- clude Boraginaceae: Heliotropium torreyi; Ebenaceae: Diospyros palmeri; Euphorbiaceae: Croton torreyanus; Fabaceae: Acacia rigidula, Mimosa malacophylla; Lauraceae: Phoebe tampicensis; Lentibulariaceae: Pinguicula gracilis; Plantaginaceae: Leucophyllum frutescens; Polygalaceae: Polygala glandulosa; Rham- naceae: Condalia hookeri; Rutaceae: Amyris cordata. Endemic fauna include Fishes: [Cichlidae] Cichlaso- ma cyanoguttatum (Rio Grande cichlid)1,6; Mammals: [Sciuridae] Cynomys mexicanus (Mexican prairie dog; Fa & Morales, 1993)2; [Talpidae] Scalopus montanus (Coahuila mole)1; Insects: [Coleoptera, Carabidae] Platynus bacatellus (ground beetle; Liebherr, 1992). 14. Sierra Madre Occidental (SMO): borders SON and a coastal strip of the Central American Neotropical area (NE) on west, and CHI, the Altiplano of central Mex- ico (MAS), and the Trans-Mexico Volcanic (TMV) re- gions on the east and south. Starts near U.S.?Mexico border and extends southeast through western Chi- huahua, Durango, a small part of Zacatecas, eastern Sinaloa and Nayarit, to central Jalisco. The main cor- dillera consists of an extensive volcanic terrain from 200 to 2200 m, with a pronounced eastern tilt. The region is characterized by a variety of habitats in- cluding both dry and subtropical forests at lower el- evations, dry mixed forests at mid-elevations, and pine/oak forests above 2000 m. Endemic plants in- clude Onagraceae (tribe Lopezieae): Lopezia ciliatula, L. conjugens, L. gentry, L. laciniata, L. lopezioides, L. ovata, L. semeiandra, L. sinaloensis, and L. suffrutes- cens, and species in various other families, including Asteraceae: Alvordia congesta, Hofmeisteria sinaloen- sis, Perityle grandifolia; Cactaceae: Ferocactus schwarzii, Mamillaria rubidea, Stenocereus martinezii; Crassulaceae: Echeveria kimnachii, Sedum copalense; Ericaceae: Arbutus madrensis; Euphorbiaceae: Ditaxis sinaloae; Polygonaceae: Ruprechtia occidentalis. En- demic fauna include Birds: [Picidae] Campephilus im- perialis (imperial woodpecker)1,3; Insects: [Coleoptera, Carabidae] Elliptoleus olisthopoides (ground beetle; Liebherr, 1991a); [Neuroptera, Myrmeleontidae] Mar- acandula apicalis (antlion)8. 15. Trans-Mexican Volcanic Belt (TMV): extends in nar- row, slightly northwest to southeast band in central Mexico, from central Jalisco and Guerrero through southern Estado Mexico barely to Puebla. Borders SMO and the coastal NE strip on west and south, MAS on north, and a transitional montane area be- tween SMR and SMS on east. Major volcanic peaks (3900?4000 m) covered by Pinus hartwegii and coarse bunchgrasses Festuca tolucensis, Calamagros- tis tolucensis, and Muhlenbergia quadridentata. Other characteristic taxa included species of Achillea, Al- chemilla, Arenaria, Cerastium, Geranium, Ranuncu- lus, and Trifolium. Among the very large number of endemic plant species are Onagraceae (tribe Lope- zieae): Lopezia longiflora; at least seven endemic al- pine species of Asteraceae: Cirsium nivale, Gnaphal- ium sarmentosum, G. vulcanicum, Senecio calcarius, 184 Annals of the Missouri Botanical Garden S. gerberaefolius, S. procumbens, and S. roseus; and many other taxa, including Garryaceae: Garrya lon- gifolia; Meliaceae: Cedrela saxatilis; Orchidaceae: Pleurothallis nigriflora; Oxalidaceae: Oxalis stoloni- fera, O. cuernavacana. Endemic fauna include Am- phibians: [Ambystomidae] Ambystoma (Rhyacosire- don) rivularis (Michoaca?n stream salamander)4; Mammals: [Muridae] Neotomodon altstoni (Mexican volcano mouse)2, Reithrodontomys chrysopsis (volcano harvest mouse)2; Insects: [Coleoptera, Carabidae] Cal- athus azteca, Elliptoleus corvus, E. luteipes (ground beetles; Liebherr, 1991b), Platynus machetellus (ground beetle; Liebherr, 1992); [Hymenoptera, An- thophoridae] Loxoptilus (digger bees; Ayala et al., 1993). 