Journal of Fish Biology (2008) 72, 418–434 doi:10.1111/j.1095-8649.2007.01732.x, available online at http://www.blackwell-synergy.com History repeated: recent and historical mitochondrial introgression between the current darter Etheostoma uniporum and rainbow darter Etheostoma caeruleum (Teleostei: Percidae) J. M. R AY *, N. J. L ANG †, R. M. W OOD AND R. L. M AYDEN Department of Biology, Saint Louis University, 3507 Laclede Avenue, St Louis, MO 63103, U.S.A. (Received 6 July 2007, Accepted 10 October 2007) Incongruence between recognized taxonomy and phylogenetic relationships between two species from a diverse clade (Percidae: Etheostomatinae) of stream fishes was found in a mitochondrial (mt) DNA gene tree. Two darters in subgenus Oligocephalus, Etheostoma uniporum current darter and Etheostoma caeruleum rainbow darter were sampled throughout their sympatric distribution in the Ozark Highlands of the central United States. Sequences from cytochrome (cyt) b and the first intron of the nuclear marker S7 were analysed separately using maximum parsimony and Bayesian methods. Cyt b recovered both species as polyphyletic; E. uniporum haplotypes were interspersed within E. caeruleum. However, both species were monophyletic and non-sister taxa based on S7. The cyt b gene tree pattern is caused by introgressive hybridization resulting in the mtDNA replacement of E. uniporum haplotypes by those of E. caeruleum. Some E. uniporum haplotypes are shared with geographically proximate E. caeruleum, and this is consistent with recent hybridization, while other E. uniporum haplotypes indicate historical sorting of introgressed lineages. The mechanism of introgression is likely asymmetric sneaking behaviour by male E. uniporum, a mating tactic observed in related species. MtDNA replacement may have occurred in E. uniporum due to drift fixation in a historically small female effective population. Additional evidence for darter hybridization will likely be discovered in future molecular genetic surveys of the nearly 200 species in eastern # 2008 The Authors North America. Journal compilation # 2008 The Fisheries Society of the British Isles Key words: darters; Etheostoma; hybridization; introgression; mitochondrial DNA replacement; polyphyly. INTRODUCTION As the size and taxonomic breadth of molecular datasets grow, species level polyphyly is an increasingly encountered pattern in mitochondrial (mt) DNA gene trees. Distinguishing among alternative explanations for polyphyly can *Author to whom correspondence should be addressed at present address: Department of Biological Sciences, The University of Tennessee at Martin, 574 University Street, Martin, TN 38238, U.S.A. Tel.: þ731 881 7181; fax: þ731 881 7187; email: [email protected] †Present address: Department of Zoology, Oklahoma State University, 430 Life Sciences West, Stillwater, OK 74078, U.S.A. 418 2008 The Authors Journal compilation # 2008 The Fisheries Society of the British Isles # INTROGRESSION IN ETHEOSTOMA DARTERS 419 be difficult since processes such as incomplete lineage sorting and hybridization may produce nearly identical mtDNA patterns in closely related species (Funk & Omland, 2003). Examining the geographical distribution of haplotypes may be useful in detecting hybridization since the clearest signature of hybridization is the sharing of haplotypes between sympatric species (Hare & Avise, 1998; Masta et al., 2002). However, if introgression has occurred and haplotypes have sorted over time (lineage sorting), this phenomenon will be difficult to detect with mtDNA data alone (Moore, 1995; Funk & Omland, 2003). Comparisons with morphology or nuclear data may provide additional insights on mtDNA gene tree polyphyly (Zink, 1994; McMillan & Palumbi, 1995; Redenbach & Taylor, 2002). Since hybridization is not always detectable via morphological examination (Rhymer & Simberloff, 1996; Sang & Zhong, 2000), molecular data may provide insights that might otherwise go undetected (Avise, 2004). Hybridizations between vertebrate species are most common between freshwater fishes with external fertilization and have been documented in a variety of ecological settings (Hubbs, 1955; Schwartz, 1972). Hybridization often follows human-mediated introductions of non-native species and can reduce or eliminate the genetic integrity of endemics (Allendorf & Leary, 1988; Echelle & Connor, 1989). Hybridization may also occur naturally in altered environments (e.g. glaciated regions) or in areas that are seemingly undisturbed. In areas affected by glaciation, introgression between currently allopatric species may be due to mitochondrial replacement (Bernatchez et al., 1995; Wilson & Bernatchez, 1998; Gerber et al., 2001; Lu et al., 2001; Redenbach & Taylor, 2002; Gum et al., 2005). Molecular studies of fishes have also documented recent hybridization between sympatric species in a variety of other situations (Avise, 2004). Streams of eastern North America support one of the most diverse temperate fish faunas in the world. Darters (Percidae: Etheostomatinae) represent approximately one-fifth of this diversity with 173 described species in 2000 (Page, 2000; Warren et al., 2000). Darters exhibit a range of behavioural and lifehistory adaptations, and although some are widespread and abundant, others are rare and endemic to single rivers (Page, 1983). The relationships among many darter species and subgenera are not well resolved, but hypothesized sister taxa are frequently allopatric (Ceas & Page, 1997; Page et al., 2003). Overlapping ranges of many non-sister species, however, provide the potential for interspecific hybridization. Surprisingly, darter hybridization in nature has not been widely investigated with molecular methods (Scribner et al., 2000), despite extensive laboratory studies of this phenomenon. Laboratory-produced hybrids are often viable (Hubbs & Strawn, 1957; Hubbs, 1958, 1967; Linder, 1958), even among species pairs exhibiting sexual isolation (Mendelson, 2003b). Additionally, darters exhibiting intermediate morphological characteristics (presumably, F1 