* Your assessment is very important for improving the workof artificial intelligence, which forms the content of this project
Download No Boundaries: Genomes, Organisms, and
Survey
Document related concepts
Transcript
Journal of Heredity 2014:105(Special Issue):756–770 doi:10.1093/jhered/esu039 © The American Genetic Association. 2014. All rights reserved. For permissions, please e-mail: [email protected] No Boundaries: Genomes, Organisms, and Ecological Interactions Responsible for Divergence and Reproductive Isolation William J. Etges From Program in Ecology and Evolutionary Biology, Department of Biological Sciences, 1 University of Arkansas, Fayetteville, AR. Address correspondence to William J. Etges at the address above, or e-mail: [email protected]. Abstract Revealing the genetic basis of traits that cause reproductive isolation, particularly premating or sexual isolation, usually involves the same challenges as most attempts at genotype–phenotype mapping and so requires knowledge of how these traits are expressed in different individuals, populations, and environments, particularly under natural conditions. Genetic dissection of speciation phenotypes thus requires understanding of the internal and external contexts in which underlying genetic elements are expressed. Gene expression is a product of complex interacting factors internal and external to the organism including developmental programs, the genetic background including nuclear–cytotype interactions, epistatic relationships, interactions among individuals or social effects, stochasticity, and prevailing variation in ecological conditions. Understanding of genomic divergence associated with reproductive isolation will be facilitated by functional expression analysis of annotated genomes in organisms with well-studied evolutionary histories, phylogenetic affinities, and known patterns of ecological variation throughout their life cycles. I review progress and prospects for understanding the pervasive role of host plant use on genetic and phenotypic expression of reproductive isolating mechanisms in cactophilic Drosophila mojavensis and suggest how this system can be used as a model for revealing the genetic basis for species formation in organisms where speciation phenotypes are under the joint influences of genetic and environmental factors. Subject areas: Genomics and gene mapping; Gene action, regulation, and transmission Key words: cactus, courtship song, cuticular hydrocarbon, Drosophila, gene ontology, microarray, Sonoran Desert, speciation, transcriptome Deciphering genetic architectures of phenotypic traits associated with reproductive divergence and speciation often requires a quantitative genetic approach to estimate variance components, gene numbers, effect size, and the extent of genotype by environment (G × E) interactions if these traits are polygenic and sensitive to local environmental conditions. Study of genes with large qualitative phenotypic effects, for example, the genetic basis of shell color and banding patterns in species of Cepea snails, melanic morphs of Biston betularia and other species (Majerus 1998; Cook et al. 2012), wing color and banding patterns in Heliconius butterflies (Turner 1977; Naisbit et al. 2003; Mallet and Dasmahapatra 2012), and mammalian pelage color differences (Dice and Blossom 1937; Blair 1947; Kaufman 1974; Nachman et al. 2003; Linnen et al. 2013) have remained at the heart of ecological genetics for over 80 years largely because one or a few gene loci are involved for each trait, 756 phenotype expression showed relatively little environmental influence, and the selective forces maintaining polymorphism were largely identifiable (Ford 1975). Some genetic analyses of speciation have often focused on one or a few gene regions without regard to the influences of relevant ecological variation or controlled environmental differences in the laboratory on reproductive isolation. For some “speciation genes,” such as those underlying species differences involved with premating (Doi et al. 2001) and postmating isolation (Orr et al. 2004; Ting et al. 2004), genetic analysis has been devoid of assessing environmental influences on these phenotypes. Fortunately, the role of ecology in driving reproductive isolation has become better integrated into the analysis of genetic architectures of diverging populations and species (e.g., Bradshaw et al. 1995; Hawthorne and Via 2001; Feder et al. 2005; Egan and Funk 2009; Feder and Nosil 2009; Gompert et al. 2014). Etges • Genetics, Environments, and Speciation Most traits associated with reproductive isolation, whether premating, postmating-prezygotic, or postzygotic, are genetically complex traits and the identifying genes underlying them has remained elusive except in a small number of cases (Coyne and Orr 2004). Further, many kinds of phenotypes that mediate reproductive isolation are influenced by the environments in which they are expressed, for example, insect and amphibian courtship songs (Gerhardt and Huber 2002; Rodríguez et al. 2008), pheromones (Howard and Blomquist 1982; Toolson 1982; Etges 1992; Greenfield 2002; Etges et al. 2009), species-specific visual cues (Seehausen et al. 1997; Taylor et al. 2006), host-dependent premating isolation (Dambroski et al. 2005; Feder and Nosil 2009), and postmating isolation (Funk et al. 2002; Egan and Funk 2009; Singer and McBride 2010), suggesting that environmentally mediated patterns of trait expression need to be studied when evaluating the nature of reproductive divergence and its causes. Thus, in order to understand the evolution of reproductive divergence and how it is expressed, phenotypic analysis requires estimates of genetic, environmental, and G × E interaction effects on traits thought to drive reproductive isolation and speciation, as well as how ambient ecological conditions influence patterns of gene expression. The “top-down” approach to genetic analysis (Via 2009) assumes that genetic influences can effectively be separated from those of the environment, yet a central tenet of quantitative genetics is that gene expression is a consequence of the internal and external environments in which they are expressed. Lewontin (2000) emphasized this relationship by asserting there is no necessary demarcation between organisms and their environments, and that organisms can define their environments as environments can define organisms. Thus, understanding the consequences of how and why reproductive isolation evolves beyond characterizing the genetic basis of traits causing isolation (Shaw and Mullen 2011) assumes an environmental context. The causal connections and feedbacks between genes, organisms, and their environments may not be easily disentangled, and noncontextual focus on any one level, particularly DNA sequence variation, may not resolve sources of causation (Lewontin 1991). Thus, any attempt to localize the “genes” or candidate nucleotide substitutions (single nucleotide polymorphisms [SNPs] or quantitative trait nucleotides [QTNs]) contributing to speciation phenotypes is dependent on the environment(s) in which the phenotype is assessed (Burga and Lehner 2012; Nuzhdin et al. 2012). Consequences of this approach are, for example, discordance between quantitative trait loci (QTL) localization and known candidate genes (Gleason et al. 2009) and differences in QTL localization when analyses are performed in multiple environments (Leips and Mackay 2000), as well as G × E interactions for QTL and QTNs (Gurganus et al. 1998; Mackay and Anholt 2007; Etges et al. 2009; Stranger et al. 2011; Kang et al. 2014). Here, identifying impacts on transcriptional variation, as well as understanding G × E interactions in gene expression for speciation phenotypes can more efficiently help to identify sources of genetic variation expressed in different environments (Grishkevich and Yanai 2013). This type of functional genetic analysis can complement genetic and genomic mapping attempts and can be extended with proteome studies to complete genotype– phenotype mapping. Genotype–phenotype maps are contextual due not only to external environments but also the internal environment, including other genes. Genetic background effects may reduce the generality of QTL identification and fine mapping, namely, “Instead, the phenotype is a function of the allele, the genetic background in which it occurs and the environment where the mutational effects are expressed.”