vol. 165, no. 3 the american naturalist march 2005 E-Article Explosive Radiation of Malpighiales Supports a Mid-Cretaceous Origin of Modern Tropical Rain Forests Charles C. Davis,1,* Campbell O. Webb,2,? Kenneth J. Wurdack,3,? Carlos A. Jaramillo,4,? and Michael J. Donoghue2,k 1. Department of Ecology and Evolutionary Biology, University of Michigan Herbarium, Ann Arbor, Michigan 48108-2287; 2. Department of Ecology and Evolutionary Biology, Yale University, P.O. Box 208106, New Haven, Connecticut 06520; 3. Department of Botany and Laboratories of Analytical Biology, Smithsonian Institution, P.O. Box 37012, National Museum of Natural History, MRC-166, Washington DC 20013-7012; 4. Biostratigraphy Team, Instituto Colombiano del Petro?leo, AA 4185, Bucaramanga, Colombia Submitted May 12, 2004; Accepted October 27, 2004; Electronically published February 1, 2005 abstract: Fossil data have been interpreted as indicating that Late Cretaceous tropical forests were open and dry adapted and that mod- ern closed-canopy rain forest did not originate until after the Cretaceous-Tertiary (K/T) boundary. However, some mid-Cretaceous leaf floras have been interpreted as rain forest. Molecular divergence- time estimates within the clade Malpighiales, which constitute a large percentage of species in the shaded, shrub, and small tree layer in tropical rain forests worldwide, provide new tests of these hypotheses. We estimate that all 28 major lineages (i.e., traditionally recognized families) within this clade originated in tropical rain forest well before the Tertiary, mostly during the Albian and Cenomanian (112?94 Ma). Their rapid rise in the mid-Cretaceous may have resulted from the origin of adaptations to survive and reproduce under a closed forest canopy. This pattern may also be paralleled by other similarly diverse lineages and supports fossil indications that closed-canopy tropical rain forests existed well before the K/T boundary. This case illustrates that dated phylogenies can provide an important new source of ev- idence bearing on the timing of major environmental changes, which may be especially useful when fossil evidence is limited or controversial. * Corresponding author; e-mail: chdavis@umich.edu. ? E-mail: campbell.webb@yale.edu. ? E-mail: kwurdack@lms.si.edu. ? E-mail: carlos.jaramillo@ecopetrol.com.co. k E-mail: michael.donoghue@yale.edu. Am. Nat. 2005. Vol. 165, pp. E36?E65.  2005 by The University of Chicago. 0003-0147/2005/16503-40446$15.00. All rights reserved. Keywords: biome evolution, fossils, K/T boundary, Malpighiales, pe- nalized likelihood, tropical rain forest. Modern tropical rain forests are one of the most important and species rich biomes on the planet. They can be defined as having a stratified closed canopy, as receiving abundant precipitation, as experiencing equable temperatures, and as containing woody angiosperm species, at least in the understory (Richards 1996; Whitmore 1998; Morley 2000). During the past 20 years the view has become widespread that the expansion and diversification of this vegetation type occurred principally during the past 65 million years, following the mass extinction event at the Cretaceous- Tertiary (K/T) boundary (?65 Ma [Tiffney 1984; Wing and Boucher 1998; Morley 2000; Johnson and Ellis 2002; Ziegler et al. 2003]; Cretaceous and Cenozoic timescales following Gradstein et al. [1995] and Berggren et al. [1995]). This hypothesis was initially supported by the rarity of large stems (Wheeler and Baas 1991; Wing and Boucher 1998) and large diaspores (Tiffney 1984; Wing and Boucher 1998) of angiosperms in the Cretaceous and by the marked increase in diaspore size in the Early Ter- tiary. Large seeds facilitate the establishment of seedlings under a rain forest canopy (Grime 1979). Studies of fossil leaves and wood (Upchurch and Wolfe 1987, 1993; Wolfe and Upchurch 1987) partially corrob- orated this pattern by indicating that most Late Cretaceous floras of southern North America, which was tropical or nearly so, represented open and subhumid (though not deciduous) forests. This contrasts with fossil floras in the same areas after the recovery from the K/T extinction event, which resemble modern tropical rain forests (Wolfe and Upchurch 1987; Johnson and Ellis 2002). However, floras from the early Late Cretaceous (Cenomanian; ?100 Ma) of Kansas, Nebraska, and New Jersey have leaf sizes and morphologies characteristic of wetter climates (Wolfe and Upchurch 1987). Upchurch and Wolfe (1993) inter- preted one flora (Fort Harker, KS) as typical megathermal (120 mean annual temperature [Upchurch and Wolfe Dating the Origin of Tropical Rain Forests E37 Table 1: Contemporary importance of tree species of Malpighiales and Ericales (APG 2003) in three tropical rain forests Location All species Malpighiales Ericales No. spp. No. ind. No. spp. No. ind. No. spp. No. ind. All trees ?10 cm diameter at breast height: Gunung Palung 325 2,807 69 (21.2) 671 (23.9) 32 (9.8) 320 (11.4) Dzanga-Sangha 258 2,254 59 (22.8) 537 (23.8) 23 (8.9) 413 (18.3) Yasun?? 1,092 9,184 107 (9.7) 871 (9.4) 100 (9.1) 832 (9.0) Trees ?10 cm diameter at breast height:a Gunung Palung 164 655 46 (28.0) 250 (38.1) 17 (10.3) 114 (17.4) Dzanga-Sangha 105 407 28 (26.6) 135 (33.1) 7 (6.6) 90 (22.1) Yasun?? 583 2,139 62 (10.6) 270 (12.6) 44 (7.5) 100 (4.6) Note: Gunung Palung National Park, West Kalimantan (Webb 1997; Webb and Peart 2000); Dzanga- -Palung p Gunung Sanghap Dzanga Sangha National Park, Central African Republic (D. Harris and J. Hall, unpublished data; Hall 2003); Yasun?? p Yasun??, Ecuador (Pitman et al. 2001). Figures are the sum of trees and species at a number of sample plots at each site. Percentages of species diversity and of the total number of individuals are shown in parentheses. (Some plant groups at Dzanga-Sangha have not yet been fully separated into morphotype, and the numbers here represent an underestimate of the number of species.) a Species that were not observed to have a maximum diameter 125 cm (i.e., understory trees). 1987]) rain forest and as evidence against the view that such forests did not originate until the Tertiary. The advent of strongly supported phylogenies of living plants based primarily on molecular sequence data pro- vides a new source of evidence on questions of this sort. Here we argue that insights into the origin of modern tropical rain forests (as defined above) can be obtained by estimating the timing of the diversification of major an- giosperm clades that inhabit these forests and by dem- onstrating that the habitat of the ancestral species of these diversifications most likely occurred in warm, wet, closed- canopy forests. This novel approach to examining biome evolution may help to break the impasse on the question of the age of the modern tropical rain forest when direct fossil evidence is limited. One large clade of tropical flowering plants that is es- pecially suited for such an analysis is Malpighiales (APG 2003). Members of Malpighiales were previously assigned to 13 different angiosperm orders (Cronquist 1981) and are highly diverse in both morphology and species (Chase et al. 2002). They include ?16,000 species (?6% of all angiosperms; numbers of species from Stevens [2003]; to- tal angiosperm species diversity from Thorne [2002]) be- longing to many well-known tropical groups and are an important component of the understory of tropical rain forests worldwide (table 1). We used Bayesian, likelihood, and parsimony methods to estimate the phylogeny and divergence times of Malpighiales from approximately 6,300 base pairs (bp) of DNA sequence data representing all three plant genomes: plastid atpB and rbcL, nuclear ribosomal 18S, and mitochondrial nad1B-C. Given the resulting trees and data on the ecology of all major lineages of Malpighiales, we used both parsimony and maximum likelihood to reconstruct the probable habitat occupied by the first members of this highly diverse clade. Material and Methods Gene Sequencing Our data sets include 124 species representing all tradi- tionally recognized