individuals) have been found in nature (Hubbs & Laritz, 1961; Page, 1976; Mayden & Burr, 1980; Hubbs et al., 1988). The current darter Etheostoma uniporum Distler and the rainbow darter Etheostoma caeruleum Storer are both members of subgenus Oligocephalus (Bailey & Etnier, 1988). Within the subgenus, E. uniporum is a member of the Etheostoma spectabile (Agassiz) species group and is endemic to portions # 2008 The Authors Journal compilation # 2008 The Fisheries Society of the British Isles, Journal of Fish Biology 2008, 72, 418–434 420 J. M. RAY ET AL. of the Black River system (White River drainage–Mississippi River basin), including the Current and Spring rivers in the Ozark Highlands of the central United States (Distler, 1968; Ceas & Page, 1997; Fig. 1). Other members of the E. spectabile species group occur in adjacent streams, and the distribution of the entire E. spectabile species group largely overlaps with E. caeruleum in the eastern United States. Etheostoma caeruleum is distributed in much of the eastern North America and occurs in tributaries to the Great Lakes, Hudson Bay, Mississippi and Potomac rivers [Page, 1983; Fig. 1 (inset)]. Both E. uniporum and E. caeruleum are widespread in upland streams of the Black River system and were present in 19 and 51% of 461 total collections, respectively, from this system (Missouri Department of Conservation, unpubl. data). These species may be collected at the same locality, although E. uniporum more often occurs in headwater streams, while E. caeruleum is found in larger, permanent stream reaches (Pflieger, 1997; pers. obs.). Populations of both species in this system are fragmented by intervening lowland and big river habitats (Pflieger, 1997). These species overlap in several meristic counts, but are diagnosable by pigmentation patterns and infraorbital canal characteristics (complete in E. caeruleum and incomplete in E. uniporum), and are unambiguously identifiable (Page, 1983; Ceas & Page, 1997; Pflieger, 1997). While no comparisons of reproductive habits have been made between E. uniporum and E. caeruleum, Winn (1958) found no difference in migration, FIG. 1. Map showing sample localities (1–35) for Etheostoma species from streams in the Ozark Highlands of the central United States. The shaded area represents the distribution of Etheostoma uniporum. Sample localities correspond to Fig. 2 and Table I. Inset: Distribution of Etheostoma caeruleum (grey) including area of sympatry with Etheostoma uniporum ( ). , Etheostoma caeruleum; , Etheostoma uniporum; , Etheostoma caeruleum and E. uniporum and , Etheostoma spectabile; R., River. Journal compilation # # 2008 The Authors 2008 The Fisheries Society of the British Isles, Journal of Fish Biology 2008, 72, 418–434 INTROGRESSION IN ETHEOSTOMA DARTERS 421 territorial or spawning behaviour between E. caeruleum and E. spectabile. However, E. caeruleum and E. spectabile may segregate by water depth, velocity and substrate (Winn, 1958; Page, 1983, 2000). Breeding males of both species actively defend shifting territories in riffles against conspecifics and spawn when a female enters their territory and buries her ventral half in the substrate. Eggs are externally fertilized and left unguarded in the substrate (Winn, 1958). Hybridization in nature has been reported between E. caeruleum and E. spectabile (Distler, 1968). Using allozymes, Martin & Richmond (1973) found that presumed E. caeruleum E. spectabile hybrids did not have genotypes consistent with a hybrid origin and suggested that F1 hybrids must be rare in nature. Spawning occurred in laboratory experiments, in which F1 hybrids were produced in tanks containing only reciprocal sexes of E. caeruleum and E. spectabile (Distler, 1968). Hubbs (1967) found no differences in survival of F1 offspring between crosses of E. caeruleum and E. spectabile v. conspecific crosses. From both laboratory and field observations, Distler (1968) hypothesized that the evolution of the E. spectabile species group (although not specifically of E. uniporum) was influenced by hybridization with E. caeruleum or Etheostoma whipplei (Girard). In molecular systematic studies of the subgenus Oligocephalus, a discrete inconsistency was discovered between recognized taxonomy and relationships suggested by mtDNA gene trees (Lang & Mayden, 2007). This inconsistency involved the recovery of E. uniporum (a recognized E. spectabile species group member) with E. caeruleum. In this study, an in-depth investigation of potential hybridization and introgression between E. uniporum and E. caeruleum from throughout their sympatric range is reported. Sequences of the mitochondrial cytochrome (cyt) b gene and first intron of the nuclear ribosomal protein S7 were used. The objectives of this study were to characterize the cyt b and S7 tree patterns of E. uniporum and E. caeruleum to test whether introgression explains the incongruence between taxonomy and gene-based relationships observed by Lang & Mayden (2007). MATERIALS AND METHODS STUDY SPECIES Etheostoma uniporum and E. caeruleum were comprehensively sampled throughout their sympatric distribution (Fig. 1 and Table I). Within the Black River system, E. uniporum and E. caeruleum shared six collection localities. Etheostoma caeruleum was recorded separately at 12 sites, and E. uniporum at seven sites. Etheostoma caeruleum were sampled at 13 additional localities outside the range of E. uniporum. Specimens of focal taxa were independently identified by two researchers using standard meristic counts, pigmentation pattern, characteristics and completeness of infraorbital canals (Page, 1983; Ceas & Page, 1997; Pflieger, 1997). Allopatric members of the E. spectabile species group were sampled from four adjacent Ozark streams systems, including the upper Black River proper (Etheostoma burri Ceas & Page), Strawberry River (Etheostoma fragi Distler), White River proper (E. spectabile) and St Francis River (E. spectabile). Other species in subgenus Oligocephalus were sampled from outside the study area and included Etheostoma collettei Birdsong & Knapp, Etheostoma