16. Mexican Altiplano (MAS): in central Mexico lies be- tween CHI on north, the mountains of SMO on the west and SMR on the east, and TMV on the south. Includes central and southern Zacatecas, southeast- ern Durango, eastern Jalisco and Michoaca?n, northern Estado Me?xico, western San Luis Potos?? and Hidalgo, the Federal District, Aguascalientes, Guanajuato, and Quere?taro. This region is characterized by mixed, less xeromorphic tree communities of Acacia, Ipomoea, and Opuntia. Endemic plant species include Agava- ceae: Yucca queretaroensis; Asteraceae: Acourtia eli- zabethiae; Berberidaceae: Berberis albicans; Cacta- ceae: Lophophora diffusa, Mammillaria camptotricha; Fabaceae: Acacia sororia; Lentibulariaceae: Pinguic- ula agnata. Endemic fauna include Insects: [Cole- optera, Carabidae] Agonum suturale (ground beetles; Liebherr, 1991a); [Hymenoptera, Halictidae] Para- gapostemon (halictic bees; Ayala et al., 1993). 17. Sierra Madre Oriental (SMR): borders CHI and MAS on west and TAM on east, including parts of southern Coahuila and Nuevo Leo?n, eastern Zacatecas, San Luis Potos?? and Hidalgo, most of Tlaxcala, western Puebla, and a small part of western Veracruz and southwestern Tamaulipas. A geologically complex montane area with high levels of endemism in the relatively moist eastern part; lower elevations in the southeast support tropical evergreen forest. At middle to higher elevations (1000?2000 m), strips of warm- temperate to subtropical mesophytic forest occur, with deciduous/semi-evergreen species. Pine and/or oak forest occur at highest elevations. The mixed forest contains genera characteristic of the Appalachian re- gion, such as Carpinus, Cornus, Fagus, Hamamelis, Liquidambar, Pinus, Platanus, and Quercus, as well as more typically tropical elements, like Eugenia, Me- liosma, Rapanea, and Turpinia. Among the very large number of endemic plants are Onagraceae (tribe Lo- pezieae): Lopezia nuevoleonis; and many other taxa, including Caprifoliaceae: Viburnum cuneifolium; Ce- lastraceae: Wimmeria concolor; Clethraceae: Clethra pringlei; Crossosomataceae: Velascoa; Fagaceae: Fa- gus mexicana, Quercus germana, Q. rysophylla; Jug- landaceae: Juglans mollis; Oleaceae: Forestiera race- mosa; Sabiaceae: Meliosma alba. Endemic fauna include Reptiles: [Anguidae] Abronia graminea (ter- restrial arboreal alligator lizard)7, A. taeniata (bro- meliad arboreal alligator lizard)7; Insects [Coleoptera, Carabidae] Calathus rotgeri, C. potosi (ground beetles; Liebherr, 1991b), Platynus robustulus (ground beetle; Liebherr, 1992); [Lepidoptera, Papilionidae; Llorente- Bousquets & Luis-Mart??nez, 1993] Parides alexiares (Oaxacan swallowtail), Priamides erostratinus (swal- lowtail), Protesilaus epidaus tepicus (swallowtail). 18. Sierra Madre del Sur (SMS): east-west oriented moun- tain area, ranging from 1200 to 3500 m, including eastern Guerrero, northwestern Oaxaca, and southern Puebla and Morelos. Connects to north with TMV, MAS, and SMR, but mostly surrounded by lowland NE, and as such is southernmost part of the Madrean Region (Takhtajan, 1986). Includes mesic habitats with temperate evergreen forests and woodlands. The diversity of these woodlands is very high, including species of Quercus and Juniperus, as well as genera of more southern, tropical derivation. Endemic plants include Onagraceae: (tribe Fuchsieae) Fuchsia