families of Malpighiales (APG 2003); outgroup species from the closely related clades Celastrales, Oxalidales, and Huaceae (APG 2003; Soltis et al. 2003); and members of the core eudicot clades Saxifragales (Davis and Chase 2004) and Caryophyllales (Soltis et al. 2003). Seventy-seven, 32, 20, and 11 sequences were newly ob- tained for this study for atpB, rbcL, 18S, and nad1B-C, respectively; the remaining were obtained from GenBank. Amplification and sequencing protocols for atpB, rbcL, 18S, and nad1B-C followed Chase et al. (2002), Hoot et al. (1995), Soltis and Soltis (1997), and Davis and Wurdack (2004), respectively. Nucleotide sequences were aligned by eye; the ends of sequences, as well as ambiguous internal regions, were trimmed from each data set to maintain complementary data between taxa. The aligned plastid, nuclear, and mitochondrial data sets included 2,825, 1,653, and 1,887 bp, respectively. Supplementary information, including data matrices and trees analyzed in this study, is available from TreeBASE (http://www.treebase.org) or the appendixes to this article. Phylogenetic Analysis Parsimony bootstrap percentages (Felsenstein 1985) for each clade were estimated in PAUP? version 4.0b10 (Swof- ford 2003) from 10,000 heuristic search replicates, tree bisection-reconnection branch swapping, MulTrees on, and simple taxon addition (saving 10 trees per replicate). Parsimony bootstrap consensus trees generated from the three data sets revealed no strongly supported (?90% bootstrap) incongruent clades between the independent E38 The American Naturalist analyses of the plastid, nuclear, and mitochondrial data sets and were subsequently analyzed simultaneously with parsimony and Bayesian methods (Whitten et al. 2000; Reeves et al. 2001). Parsimony searches were performed as above, but with 100 random taxon addition replicates saving all optimal trees at each step. To choose the optimal model of sequence evolution, we performed a series of hierarchical likelihood ratio tests (Fel- senstein 1981; Huelsenbeck and Rannala 1997) using Mo- deltest version 3.06 (Posada and Crandall 1998). Bayesian analyses were implemented in MrBayes version 3.0b4 (Huel- senbeck and Ronquist 2001) under the modelGTR I G with default priors for the rate matrix, branch lengths, gamma shape parameter, and the proportion of invariant sites. A Dirichlet distribution was used for the base fre- quency parameters, and an uninformative prior was used for the tree topology. Ten chains were initiated with a ran- dom starting tree and run for one million generations sam- pled every 1,000 generations. Following a burn-in period of 200,000 generations, trees were sampled from the pos- terior distribution to calculate clade posterior probabilities. Habitat Reconstruction To infer the ancestral habitat of Malpighiales, we optimized the habitat of major lineages of extant Malpighiales onto the Bayesian tree with the highest likelihood score and onto the 162 most parsimonious trees using parsimony and maximum likelihood as implemented in Mesquite ver- sion 1.0 (Maddison and Maddison 2003). The habitat of major lineages of extant Malpighiales was scored as a two- state character: either inhabiting warm, wet, closed-canopy forest (i.e., rain forest) or not. Habitat was either ascer- tained directly from floristic and monographic treatments or inferred with the aid of distributional information on rain forests in the Americas (Prance 1989a; Richards 1996), Africa (White 1983; Richards 1996), Asia (Richards 1996; Morley 2000), and Australia (Richards 1996). Malpighiales not found in tropical rain forests typically occur in sa- vannahs or open woodland habitats in tropical latitudes. A relatively small number of clades (e.g., some Euphor- biaceae, Salicaceae, and Violaceae), however, occur in tem- perate zones. We scored tropical open forest and temper- ate-zone inhabitants as a single state, ?nonwarm/wet/ closed,? because our primary concern was whether Malpighiales occupied warm, wet, closed-canopy forest an- cestrally. Habitat occupancy is a valid character for an- cestral state reconstruction because it is directly related to intrinsic (genetically based) physiological characteristics of taxa that inhabit this biome (Webb et al. 2002). For habitat scoring see appendix B. We performed two reconstructions to ascertain the an- cestral habitat of Malpighiales: one in which habitat was scored for each family (sensu APG [2003]) and the other in which it was scored for all genera sampled in the phy- logenetic analysis. The family-level scoring helped to avoid sampling bias by ensuring that habitats occupied by un- sampled genera were also included. Taxa inhabiting both rain forest and open tropical/temperate habitats were coded as polymorphic. Assumptions about character weighting were evaluated under parsimony using step ma- trices (Maddison 1994) to explore how great a cost must be imposed on the transition from rain forest for the an- cestral condition to be unambiguously open tropical/tem- perate (Ree and Donoghue 1998). For the likelihood re- constructions, the single fixed tree topology with the highest likelihood score from Bayesian searches was input with branch lengths and analyzed under the general Mk1 model (Lewis 2001) with the rate parameter estimated from the data. Polymorphic taxa were analyzed as either 1 or 0, and each of these reconstructions was performed twice under the alternative state (i.e., four analyses in total). Divergence Time Estimates We chose the Bayesian tree from above to test for rate constancy among lineages. Branch lengths and an asso- ciated likelihood score were calculated on this tree in PAUP? under the optimal sequence model and associated parameters with, and without, a molecular clock enforced. The test statistic 2( ) was compared to a x2 ln L1 ln L0 distribution (with degrees of freedom;n 2 n p of taxa) to assess significance. A global molecularnumber clock was rejected ( ) for the combined data set.P ! .05 The nonclock tree was rooted with Dillenia and Peri- discus, which are members of the core eudicot clades Car- yophyllales (Soltis et al. 2003) and Saxifragales (Davis and Chase 2004), respectively (see app. C for full tree). Di- vergence times were estimated on this tree using penalized likelihood (PL; Sanderson 2002) as implemented in r8s version 1.7 (Sanderson 2003). Penalized likelihood has been shown to outperform both clock and nonclock non- parametric rate smoothing methods when data depart from a molecular clock (Sanderson 2002). This method relies on a data-driven, cross-validation procedure that sequentially removes taxa from the tree, estimates param- eters without the removed branch, and calculates the x2 error associated with the difference between the predicted and actual values. The optimal smoothing value for the global data set was 31.62. To estimate standard errors associated with divergence times, we used the parametric bootstrapping strategy out- lined by Davis et al. (2002): 100 data sets were simulated on the r8 smoothed topology using the computer software Seq-Gen version 1.2.7 (Rambaut and Grassly 1997); re- Dating the Origin of Tropical Rain Forests E39 Table 2: Fossil age constraints Extant taxon Fossil taxon Fossil type Oldest reliable age (Ma) Location Acalypha1 Acalypha type Pollen Early Paleocene (61.0) China (Kiangsu) Austrobuxus-Dissilaria clade2 Malvacipollis diversus Pollen Late Paleocene (55.5) Australia Balanops3 Balanops caledonica Pollen Late Oligocene (23.8) Scotland (Hebrides) Caryocar4 Retisyncolporites angularis Pollen Early Eocene (55.5) Venezuela Casearia5 Casearia type Pollen (Late) Middle Eocene (37.0) Panama Chrysobalanus6 Chrysobalanus type Pollen (Early) Middle Eocene (49.0) Colorado Clusiaceae7 Palaeoclusia chevalieri Flower Late Turonian (89.0) New Jersey Ctenolophon8, 9 Ctenolophonidites costatus Pollen Maastrichtian (66.0) Nigeria Cunoniaceae10 Platydiscus peltatus Flower Early Campanian (83.5) Sweden (Kristianstad Basin) Drypetes11 Drypetes type Pollen Late Eocene (33.7) France (Aisne) Hippomaneae (Homalanthus)12, 13 Crepetocarpon perkinsii Fruit Middle Eocene (40.0) Tennessee Phyllanthus14 Phyllanthus type Pollen Late Eocene (33.7) Atlantic Ocean Rhizophoraceae sensu lato (incl. Erythroxylaceae)15, 16 Zonocostites ramonae Pollen (Early) Late Eocene (36.9) Colombia Salix-Populus clade17 Pseudosalix handleyi Twigs, leaves, flowers Middle Eocene (48.0) Utah Stigmaphylloids (Malpighiaceae crown group)18?20 Perisyncolporites pokornyi Pollen Middle Eocene (49.0) Colombia Note: Each fossil taxon provides a reliable minimum age estimate for taxa sampled in this study. In the case of palynofossils, we selected only pollen types that were easily assignable to taxa included in our phylogenetic analyses. Palynofossils assigned to extant taxa are based on taxonomic assessments by Muller (1981) and updated accordingly for taxonomy and stratigraphy following the numerical references in appendix A (which includes a tree showing fossil constraints). For Cretaceous and Cenozoic timescales see Gradstein et al. (1995) and Berggren et al. (1995). sulting simulated data sets were imported into PAUP?, and branch lengths were estimated on the smoothed topology for each of these data sets with the sequence model and parameters estimated from the original data; and resulting branch length estimates from the simulated data sets were used to calculate the variance in divergence time estimates (i.e., 95% confidence interval). We used four macrofossils and 11 palynofossils from the Cretaceous and Tertiary as reliable minimum age con- straints for several internal clades (table 2). Two maximum age constraints were independently enforced for the basal node of the tree. We first constrained the basal node to be no older than 125 m.yr. This corresponds to the earliest known occurrence of tricolpate pollen, a synapomorphy that marks the eudicot clade, of which Malpighiales are a member (Magallo?n et al. 1999; Sanderson and Doyle 2001; APG 2003). The pollen fossil record has been intensively studied throughout the initial rise of angiosperms, and tricolpate pollen increases steadily in abundance and di- versity from its first isolated reports in the late Barremian, becoming ubiquitous in the Albian. Hence, it has been considered unlikely that the eudicot clade originated much earlier than the late Barremian (Magallo?n et al. 1999; San- derson and Doyle 2001). This may be an overestimate for the age of our basal node, which does not correspond to the entire eudicot clade but rather to core eudicots exclu- sive of Gunnerales (Soltis et al. 2003). We also chose this date because it corresponds to the oldest molecular age estimate by Wikstro?m et al. (2001) for our basal node (their node 12). We also constrained the basal node to be no older than 109 m.yr., which was the youngest (and therefore the most conservative) age estimate by Wikstro?m et al. (2001) for the same node. Our choice of this constraint was influ- enced in part by the fact that their youngest estimates dated the entire eudicot clade (their node 6) as 125 m.yr., which we have taken as a maximum age for eudicots based on the fossil record of tricolpate pollen (Magallo?n et al. 1999; Sanderson and Doyle 2001). Results Our phylogenetic analyses and clock-independent dating estimates indicate that all of the 28 major lineages within Malpighiales, plus the previously unplaced taxon Centro- placus (APG 2003), originated well before the K/T bound- E40 The American Naturalist ary. Given our maximum age constraint of 125 m.yr. (fig. 1), Malpighiales originated in the late Aptian (114 Ma), and most major clades began to diversify shortly thereafter. The optimal age estimates for 24 of these 29 clades imply that they originated within a 20-m.yr. time window (114? 94 Ma), between the Aptian and through the Cenomanian: five during the late Aptian (114?112 Ma), 16 during the Albian (111?100 Ma), and three during the Cenomanian (98?94 Ma). Three more clades appeared during the Con- iacian (89?85 Ma), and the two most recently derived originated during the Campanian (76 Ma). Optimal age estimates in which the maximum age con- straint for our basal node was 109 m.yr. yielded similar results: Malpighiales originated in the mid-Albian (102 Ma), 24 of the 29 clades originated within a 13-m.yr. win- dow (102?89 Ma) from the Albian to the Turonian, one during the Santonian (84 Ma), and four during the Cam- panian (78?72 Ma). These ages are more consistent with the fossil pollen record because most core eudicots have tricolpate pollen, which does not appear until within the Albian (e.g., Doyle and Robbins 1977). All of our age estimates for crown group Malpighiales are much older than those inferred by Wikstro?m et al. (2001; their node 22, 81?74 Ma vs. our estimates of 119? 101 Ma). The conclusion that their estimates are too young holds even without the use of molecular dating methods because fossil flowers of Clusiaceae, representing a fairly derived clade within Malpighiales (perhaps related to the modern genera Clusia and Garcinia), are known from the Turonian, about 89 Ma (Crepet and Nixon 1998). Tropical rain forest was inferred to be the ancestral hab- itat for Malpighiales, and for most of the clades shown in figure 1. Under parsimony, a cost of between 2.67 and 3.01 for the Bayesian tree, and between 2.64 and 3.01 for the parsimony trees, had to be imposed on the transition from rain forest to open tropical/temperate habitats before the ancestral condition was inferred to be open tropical/ temperate. Maximum likelihood reconstructions yielded similarly robust results (table 3). Discussion As we have noted, fossil evidence indicates that tropical rain forest appeared after the K/T event in many areas where Late Cretaceous forests were apparently more open and dry adapted (Tiffney 1984; Upchurch and Wolfe 1987, 1993; Wolfe and Upchurch 1987; Wing and Boucher 1998; Morley 2000; Johnson and Ellis 2002; Ziegler et al. 2003). Further expansion and taxonomic diversification of this biome took place during the Cenozoic. The Paleocene- Eocene transition (?50 Ma) was characterized by high global temperatures (Wolfe 1978; Upchurch and Wolfe 1987; Zachos et al. 2001) and coincided with a significant increase in low-latitude palynofloral diversity (Jaramillo 2002). A similar, although less pronounced, climatic op- timum during the mid-Miocene (?15 Ma; Zachos et al. 2001) resulted in the reexpansion and diversification of rain forests worldwide (Morley 2000). Finally, Quaternary (1.6?0 Ma) glacial cycles are thought to account for the diversification of many species-rich rain forest clades (Prance 1982; Whitmore and Prance 1987; Behrensmeyer et al. 1992; Richardson et al. 2001). Major geological events during the Cenozoic also facilitated the intercontinental migration of tropical plants, for example, the closing of the Tethys Seaway (Hall 1998), Paleogene land connections across the North Atlantic (Tiffney 1985a, 1985b; Davis et al. 2002a), and Neogene uplift of the Andes and the closure of the Isthmus of Panama (Gentry 1982; Burnham and Graham 1999). Although these Cenozoic events surely contributed to the diversification of many rain forest clades, age estimates for Malpighiales suggest that its major lineages originated well before the K/T boundary. The simplest interpretation of our results is that Malpighiales occupied closed-canopy, moist, megathermal forests (i.e., rain forests) during their early evolution in the mid-Cretaceous. The alternative, that preexisting lineages in Malpighiales entered the rain forest habitat independently, would require that all the various morphological and physiological adaptations associated with living in this environment (Richards 1996; Whitmore 1998) evolved independently in most of the 29 major line- ages and that all their non?rain forest ancestors went ex- tinct. It could be that Late Cretaceous Malpighiales lived in the wettest, most shaded local habitats in open sub- humid forests, as suggested by the fact that Turonian Clu- siaceae, used as our oldest minimum age constraint (Cre- pet and Nixon 1998), are from