radiosum (Hubbs & Black) and E. whipplei. Percina caprodes (Rafinesque) was designated as the outgroup taxon. Specimen vouchers were # 2008 The Authors Journal compilation # 2008 The Fisheries Society of the British Isles, Journal of Fish Biology 2008, 72, 418–434 Etheostoma caeruleum Meramec River (1) St Francis River (2) Upper Black River (4) Upper Black River (5) Cane Creek (7) Barren Fork (10) Jacks Fork (11) Jacks Fork (12) Little Shawnee Creek (13) Rocky Creek (14) Current River (15) Current River (16) Current River (17) Little Black River (19) Fourche Creek (20) Eleven Point River (22) Eleven Point River (23) Frederick Creek (25) Spring River (26) S. Fork Spring River (27) Spring River (28) Spring River (29) Strawberry River (33) White River (34) Stream (locality) 024, 025 020, 021 069 070 164 072 160 163 184 169, 170 161 185, 186 172, 174 165, 171 071, 173 157 168 166 167 162 006, 031 100, 101 098, 099 028, 029 Specimens D D D D D D D D F F D F D, F D D B B B B B B B C H cyt b Clades Journal compilation # J J J J J J J J J J J S7 STL STL STL STL STL STL STL STL STL STL STL STL STL STL STL STL STL STL STL STL STL STL STL STL 8.12 1026.01 173.01 6.11 1060.01 1034.01 246.01 1059.01 1068.02 1065.01 1057.01 32.17 832.11 1061.01 79.04, 1066.01 247.01 1064.01 1062.01 1063.01 1058.01 1017.01 382.01 384.04 78.11 Museum accession DQ465090–91/EU046652 DQ465086–87/EU046649 DQ465129/EU046655 DQ465130 DQ465210 DQ465132/EU046657 DQ465206 DQ465209 EU046707/EU046667 EU046704–05/EU046664–65 DQ465207 EU046702–03/EU046668–69 EU046706, DQ465217/EU046666 DQ465211, DQ465215 DQ465131, DQ465216/EU046656 DQ465203 DQ465214 DQ465212 DQ465213 DQ465208 DQ465076, DQ465096 DQ465156–57/EU046659 DQ465154–55/EU046658 DQ465094–95/EU046653 GenBank accession number (cyt b/S7) TABLE I. Specimen information for darters sampled in this study. Streams and localities correspond to those in Fig. 1; specimens and clades correspond to those in Fig. 2 422 J. M. RAY ET AL. # 2008 The Authors 2008 The Fisheries Society of the British Isles, Journal of Fish Biology 2008, 72, 418–434 Spring River (30) Frederick Creek (25) Spring River (26) 435 005, 009 010, 016, 098 001, 002 179 007 018, 078 008 013 185 006, 011 Barren Fork (10) Jacks Fork (11) Little Shawnee Creek (13) Little Black River (18) Fourche Creek (20) Tennessee Creek (21) Eleven Point River (22) Hurricane Creek (24) 058 179 017 045 132 134 153 155 51 014, 617 017, 175 057, 033, 016, 037, 131, 133, 152, 154, Specimens Little Red River (35) Upper White River Gasconade River Otter Creek Sandusky River Tennessee River Green River Osage River Total E. uniporum Cane Creek (8) Pigeon Creek (9) Stream (locality) A A A, B A D A G D D A A, B E D H H N. Ozarks Upper Mississippi Eastern U.S.A. Eastern U.S.A. Eastern U.S.A. N. Ozarks cyt b Clades I I I I I I I I I I I J J J J J J J J S7 1034.02 246.02 1068.01 61.04 1066.02 833.04 247.02 1067.01 STL 383.04 STL 1062.01 STL 180.09, 1063.02 STL STL STL STL STL STL STL STL STL 831.04 STL 243.01 STL 1019.01 STL 1013.01 STL 64.04 JFBM 31430 STL 1051.01 STL 1052.01 STL 1020.01, 1024.01 STL 1055.01 Museum accession TABLE I. Continued EU046689, EU046700/EU046640 EU046692, EU046696/EU046643, EU046646 EU046678–79/EU046632 EU046697/EU046647 EU046682/EU046634 EU046693–94/EU046644 EU046683/EU046635 EU046688/EU046639 EU046698 EU046681, EU046686/EU046633, EU046638 EU046680, EU046684/EU046636 EU046685, EU046691, EU046695/ EU046637, EU046642 EU046645 EU046699 DQ465118–19/EU046654 DQ465098, DQ465222/EU046650 DQ465083–84/EU046648 DQ465101, DQ465109/EU046651 DQ465181–82/EU046660 DQ465183–84/EU046661 DQ465198–99/EU046662 DQ465200–01/EU046663 GenBank accession number (cyt b/S7) INTROGRESSION IN ETHEOSTOMA DARTERS 423 # 2008 The Authors Journal compilation # 2008 The Fisheries Society of the British Isles, Journal of Fish Biology 2008, 72, 418–434 Journal compilation # STL 1069.01 STL 183.01 STL 1070.01 KU 29327 STL 174.01 STL 1069.02 STL 195.06 1 2 1 1 2 1 STL 835.02 Museum accession 2 I S7 UAIC 11396.04 A cyt b 1 015, 618 23 Specimens EU046670/EU046624 DQ465069, EU046674/EU046626 DQ465068/EU046628 EU046673/EU046630 DQ465070, EU046675/EU046625 EU046672/EU046631 EU046676–77/EU046627 EU046671/EU046629 EU046690, EU046701/EU046641 GenBank accession number (cyt b/S7) JFBM, the Bell Museum of Natural History; KU, the University of Kansas Museum of Natural History; STL, Saint Louis University; UAIC, the University of Alabama Ichthyological Collection. Flat Creek (31) Total E. burri Upper Black River (6) E. collettei Red River drainage E. fragi Strawberry River (32) E. radiosum Ouachita River drainage E. spectabile White River drainage St Francis River (3) E. whipplei Red River drainage Percina caprodes Arkansas River drainage Stream (locality) Clades TABLE I. Continued 424 J. M. RAY ET AL. # 2008 The Authors 2008 The Fisheries Society of the British Isles, Journal of Fish Biology 2008, 72, 418–434 INTROGRESSION IN ETHEOSTOMA DARTERS 425 deposited at Saint Louis University, the University of Kansas Museum of Natural History, the University of Alabama Ichthyological Collection and the Bell Museum of Natural History, and sequences were deposited in GenBank (Table I). MOLECULAR METHODS Genomic DNA was extracted from specimens with a QIAGEN DNeasy Tissue Kit (QIAGEN, Inc., Valencia, CA, U.S.A.). Cyt b was polymerase chain reaction (PCR) amplified with flanking primers L14724 and H15915 (Schmidt & Gold, 1993). PCR reactions included a total volume of 50 ml. Each reaction was conducted with 30 cycles of 96° C, 1 min; 48° C, 1 min and 72° C, 2 min. The S7 marker was PCR amplified with flanking primers S7RPEX1F and S7RPEX2R (Chow & Hazama, 1998). PCR reactions consisted of a total volume of 50 ml. Each reaction was conducted with 30 cycles of 96° C, 1 min; 53° C, 1 min; 72° C, 2 min. PCR products were purified with a QIAGEN’s QIAquick Gel Extraction Kit (QIAGEN, Inc.). The light strand of cyt b was sequenced for E. caeruleum in two segments with primer L14724 and an internal forward primer, LECO1 (Ray et al., 2006). Other taxa were sequenced with the PCR primers for both cyt b