(Chari and Dworkin 2013) Thus, population and species-specific differences in genetic analyses of reproductive isolation traits are expected due to genetic background effects, that is, epistasis (Galvan et al. 2010; Mackay 2014), nuclear–mtDNA interactions (Pritchard et al. 2011; Burton and Barreto 2012), maternal effects, and stochastic variation (Burga and Lehner 2012) rendering general conclusions about the effects of single genes or SNPs on phenotypic trait variation difficult unless great care is taken to assess both population and environmental influences on expression of reproductive isolating traits. Analysis of gene expression differences mediated by ecological variation can also be teased apart by mapping regulatory regions or expression QTLs, but this can be complicated by tissue-specific patterns of gene expression (Michaelson et al. 2009). Further, as natural selection operates on such standing variation, convergent evolution may result making genotype–phenotype mapping difficult even for suspected candidate genes (Nachman et al. 2003; Rosenblum et al. 2004). Results of quantitative genetic analysis are, as always, dependent on the environment(s) in which they are measured. Much current interest in ecological speciation rests on inferences that causal mechanisms that drive reproductive isolation in ecologically diverging populations can result in relatively rapid divergence in sympatry and/or allopatry (Nosil 2012). In the latter and more common case, allopatry with reduced gene flow should allow for rapid divergence depending on the strength of local adaptation. In an intensively studied species group, flies in the genus Drosophila, allopatric divergence is thought to be the rule as few cases of sympatric speciation have been identified (Turelli et al. 2014; Yukilevich 2014). Here, I review progress and prospects in understanding the genetics of premating isolating mechanisms in Drosophila mojavensis, a cactophilic member of the genus in which ecological influences of its host plants have been shown to cause differences in premating isolation between populations, QTL G × E interactions in traits responsible for courtship success, and patterns of gene expression across the genome. Whole-genome microarray experiments and transcriptome sequencing have revealed host plant effects on expression of nervous system and courtship behavior genes suggesting direct links between genome expression and ecologically determined reproductive isolation. Together with ongoing studies of genomic divergence, such functional genomic data in an organism with a sequenced and partially annotated genome should help resolve the interactions between genomes, the organism, and ecologically relevant variation in the evolution of reproductive divergence and adaptation to different environments. 757 Journal of Heredity Ecology of Divergence and Reproductive Isolation in a Desert Drosophilid A member of the large D. repleta group, D. mojavensis is endemic to the Sonoran Desert and adjacent arid lands in northwestern Mexico and southern Arizona, as well as the Mojave Desert in southern California (Heed 1978; Heed 1982; Etges et al. 1999). In Baja California, the islands in the Gulf of California, and a small patch in coastal Sonora, D. mojavensis uses pitaya agria cactus, Stenocereus gummosus, almost exclusively. The remaining mainland populations in Sonora, Sinaloa, and southern Arizona use organ pipe cactus, S. thurberi, with occasional use of cina cactus, S. alamosensis, with which it sometimes shares with its sibling species, D. arizonae (Fellows and Heed 1972; Markow et al. 1983; Ruiz and Heed 1988). California barrel cactus, Ferocactus cylindraceus, is the principal host plant in the Mojave Desert, and prickly pears, Opuntia littoralis, O. oricola, and O. demissa (O. oricola × O. ficus-indica hybrids) are the only known host plants on Santa Catalina Island near Los Angeles, California (Barbour et al. 2007; Beckenbach et al. 2008). The phylogeography of North American D. repleta group species was shaped in part by the northwestward movement of present-day Baja California on the Pacific tectonic plate (Gastil et al. 1975) and the relatively recent formation of the Sonoran Desert ca 13 kya (Axelrod 1979; Van Devender 1990). Along with changing sea levels forming the Gulf of California, an effective isolating barrier between peninsular and mainland species, D. mojavensis diverged from its closest mainland ancestor, D. arizonae, ca 1–2 mya based on Adh and mtCOI sequence divergence (Mills et al. 1986; Matzkin and Eanes 2003; Reed et al. 2007) and was isolated in Baja California. Recent whole-genome comparisons of these 2 species suggest divergence was <1 mya (Lohse et al., unpublished data). This evolutionary history was first revealed from studies of chromosomal inversions in D. mojavensis and its closest relatives (Wasserman 1962; Ruiz et al. 1990; Wasserman 1992) and the geographical patterns of inversion polymorphisms throughout the range of D. mojavensis (Heed 1981; Etges et al. 1999). Ancestral populations of D. mojavensis in Baja California colonized the islands in the gulf and mainland Sonora ca 270 kya based on coalescent analyses of X chromosome intron sequence variation. In southern California, Mojave Desert populations of D. mojavensis subsequently diverged from mainland populations ca 117 kya and experienced a genetic bottleneck that reduced sequence variation 10-fold (Smith et al. 2012). The Santa Catalina Island population represents a fourth lineage that presumably arose from mainland California populations due to geographical proximity, but its closest mainland relative remains unknown (Counterman and Noor 2006; Ross and Markow 2006). Thus, intraspecific divergence in D. mojavensis has been facilitated by host plant shifts within the last ca 250 kya and has resulted in host plant adaptation and partial reproductive isolation between Baja California and mainland Mexico and Arizona populations (Etges 1990, 1998; Etges et al. 2007, 2009, 2010). Life-History Variation Colonization of mainland Mexico by switching to organ pipe cactus from agria has caused significant genetic shifts in life history and other physiological traits in D. mojavensis (Table 1; Etges 1990) and has resulted in premating isolation between Baja California and mainland Mexico and Arizona populations (Zouros and d’Entremont 1974; Wasserman and Koepfer 1977; Zouros and d’Entremont 1980; Markow 1991). Tying adaptive shifts in life history to the evolution of reproductive isolation suggested a role for ecological speciation in this system mediated by a host plant shift. In common garden experiments and population crosses reared on both host cacti, Baja California populations exhibit genetically shorter egg to adult development times, higher viabilities, and smaller adult body sizes than mainland Mexico and Arizona populations (Etges 1990; Etges et al. 2010). For development time, there were significant population × cactus and region × Table 1 Summary of life history and physiological differences between Baja California and mainland Mexico and Arizona populations of Drosophila mojavensis Phenotype Mainland Baja California Region × host plant Development time (DEVT) DEVT homeostasis Egg to adult viability Thorax size ↑↑ ↓↓ ↓↓ ↑↑ ↓↓ ↑↑ ↑↑ ↓↓ □ — □ — Female age at maturity Ovariole number Lifetime fecundity ↓↓ ↑↑ ↑↑ ↑↑ ↓↓ ↓↓ □ — — Equivalent ↑↑ ↑↑ Equivalent ↓↓ ↓↓ — — — Standard metabolic rate Adult starvation resistance EtOH vapor adult longevity Reference (Etges 1990; Etges et al. 2010) (Etges 1989) (Etges 1990; Etges et al. 2010) (Heed and Mangan 1986; Etges 1990; Etges 1992) (Etges and Klassen 1989) Heed WB, unpublished data (Etges and Klassen 1989; Etges and Heed 1992) (Etges and Klassen 1989) (Etges and Klassen 1989) (Starmer et al. 1977; Etges 1989; Etges and Klassen 1989) Up and down arrows show direction of differences, all statistically significant. For experiments based on cactus-cultured populations, presence of significant region × host plant interactions is also shown. 