a flora (South Amboy) thought to represent the subhumid interval (Wolfe and Upchurch 1987) and were ?preadapted? to the appearance of rain forest climates. However, under this scenario we would expect to find more lines of Malpighiales persisting today in drier areas. Limited Cretaceous fossil data (Upchurch and Wolfe 1987, 1993; Wolfe and Upchurch 1987; Morley 2000) sug- gest that angiosperm-dominated moist megathermal for- ests had arisen by the Cenomanian in the interval of the inferred origin of most rain forest clades in Malpighiales. Cenomanian leaves from the Dakota Formation of Kansas and Nebraska and the lower Raritan Formation of New Jersey (Woodbridge Clay) are physiognomically diverse and show many of the foliar adaptations characteristic of understory plants of modern tropical rain forests (Richards 1996), including large leaves with entire margins and drip tips, as well as plants with probable vining habits (Up- church and Wolfe 1987, 1993; Wolfe and Upchurch 1987; Morley 2000). A flora from the Dakota Formation near Figure 1: Penalized likelihood chronogram of Malpighiales. Figure reduced from 124-taxon data set to represent only the 28 recommended families of Malpighiales sensu APG (2003) plus the previously unplaced taxon Centroplacus. For outgroups and rooting see text. Bootstrap values and Bayesian posterior clade probabilities (150%/0.50), respectively, indicated near nodes; bullet p support values ?50%/0.50. The monophyly of Malpighiales was supported by a very high bootstrap value (100%) and posterior probability (1.0). Confidence intervals shown with shaded bars. Divergence times were calculated on this rate-smoothed topology by calibrating nodes with several minimum age constraints from macrofossil and palynological data (table 1). A maximum age constraint of 125 m.yr. was enforced for the root node based on the oldest occurrence of tricolpate pollen grains representing the eudicot clade (see text). The K/T boundary (?65 Ma) is marked with a dashed line. The origin of Malpighiales is estimated at 114 Ma. The scale bar indicates major Cretaceous and Cenozoic intervals: , , , ,A p Aptian Al p Albian Ce p Cenomanian T p Turonian Cp , , , , , , , ,Coniacian S p Santonian Cap Campanian M p Maastrichtian Pp Paleocene E p Eocene O p Oligocene Mi p Miocene P/Pp . For complete 124-taxon chronogram, see appendix C.Pliocene/Pleistocene E42 The American Naturalist Table 3: Ancestral habitat for major Malpighiales clades illus- trated in figure 1 as inferred from maximum likelihood Taxa Family scoring (TRF : OT/T) Generic scoring (TRF : OT/T) TRF OT/T TRF OT/T Achariaceae 1.0 : 0a .11 : .89a .96 : .04a .99 : .01a Balanopaceae 1.0 : 0a .99 : .01a .92 : .08a .98 : .02a Bonnetiaceae .88 : .12 .30 : .70 .61 : .39 .50 : .50 Caryocaraceae 1.0 : 0a .96 : .04a .98 : .02a 1.0 : 0a Centroplacus 1.0 : 0a .93 : .07a .97 : .03a .98 : .02a Chrysobalanceae 1.0 : 0a .99 : .01a .92 : .08a .99 : .01a Clusiaceae .91 : .09a .78 : .22 .75 : .25 .75 : .25 Ctenolophonaceae 1.0 : 0a .93 : .07a .97 : .03a .99 : .01a Elatinaceae 1.0 : 0a .56 : .44 .87 : .13 .78 : .22 Euphorbiaceae 1.0 : 0a .85 : .15 .99 : .01a 1.0 : 0a Goupiaceae 1.0 : 0a .11 : .89a .96 : .04a .99 : .01a Humiriaceae 1.0 : 0a .96 : .04a .98 : .02a 1.0 : 0a Hypericaceae .01 : .99a .11 : .89a .69 : .31 .38 : .62 Irvingiaceae 1.0 : 0a .95 : .05a .93 : .07a .98 : .02a Ixonanthaceae 1.0 : 0a .96 : .04a .95 : .05a .98 : .02a Lacistemataceae 1.0 : 0a .11 : .89a .91 : .09a .82 : .18 Linaceae 1.0 : 0 .95 : .05a .93 : .07a .98 : .02a Lophopyxidaceae 1.0 : 0a .94 : .06a .84 : .16 .91 : .09a Malpighiaceae 1.0 : 0a .56 : .44 .87 : .13 .78 : .22 Malpighiales (CG) 1.0 : 0a .86 : .14 .99 : .01a 1.0 : 0a Ochnaceae 1.0 : 0a .78 : .22 .97 : .03a .99 : .01a Pandaceae 1.0 : 0a .92 : .08a .99 : .01a .99 : .01a Passifloraceae 1.0 : 0a .12 : .88a .96 : .04a .98 : .02a Phyllanthaceae 1.0 : 0a .22 : .78 .94 : .06a .96 : .04a Picrodendraceae 1.0 : 0a .22 : .78 .94 : .06a .96 : .04a Podostemaceae .01 : .99a .11 : .89a .69 : .31 .38 : .62 Putranjivaceae 1.0 : 0a .94 : .06a .84 : .16 .91 : .09a Rhizophoraceae 1.0 : 0a .92 : .08a .99 : .01a 1.0 : 0a Salicaceae 1.0 : 0a .11 : .89a .91 : .09a .82 : .18 Violaceae 1.0 : 0a .11 : .89a .96 : .04a .98 : .02a Note: Proportional likelihood values of rain forest habitat (TRF) versus those in open tropical/temperate environments (OT/T) are separated by a colon. Reconstructions for both familial and generic scorings are shown and are further subdivided into analyses in which all taxa that had been scored as polymorphic were coded as either TRF or OT/T. Boldface indicates stem groups for which there is significant statistical support for OT/T environments. Stem clade reconstructions are shown unless otherwise indicated as CG (crown group). a Reconstruction judged best as determined by a log-likelihood decline of at least two units between states (i.e., the threshold value). Fort Harker, Kansas, contains especially large leaves and was cited (Upchurch and Wolfe 1987, 1993; Wolfe and Upchurch 1987) as evidence that typical rain forest orig- inated much earlier than others have argued. This inferred period of wetter climates is also supported by paleoclimatic reconstructions for the Cenomanian (Barron and Wash- ington 1985; Barron et al. 1989; Beerling and Woodward 2001), which indicate that mid latitudes may have been similar in precipitation and temperature to present-day low latitudes. Moreover, vegetation simulations for the mid-Cretaceous suggest that rain forests could have existed in low-latitude regions of present-day South America, Af- rica, northern Australia, and India (Beerling and Wood- ward 2001), and they may have persisted in similar areas until the latest Cretaceous (Otto-Bliesner and Upchurch 1997; Upchurch et al. 1998; Beerling and Woodward 2001). Extraordinary fossil evidence from the Castle Rock flora of Colorado suggests that highly diverse rain forests were present in North America shortly after the K/T boundary (Johnson and Ellis 2002). Johnson and Ellis (2002) inter- preted these forests as a new phenomenon of the Cenozoic, but our phylogenetic evidence from Malpighiales, ancillary evidence from Cenomanian floras such as Fort Harker, and paleoclimate models suggest instead that on a global scale, rain forests may be much older. Any Cretaceous rain forests, however, must have been more geographically re- stricted than those that developed during the Cenozoic. Although tropical floras are well known at middle latitudes in the Late Cretaceous, most of them indicate subhumid conditions. However, this does not rule out the existence of wet megathermal vegetation at lower latitudes, where there are numerous fossil pollen floras but megafossil flo- ras, which allow more direct inferences on physiognomy of the vegetation, are rare and poorly known (Upchurch and Wolfe 1987). The rarity of large angiosperm diaspores during the Cre- taceous and their increased size after the K/T boundary have also been cited as evidence that closed-canopy en- vironments like those of modern rain forests were not present during the Cretaceous (Tiffney 1984; Wing and Boucher 1998). This assumed that larger diaspores help seedlings become established and survive better in heavily shaded environments such as the understory of tropical rain forests. Recent studies (Grubb 1996, 1998; Grubb and Metcalfe 1996), however, suggest that large diaspores, while an advantage in low-light environments, are not a requirement for successful germination and establishment in the rain forest and may relate more to the ability to germinate on dense leaf litter than to light availability (see also Feild et al. 2004). Seeds of contemporary Malpighiales are on average larger than the mean for samples of all angiosperms (A. Moles, personal communication, Seed In- formation Database, Kew Gardens). However, the clusia- ceous fossil flower from the Turonian of New Jersey was small, with a multiovulate ovary !1 mm in diameter (Cre- pet and Nixon 1998). It is possible that the paucity of large Cretaceous diaspores is partly a function