and S7. Sequencing reactions used a Beckman Coulter DTCS Kit (Beckman Coulter, Inc., Fullerton, CA, U.S.A.) at a total volume of 10 ml for 30 cycles at 96° C, 20 s; 50° C (53° C for S7), 20 s and 60° C, 4 min. Sequences were recorded with a Beckman Coulter CEQ 8000 DNA Analysis System aligned in CLUSTALX 1.8 (Thompson et al., 1997) and edited in MACCLADE 4.0 (Maddison & Maddison, 2000). All individuals were sequenced for cyt b; a sub-set of E. uniporum and E. caeruleum were sequenced for S7 based on the phylogenetic position of their cyt b haplotypes. All cyt b clades were represented by one or more individual in the S7 dataset for each species, and samples not recovered with conspecifics from the same locality in analysis of cyt b were also sequenced for S7. Heterozygosity in S7 sequences was detected with CEQ 8000 under the default heterozygote analysis parameters (Dobbs & Gee, 2002), and all individual heterozygous nucleotide sites were verified by eye. Heterozygous sites appeared in both E. uniporum and E. caeruleum, although only eight of 52 positions were shared among 13 individuals. A sub-set of individuals was cloned and sequenced for each S7 allele, but analyses of the dataset containing individual alleles recovered clades identical to those containing only heterozygous bases. Therefore, only the results of the analyses containing heterozygous sites are presented (Domingues et al., 2005). P H Y L O G E N E T I C A N A L Y SE S A N D G E N E T I C V A R I A T I O N All phylogenetic analyses were performed separately on the cyt b and S7 datasets. Maximum parsimony analysis was run in PAUP* 4.0b10 (Swofford, 2003) by heuristic search with 1000 replicates of random addition sequence and tree-bisectionreconnection (TBR) branch swapping. Nodal support was calculated with 1000 bootstrap (Felsenstein, 1985) replicates in a full heuristic search with TBR branch swapping. MRMODELTEST 2.2 (Nylander, 2004) was used to select the best-fit model of DNA sequence evolution for each of the three codon positions in cyt b sequences; these models were used in subsequent Bayesian analysis. Bayesian analysis was conducted in MRBAYES 3.1 (Huelsenbeck & Ronquist, 2001; Ronquist & Huelsenbeck, 2003). Four independent runs were each conducted for six million generations with a variable rate parameter, with other parameters set on default. Trees were sampled every 1000 generations, with posterior probability and branch length values saved to the output file. The burn-in period was determined by graphing the log-likelihood scores against generation time, and trees generated before the burn-in were discarded. Each Bayesian run was examined to ensure that independent runs produced comparable topologies and posterior probabilities. Nodal support was calculated using mean posterior probability from each run after discarding burn-in trees. From these analyses, a 50% majority-rule consensus phylogram was generated for cyt b and S7. # 2008 The Authors Journal compilation # 2008 The Fisheries Society of the British Isles, Journal of Fish Biology 2008, 72, 418–434 426 J. M. RAY ET AL. Per cent nucleotide sequence divergence between individuals was calculated using uncorrected (p) distances in MEGA 3.0 (Kumar et al., 2004). Clades for the cyt b and S7 datasets were determined based on monophyletic groups recovered in all analyses and geographic distribution of samples. Divergences between clades were corrected for within-group variation in MEGA. RESULTS M I T O C HO N D R I A L D A T A Complete cyt b sequences (1140 bp) were generated for 85 individuals of Etheostoma and Percina: 51 E. caeruleum, 23 E. uniporum, two each of E. collettei, E. radiosum, E. spectabile, E. whipplei, and one each of E. burri, E. fragi and P. caprodes with 60 haplotypes recovered (Table I). A total of 750 (66%) nucleotide sites were constant, and 339 (30%) were parsimony informative; 90% of parsimony-informative characters occurred in the third codon position. Maximum parsimony analysis produced 289 equally parsimonious trees with 1102 steps. The best-fit model of sequence evolution for each codon position was first: HKYþ I þ G, second: GTRþ I, third: GTRþ I þ G based on the Akaike information criteria (AIC). Bayesian analyses reached stationarity after c. 100 000 generations; trees from the first 150 000 generations were discarded as burn-in, leaving 5850 trees for phylogeny estimation. Both Bayesian and parsimony analyses recovered the same monophyletic groups [clades A–H; Fig. 2(a)], which were 14–62% divergent. Phylogenetic analyses recovered both species as polyphyletic; E. uniporum haplotypes were completely interspersed within E. caeruleum [Fig. 2(a)]. Seven individuals of E. uniporum were recovered in clades B and D and were most similar to E. caeruleum from the same stream system (0–088% cyt b sequence divergence). The remaining 16 E. uniporum occurred at multiple positions within the E. caeruleum branches (clades A, E and G) and had sequences 17–35% divergent from E. caeruleum from the Black River system. A single E. caeruleum clade (clade F) from the Current River was basal to other E. caeruleum from streams within the Black River system (29–35% divergent). Etheostoma caeruleum from the upper White and Little Red rivers (clade H) were sister to all other E. caeruleum plus E. uniporum. Allopatric members of the E. spectabile species group were not recovered with E. uniporum and had large corrected cyt b sequence divergence values from this species (13–16%). NUCLEAR DATA S7 sequences were generated for 46 individuals: 22 E. caeruleum, 16 E. uniporum, four other E. spectabile species group members, three additional species of Oligocephalus and P. caprodes. Of 515 nucleotide sites, 398 (77%) were invariant and 72 (14%) were parsimony informative. Heuristic searches with unweighted characters recovered 4003 equally parsimonious trees with 199 steps. The best-fit model of sequence evolution was HKYþ I þ G based on the AIC. The four Bayesian analyses reached stationarity after c. 50 000 generations; trees from the first 100 000 generations were discarded