758 Etges • Genetics, Environments, and Speciation cactus interactions, and for egg to adult viability, a significant region × cactus interaction revealed host plant adaptation where Baja California populations expressed higher viability on agria versus organ pipe cactus while mainland populations expressed higher viability on organ pipe cactus, host plants these populations use in nature (Table 1). In many replicate population crosses, F1, F2, and backcross generations showed higher egg to adult viability than parental populations particularly when reared on agria cactus revealing hostspecific heterosis for fitness. Host plant, additive, dominance, and cytoplasmic effects were detected for development time, as well as a significant X chromosome effect associated with the typically shorter development times of Baja California populations. Higher egg to adult viability in Baja flies showed a significant X chromosome effect, but this was not observed in both sets of populations crosses suggesting geographic variation in X-linked genes that increase fitness relative to mainland populations (Etges et al. 2010). Reproductive Isolation Premating and postmating-prezygotic isolation (Knowles and Markow 2001) between Baja California and mainland Mexico and Arizona populations have long suggested that allopatric populations of D. mojavensis are currently in the initial stages of reproductive isolation making them an ideal system with which to explore the early stages of divergence where no postmating isolation has arisen (Ruiz et al. 1990). A causal relationship between host plant adaptation and reproductive isolation predicted from the hypothesis of ecological speciation suggested a testable alternative to earlier inferences about premating isolation between the Baja mainland populations of D. mojavensis. Previous studies suggested the cause was due to reproductive character displacement because of the presence of D. arizonae on the mainland, but not in Baja California, causing shifts in mate choice of mainland D. mojavensis (Mettler and Nagle 1966; Wasserman and Koepfer 1977). The latter hypothesis has not been tested experimentally in part because these species hybridize in the laboratory (Mettler 1957; Jennings and Etges 2010) but do not currently hybridize in nature (Etges et al. 1999; Counterman and Noor 2006; Machado et al. 2007), so reinforcement is unlikely to be involved. Laboratory multiple-choice tests involving Mojave Desert and Santa Catalina Island populations with Baja California and mainland Mexico populations revealed little evidence for sexual isolation between California populations with either Baja California or mainland populations with few exceptions (Markow 1991; Massie and Markow 2005). Also, D. arizonae populations sympatric with D. mojavensis do not exhibit increased premating isolation with other populations, so there may have been the evolution of local mate recognition systems unrelated to the presence of D. arizonae. A more parsimonious explanation, historical gene flow between species, was suggested from emerging patterns of genomic divergence between allopatric and sympatric populations of D. arizonae and D. mojavensis, suggesting that interspecific hybridization ceased ca 200–250 kya (Lohse et al., unpublished data). Why these genomic differences were not detected in earlier studies (Counterman and Noor 2006; Machado et al. 2007) maybe due to a lack of power due to smaller numbers of loci studied or the choice of divergence with gene flow models that were used (Lohse, personal communication). Observations that premating isolation between Baja California and mainland populations is significantly influenced by rearing substrates (Brazner 1983; Etges 1992) suggested the preadult rearing environments determined the strength of assortative mating between populations, and hence is critical to understanding divergence and reproductive isolation. Rearing D. mojavensis on laboratory media significantly increases the strength of sexual isolation causing decreased mating propensity of Baja California males and a dearth of matings between mainland females and Baja males in multiple-choice tests. Cactus-reared flies exhibit lower levels of sexual isolation, with agria-reared flies typically showing little or no premating isolation and organ pipe-reared flies showing low, but significant levels of behavioral isolation (Brazner and Etges 1993). Further, sexual isolation between D. mojavensis and D. arizonae increased when flies were reared on cactus versus those reared on laboratory food and when exposed to fermenting host plant tissue during mating trials (Jennings and Etges 2010). Thus, for these sibling species as well as allopatric, ecologically diverged populations of D. mojavensis, understanding the earliest stages of reproductive isolation requires knowledge of the consequences of host plant use. As in many drosophilids, courtship decisions result from a progressive, multistage interaction between males and females involving visual, auditory, and tactile cues (Greenspan and Ferveur 2000). In D. mojavensis, courtship success is determined mainly by female choice (Havens et al. 2011) based on variation in male courtship songs (Byrne 1999; Etges et al. 2006) and cuticular hydrocarbons (Markow and Toolson 1990; Etges and Ahrens 2001). Selection gradient analysis revealed that variation in multiple components of courtship songs, that is, long interpulse interval (L-IPI), burst duration, interburst interval (IBI), and number of bursts produced all influenced male courtship success with mainland females, but rearing substrates had no additional effects on any component of courtship song on mating success (see Table 1 in Etges et al. 2007). Mainland females preferred copulating with males that produce songs with shorter L-IPIs, shorter burst durations, and shorter IBIs. However, courtship success was significantly higher in males reared on organ pipe cactus, was influenced by a single detected QTL very near the desat-2 locus, and 4 G × E interactions (Etges et al. 2007). In a common garden experiment with 5 mainland populations and 6 Baja populations reared on agria and organ pipe cactus, few cuticular hydrocarbons (CHCs) showed effects of rearing substrate effects, but differences due to sex and region were strongly significant including a number of sex × region interactions for CHCs associated with mating success. These results suggested that male courtship songs and contact pheromones are part of Baja California versus mainland mate recognition systems in D. mojavensis (Etges and Ahrens 2001). 