of poor sampling of low-latitude floras. Large fruits and seeds from the Cam- panian-Maastrichtian of West Africa were the main ex- ception noted by Wing and Tiffney (1987) to their gen- eralization that Cretaceous angiosperm diaspores were small (cf. Chesters 1955). Another possibility is that the Dating the Origin of Tropical Rain Forests E43 small size of Cretaceous diaspores reflects not so much open environments as the absence of bird and mammal dispersers, whose radiation after the K/T event has been proposed as an alternative explanation for the Early Ter- tiary increase in diaspore size (Wing and Tiffney 1987). Malpighiales account for up to 40% of the understory tree community in tropical rain forests (table 1). We sug- gest that Malpighiales were among the earliest angiosperm colonizers of the understory in the Cretaceous (Crane 1987), following representatives of the basal ANITA grade, which have been depicted as playing a similar role at the earliest stages of the angiosperm radiation (Feild et al. 2004). ANITA-grade plants, some eumagnoliids, and Mal- pighiales may have successfully competed with existing nonangiospermous plants in the understory, and Mal- pighiales may have filled a niche that was less occupied by the other new angiosperm groups: the small, subcanopy tree. Modern Malpighiales are often 2?10 m tall, are able to grow and reproduce without direct sunlight, and are more flexible in growth habit than cycad-like seed plants (Crane 1987; Feild et al. 2004), that is, like ANITA-grade plants but generally taller. The recently documented (Schneider et al. 2004) Late Cretaceous radiation of de- rived ferns (Polypodiaceae sensu lato) may represent a parallel occupation of forest floor and epiphytic niches. Most angiosperm wood fossils from the mid-Cretaceous are relatively small (Crane 1987; Wing and Boucher 1998), suggesting that the forest canopy at the beginning of the radiation of Malpighiales was dominated by large conifers (Crane 1987). The diversity of conifers remained relatively steady during the late Albian?early Cenomanian, whereas cycadophytes, pteridophytes, and pteridosperms exhibited dramatic declines. Crane (1987) suggested that the latter taxa were replaced by angiosperm shrubs or small trees. A similar mixture of dicotyledonous trees and conifers is found today in the heath and montane forests of southeast Asia, which contain emergent Agathis or Dacrydium spe- cies, and the giant Araucaria- and Agathis-dominated rain forests of Queensland, New Guinea, New Caledonia, and New Zealand (Richards 1996). By the time of the Ceno- manian Dakota and Raritan floras, however, the shift in the dominant trees from conifers to angiosperms had probably occurred (Upchurch and Wolfe 1987, 1993; Wolfe and Upchurch 1987; Cantrill and Poole 2005). The pattern exhibited by Malpighiales may be paralleled by other similarly diverse tropical clades. Ericales (APG 2003), for example, form a well-supported clade (Bremer et al. 2002) and are morphologically heterogeneous; their members have been placed in 11 different angiosperm orders (Cronquist 1981), and they are similarly species rich (?11,000 species; see Stevens 2003 and Thorne 2002). Er- icales also form an important component of the under- story diversity in tropical rain forests (up to ?22%; table 1). Together, Ericales and Malpighiales account for more than half of the understory stems in some of these forests (?55% in Asia and Africa). Molecular divergence-time es- timates for Ericales suggest that they originated in the Cretaceous during approximately the same time period as Malpighiales (?106 Ma [Wikstro?m et al. 2001]). Like Mal- pighiales, Ericales have a fossil record dating back to the Turonian (Magallo?n et al. 1999), and it appears that many of their major lineages may extend back to the Cretaceous (Bremer et al. 2002) and originated rapidly (Anderberg et al. 2002). The coincident pattern of diversification in these two major clades may mark the origin of tropical rain forests as we know them today. In the case of Malpighiales, we have demonstrated that dated phylogenies can provide an important new source of evidence on the timing of major environmental changes, which may be especially useful in such cases where direct fossil evidence is limited or controversial. Acknowledgments We thank W. Anderson, P. Ashton, R. Burnham, J. Doyle, B. O?Meara, J. Rest, M. Sanderson, G. Upchurch, S. Wing, and M. Wojciechowski for helpful discussion; J. Hall, D. Harris, and N. Pitman for sharing forest plot data; A. Moles and the Kew Seed Information Database for seed size data; D. Mindell and P. Tucker for lab space; and M. Alford, M. Chase, and M. Simmons for DNA samples. C.C.D. was supported by the National Science Foundation (NSF) Assembling the Tree of Life grant (EF 04-31242), by a Rackham faculty grant from the University of Mich- igan, and by the Michigan Society of Fellows. C.O.W. was funded by the NSF (DEB-0212873). K.J.W. was supported by the Smithsonian Institution and the Lewis B. and Do- rothy Cullman Program for Molecular Systematic Studies at the New York Botanical Garden. This article is dedicated to A. H. Gentry. APPENDIX A Numbered references for fossil minimum age constraints presented in table 2 and figure A1. Exact placement of fossil constraints are shown in figure A1 using the same numbered references. Palynofossils assigned to extant taxa sampled in our data set were based on taxonomic assessments by Muller (1981) and updated accordingly for taxonomy and stratigraphy using the references below. Maximum age constraints of 125 and 109 Ma assigned to the basal node from Magallo?n et al. (1999) and Wikstro?m et al. (2001), respectively. Figure A1: Fossil constraints; minimum age fossil constraints shown on tree using numbered references in appendix A Dating the Origin of Tropical Rain Forests E45 Literature Cited in Table 2 and Figure A1 1. Sun, M., X. Sun, Y. Zhao, O. Wang, Z. Li, Z. Hu, and P. Mei. 1989. Sporo-pollen. Pages 6?111 in Division of Comprehensive Studies on Ocean Geology of the Ministry of Geology and Minerals of P. R. China and Institute of Geology of the Chinese Academy of Geological Sciences, ed. Cenozoic paleobiota of the continental shelf of East China Sea (Donghai) (Micropaleobotanical Volume). Geological Publishing House, Beijing. 2. Martin, H. A. 1981. Changing Cenozoic barriers and the Australian paleobotanical record. Annals of the Missouri Botanical Garden 69:625?667. 3. Simpson, J. B. 1961. The Tertiary pollen-flora of Mull and Ardnamurchan. Transactions of the Royal Society of Edinburgh Earth Sciences 64:421?468. 4. Rull, V. 2000. Ecostratigraphic study of Paleocene and Early Eocene palynological cyclicity in northern South America. Palaios 15:14?24. 5. Graham, A. 1985. Studies in neotropical paleobotany. IV. The Eocene communities of Panama. Annals of the Missouri Botanical Garden 72:504?534. 6. Wodehouse, R. P. 1932. Tertiary pollen. I. Pollen of the living representatives of the Green River flora. Bulletin of the Torrey Botanical Club 59:313?340. 7. Crepet, W. L., and K. C. Nixon. 1998. Fossil Clusiaceae from the Late Cretaceous (Turonian) of New Jersey and implications regarding the history of bee pollination. American Journal of Botany 85:1122?1133. 8. Edet, J. J., and E. E. Nyong. 1994. Palynostratigraphy of Nkporo Shale exposures (late Campanian-Maastrichtian) on the Calabar Flank, SE Nigeria. Review of Palaeobotany and Palynology 80:131?147. 9. Schrank, E. 1994. Palynology of the Yesomma Formation in northern Somalia: a systematic study of pollen, spores and associated phytoplankton from the Late Cretaceous Palmae Province. Palaeontographica Abteiling B Pala?o- phytologie 231:63?112. 10. Scho?nenberger, J., E. M. Friis, M. L. Matthews, and P. K. Endress. 2001. Cunoniaceae in the Cretaceous of Europe: evidence from fossil flowers. Annals of Botany 88:423?437. 11. Gruas-Cavagnetto, C., and P. Anado?n. 1995. Une mangrove complexe dans le Bartonien du Bassin de l?Ebre (NE de l?Espagne). Palaeontographica Abteiling B Pala?ophytologie 236:147?165. 