ravenii and (tribe Lopezieae): Lopezia smithii, as well as Aga- vaceae: Yucca mixtecana; Lauraceae: Mocinnodaphne cinnamomoidea; Malvaceae: Hibiscus tenorii; Melas- tomataceae: Miconia teotepecensis; Ruscaceae: Maianthemum amoenum, M. macrophyllum, M. com- altepecense. Endemic fauna include Amphibians: [Plethodontidae] Thorius grandis (grand minute sala- mander), T. infernalis (Atoyac minute salamander); Reptiles: [Anguidae] Abronia deppii (alligator lizard); Insects: [Coleoptera, Carabidae] Calathus ovipennis, Elliptoleus crepericornis, E. whiteheadi (ground bee- tles; Liebherr, 1991b), Platynus platynellus (ground beetle; Liebherr, 1992). 19. Neotropical (NE): large region, essentially the Neo- tropical Kingdom of Takhtajan (1986), comprises ev- erything south of the Madrean and North American regions. For purposes of this analysis, NE includes a broad spectrum of tropical sub-regions, from the southernmost, tropical part of the Florida Peninsula through the islands of the Caribbean region, most of the coastal plains of Mexico, and all of Central Amer- ica to most of South America. Among the very large number of endemic plant taxa are Onagraceae, tribe Hauyeae and numerous species of Fuchsia (tribe Fuchsieae) and Ludwigia (tribe Jussieeae), and the plant families Brunelliaceae, Cyclanthaceae, Desfon- tainiaceae, and Marcgraviaceae. Endemic fauna in- clude Amphibians: [Hylidae] Gastrotheca (Notodel- phis) ovifera (giant marsupial frog)4; Reptiles: [Boidae] subfamily Boinae (boas and constrictors)7; Birds: fam- ily Rheidae (rheas)3; Mammals2,5: [Camelidae] Lama (alpacas, guanacos, llamas); family Caviidae (cavies, guinea pigs); family Chinchillidae (chinchillas and viscachas); [marsupials, Microbiotheriidae] Dromi- ciops (monitos del monte). 20. East Palearctic (EP): defined here to include the northeast Asian parts of the Circumboreal Region and essentially all of the diverse Eastern Asiatic Region of Takhtajan (1986), including the eastern Himalayas, most of China, the Korean Peninsula, Japan and the north Pacific Ocean island series. The flora of this region is enormous and very rich in endemics, in- cluding in Onagraceae several species of Circaea (tribe Circaeeae; Boufford, 1982) and Epilobium (tribe Epilobieae; Chen et al., 1992), as well as the endemic families Cephalotaxaceae, Ginkgoaceae, and Trochod- endraceae, and more than 300 endemic genera [e.g., Apiaceae: Tetrapanax; Berberidaceae: Nandina; Cor- naceae: Aucuba; Lardizabalaceae: Akebia; Rosaceae: Chaenomeles; Rutaceae: Poncirus; Taxodiaceae: Cryp- tomeria]. Endemic fauna include Fishes: [Siluridae] Silurus asotus (Amur catfish)6; Reptiles?Crocodilians: family Gavialidae (gharial)7; Birds [Phasianidae] Gal- Volume 91, Number 1 2004 185Katinas et al. Geographical Diversification lus gallus (red jungle fowl, chicken)3; Mammals2,5: or- der Dermoptera (flying lemurs); family Hylobatidae (gibbons and lesser apes); [Leporidae] Pentalagus (Ryukyu rabbit). 21. West Palearctic (WP): defined here to include Euro- pean and west Asian parts of the Circumboreal Re- gion (Takhtajan, 1986), essentially everything west of EP in Eurasia. The flora includes many endemic plants, including Apiaceae: Agasyllis, Endressia, Tho- rella; Asteraceae: Berardia; Boraginaceae: Megacar- yon, Trigonocaryum; Brassicaceae: Microstigma, Pseudovesicaria; Fabaceae: Petteria; Gesneriaceae: Haberlea). Endemic fauna include Fishes: [Siluridae] Silurus aristotelis (Aristotle?s catfish)6; Amphibians: [Pelobatidae] Pelobates (European spadefoot toads)4; Mammals: [Bovidae] Ovis musimon (mouflon sheep)2,5.