759 Journal of Heredity Allopatry and reduced gene flow between diverging populations should allow for rapid, evolution of local mate recognition, that is, sexual selection, postmating-prezygotic mechanisms, and drivers of sexual conflict (Williams 1966). As gene flow between Baja California, mainland Mexico, and southern California populations is insignificant or too low to be detected (Smith et al. 2012), genomic divergence should be unconstrained by possible effects of immigrant alleles that are poorly adapted locally (Nosil et al. 2005). So, genomic regions containing loci associated with ecological adaptation are not expected to be closely linked with genes inflecting reproductive isolation or be located within inversions protecting them from recombination (Feder et al. 2012; Nosil et al. 2012). Thus, divergence genetics of premating isolation should reveal how the initial stages of speciation evolve in allopatric populations of D. mojavensis. Both male courtship songs and CHCs are polygenic traits (Gleason et al. 2002, 2005; Howard and Blomquist 2005), so an understanding of their genetic architectures, as well as the genetic basis of life-history variation, is necessary to begin to understand the forces that have shaped their variation (Shaw and Parsons 2002). In a test of the ecological speciation hypothesis, a genetic correlation was observed between variation in egg to adult development time and premating isolation (Etges 1998), suggesting an alternate explanation for the evolution of premating isolation in D. mojavensis and that even in allopatry, regions of the genomes associated with ecological adaptation can overlap those associated with reproductive isolation (cf., Hawthorne and Via 2001). We still do not know the nature of this association in D. mojavensis, that is, how many loci are involved or whether pleiotropy or linkage is responsible, but genetic evidence derives from 4 separate experimental observations. First, this genetic correlation was identified in a bidirectional artificial selection experiment on egg to adult development time in Baja California and mainland populations of D. mojavensis reared on agria and organ pipe cactus. Significant selection responses in development time with realized heritabilities of 8–11% were observed together with correlated responses in decreased premating isolation between populations (Etges 1998). Second, in populations cultured in a common garden experiment to assess variation in CHCs across the species range (Etges and Ahrens 2001), adults from mainland populations with longer development times had significantly more CHCs than adults that eclosed earlier (Figure 1). Third, F2 males that eclosed on the first 2 days from cactus cultures and aged to sexual maturity had less CHCs than those eclosing later, although this was influenced by exposure/no exposure to females (Etges et al. 2009). Four, QTL influenced both CHCs and development time from the same large-scale genetic analysis of cactus-reared F2 males. QTL genotype scores for development time and CHC variation known to influence mating Figure 1. Replicate CHC samples from adults pooled by sex and rearing substrates of mainland populations from Punta Onah and Rancho Diamante, Sonora. All adults in each replicate culture that emerged on the first 2 days were labeled “fast” and the remaining flies labeled “slow.” Amounts of 11 CHC components were significantly greater in the “slow” groups (n = 24) than in the “fast” groups (n = 22) using paired t-tests (all P ≤ 0.02). Total hydrocarbons per fly were also greater in the “slow” groups than in the “fast” groups (3075.5 vs. 2632.3 ng/fly, t = 2.38, P < 0.022). CHC components are labeled by equivalent carbon chain lengths defined in Etges and Ahrens (2001). 760 Etges • Genetics, Environments, and Speciation success between Baja and mainland D. mojavensis were positively correlated, r = 0.59, P = 0.02 (Etges et al. 2010). Two of these QTL, marked by microsatellite loci Dmoj2010 and Dmoj2_6540c, are located on the second chromosome with the latter very near fruitless, a gene with known effects on mating behavior (Ryner et al. 1996; Greenspan and Ferveur 2000). Dmoj2010 is downstream from crossveinless c that functions in lipid binding and multiple developmental processes. The other 2 are on different chromosomes, Dmoj3030 that is very close to GI10093: its Drosophila melanogaster ortholog encodes a type of immunoglobulin, and Dmoj4300 is near GI13245, an unannotated protein coding gene. Further fine scale mapping of these QTL regions, given the mostly annotated genome of D. mojavensis (Tweedie et al. 2009), is of high priority to assess the causes for this genetic correlation between development time, premating isolation, and CHCs. Host Plant Effects on Gene Expression A clearer genetic understanding of genetic and environmental influences on phenotypic variation is now possible using whole genome expression patterns at either the transcriptome or proteome levels (Gibson 2008; Pavey et al. 2012; Wray 2013). Here, we tested the hypothesis that host cacti cause differences in expression of genes known to be involved with courtship success as suggested by the previous observations of differences in premating isolation and sexual selection caused by rearing populations of D. mojavensis on agria or organ pipe cactus. We investigated the effects of different host plants on patterns of whole transcriptome expression to directly identify genes involved with courtship success, songs, and CHCs. These approaches offer the exciting opportunity to answer the ultimate questions in evolutionary genetics concerning the differential expression of genes and genomic elements responsible for divergence in speciation phenotypes. In nonmodel systems, expressed sequence tags can be used (Frentiu et al. 2009; Schwarz et al. 2009), but identification of genetic elements of known function, that is, annotated genes, is critical to inferences about genetic architecture allowing understanding of the consequences of ecological divergence on reproductive isolation. Microarray technology (Quackenbush 2001) and RNAseq methods (Oshlack et al. 2010) both have advantages/disadvantages, but functional genomic inferences from both techniques are limited by the extent of genome annotation for most organisms. Microarray design allows for highly controlled hybridization with each oligonucleotide on a predesigned array and does not require population samples to be inbred. RNAseq is not limited to coding regions and can identify patterns of alternate exon splicing (Malone and Oliver 2011), but is sensitive to any residual sample heterozygosity, that is, inbreeding is required. Host plant effects on expression of life-history variation in D. mojavensis (Etges 1990; Etges et al. 2010), premating isolation between Baja California and mainland populations (Etges 1992; Brazner and Etges 1993), male mating success mediated by courtship songs (Etges et al. 2007), and QTL analysis of CHCs (Etges et al. 2009) all suggest that revealing host plant mediated differences in gene expression should help to identify how rearing substrates have such large effects on life-history traits and courtship behavior. Here, data from 2 experiments demonstrate the efficacy of this approach for 1) adult virgin females exposed to fermenting cactus throughout adulthood (Etges et al., submitted), and 2) cactus-reared males that were either successful or unsuccessful in copulating with females in mating choice trials (for details, see Smith et al. 2013). For the first experiment, we used gene predictions from the D. mojavensis reference genome (Drosophila-12Genomes-Consortium 2007) to design a 12-plex microarray from Roche-Nimblegen containing 14 528 unique oligomers corresponding to different genes. We designed replicated laboratory experiments to investigate effects of cactus-rearing and population differentiation on life cycle stage/age differences in gene expression in order to identify candidate genes that were differentially expressed over the life cycle. Array design, hybridization protocols, and data analysis are described in Rajpurohit et al. (2013), but only 9114 coding regions (63%) are orthologous with D. melanogaster genes limiting our interpretations of differential gene expression and gene ontology in D. mojavensis. Far