as burn-in, Journal compilation # # 2008 The Authors 2008 The Fisheries Society of the British Isles, Journal of Fish Biology 2008, 72, 418–434 427 INTROGRESSION IN ETHEOSTOMA DARTERS 100 100 100 100 100 81 100 79 0·01 substitutions/site CAP110* Percina caprodes SPE141* Etheostoma spectabile BUR006* [6] E. burri SPE077* [3] E. spectabile FRA100* [32] E. fragi 100 EW01, 02* E. whipplei RAD01*, 02 E. radiosum 100 100 BBC01 E. collettei U002 [10] BBC02* 100 U001* [10] U007* [13] 100/100 U005 [25] U011* [24] CLADE A 100 widespread U009* [25] U435 [30] 78 100 U010* U016* [26] U185 [22] 100 U015* U618 [31] U006* [24] U098* [26] EC006 [28] CLADE B 100 EC031 [28] EC157 [22] Spring R. 100 98 EC100* [29] EC166 [25] system EC101 [29] EC168 [23] 84 EC162 [27] EC167 [26] CLADE C EC098* EC099 [33] Strawberry R. U008* [20] U013* [21] 100 EC020 [2] 100 100 100 EC021 [2] 84 97 EC024* [1] EC025 [1] CLADE D EC069* [4] EC164 [7] Current, EC070 [5] upper Black, St. Francis, EC071* [20] Meramec EC160 [11] rivers EC165 EC171 [19] EC173 [20] U 175* [9] 100 87 U017* [9] EC161 [15] U179* [11] EC174 [17] EC072* [10] EC163 [12] CLADE E 100 U014* U617 [8] Cane Cr. 100 EC170* [14] 52 100 EC169* [14] 77 98 CLADE F EC172* [17] 100 80 Current R. EC186* [16] 97 EC184* [13] EC185* [16] CLADE G U018 [18] 100 Little Black R. 100 U078* [18] EC016 100 Northern Ozarks 100 82 EC017* 56 100 EC037* EC045 Upper Mississippi R. EC154* 100 Northern Ozarks EC155 100 85 100 100 96 100 EC131* EC132 EC152 EC153* EC133* EC134 EC028 [34] EC029* [34] EC033* EC179 EC057* EC058 [35] Eastern US streams CLADE H White, Little Red rivers FIG. 2. (a) Bayesian 50% majority-rule tree from 5850 trees retained after burn-in period based on cytochrome b sequences. Asterisks indicate that the specimen was also sequenced for S7. (b) Bayesian 50% majority-rule tree from 5900 trees retained after burn-in period based on S7 sequences. EC, Etheostoma caeruleum and U, Etheostoma uniporum. Values above branches indicate bootstrap support from parsimony searches and values below branches indicate posterior probabilities. Numbers in brackets that follow sample codes represent localities in Fig. 1 and Table I. leaving 5900 trees for phylogeny estimation. Bayesian analysis [Fig. 2(b)] was consistent with parsimony analysis (not shown) and had greater resolution within each focal species (clades I–J). In contrast to the cyt b trees, both E. uniporum # 2008 The Authors Journal compilation # 2008 The Fisheries Society of the British Isles, Journal of Fish Biology 2008, 72, 418–434 428 J. M. RAY ET AL. and E. caeruleum were monophyletic and non-sister taxa (2–3% divergent) in the S7 tree, as E. uniporum was recovered with other E. spectabile species group members from the Ozark Highlands. Overall, greater interspecific sequence divergences appeared for cyt b (186–0%) than for S7 (99–0%). Intraspecific divergence of E. uniporum and E. caeruleum was also greater for cyt b (54–0 and 75–0%, respectively) than for S7 (23–0 and 44–0%, respectively), indicating a greater substitution rate in cyt b than in S7. DISCUSSION While interspecific hybridization, inadequate phylogenetic information or incomplete lineage sorting may each result in polyphyly (Funk & Omland, 2003), careful consideration of the data suggests that hybridization is the most likely cause for mtDNA polyphyly and has resulted in the replacement of E. uniporum cyt b haplotypes by those of E. caeruleum. Neither incomplete lineage sorting nor inadequate phylogenetic information is a plausible alternative explanation for the observed pattern. The expectation for incomplete lineage sorting is a basal position of haplotypes, not their interspersion (Funk & Omland, 2003). Further, incomplete lineage sorting of S7 sequences would also be expected due to a lower substitution rate, but both species are monophyletic and non-sister taxa based on nuclear data. The phylogenetic pattern of cyt b is also not caused by inadequate phylogenetic information as this marker differentiated E. uniporum and E. caeruleum from all other species sampled and has proven useful in molecular systematic and phylogeographic studies of darters (Kinziger et al., 2001; Switzer & Wood, 2002; Ray et al., 2006). Hybridization, resulting in mtDNA introgression, is interpreted to have caused the observed pattern for two primary reasons. First, all 23 E. uniporum cyt b haplotypes were recovered within E. caeruleum and had sequence divergences from E. caeruleum (0–35%) within the range of intraspecific variation in E. caeruleum clades (maximum corrected value 62%). Second, cyt b haplotypes from the Black River system were shared or nearly identical between E. uniporum and E. caeruleum, and provide the clearest signature of hybridization. Two of six sites where both species were sampled showed signs of recent hybridization. Seven E. uniporum were classified as recent hybrids based on their position in clades B and D and their similarity in cyt b sequences (0–088% divergence) to E. caeruleum from the same clade and stream. As lineages are more likely to be phylogenetically basal as the time since last gene flow increases (Moore, 1995; Funk & Omland, 2003), the other 16 E. uniporum possess introgressed haplotypes that have sorted over time, as evidenced by their phylogenetic position and larger cyt b sequence divergence values (20–35%) relative to E. caeruleum from the Black River system. The interspersion of E. uniporum haplotypes within E. caeruleum may have been caused both by episodes of historical and by more recent introgressive hybridization, and the E. uniporum mitochondrial genome has been completely eliminated and replaced by an E. caeruleum mitochondrial genome. Analyses further suggest that mitochondrial introgression is not strictly unidirectional as six E. caeruleum (clade F) were not recovered with conspecifics from the Current River system Journal compilation # # 2008 The Authors 2008 The Fisheries Society of the British Isles, Journal of Fish Biology 2008, 72, 418–434 INTROGRESSION IN ETHEOSTOMA DARTERS 429 CAP110 Percina caprodes RAD01 Etheostoma