12. Dilcher, D. L., and S. R. Manchester. 1988. Investigations of angiosperms from the Eocene of North America: a fruit belonging to the Euphorbiaceae. Tertiary Research 9:45?58. 13. Potter, F. W., Jr., and D. L. Dilcher. 1980. Biostratigraphic analysis of Eocene clay deposits in Henry County, Tennessee. Pages 211?225 in D. L. Dilcher and T. N. Taylor, eds. Biostratigraphy of fossil plants. Dowden, Hutchinson & Ross, Stroudsburg, PA. 14. Zaklinskaya, E. D. 1978. Palynology of Paleogene Clay from DSDP Site 368, Cape Verde Rise. Deep Sea Drilling Project (U.S. Government Printing Office) 41:933?937. 15. Jaramillo, C. A. 2002. Response of tropical vegetation to Paleogene warming. Paleobiology 28:222?243. 16. Muller, J., E. Di Giacomo, and A. Van Erve. 1987. A palynological zonation for the Cretaceous, Tertiary, and Quaternary of northern South America. AASP Contributions Series 19:7?76. 17. Boucher, L. D., S. R. Manchester, and W. S. Judd. 2003. An extinct genus of Salicaceae based on twigs with attached flowers, fruits, and foliage from the Eocene Green River Formation of Utah and Colorado, USA. American Journal of Botany 90:1389?1399. 18. Jaramillo, C. A., and D. L. Dilcher. 2001. Middle Paleogene palynology of central Colombia, South America: a study of pollen and spores from tropical latitudes. Palaeontographica Abteiling B Pala?ophytologie 285:87?213. 19. Davis, C. C., W. R. Anderson, and M. J. Donoghue. 2001. Phylogeny of Malpighiaceae: evidence from chloroplast ndhF and trnL-F nucleotide sequences. American Journal of Botany 88:1830?1846. 20. Davis, C. C., P. W. Fritsch, C. D. Bell, and S. Mathews. 2004. High-latitude Tertiary migrations of an exclusively tropical clade: evidence from Malpighiaceae. International Journal of Plant Sciences 165(suppl.):S107?S121. E46 APPENDIX B Table B1: Taxa sequenced, voucher information, and GenBank accession numbers Taxon Voucher Plastid (atpB) Plastid (rbcL) Mitochondrial (nad1B?C) Nuclear (18S) Habitat Achariaceae OT/T and TRF (Cronquist 1981) (SRFG) Acharia tragodes Thunb. Cloete s.n. (BOL) AF209520 AJ418795 AY674643 AF206728 OT/T (Cronquist 1981) Hydnocarpus sp. Chase 1301 (K) (origi- nally misdet. as Ixonanthes icosandra) AF209607 AF206783 AY674714 AF206941 TRF (Sleumer 1938, 1954) Kiggelaria sp. Alford 51 (BH) AY788231 AY788180 AY674719 AY674609 TRF (Sleumer 1975) Pangium edule Reinw. Chase 1285 (K) AF209644 AJ18801 AY674742 AF206979 TRF (Sleumer 1954) Balanopaceae TRF (Carlquist 1980; Cronquist 1981) Balanops vieillardii Baill. Chase 1816 (K) AF209534; AF089760 AF089760 AY674479 AF206860 TRF (Carlquist 1980; Cronquist 1981) Bonnetiaceae OT/T (Maguire 1972; Robson 1981; Gen- try 1996) Archytaea multiflora Benth. Kubitzki & Feuerer 97-26 (HBG) AY788202 AY380342 AY674648; AY674649 AY674574 OT/T (Maguire 1972; Gentry 1996) Caryocaraceae TRF (Prance 1973; Prance and Freitas da Silva 1973; Cronquist 1981) Caryocar glabrum Pers. Mori 22997 (NY) AF206745 Z75671 AY674662 AF206881 TRF (Prance 1973; Prance and Freitas da Silva 1973; Cronquist 1981) Celastraceaea OT/T and TRF (SRFG) Brexia madagascar- iensis Thouars Schwerdtfeger 25471 (B); Kew 1977- 14901 (K?); Wur- dack s.n. (US) AJ235419 L11176 AY674655 U42543 OT/T (Fosberg and Renvoize 1980) Celastrus orbiculatus Thunb. Simmons 1773 (BH) AY788263 AY788194 AY674664 AY788162 OT/T and TRF (Hou 1955, 1962) Celastrus scandens L. Simmons 1783 (BH) AY788264 AY788195 AY674665 AY674581 OT/T and TRF (Hou 1955, 1962) Denhamia celastro- ides (F. Muell.) L. W. Jessup Chase 2050 (K) AY788267 AJ402941 AY674680 AY674591 TRF (Jessup 1984) E47 Table B1 (Continued) Taxon Voucher Plastid (atpB) Plastid (rbcL) Mitochondrial (nad1B?C) Nuclear (18S) Habitat Elaeodendron orien- tale Jacq. Chase 1213 (K) AY788269 AY380347 AY674689 AY674593 OT/T (de la Bathie 1946; Fosberg and Renvoize 1980) Euonymus alatus Siebold Simmons 1772 (BH) AY788270 AY788197 AY674694 AY788164 OT/T and TRF (Blak- elock 1951; Hou 1962) Maytenus arbutifolia (Hochst. ex A. Rich.) R. Wilczek Collenette 2/93 (K) AY788271 AY380352 AY674732 AY674616 OT/T and TRF (Hou 1962; Demissew 1985) Maytenus senegalen- sis (Lam.) Exell Collenette 4/93 (K) AY788272 AY380353 AY788286 AY788165 OT/T and TRF (Hou 1962; Demissew 1985) Paxistima canbyi A. Gray Simmons 1775 (BH) AY788273 AY788198 AY674746 AY674623 OT/T (Navaro and Blackwell 1990) Plagiopteron suaveo- lens Griff. Chase 1335 (K) AJ235562 AJ235787 AY674751 AF206993 TRF (Baas et al. 1979) Siphonodon celastri- neus Griff. Chase 2097 (K) AF209676 AF206821 AY674771 AF207021 OT/T and TRF (Hou 1964; Jessup 1984) Stackhousia minima Hook. f. Molloy s.n. (CHR) AJ235610 AJ235795 AY674773 AF207026 OT/T (Barker 1984; Carlquist 1987) Tripterygium regelii Sprague & Takeda Simmons 1776 (BH) AY788260 AY788193 AY674781 AY788161 OT/T (Ma et al. 1999) Cephalotaceaea OT/T (Lowrie 1998) Cephalotus folicu- laris Labill. Chase 147 (NCU) AY788265 L01894 AY674666 U42516 OT/T (Lowrie 1998) Chrysobalanaceae s.s.b TRF (Prance 1970, 1972a, 1973, 1989a; 1989b) Atuna racemosa Rafin. Chase 2118 (K) AY788203 AF089758 AY674650 AY674575 TRF (Prance 1989b) Chrysobalanus icaco L. FTG 76-311 (voucher loc.); Wurdack AF209562 L11178 AY674668 U42519 TRF (Prance 1970, 1972a) Hirtella bicornis Mart. & Zucc. Ducke Res. 2- 303Z.489 (K?) AY788225 AF089756 AY674706 AY674603 TRF (Prance 1972a, 1973) Licania sp. Ducke Res. 2-302 (K?); FTG 64-734 (FTG?) AF209617 L11193 AY788279 U42520 TRF (Prance 1972a, 1973, 1989b) Clusiaceae TRF (Kubitzki 1978; Cronquist 1981; Robson 1981) Clusia gundlachii Stahl Chase 341 (NCU) AY788209 Z75673 AY788278 AY674584 TRF (Cronquist 1981) E48 Table B1 (Continued) Taxon Voucher Plastid (atpB) Plastid (rbcL) Mitochondrial (nad1B?C) Nuclear (18S) Habitat Ctenolophonaceae TRF (Van Hooren and Nooteboom 1988a) Ctenolophon engleri- anus Mildbr. Dourse 1572 (K); Mc- Pherson 16911 (MO) AY788215 AJ402940 AY674676 AY674589 TRF (Van Hooren and Nooteboom 1988a) Cunoniaceaea OT/T and TRF (Hoogland 1979, 1981; Bradford 1998, 2002) Eucryphia sp. Strybing Arb 86-0250; Chase 2528 (K) AF209584 L01918 AY674693 U42533 OT/T (Bentham and Mueller 1864) Dichapetalaceae TRF (Prance 1972b, 1973; Breteler 1991) Dichapetalum spp. Fisson s.n. (K); Chase 624 (K) AJ235455 AF089764 AY674683 AF206902 TRF (Prance 1972b, 1973; Breteler 1991) Dilleniaceaea TRF (Hoogland 1951, 1952) Dillenia philippine- nesis Rolfe Chase 2102 (K) AY788268 L01903 AY674684 AY788163 TRF (Hoogland 1952) Elaeocarpaceaea OT/T and TRF (Bri- zicky 1965; Baker et al. 1998) Crinodendron hook- erianum Gay Chase 909 (K?) AF209570 AF206754 AY674673 AF206893 OT/T and TRF (Bricker 1991) Elaeocarpus spp. D. M. Hicks 8455 (K?); Alverson s.n. (WIS) AF209581 AF20675 AY788285 AF206906 TRF (Baker et al. 1998; Coode 2001) Sloanea spp. Alverson 2211 (WIS); Chase 343 (NCU) AJ235603 AF022131 AY674772 U42826 TRF (Smith 1944, 1954) Elatinaceae OT/T (Tucker 1986; Leach 1989) Elatine triandra Schkuhr Brunton et al. 13384 (MICH); Crins & Stabb 9600 (MICH) AY788219 AY380349 AY674690 AY674594 OT/T (Tucker 1986) Erythroxylaceae OT/T and TRF (Cronquist 1981) (SRFG) Erythroxylum spp. FTG63-251E; Chase 134 (NCU?); Wur- dack D713 (US) AJ235466 L13183 AY674692 AF206909 OT/T and TRF (de la Bathie 1952; Payens 1958; Cronquist 1981; Verdcourt 1984; Plowman 1989; Webster 1994b; Plowman and Berry 1999) E49 Table B1 (Continued) Taxon Voucher Plastid (atpB) Plastid (rbcL) Mitochondrial (nad1B?C) Nuclear (18S) Habitat Euphorbiaceae OT/T and TRF (Cronquist 1981; Webster 1994a; 1994b) (SRFG) Acalypha californica Benth. Levin 2192 (SD) AY788199 AY380341 AY674642 AY674571 OT/T and TRF (Web- ster 1994b) Clutia tomentosa L. Geumshuizan 6505 (MO) AY788210 AY788168 AY674669 AY674585 OT/T (Webster 1994a, 1994b) Codiaeum variega- tum (L.) Blume Wurdack D33 (US) AY788211 AY788169 AY674670 AY674586 TRF (Airy Shaw 1980a; Radcliffe- Smith 1987; Web- ster 1994b) Conceveiba marti- ana Baill. Bell 93-176 (US) AY788212 AY788170 AY674671 AY674587 TRF (Webster 1994b; Murillo 2000) Croton alabamensis var. alabamensis E. A. Smith ex Chapman Wurdack D8 (US) AY788214 AY788171 AY674675 AY674588 OT/T (Webster 1993, 1994b) Dalechampia