fewer genes, ca 75, have been directly annotated in D. mojavensis. Nevertheless, the results of these experiments have revealed the identity of genetic systems with inferred biological functions that differed in gene expression in response to those factors suspected to have influenced the diversification of geographically differentiated populations that use different host cacti (Etges et al., submitted). A mainland D. mojavensis population from Las Bocas, Sonora, and a Baja California population from Punta Prieta were cultured on both fermenting agria and organ pipe cactus from eggs to 28-day old adults such that flies were never exposed to lab food. All preadult life stages and adults of different ages adults were sampled for analysis of gene expression using whole genome microarrays. Groups of 30 adult flies that had been reared on fermenting agria or organ pipe cactus (Etges 1992) were transferred to 25 × 95 mm glass tubes on the day of eclosion. The ends of each tube were plugged with fine mesh to allow air circulation at one end and a feeding cup containing either fermenting agria or organ pipe cactus at the other. Every day, the tubes were placed in sealed desiccators containing 1 L of 4% ethanol from 8:00 AM to 6:00 PM allowing adults to feed on ethanol vapor. For the remaining 14 h each day, all tubes were removed from each desiccator and kept in the incubator set to a 14:10 LD photoperiod and 27:17 °C to minimize condensation inside the tubes. Every 4 days, the food cups were replaced. At 0, 3, 6, 10, 14, 18, 24, and 28 days of age, groups of 24 adult females were snap frozen in liquid nitrogen resulting in an experimental design of 2 populations × 2 host cacti × 7 ages (24- and 28-day old flies were pooled due to small numbers of surviving 28-day adults) × 4 replicates for RNA processing and microarray hybridization. General experimental details, bioinformatic approaches, and statistical approaches are detailed in Rajpurohit et al. (2013). In short, we assessed 761 762 False Discovery rate P values, *P < 0.05, **P < 0.01, ***P < 0.001, ****P < 0.0001. in parentheses indicate the percentage of genes with annotation in Drosophila melanogaster. aNumbers Significantly enriched GOTerms (P < 0.05) are indicated. Each population comparison denotes genes that were overexpressed in each population. Mainland population LB = Las Bocas, Baja California population PP = Punta Prieta. There were no cases of significantly greater gene expression for the agria > organ pipe cactus comparison. FDR, false discovery rate. 1.5 2. Circadian rhythm, courtship behavior 2.2* 2.1**** 2. Iron/ heme binding, oxidation reduction 2. Fatty acid biosynthesis 2.3*** 1. Iron/heme binding/P450 1. Transcription/ RNA biosynthetic process 2.7**** 1. Neurotransmitter binding/receptors 2.2** 1. Fatty acid/ lipid biosynthesis 2.5*** Enrich score GOTerm Enrich score Enrich score GOTerm GOTerm Enrich score GOTerm Number of genes = 514, number annotated = 302 (62.3) Number of genes = 66, number annotated = 45 (68.2) Number of genes = 251, number annotated = 146 (58.2) Number of genes = 184, number annotated = 79 (42.9)a Cactus × population Cactus (organ pipe > agria) Population (PP > LB) Population (LB > PP) age-specific differences in gene expression using false discovery rate corrected paired t-tests (Benjamini and Hochberg 1995) that had absolute fold changes >1.5. Using the 9114 orthologs from D. melanogaster, we performed gene ontology analysis with DAVID Bioinformatics Resources 6.7 (Huang et al. 2009) in order to identify functionally related genes that changed with age. For the present analysis focusing on cactus effects, we pooled the data across adult ages and performed a mixed model Anova in SAS (SAS-Institute 2004) with population, cactus, and population × cactus effects on gene expression (Table 2, Supplementary Table 1). We limited our analyses to adult females due to the large number of whole genome hybridizations (n = 86, some replicates were missing). Organ pipe-reared adults showed significantly increased expression of genes that were enriched for neurotransmitter binding, circadian rhythm, and courtship and mating behavioral functions, but no genes were expressed at significantly greater levels due to agria than organ pipe cactus (AG > OP) for females from these 2 populations (Tables 2 and 3). Thus, organ pipe cactus increased expression of a small group of gated ion channel genes associated with neurotransmission, circadian rhythm, and courtship behavior genes in female D. mojavensis. One odorant binding gene, Obp56h, was also upregulated due to organ pipe cactus, showed significant increases in transcription starting in the first larval instar (Etges et al., submitted), is expressed in antennae of both sexes, the pharyngeal organs, and possibly functions in both olfactory and gustatory systems (Galindo and Smith 2001), but ligands that it interacts with remain unknown. Given that organ pipe-reared females, particularly those from mainland populations, express increased discrimination among males during courtship (Etges 1992; Brazner and Etges 1993), and organ pipe-reared F2 males had higher mating success than those reared on agria cactus and exhibited G × E interactions for CHCs (Etges et al. 2009), these groups of genes (Table 3) are good candidates for further analysis of why organ pipe cactus increases premating isolation between Baja and mainland populations of D. mojavensis. These results also indicated that mainland, Las Bocas females showed significant enrichment for fatty acid metabolism genes, as well as genes with iron binding functions, such as P450 genes associated with detoxification of xenobiotics, secondary compounds in these cacti including fatty acids, sterol diols, and high levels of triterpene glycosides (Fogleman et al. 1998). Of the 251 genes showing higher expression in Punta Prieta versus Las Bocas females, 146 (58.2 %) were annotated and showed significant enrichment for transcription/RNA synthesis indicating these Baja females had higher overall rates of gene expression than mainland females when reared on fermenting cactus and ethanol vapor (Table 2). For transcript abundance showing significant cactus × population interactions, the 302/514 annotated orthologs were significantly enriched for iron binding/P450 function and fatty acid synthesis similar to the LB > PP population level differences (Table 2). Overall, the patterns of differential gene expression in these populations of D. mojavensis revealed that differences in cactus rearing substrates had significant effects Table 2 Significant overall adult gene expression differences (FDR <0.01 and >1.5-fold difference) due to population, cactus, and population × cactus interaction Journal of Heredity Etges • Genetics, Environments, and Speciation Table 3 Orthologous Drosophila melanogaster genes that were significantly overexpressed in adult Drosophila mojavensis reared on organ pipe versus agria cactus that comprised the 2 significant enriched GO clusters from Table 2, 1) neurotransmitter binding/receptors and 2) circadian rhythm, courtship behavior 1. 