radiosum EW02 E. whipplei EC017 EC154 EC170 [14] EC172 [17] EC020 [2] EC100 [29] EC131 EC133 EC024 [1] EC069 [4] CLADE I EC029 [34] EC098 [33] E. caeruleum EC184 [13] EC057 [35] EC185 [16] EC071 [20] EC033 EC072 [10] EC169 [14] EC186 [16] EC037 EC153 BBC02 E. collettei SPE141 E. spectabile BUR006 [6] E. burri SPE077 [3] E. spectabile FRA100 [32] E. fragi U001 [10] U017 [9] U175 [9] U007 [13] U179 [11] U014 [8] U016 [26] U006 [24] U010 [26] U011 [24] U098 [26] U008 [20] U013 [21] U009 [25] U015 [31] U078 [18] 0·005 substitutions/site CLADE J E. uniporum FIG. 2. Continued. (clade D). Clade F may represent a mitochondrial ‘recapture’ caused by hybridization between E. caeruleum males and E. uniporum females. The monophyly of E. uniporum and E. caeruleum based on S7 was concordant with the morphological identification of all individuals and established taxonomy (Distler, 1968; Ceas & Page, 1997), and places E. uniporum with other E. spectabile species group members. This marker clearly establishes incongruence among mtDNA and nuclear sequence data and confirms interspecific hybridization as the mostly likely cause for this discordance. The mechanism for the mitochondrial introgression between E. caeruleum and E. uniporum may be due to interspecific male sneaking behaviour. In # 2008 The Authors Journal compilation # 2008 The Fisheries Society of the British Isles, Journal of Fish Biology 2008, 72, 418–434 430 J. M. RAY ET AL. egg-burying darters like E. uniporum and E. caeruleum, subdominant males may position themselves next to the spawning pair and sneak fertilization or sneak spawning while dominant males are engaged in antagonistic interactions with other males (Fisher, 1990; Page, 2000; Fuller, 2003). Interspecific sneaking has been observed in laboratory studies of taxa from the same subgenus, E. radiosum and Etheostoma spectabile pulchellum (Girard) (Mendelson, 2003a), which hybridize extensively in the Blue River, Oklahoma (Distler, 1968; Branson & Campbell, 1969; Echelle et al., 1974). This interspecific sneaking is strongly asymmetric as E. s. pulchellum males and E. radiosum females spawned more frequently than E. radiosum males and E. s. pulchellum females. Etheostoma s. pulchellum males achieved this by quickly entering spawning territory and mating with E. radiosum females, while E. radiosum males were actively guarding against conspecifics (Mendelson, 2003a). A similar pattern of behavioural asymmetry involving interspecific matings that occur more frequently between E. uniporum males and E. caeruleum females is revealed by the data in this study, but has not been previously suggested based on morphology or laboratory observations. Why has a mtDNA replacement occurred in E. uniporum? One potential explanation is drift fixation, which in a small population, could have been rapid and significant (Avise & Saunders, 1984; Wilson & Bernatchez, 1998). Etheostoma uniporum may have had historically small female effective population sizes that resulted in the complete introgression of E. caeruleum mtDNA haplotypes. Periodic isolation in upland streams separated by lowland or big river habitats, during the Pleistocene and recent (Fenneman, 1938; Fisk, 1944; Pflieger, 1971), may have contributed to differential sorting of introgressed E. uniporum lineages [clades A, E and G; Fig. 2(a)]. These clades fit the expected pattern of a more basal phylogenetic position, a product of lineage sorting since last gene flow. Fortunately, E. uniporum has not sorted out of the E. caeruleum cyt b phylogeny and still shows a geographic association of haplotypes. Otherwise, it may have been extremely difficult to conclusively identify hybridization as the cause of the gene tree pattern. Although the sampling of representatives of the E. spectabile species group does not indicate that mtDNA introgression has occurred outside the Black River system, Sloss et al. (2004) presented a mtDNA phylogeny for Percidae in which a putative E. burri (GenBank AY374262) was the sister taxa to a single E. caeruleum (GenBank AY374263). Comparison of this E. burri sequence to two sequences of sympatric E. caeruleum from the present study (EC069 and EC070) showed that these individuals were virtually identical (01–02% sequence divergence). It is concluded that the E. burri specimen possesses a mtDNA haplotype of E. caeruleum as previously suggested (Lang & Mayden, 2007). Interestingly, no E. caeruleum from outside the Black River system possessed a mitochondrial haplotype of sympatric E. spectabile group members (Ray et al., 2006), suggesting that the pattern is strongly asymmetric throughout the area of sympatry. Interspecific hybridizations between darters have been known for some time, but its potential influence on systematics of darters have not previously been intensively examined with molecular data. This in-depth study of sympatric E. uniporum and E. caeruleum provides insights into interactions between these Journal compilation # # 2008 The Authors 2008 The Fisheries Society of the British Isles, Journal of Fish Biology 2008, 72, 418–434 INTROGRESSION IN ETHEOSTOMA DARTERS 431 species that would not have otherwise been detected. Since mtDNA gene trees may aid in taxonomy and the design of comparative ecological studies, the importance of accurate phylogenies cannot be over stated. With nearly 200 species confined to the streams of eastern North America, many of which occur in sympatry, it seems likely that additional evidence for darter hybridization and introgression will be discovered with molecular data in the near future. We thank R. Blanton, A. Kinziger, A. Simons and J. Switzer for assistance with the collection of specimens. K. Conway, C. Dillman and K. Tang made helpful suggestions on earlier versions of the manuscript. Procedures used in this study have been approved by the Animal Care Committee of Saint Louis University (STL). Fishes were collected under state permits issued to the authors and individuals listed above. Laboratory work was supported by grants from the Beaumont Fund of STL. References Allendorf, F. W. & Leary, R. F. (1988). Conservation