spa- thulata (Scheidw.) Baill. Wurdack D10 (US) AY788216 AY788172 AY674677 AY788149 OT/T and TRF (Web- ster and Armbrus- ter 1991; Webster 1994b) Endospermum mol- uccanum (Teijsm. & Binn.) Kurz Chase 1258 (K) AY788220 AJ402950 AY674691 AY674595 TRF (Airy Shaw 1972; Webster 1994b) Euphorbia spp. Chase 102 (NCU); voucher unknown for U42535 AJ235472 AY788174 AY674695 U42535 OT/T and TRF (Web- ster 1994b) Hevea sp. Gillespie 4272 (US) AY788223 AY788175 AY674703 AY674601 TRF (Schultes 1990; Webster 1994b) Homalanthus popul- neus (Geiseler) Pax Chase 1266 (K) AY788226 AY380350 AY674707 AY674604 TRF (Airy Shaw 1968; Webster 1994b) Hura crepitans L. Wurdack D89 (US) AY788228 AY788177 AY674711 AY674606 OT/T and TRF (Stan- dley and Steyer- mark 1949; Webster 1994b) Lasiocroton baha- mensis Pax & K. Hoffm. Wurdack D58 (US) AY788233 AY788181 AY674723 AY788152 OT/T (Adams 1972; Webster 1994b) Neoscortechinia kin- gii (Hook. f.) Pax & K. Hoffm. Chase 1265 (K) AY788239 AJ402977 AY674738 AY674619 TRF (Webster 1994b) E50 Table B1 (Continued) Taxon Voucher Plastid (atpB) Plastid (rbcL) Mitochondrial (nad1B?C) Nuclear (18S) Habitat Omphalea diandra L. Chase 570 (K) AY788241 AY788183 AY674740 AY674622 OT/T and TRF (Airy Shaw 1980a; Web- ster 1994b) Pera bicolor Muell. Arg. Gillespie 4300 (US) AY788244 AY380355 AY674747 AY674624 TRF (Webster 1994b) Pimelodendron zoanthogyne J. J. Sm. Chase 1268 (K) AY788247 AJ418812 AY674750 AY674628 TRF (Airy Shaw 1980a, 1980b; Web- ster 1994b) Pogonophora schom- burgkiana Miers ex Benth. Larpin 1022 (US) AY788250 AY788185 AY674755 AY788156 TRF (Webster 1994b) Ricinus communis L. Wurdack D9 (US); Hills, unvouchered AY788253 AY788188 AY674763 AY674633 OT/T (Webster 1994b) Spathiostemon jav- ensis Blume Chase 1261 (K) AY788227 AY788176 AY674708 AY788151 TRF (Airy Shaw 1972; Webster 1994b) Suregada boiviniana Baill. Rakotomalaza et al. 1292 (MO) AY788255 AY788189 AY788284 AY788157 TRF (Airy Shaw 1975, 1980a; Webster 1994b) Tetrorchidium sp. Bell 93-204 (US) AY788257 AY788191 AY674777 AY788159 TRF (Radcliffe-Smith 1987; Webster and Huft 1988; Webster 1994b) Trigonostemon ver- rucosus J. J. Sm. Chase 1274 (K) AY788259 AY788192 AY674780 AY788160 TRF (Airy Shaw 1975, 1980a; Webster 1994b) Euphroniaceae OT/T (Steyermark 1987) Euphronia guianen- sis (R. H. Schomb.) H. Hallier Mori 23699 (NY) AY788221 AF089762 AY674696 AY674597 OT/T (Steyermark 1987) Goupiaceae TRF (Lundell 1985; Takhtajan 1997) Goupia glabra Aubl. Prevost 3031 (CAY) AJ235484 AJ235780 AY674699 AF206920 TRF (Lundell 1985; Takhtajan 1997) Huaceaea TRF (Perkins 1909; Baas 1972; Takhta- jan 1997) Afrostyrax sp. Cheek 5007 (K) AJ235385 AJ235771 AY674645 AF206840 TRF (Perkins 1909; Baas 1972; Takhta- jan 1997) E51 Table B1 (Continued) Taxon Voucher Plastid (atpB) Plastid (rbcL) Mitochondrial (nad1B?C) Nuclear (18S) Habitat Humiriaceae TRF (Cuatrecasas 1961; Cronquist 1981) Humiria spp. Anderson 13654 (MICH), Wurdack s.n. (US) AJ235495 L01926 AY674710 AF206930 TRF (Cuatrecasas 1961; Cronquist 1981) Vantanea guianensis Aubl. Pennington 13855 (K) AY788261 Z75679 AY674783 AY674639 TRF (Cuatrecasas 1961; Cronquist 1981) Hypericaceae OT/T (Hutchinson 1973; Robson 1974, 1977, 1981, 1987, 1990) Hypericum spp. Chase 837 (K); Wur- dack D492 (US) AF209602 AF206779 AY674715 AF206934 OT/T (Hutchinson 1973; Robson 1974, 1977, 1981, 1987, 1990) Vismia spp. Miller et al. 9313 (MO); Gustafsson 302 (NY) AY788262 AF518382 AY674784 AF674640 OT/T (Hutchinson 1973; Robson 1974) Irvingiaceae TRF (Harris 1996) Irvingia malayana Oliv. Simpson 2638 (K?) AF209605 AF123278 AY674717 AF206939 TRF (Harris 1996) Klainedoxa gabonen- sis Pierre Bradley et al. 1092 (MO) AY788232 AY663630 AY674720 AY674610 TRF (Harris 1996) Ixonanthaceaec TRF (Kool 1988) Ixonanthes chinensis Champ. Chen 9812087 (K?) AY788230 AY788179 AY674718 TRF (Kool 1988) Ochthocosmus longi- pedicellatus Stey- erm. & Luteyn Berry 6561 (MO) AY674621 TRF (Kool 1988) Lacistemataceae TRF (Adams 1972; Sleumer 1980; Cronquist 1981; Takhtajan 1997) Lacistema aggrega- tum Rusby Pennington et al. 583 (K) AF206949 AF206787 AY674722 AF206949 TRF (Adams 1972; Sleumer 1980; Cronquist 1981; Takhtajan 1997) Lepidobotryaceaea TRF (Hammel and Zamora 1993; Takhtajan 1997) Ruptiliocarpon cara- colito Hammel & Zamora Pennington & Zamori 631 (K); Hammel 19102 (MO) AY788275 AJ402997 AY674765 AY788166 TRF (Hammel and Zamora 1993; Takhtajan 1997) E52 Table B1 (Continued) Taxon Voucher Plastid (atpB) Plastid (rbcL) Mitochondrial (nad1B?C) Nuclear (18S) Habitat Linaceae OT/T and TRF (Rog- ers and Mildner 1976; Cronquist 1981; Van Hooren and Nooteboom 1988b) Durandea pentagyna K. Schum. Takeuchi 7103 (MO) AY788218 AY788173 AY674688 AY788150 TRF (Van Hooren and Nooteboom 1988b) Linum spp. Chase 111 (NCU; Chase 478 (K); Nickrent 2900 (SIU) L24401 AY380351 AY674726 L24401 OT/T (Rogers 1969; Rogers and Mildner 1976; Cronquist 1981) Reinwardtia indica Dumort. Chase 230 (NCU) AJ235577 L13188 AY674762 AF207005 OT/T (Robertson 1971; Cronquist 1981) Lophopyxidaceae TRF (Hutchinson 1973; Takhtajan 1997) Lophopyxis maingayi Hook. f. Adelbai P-10203 (US) AY788235 AY663643 AY674728 AY674614 TRF (Hutchinson 1973; Takhtajan 1997) Malesherbiaceae OT/T (Cronquist 1981; Gentry 1996; Gengler-Novak 2002) Malesherbia lineari- folia Poir. Chase 609 (K) AF209622 AF206792 AY674731 AF206957 OT/T (Cronquist 1981; Gentry 1996; Gengler-Novak 2002) Malpighiaceae OT/T and TRF (Cronquist 1981) (SRFG) Acridocarpus natali- tius Adr. Juss. Goldblatt s.n. (PRE) AY788200 AF344455 AY674644 AY674573 OT/T and TRF (Davis et al. 2002b) Byrsonima crassifolia (L.) H.B.K. FTG 81-680A (MICH) AY788206 L01892 AY674658 AY674579 OT/T (Anderson 2001) Dicella nucifera Chodat Anderson 13607 (MICH) AJ235453 AJ235802 AY674681 AF206901 OT/T and TRF (Chase 1981; Gentry 1996) Thryallis longifolia Mart. Anderson 13657 (MICH) AY788258 AF344516 AY674778 AY674638 OT/T (Anderson 1995) E53 Table B1 (Continued) Taxon Voucher Plastid (atpB) Plastid (rbcL) Mitochondrial (nad1B?C) Nuclear (18S) Habitat Medusagynaceae TRF (Robinson et al. 1989; Fay et al. 1997) Medusagyne opposi- tifolia Baker Fay s.n. (K) [Kew 1981?2059] AJ235530 Z75670 AY674733 AF206959 TRF (Robinson et al. 1989; Fay et al. 1997) Ochnaceae s.s.b OT/T and TRF (Kanis 1968, 1971; Cron- quist 1981; Amaral 1991) Cespedesia bonplan- dii Goudot Chase 1325 (K) AY788208 AJ420168 AY674667 AY674583 TRF (Kanis 1971; Amaral 1991) Ochna multiflora DC. Chase 229 (NCU) AJ235546 Z75273 AY788280 AF206974 OT/T and TRF (Kanis 1968, 1971; Amaral 1991) Ochna sp. Davis 31-01 (A) AY788240 AY380354 AY674739 AY674620 OT/T and TRF (Kanis 1968, 1971; Amaral 1991) Oxalidaceaea OT/T and TRF (Rob- ertson 1975) Averrhoa carambola L. Chase 214 (NCU) AJ235404 L14692 AY674651 AF206859 TRF (Veldkamp 1971; Robertson 1975) Dapania racemosa Korth. Ambri & Arifin 1014 (K) AY788266 AY788196 AY674678 AY674590 TRF (Veldkamp 1967, 1971; Robertson 1975) Pandaceae TRF (Forman 1966, 1971; Airy Shaw 1975; Cronquist 1981; Webster 1994b) Galearia filiformis (Blume) Boerl. Chase 1334 (K) AY788222 AJ418818 AY674698 AY674598 TRF (Forman 1966, 1971; Airy Shaw 1975; Webster 1994b) Microdesmis spp. Gereau et al. 5654 (MO); Cheek 5986 (K) AY788238 AJ402975; AJ403029 AY674737 AY674618 TRF (Le?onard 1961; Forman 1966; Airy Shaw 1975; Webster 1994b) Panda oleosa Pierre. Schmidt et al. 2048 (MO) AY788242 AY663644 AY788281 AY788153 TRF (Forman 1966, 1971; Webster 1994b) Passifloraceae s.s.b OT/T and TRF (Killip 1938; Brizicky 1961a; de Wilde 1971, 1972; Holm- Nielsen et al. 1988; MacDougal 1994) E54 Table B1 (Continued) Taxon Voucher Plastid (atpB) Plastid (rbcL) Mitochondrial (nad1B?C) Nuclear (18S) Habitat Paropsia madagas- cariensis (Baill.) H. Perrier Zyhra 949 (WIS) AF209645 AF206802 AY674744 AF206980 OT/T and TRF (Sleu- mer 1954; de Wilde 1975) Passiflora spp. Chase 2475 (K); MO 876630 AJ235553 L01940 AY674745 AF206981 OT/T and TRF (Killip 1938; Brizicky 1961a; de Wilde 1972; Holm-Nielsen et al. 1988; Mac- Dougal 1994) Peridiscaceaea TRF (Sandwith 1962) Peridiscus lucidus Benth. Soares 205 (CEPEC) AY372816 AY380356 AY674748 AY372815 