2. Dmel gene ID Dmel orthologue Dmel ortho name Biological function FBgn0034656 CG17922 FBgn0004244 Rdl Intracellular cyclic nucleotide activated cation channel complex Resistant to dieldrin FBgn0032151 nAcRα-30D FBgn0024963 GluClα FBgn0028875 nAcRα-34E Nicotinic acetylcholine receptor α 34E FBgn0004244 Rdl Resistant to dieldrin FBgn0027491 Cdk5α Cdk5 activator-like protein FBgn0031652 FBgn0039298 jet to jetlag takeout FBgn0015374 crl Courtless FBgn0004595 pros prospero FBgn0034475 Obp56h Odorant-binding protein 56h Nicotinic acetylcholine receptor α 30D GluClα Regulation of olfactory learning, regulation of circadian sleep/wake cycle Ion transport Extracellular-glutamate-gated chloride channel activity, postsynaptic membrane Acetylcholine binding, acetylcholine-gated channel complex Regulation of olfactory learning, regulation of circadian sleep/wake cycle Locomotor behavior, axonogenesis, determination of adult lifespan Circadian behavior, locomotor rhythm Courtship behavior, adult feeding behavior, circadian rhythm Ubiquitin-protein ligase activity, male courtship behavior, spermatogenesis Sequence-specific DNA binding transcription factor activity, nervous system development Olfactory behavior, response to pheromone See text for details. on nervous system and courtship behavior genes and that these populations responded differently to these host plants in transcription of genes involved with xenobiotic metabolism and fatty acid synthesis. In the second study, Smith et al. (2013) used SOLiD 4 transcriptome sequencing to assess agria and organ pipe cactus-reared males allowed to court and/or mate with organ pipe-reared females in multiple-choice tests. All flies were derived from a population collected in Organ Pipe National Monument, Arizona. Differences due to cactus-rearing substrates, male mating success and mating success × cactus interactions were assessed for both differentially expressed transcripts and those showing alternative splicing. However, these males were cultured on fermenting cactus, but reared on lab food as adults until the mating trials began as in previous studies (Etges 1992). Just 19 orthologs showed differences in expression levels due to mating success, and only 11 of these were annotated (Tables 4 and 5). In males that achieved copulation, Dmoj\GI18531, an ortholog of CG16894 in D. melanogaster, was upregulated that is associated with ubiquitin-conjugating enzyme activity in testis. Another protein-binding gene, an ortholog of Traf4, was upregulated, as were grg (no known function), esg associated with olfactory behavior regulation of transcription though zinc finger DNA binding domains, and CG1887 associated with defense response. Accessory protein gene Acp32CD was upregulated in unmated males; its function is associated with decreasing female receptivity suggesting male D. mojavensis decrease transcription of Acp32CD after mating. For rearing substrate differences, I reanalyzed the data in Smith et al. (2013) by separating the gene lists for differential expression to assess relative up/down transcript abundance (Tables 4 and 5) as they grouped these genes for functional annotation. As with cactus-reared females described above, far more genes showed significantly greater transcript abundance in organ pipe-reared males versus agria-reared males, OP > AG, n = 97, than AG > OP, n = 14. Although Smith et al. (2013) reported 4 genes enriched for chemosensory and olfactory function, this functional group was not recovered when the up/down lists were separated (Tables 4 and 5). Only 44% of these genes are annotated and showed weak functional clustering for nucleotide binding and signal transduction. Agria cactus caused increased transcript abundance for 14 genes, 11 of which were annotated, with most involved in defense and immune response (Smith et al. 2013). A larger number of differentially expressed genes exhibited cactus × mating success interactions, n = 147, that were weakly enriched for protein manufacture including mitochondrial function and assembly, as well as ribonuclear binding. Transcriptome sequencing made possible analysis of differences in alternate exon splicing (AE) influenced by mating success and cactus rearing (Table 5). An unexpectedly large number of genes with AE differences were observed caused by rearing substrates (n = 64) and the interaction between cactus and mating success (n = 48) that were functionally enriched for membrane ion channel, metal ion binding, and nucleotide binding. Gene annotations revealed multiple cases 763 764 aResults SerB phosphatase Regulation female receptivity RNA pol II Phosphatase Antibacteria resp. GTPase . Olfactory behavior G-protein coupled receptor 0.9a 0.6 0.7 from Smith et al. (2013), for cactus they did not separate up/down gene lists. Rab30 Bgb CG11425 DptB Acp32CD aay Traf4 Mated < unmated = 10 grg esg Defense response No known function Olfactory behavior Protein binding CG1887 Nucleotide binding GOTerm Mated > unmated = 9 Ubiquitin enzyme Number annotated = 43 (44.3%) Number annotated = 11 (57.9%) CG16894 Number of genes = 97 Number of genes = 19 Enrich score Cactus (organ pipe > agria) Mating success Table 4 Differences in transcript abundance No functionally enriched clusters, most genes are defense response GOTerm Enrich score Number annotated = 11 (78.6%) Number of genes = 14 Cactus (agria > organ pipe) Nucleotide binding, RNA recognition Ribosome Mitochondria GOTerm 0.7 1.1 1.1 Enrich score Number annotated = 82 (62.3%) Number of genes = 147 Cactus × mating success Journal of Heredity Etges • Genetics, Environments, and Speciation Table 5 Alternate splicing in adult Drosophila mojavensis males that either successfully mated or did not Mating success Cactus Cactus × mate Number of genes = 28 Number of genes = 64 Number of genes = 48 Number annotated = 23 (82.1) Number annotated = 49 (76.5) Number annotated = 33 (68.8) GOTerm GOTerm Enrich score GOTerm Enrich score Ion channel, membrane Ion, metal binding 1.4 Ion, metal binding 0.4 1.0 Nucleotide binding 0.2 Enrich score None Gene names are Drosophila melanogaster orthologs and GOTerms are functionally enriched clusters identified by DAVID. See text for details. Table 6 Functional clustering of alternately spliced genes due to the effects of culturing male Drosophila mojavensis on organ pipe versus agria cactus Dmoj gene Dmel ortho Dmel ortho name Biological function GOTerm–ion channel, membrane FBgn0132826 CG6723 FBgn0140123 Ca-alpha1D — Ca-alpha1D FBgn0142139 CG7882 — FBgn0146694 nAcRalpha-80B FBgn0146742 slo Nicotinic acetylcholine receptor α 80D Slowpoke FBgn0147216 Nmdar1 Sodium iodide symporter activity Voltage-gated calcium channel complex Glucose transmembrane transporter activity Nicotinic acetylcholine-gated receptor channel complex Calcium-activated potassium channel activity, courtship songs N-methyl-D-aspartate selective glutamate receptor activity, longterm memory GOTerm–ion, metal binding FBgn0133359 CG17272 FBgn0137845 rdgB Glutamate NMDA receptor subunit 1 — Retinal degeneration B FBgn0138983 peb Pebbled FBgn0142664 ari-2 Ariadne 2 FBgn0142910 Git FBgn0146608 Rim FBgn0146742 slo G protein-coupled receptor kinase interacting ArfGAP Rab3-interacting molecule Slowpoke FBgn0146746 FBgn0147079 FBgn0147489 tld CG14869 mRpL19 FBgn0147216 Nmdar1 Tolloid — Mitochondrial ribosomal protein L19 Glutamate NMDA receptor subunit 1 of cactus-caused AE for ion membrane channel function associated with memory and courtship song (Table 6), including slowpoke, known to influence pulse rate in D. melanogaster courtship songs (Peixoto and Hall 1998) due to its role in calcium-activated potassium channel activity. While none of these cactus-influenced AE genes overlapped with those that were differentially regulated in females (Table 3), there were Calcium ion binding Rhodopsin-mediated signaling pathway, phototransduction, perception of smell Transcription factor activity, zinc finger, C2H2-like Ubiquitin protein ligase activity, zinc finger, C6HC type Somatic muscle development, ARF GTPase activator activity Small GTPase regulator activity, regulation of exocytosis Calcium-activated potassium channel activity, courtship songs Metalloendopeptidase activity Metalloendopeptidase activity Mitochondrial large ribosomal subunit N-methyl-D-aspartate selective glutamate receptor activity, longterm memory a few like nAcRα-34E and nAcRalpha-80B, both with acetylcholine-gated receptor function, and Nmdar1 and GluClα, both with glutamate receptor activity and gated chloride channel activity, that exhibited functional overlap associated with neurotransmitter