and distribution of genetic variation in a polytypic species, the cutthroat trout. Conservation Biology 2, 170– 184. doi: 10.1111/j.1523-1739.1988.tb00168.x Avise, J. C. (2004). Molecular Markers, Natural History, and Evolution, 2nd edn. Sunderland, MA: Sinauer Associates. Avise, J. C. & Saunders, N. C. (1984). Hybridization and introgression among species of sunfish (Lepomis): analysis by mitochondrial DNA and allozyme markers. Genetics 108, 237–255. Bailey, R. M. & Etnier, D. A. (1988). Comments on the subgenera of darters (Percidae) with descriptions of two new species of Etheostoma (Ulocentra) from southeastern United States. Miscellaneous Publications of the Museum of Zoology University of Michigan 175, 148. Bernatchez, L., Glemet, H., Wilson, C. C. & Danzmann, R. G. (1995). Introgression and fixation of Arctic char (Salvelinus alpinus) mitochondrial genome in an allopatric population of brook trout (Salvelinus fontinalis). Canadian Journal of Fisheries and Aquatic Sciences 52, 179–185. Branson, B. A. & Campbell, J. B. (1969). Hybridization in the darters Etheostoma spectabile and Etheostoma radiosum cyanorum. Copeia 1969, 70–75. Ceas, P. A. & Page, L. M. (1997). Systematic studies of the Etheostoma spectabile complex (Percidae: subgenus Oligocephalus), with description of four new species. Copeia 1997, 496–522. Chow, S. & Hazama, K. (1998). Universal PCR primers for S7 ribosomal protein gene introns in fish. Molecular Ecology 7, 1255–1256. doi: 10.1111/j.1365-294x.1998. 00406.x Distler, D. A. (1968). Distribution and variation of Etheostoma spectabile (Agassiz) (Percidae: Teleostei). University of Kansas Scientific Bulletin 48, 143–208. Dobbs, M. & Gee, N. (2002). Automating Heterozygote Detection Using the Human p53 Gene as a Model System. Fullerton, CA: Beckman Coulter Application Information. Domingues, V. S., Bucciarelli, G., Almada, V. C. & Bernardi, G. (2005). Historical colonization and demography of the Mediterranean damselfish, Chromis chromis. Molecular Ecology 14, 4051–4063. doi: 10.1111/j.1365-294x.2005.02723.x Echelle, A. A. & Connor, P. J. (1989). Rapid, geographically extensive genetic introgression after secondary contact between two pupfish species. (Cyprinodon, Cyprinodontidae). Evolution 43, 717–727. Echelle, A. A., Schenck, J. R. & Hill, L. G. (1974). Etheostoma spectabile – E. radiosum hybridization in Blue River, Oklahoma. American Midland Naturalist 91, 182–194. Felsenstein, J. (1985). Confidence limits on phylogenies: an approach using the bootstrap. Evolution 39, 783–791. # 2008 The Authors Journal compilation # 2008 The Fisheries Society of the British Isles, Journal of Fish Biology 2008, 72, 418–434 432 J. M. RAY ET AL. Fenneman, N. M. (1938). Physiography of the Eastern United States. New York, NY: McGraw-Hill. Fisher, W. L. (1990). Life history and ecology of the orangefin darter Etheostoma bellum (Pisces: Percidae). American Midland Naturalist 123, 268–281. Fisk, H. N. (1944). Geological Investigation of the Alluvial Valley of the Lower Mississippi River. Vicksburg, MS: Mississippi River Commission. Fuller, R. C. (2003). Disentangling female mate choice and male competition in the rainbow darter, Etheostoma caeruleum. Copeia 2003, 138–148. Funk, D. J. & Omland, K. E. (2003). Species-level paraphyly and polyphyly: frequency, causes, and consequences, with insights from animal mitochondrial DNA. Annual Review of Ecology Evolution and Systematics 34, 397–423. Gerber, A. S., Tibbets, C. A. & Dowling, T. E. (2001). The role of introgressive hybridization in the evolution of the Gila robusta complex (Teleostei: Cyprinidae). Evolution 55, 2028–2039. doi: 10.1111/j.0014-3820.2001.tb01319.x Gum, B., Gross, R. & Kuehn, R. (2005). Mitochondrial and nuclear DNA phylogeography of European grayling (Thymallus thymallus): evidence for secondary contact zones in central Europe. Molecular Ecology 14, 1707–1725. doi: 10.1111/j.1365294.2005.02520.x Hare, M. P. & Avise, J. C. (1998). Population structure in the American oyster as inferred by nuclear gene genealogies. Molecular Biology and Evolution 15, 119–128. Hubbs, C. L. (1955). Hybridization between fish species in nature. Systematic Zoology 4, 1–20. Hubbs, C. (1958). Fertility of F1 hybrids between the percid fishes Etheostoma spectabile and E. lepidum. Copeia 1958, 57–59. Hubbs, C. (1967). Geographic variations in survival of hybrids between etheostomatinae fishes. Bulletin of the Texas Memorial Museum 13, 1–72. Hubbs, C. & Laritz, C. M. (1961). Occurrence of a natural intergeneric etheostomatine fish hybrid. Copeia 1961, 231–232. Hubbs, C. & Strawn, K. (1957). Relative variability of hybrids between the darters, Etheostoma spectabile and Percina caprodes. Evolution 11, 1–10. Hubbs, C., Cross, F. B. & Stevens, F. (1988). Occurrence of natural hybrids between Etheostoma and Percina (Pisces: Percidae). The Southwestern Naturalist 33, 97–99. Huelsenbeck, J. P. & Ronquist, F. (2001). MRBAYES: Bayesian inference of phylogeny. Bioinformatics 17, 754–755. Kinziger, A. P., Wood, R. M. & Welsh, S. A. (2001). Systematics of Etheostoma tippecanoe and Etheostoma denoncourti (Perciformes: Percidae). Copeia 2001, 235–239. Kumar, S., Tamura, K. & Nei, M. (2004). MEGA3: integrated software for molecular evolutionary genetics analysis and sequence alignment. Briefings in Bioinformatics 5, 150–163. Lang, N. J. & Mayden, R. L. (2007). Systematics of the subgenus Oligocephalus (Teleostei: Percidae: Etheostoma) with complete subgeneric sampling of the genus Etheostoma. Molecular Phylogenetics and Evolution 43, 605–615. Linder, A. D. (1958). Behavior and hybridization of the species of Etheostoma (Percidae). Transactions of the Kansas Academy of Science 61, 195–212. Lu, G., Basley, D. J. & Bernatchez, L. (2001). Contrasting patterns of mitochondrial DNA and microsatellite introgressive hybridization between lineages of lake whitefish (Coregonus clupeaformis): relevance for speciation. Molecular Ecology 10, 965–985. doi: 10.1046/j.1365-294x.2001.01252.x Maddison, D. R. & Maddison, W. P. (2002). MACCLADE: Analysis of Phylogeny and