TRF (Sandwith 1962) Phyllanthaceae OT/T and TRF (Airy Shaw 1975; Rad- cliffe-Smith 1987; Webster 1994b; Dorr 1999) Aporosa frutescens Blume Chase 1251 (K) AY788201 Z75674 AY674647 AY788147 TRF (Airy Shaw 1975; Webster 1994b) Bischofia javanica Blume Levin 2200 (SD) AY788205 AY663571 AY674654 AY674578 TRF (Webster 1994b) Croizatia spp. Berry et al. 4121 (US); Dorr & Yustiz 8555 (US) AY788213 AY663579 AY674674 AY788148 TRF (Webster 1994b; Dorr 1999) Heywoodia lucens Sim Saufferer et al. 1544 (US) AY788224 AY663587 AY674704 AY674602 OT/T and TRF (Rad- cliffe-Smith 1987) Phyllanthus epiphyl- lanthus L. Wurdack D56 (US) AY788246 AY380358 AY674749 AY674627 OT/T and TRF (Web- ster 1994b) Picrodendraceae OT/T and TRF (Web- ster 1994b) Androstachys john- sonii Prain Chase 1904 (K) AF209527 AJ402922 AY674646 AF206848 OT/T (Webster 1994b) Austrobuxus mega- carpus P. I. Forster Forster 21239 (BRI) AY788204 AY380343 AY788276 AY674576 TRF (Webster 1994b) Micrantheum hex- andrum Hook. f. Chase 1940 (K) AY788237 AJ418816 AY674736 AY674617 TRF (Bentham 1873; Webster 1994b) Petalostigma pubes- cens Domin Clifford s.n. (BRI) AY788245 AY380357 AY788283 AY674626 OT/T (Airy Shaw 1980b) Podocalyx loranthoi- des Klotzsch Berry & Aymard 7226 (MO) AY788248 AY663647 AY674752 AY674629 TRF (Webster 1994b) Tetracoccus dioicus Parry Levin 2202 (DUKE) AY788256 AY788190 AY674774 AY788158 OT/T (Webster 1994b) E55 Table B1 (Continued) Taxon Voucher Plastid (atpB) Plastid (rbcL) Mitochondrial (nad1B?C) Nuclear (18S) Habitat Podostemaceae OT/T (van Royen 1953, 1954; Graham and Wood 1975; Cronquist 1981) Podostemum cerato- phyllum Michx. Cusick 30042 (NY); Horn & Wurdack s.n. (DUKE) AY788249 AJ418819 AY674754 AY788155 OT/T (van Royen 1953, 1954; Graham and Wood 1975; Cronquist 1981) Putranjivaceaec TRF (Airy Shaw 1975, 1980a; Webster 1994b) Drypetes diversifolia Krug & Urb. Wurdack D57 (US) AY674687 TRF (Airy Shaw 1975, 1980a; Webster 1994b) Putranjiva roxbur- ghii Wall. FTG-83463A AF209578 M95757 U42534 TRF (Airy Shaw 1975, 1980a; Webster 1994b) Quiinaceae TRF (Cronquist 1981; Schneider et al. 2002) Quiina pteridophylla (Radlk.) Pires Pires S. A. (CPATU)d AF209664 Z75689 AY674759 AF207003 TRF (Cronquist 1981; Schneider et al. 2002) Rhizophoraceae s.s.b TRF (Cronquist 1981; Juncosa and Tom- linson 1988a, 1988b; Schwarzbach and Ricklefs 2000) Bruguiera gymnor- hiza Lam. Chase 12838 (K) AF209547 AF127693 AY674656 AF206875 TRF (Cronquist 1981; Juncosa and Tom- linson 1988a, 1988b; Schwarzbach and Ricklefs 2000) Carallia brachiata (Lour.) Merr. Chase 2151 (K) AJ235425 AF206744 AY674660 AF530810 TRF (Cronquist 1981; Juncosa and Tom- linson 1988a, 1988b; Schwarzbach and Ricklefs 2000) Paradrypetes subin- tegrifolia G. A. Levine Acevedo-Rdgz. & Ceden?o 7560 (US) AY788243 AY788184 AY788282 AY788154 TRF (Levin 1992; Webster 1994b) Salicaceae OT/T and TRF (Cronquist 1981) (SRFG) Abatia parviflora Ruiz & Pav. Pennington 676 (K) AF209519 AF206726 AY674641 AF206836 OT/T (Sleumer 1980) Table B1 (Continued) Taxon Voucher Plastid (atpB) Plastid (rbcL) Mitochondrial (nad1B?C) Nuclear (18S) Habitat Casearia spp. Chase 337 (K); Litt 17 (NY); Alford 26 (BH) AF209557 AF206746 AY674663 AF206882 OT/T and TRF (Sleu- mer 1954, 1980) Dovyalis rhamnoides Burch. ex Harv. & Sond. Chase 271 (NCU) AY788217 Z75677 AY674686 AY674592 TRF (Sleumer 1975) Flacourtia jangomas Steud. Chase 2150 (K) AF209588 AF206768 AY674697 AF206912 OT/T and TRF (Sleu- mer 1954, 1975) Idesia polycarpa Maxim. Chase 561 (K); Wur- dack D22 (US) AF209604 AF206781 AY674716 AF206936 OT/T (Mabberley 1997) Lunania sp. Alford 69 (BH) AY788236 AY788182 AY674729 AY674615 OT/T and TRF (Sleu- mer 1980) Poliothyrsis sp. Alford 44 (BH) AY788251 AY788186 AY674756 AY674631 OT/T (Mabberly 1997) Populus spp. Chase 996 (K); Soltis & Soltis 2552 (WS) AF209658 AJ418836 AY674757 AF206999 OT/T (Cronquist 1981; Mabberley 1997) Prockia sp. Alford 85 (BH) AY788252 AY788187 AY674758 AY674632 OT/T and TRF (Sleu- mer 1980) Salix reticulata L. Chase 840 (K) AJ235590 AJ235793 AY674767 AF207011 OT/T (Cronquist 1981) Scyphostegia bor- neensis Stapf Beaman 911 (BH) AY788254 AJ403000 AY674770 AY674635 TRF (van Steenis 1957) Trigoniaceae TRF (Cronquist 1981) Trigonia nivea Cambess. Anderson 13656 (MICH) AF209691 AF089761 AY674779 AF207047 TRF (Cronquist 1981) Turneraceae OT/T (Lewis 1954; Brizicky 1961a; Cronquist 1981; Arbo 1987, 1995) Turnera ulmifolia L. Chase 220 (NCU); Wurdack s.n. (US) AJ235634 Z75691 AY674782 U42817 OT/T (Lewis 1954; Brizicky 1961a; Cronquist 1981; Arbo 1987, 1995) Violaceae OT/T and TRF (Bri- zicky 1961b; Cron- quist 1981; Hekking 1988) Hybanthus sp. Alford 89 (BH) AY788229 AY788178 AY674712 AY674607 OT/T and TRF (Bri- zicky 1961b) Hymenanthera al- pina Oliv. Chase 501 (K) AJ235499 Z75692 AY674713 AF206933 OT/T (Brizicky 1961b; Cronquist 1981; Hekking 1988) Leonia glycycarpa Ruiz. & Pav. Pennington 13852 (K) AY788234 Z75693 AY674725 AY674613 TRF (Brizicky 1961b; Cronquist 1981; Hekking 1988) Dating the Origin of Tropical Rain Forests E57 Table B1 (Continued) Taxon Voucher Plastid (atpB) Plastid (rbcL) Mitochondrial (nad1B?C) Nuclear (18S) Habitat Incertae sedis (Centroplacaceae) Centroplacus glauci- nus Pierre White 128, ser. 1 (MO) AY788207 AY663646 AY788277 AY674582 TRF (Webster 1994a) Note: Families follow APG (2003; but see footnoted modifications), and herbarium acronyms follow Holmgren et al. (1990). Primary habitat shown with source in parentheses: rain forest; tropical/temperate forest. references for genera; stricto.TRF p tropical OT/Tp open SRFG p see s.s. p sensu a Indicates outgroups. b Several small segregate families sampled were maintained for the family-level scoring of habitat following the strict circumscriptions of APG (2003). For example, representatives of Chrysobalanaceae, Dichapetalaceae, Euphroniaceae, and Trigoniaceae were scored separately rather than as Chrysobalanceae sensu lato. Other similar strict circumscriptions were followed for Ochnaceae, Passifloraceae, and Rhizophoraceae. Peridiscaceae have been excluded from Malpighiales following Davis and Chase (2004). Recent molecular evidence indicates that holoparasitic Rafflesiaceae s.s. are members of Malpighiales (Barkman et al. 2004; Davis and Wurdack 2004). They were not included in our data sets due to missing data. 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Ixonanthaceae 105.9 109.2 114.9 97.5 98.7 102.0 9. Phyllanthaceae 105.8 108.1 114.0 95.6 97.1 101.9 10. Picrodendraceae 105.8 108.1 114.0 95.6 97.1 101.9 11. Passifloraceae s.l. 103.7 108.1 113.9 96.5 96.9 102.1 12. Violaceae 102.4 105.7 112.3 94.4 94.8 99.7 13. Irvingiaceae 102.5 105.0 112.5 93.3 94.5 98.4 14. Linaceae 102.5 105.0 112.5 93.3 94.5 98.4 15. Achariaceae 98.1 104.2 108.1 90.9 93.4 96.1 16. Goupiaceae 98.1 104.2 108.1 90.9 93.4 96.1 17. Centroplacus 96.6 101.8 109.6 88.1 91.0 97.1 18. Ctenolophonaceae 96.6 101.8 109.6 88.1 91.0 97.1 19. Lacistemataceae 96.1 99.8 107.7 89.0 90.1 95.9 20. Salicaceae 96.1 99.8 107.7 89.0 90.1 95.9 21. Balanopaceae 95.5 99.6 106.2 88.5 90.2 94.9 22. Chrysobalanceae s.l. 95.5 99.6 106.2 88.5 90.2 94.9 23. Elatinaceae 89.0 98.2 113.2 85.0 89.1 99.6 24. Malpighiaceae 89.0 98.2 113.2 85.0 89.1 99.6 25. Clusiaceae 92.4 94.1 103.7 87.1 89.0 94.7 26. Bonnetiaceae 85.9 88.5 97.2 83.0 83.8 88.3 27. Lophopyxidaceae 82.9 86.7 97.0 74.8 77.8 85.2 28. Putranjivaceae 82.9 86.7 97.0 74.8 77.8 85.2 29. Hypericaceae 68.9 76.4 82.4 66.4 72.4 73.9 30. Podostemaceae 68.9 76.4 82.4 66.4 72.4 73.9 Note: Optimal age estimates, with minimum and maximum error estimates, for major Malpighiales clades (i.e., families [stem group], except for Centroplacus). Sensu lato (s.l.) designations follow APG (2003). See figure C1 for full penalized likelihood chronogram and figure C2 for Bayesian tree with likelihood branch lengths. E61 Figure C1: Complete 124-taxon penalized likelihood chronogram (from main text, fig. 1). Numbered nodes on chronogram correspond to numbered clades shown in table C1. The K/T boundary (?65 Ma) is marked with a dashed line. 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