binding/receptor activity. Thus, differences in gene expression due to cactus-rearing substrates influenced males and females in somewhat similar ways involving neural 765 Journal of Heredity function and gated ion channel activity including variation in expression of calcium-activated potassium channels controlled by the slowpoke protein thought to alter flight muscle excitability and several courtship song components (Greenspan and Ferveur 2000). In D. mojavensis, a handful of QTL and QTL × cactus interactions influenced courtship song variation. The second chromosome region containing slowpoke, linked to microsatellite locus Dmoj2_2868a, was associated with variation in male time to copulation; P = 0.01, components of courtship song variation including interburst interval, IBI; P = 0.003, and number of bursts; P = 0.009 (Etges et al. 2007). IBI and number of bursts were also influenced by Dmoj2_2868a × cactus interactions (P = 0.036, and 0.039 respectively). Thus, in cactusreared D. mojavensis, male courtship song differences expressed in a cactus-specific manner were associated with both genetic differences between mainland and Baja populations and were localized around slowpoke, as well as cactus influenced differences in patterns of alternate messenger RNA splicing involving slowpoke and other genes. Without the environmental context of host cactus differences, it would not be possible to both investigate why cactus-specific sets of genes are differentially expressed in males and females, and certainly be more difficult to begin isolating candidate genes like slowpoke in order to investigate how alternate splicing patterns caused by different host plants may contribute to differences in courtship success and premating isolation between populations. Prospects for Speciation Genetics A major goal in most speciation research programs is to isolate the genetic factors responsible for reproductive isolation. In systems where ecological divergence can be shown to be associated with adaptations that have caused reproductive isolation thought to be driving speciation, an ultimate goal is to identify and understand the particular sets of interacting genes and their patterns of expression that have evolved in response to differences in both sexual and ambient environmental conditions. Whole-genome transcriptomic analysis is a first step in understanding the nature of genome–organism–environment interactions for speciation phenotypes, but much more work will be necessary to understand the subtle connections between gene expression and phenotypic variation. At the very least, we have isolated groups of differentially and alternately expressed candidate genes that are sensitive to rearing on alternate host plants. As these host plant effects are known to directly influence the degree of premating isolation mediated by CHCs and courtship songs, this approach has brought us closer to identifying functional groups of genes responsible for reproductive isolation. Given the long-term interest in D. mojavensis as a model species for understanding interactions between its patterns of host plant use (Fellows and Heed 1972), patterns of premating isolation (Zouros and d’Entremont 1974; Wasserman and Koepfer 1977), phylogeography (Heed 1978), history (Ruiz et al. 1990), use of cactophilic yeasts and bacteria (Starmer et al. 1976; Young et al. 1981; Fogleman and Foster 1989), 766 adaptation to host plants (Etges 1990), and systematic relationships (Durando et al. 2000; Oliveira et al. 2012), these efforts in understanding genome evolution and expression in different environments will reveal the genetic basis for adaptation and reproductive isolation, and how they are connected. Both regulatory and structural genetic elements are expected to be involved, so faster progress will be made when fully sequenced and assembled genomes are made available that have been functionally annotated. Although the logic of gene ontology relies on critical assumptions about structure and function that may not always hold as structurally similar genes may evolve new functions in other species, it remains a major tool in functional genomics. Because functional gene clusters have been identified that influence expression of traits responsible for reproductive isolation in the context of the environments in which they are expressed, we expect further progress will be made by isolating downstream expression differences, proteomics, and then assembling protein networks in the context the of biochemical pathways and tissue-specific patterns of expression. As most of the phenotypes of interest are expected to be polygenic, a gene network approach will be required as classical genetic tools in nonmodel species such as gene knockouts are not yet available. Identification of candidate genes with known physiological functions can, however, speed genetic analysis to reveal examples of simpler genotype–phenotype relationships with potential relevance to ecological divergence and reproductive isolation (e.g., Chung et al. 2014). Perhaps the greatest impediment to revealing underlying mechanisms in speciation genetics in almost all organisms is the lack of fully annotated genomes. A major challenge to complete the detailing of the interactions between genomes and the environments in which they are expressed is to understand the functional interaction of all genetic elements that contribute to reproductive isolation. Without documented gene functions in the organisms in which they are expressed, this goal will remain elusive. Supplementary Material Supplementary material can be found at http://www.jhered. oxfordjournals.org/. Funding National Science Foundation grants (NSF DEB-02111025 to W.J.E., EF-0723930 to A. G. Gibbs and W.J.E.). Microarray processing at the UNLV Genomics Core Facility was supported by grants from the National Center for Research Resources (5P20RR016464-11); the National Institute of General Medical Sciences (8P20GM103440-11). Acknowledgments I want to thank K. Shaw for organizing the 2013 AGA symposium on speciation and making this collection of symposium papers possible, A. J. Etges • Genetics, Environments, and Speciation Marlon and G. Almeida for excellent technical assistance, S. Rajpurohit and A. Gibbs for microarray data processing and discussion, and C. Ross for statistical help with the microarray studies. MIAME compliant microarray data is deposited at Gene Expression Omnibus (http://www.ncbi.nlm.nih. gov/geo/) with accession number GSE54510. References Axelrod DI. 1979. Age and origin of Sonoran Desert vegetation. Calif Acad Sci Occas Papers. 132:1–74. Barbour M, Keeler-Wolf T, Schoenherr AA. 2007. Terrestrial vegetation of California. Berkeley (CA): University of California Press. Beckenbach AT, Heed WB, Etges WJ. 2008. A mitochondrial DNA analysis of vicariant speciation in two lineages in the Drosophila mulleri subgroup. Evol Ecol Res. 10:475–492. Benjamini Y, Hochberg Y. 1995. Controlling the false discovery rate: a practical and powerful approach to multiple testing. J Royal Stat Soc B. 57:289–300. Drosophila-12-Genomes-Consortium. 2007. Evolution of genes and genomes on the Drosophila phylogeny. Nature. 450:203–218. Durando CM, Baker RH, Etges WJ, Heed WB, Wasserman M, DeSalle R. 2000. Phylogenetic analysis of the repleta species group of the genus Drosophila using multiple sources of characters. Mol Phylogenet Evol. 16:296–307. Egan SP, Funk DJ. 2009. Ecologically dependent postmating isolation between sympatric host forms of Neochlamisus bebbianae leaf beetles. Proc Natl Acad Sci USA. 106:19426–19431. Etges WJ. 1989. Divergence in cactophilic Drosophila: the evolutionary significance of adult ethanol metabolism. Evolution. 