Character Evolution, Version 4.02. Sunderland, MA: Sinauer Associates. Martin, F. D. & Richmond, R. C. (1973). An analysis of five enzyme-gene loci in four etheostomid species (Percidae: Pisces) in an area of possible introgression. Journal of Fish Biology 5, 511–517. doi: 10.1111/j.1095-8649.1973.tb04481.x Masta, S. E., Sullivan, B. K., Lamb, T. & Routman, E. J. (2002). Molecular systematics, hybridization, and phylogeography of the Bufo americanus complex in eastern North America. Molecular Phylogenetics and Evolution 24, 302–314. Journal compilation # # 2008 The Authors 2008 The Fisheries Society of the British Isles, Journal of Fish Biology 2008, 72, 418–434 INTROGRESSION IN ETHEOSTOMA DARTERS 433 Mayden, R. L. & Burr, B. M. (1980). Two natural darter hybrids involving members of the genus Etheostoma (Pisces: Percidae). American Midland Naturalist 104, 390–393. McMillan, W. O. & Palumbi, S. R. (1995). Concordant evolutionary patterns among Indo-West Pacific butterflyfishes. Proceedings of the Royal Society of London. Series B, Biological Sciences 260, 229–236. Mendelson, T. C. (2003a). Evidence of intermediate and asymmetrical behavioral isolation between orangethroat and orangebelly darters (Teleostei: Percidae). American Midland Naturalist 150, 343–347. doi: 10.1111/j.0014-3820.2003.tb00266.x Mendelson, T. C. (2003b). Sexual isolation evolves faster than hybrid inviability in a diverse and sexually dimorphic genus of fish (Percidae: Etheostoma). Evolution 57, 317–327. Moore, W. S. (1995). Inferring phylogenies from mtDNA variation: mitochondrial-gene trees versus nuclear-gene trees. Evolution 49, 718–726. Nylander, J. A. A. (2004). MRMODELTEST version 2.2. Program Distributed by the Author, Evolutionary Biology Centre. Sweden: Uppsala University. Page, L. M. (1976). Natural darter hybrids: Etheostoma gracile Percina maculata, Percina caprodes Percina maculata, and Percina phoxocephala Percina maculata. The Southwestern Naturalist 21, 161–168. Page, L. M. (1983). The Handbook of Darters. Neptune City, FL: TFH Publications. Page, L. M. (2000). Etheostomatinae. In: Percid Fishes: Systematics, Ecology, and Exploitation (Craig, J. F., ed.), pp. 225–253. Oxford: Blackwell Science. Page, L. M., Hardman, M. & Near, T. J. (2003). Phylogenetic relationships of barcheek darters (Percidae: Etheostoma, Subgenus Catonotus) with descriptions of two new species. Copeia 2003, 512–530. Pflieger, W. L. (1971). A distributional study of Missouri fishes. Museum of Natural History, University of Kansas Publications 20, 225–570. Pflieger, W. L. (1997). The Fishes of Missouri. Jefferson City, MO: Missouri Department of Conservation. Ray, J. M., Wood, R. M. & Simons, A. M. (2006). Phylogeography and post-glacial colonization patterns of the rainbow darter Etheostoma caeruleum (Teleostei: Percidae). Journal of Biogeography 33, 1550–1558. doi: 10.1111/j.1365-2699.2006. 01540.x Redenbach, Z. & Taylor, E. B. (2002). Evidence for historical introgression along a contact zone between two species of char (Pisces: Salmonidae) in northwestern North America. Evolution 56, 1021–1035. doi: 10.1111/j.0014-3820.2002.tb01413.x Rhymer, J. M. & Simberloff, D. (1996). Extinction by hybridization and introgression. Annual Review of Ecology and Systematics 27, 83–109. Ronquist, F. & Huelsenbeck, J. P. (2003). MRBAYES 3: Bayesian phylogenetic inference under mixed models. Bioinformatics 19, 1572–1574. Sang, T. & Zhong, Y. (2000). Testing hybridization hypotheses based on incongruent gene trees. Systematic Biology 49, 422–434. Schmidt, T. R. & Gold, J. R. (1993). Complete sequence of the mitochondrial cytochrome b gene in the cherryfin shiner, Lythrurus roseipinnis (Teleostei: Cyprinidae). Copeia 1993, 880–883. Schwartz, F. J. (1972). World Literature to Fish Hybrids with an Analysis by Family, Species and Hybrids, Vol. 3. Ocean Springs, MS: Gulf Coast Research Laboratory and Museum. Scribner, K. T., Page, K. S. & Bartron, M. L. (2000). Hybridization in freshwater fishes: a review of case studies and cytonuclear methods of biological inference. Reviews in Fish Biology and Fisheries 10, 293–323. Sloss, B. L., Billington, N. & Burr, B. M. (2004). A molecular phylogeny of the Percidae (Teleostei, Perciformes) based on mitochondrial DNA sequence. Molecular Phylogenetics and Evolution 32, 545–562. Switzer, J. F. & Wood, R. M. (2002). Molecular systematics and historical biogeography of the Missouri saddled darter Etheostoma tetrazonum (Actinopterygii: Percidae). Copeia 2002, 450–455. # 2008 The Authors Journal compilation # 2008 The Fisheries Society of the British Isles, Journal of Fish Biology 2008, 72, 418–434 434 J. M. RAY ET AL. Swofford, D. L. (2003). PAUP* Phylogenetic Analysis Using Parsimony (*and Other Methods). Sunderland, MA: Sinauer Associates. Thompson, J. D., Gibson, T. J., Plewniak, F., Jeanmougin, F. & Higgins, D. G. (1997). The ClustalX windows interface: flexible strategies for multiple sequence alignment aided by quality analysis tools. Nucleic Acids Research 24, 4876–4882. Warren, M. L. Jr, Burr, B. M., Walsh, S. J., Bart, M. L. Jr, Cashner, R. C., Etnier, D. A., Freeman, B. J., Kuhajda, B. R., Mayden, R. L., Robison, M. W., Ross, S. T. & Starnes, W. C. (2000). Diversity, distribution, and conservation status of the native freshwater fishes of the southern United States. Fisheries 25, 7–31. Wilson, C. C. & Bernatchez, L. (1998). The ghost of hybrids past: fixation of arctic charr (Salvelinus alpinus) mitochondrial DNA in an introgressed population of lake trout (S. namaycush). Molecular Ecology 7, 127–132. doi: 10.1046/j.1365-294x.1998. 00302.x Winn, H. E. (1958). Comparative reproductive behavior and ecology of fourteen species of darters (Pisces: Percidae). Ecological Monographs 28, 155–191. Zink, R. M. (1994). The geography of mitochondrial DNA variation, population structure, hybridization, and species limits in the fox sparrow (Passerella iliaca). Evolution 48, 96–111. Journal compilation # # 2008 The Authors 2008 The Fisheries Society of the British Isles, Journal of Fish Biology 2008, 72, 418–434
© Copyright 2026 Paperzz