43:1316–1319. Etges WJ. 1989. Evolution of developmental homeostasis in Drosophila mojavensis. Evol Ecol. 3:189–201. Etges WJ. 1990. Direction of life history evolution in Drosophila mojavensis. In: Barker JSF, Starmer WT, MacIntyre RJ, editors. Ecological and evolutionary genetics of Drosophila. New York: Plenum. p. 37–56. Etges WJ. 1992. Premating isolation is determined by larval rearing substrates in cactophilic Drosophila mojavensis. Evolution. 46:1945–1950. Blair WF. 1947. Variation in shade of pelage of local populations of the cactus-mouse (Peromyscus eremicus) in the Tularosa basin and adjacent areas of southern New Mexico. Contr Lab Vert Biol Univ Michigan. 37:1–7. Etges WJ. 1998. Premating isolation is determined by larval rearing substrates in cactophilic Drosophila mojavensis. IV. Correlated responses in behavioral isolation to artificial selection on a life history trait. Am Nat. 152:129–144. Bradshaw HD, Wilbert SM, Otto KG, Schemske DW. 1995. Genetic mapping of floral traits associated with reproductive isolation in monkeyflowers (Mimulus). Nature. 376:762–765. Etges WJ, Ahrens MA. 2001. Premating isolation is determined by larval rearing substrates in cactophilic Drosophila mojavensis. V. Deep geographic variation in epicuticular hydrocarbons among isolated populations. Am Nat. 158:585–598. Brazner JC. 1983. The influence of rearing environment on sexual isolation between populations of Drosophila mojavensis: an alternative to the character displacement hypothesis [MS]. Syracuse: Syracuse University. Brazner JC, Etges WJ. 1993. Pre-mating isolation is determined by larval rearing substrates in cactophilic Drosophila mojavensis. II. Effects of larval substrates on time to copulation, mate choice, and mating propensity. Evol Ecol. 7:605–624. Burga A, Lehner B. 2012. Beyond genotype to phenotype: why the phenotype of an individual cannot always be predicted from their genome sequence and the environment that they experience. FEBS J. 279:3765–3775. Burton RS, Barreto FS. 2012. A disproportionate role for mtDNA in Dobzhansky–Muller incompatibilities? Mol Ecol. 21:4942–4957. Byrne BC. 1999. Behaviour-genetic analysis of lovesongs in desert species of Drosophila [Ph.D.]. Leicester: University of Leicester. Chari S, Dworkin I. 2013. The conditional nature of genetic interactions: the consequences of wild-type backgrounds on mutational interactions in a genome-wide modifier screen. PLoS Genet. 9:e1003661. Chung H, Loehlin DW, Dufour HD, Vaccarro K, Millar JG, Carroll SB. 2014. A single gene affects both ecological divergence and mate choice in Drosophila. Science. 343:1148–1151. Cook LM, Grant BS, Saccheri IJ, Mallet J. 2012. Selective bird predation on the peppered moth: the last experiment of Michael Majerus. Biol Lett. 8:609–612. Counterman BA, Noor MA. 2006. Multilocus test for introgression between the cactophilic species Drosophila mojavensis and Drosophila arizonae. Am Nat. 168:682–696. Etges WJ, de Oliveira CC, Gragg E, Ortíz-Barrientos D, Noor MA, Ritchie MG. 2007. Genetics of incipient speciation in Drosophila mojavensis. I. Male courtship song, mating success, and genotype x environment interactions. Evolution. 61:1106–1119. Etges WJ, de Oliveira CC, Noor MA, Ritchie MG. 2010. Genetics of incipient speciation in Drosophila mojavensis. III. Life-history divergence in allopatry and reproductive isolation. Evolution. 64:3549–3569. Etges WJ, de Oliveira CC, Ritchie MG, Noor MAF. 2009. Genetics of incipient speciation in Drosophila mojavensis. II. Host plants and mating status influence cuticular hydrocarbon QTL expression and G x E interactions. Evolution. 63:1712–1730. Etges WJ, Heed WB. 1992. Remating effects on the genetic structure of female life histories in populations of Drosophila mojavensis. Heredity. 68:515–528. Etges WJ, Johnson WR, Duncan GA, Huckins G, Heed WB. 1999. Ecological genetics of cactophilic Drosophila. In: Robichaux R, editor. Ecology of Sonoran Desert plants and plant communities. Tucson: University of Arizona Press. p. 164–214. Etges WJ, Klassen CS. 1989. Influences of atmospheric ethanol on adult Drosophila mojavensis: altered metabolic rates and increases in fitness among populations. Physiol Zool. 62:170–193. Etges WJ, Over KF, de Oliveira CC, Ritchie MG. 2006. Inheritance of courtship song variation among geographically isolated populations of Drosophila mojavensis. Anim Behav. 71:1205–1214. Coyne JA, Orr HA. 2004. Speciation. Sunderland (MA): Sinauer. Feder JL, Egan SP, Nosil P. 2012. The genomics of speciation-with-geneflow. Trends Genet. 28:342–350. Dambroski HR, Linn C Jr, Berlocher SH, Forbes AA, Roelofs W, Feder JL. 2005. The genetic basis for fruit odor discrimination in Rhagoletis flies and its significance for sympatric host shifts. Evolution. 59:1953–1964. Feder JL, Nosil P. 2009. Chromosomal inversions and species differences: when are genes affecting adaptive divergence and reproductive isolation expected to reside within inversions? Evolution. 63:3061–3075. Dice LR, Blossom PM. 1937. Studies of mammalian ecology in sourthwestern North America with special attention to the colors of desert mammals. Carnegie Inst Wash Publ. 485:1–129. Feder JL, Xie X, Rull J, Velez S, Forbes A, Leung B, Dambroski H, Filchak KE, Aluja M. 2005. Mayr, Dobzhansky, and Bush and the complexities of sympatric speciation in Rhagoletis. Proc Natl Acad Sci USA. 102(Suppl 1):6573–6580. Doi M, Matsuda M, Tomaru M, Matsubayashi H, Oguma Y. 2001. A locus for female discrimination behavior causing sexual isolation in Drosophila. Proc Natl Acad Sci USA. 98:6714–6719. Fellows DP, Heed WB. 1972. Factors affecting host plant selection in desertadapted cactiphilic Drosophila. Ecology. 53:850–858. 767 Journal of Heredity Fogleman JC, Danielson PB, MacIntyre RJ. 1998. The molecular basis of adaptation in Drosophila: the role of cytochrome P450s. Evol Biol. 30:15–77. genetics and biology of Drosophila, Vol. 3e. New York: Academic Press. p. 311–345. Fogleman JC, Foster JLM. 1989. Microbial colonization of injured cactus tissue Stenocereus gummosus and its relationship to the ecology of cactophilic Drosophila mojavensis. App Environ Microbiol. 55:100–105. Howard RW, Blomquist GJ. 1982. Chemical ecology and biochemistry of insect hydrocarbons. Ann. Rev. Entomol. 27:149–172. Ford EB. 1975. Ecological genetics. New York: Wiley and Sons. Howard RW, Blomquist GJ. 2005. Ecological, behavioral, and biochemical aspects of insect hydrocarbons. Annu Rev Entomol. 50:371–393. Frentiu FD, Adamski M, McGraw EA, Blows MW, Chenoweth SF. 2009. An expressed sequence tag (EST) library for Drosophila serrata, a model system for sexual selection and climatic adaptation studies. BMC Genomics. 10:40. Huang da W, Sherman BT, Lempicki RA. 2009. Systematic and integrative analysis of large gene lists using DAVID bioinformatics resources. Nat Protoc. 4:44–57. Funk DJ, Filchak KE, Feder JL. 2002. Herbivorous insects: model systems for the comparative study of speciation ecology. Genetica. 116:251–267. Jennings JH, Etges WJ. 2010. Species hybrids in the laboratory but not in nature: a reanalysis of premating isolation between Drosophila arizonae and D. mojavensis. Evolution. 64:587–598. Galindo K, Smith DP. 2001. A large family of divergent Drosophila odorantbinding proteins expressed in gustatory and olfactory sensilla. Genetics. 159:1059–1072. Galvan A, Ioannidis JP, Dragani TA. 2010. Beyond genome-wide association studies: genetic heterogeneity and individual predisposition to cancer. Trends Genet. 26:132–141. Gastil RG, Phillips RP, Allison EC. 1975. Reconnaissance geology of the state of Baja California. Geol Soc Amer Mem. 140:1–170. Gerhardt HC, Huber F. 2002 Acoustic communication in insects and anurans. Chicago: Univ. Chicago Press. Gibson G. 2008. The environmental contribution to gene expression profiles. Nat Rev Genet. 9:575–581. Gleason JM, Jallon JM, Rouault JD, Ritchie MG. 2005. Quantitative trait loci for cuticular hydrocarbons associated with sexual isolation between Drosophila simulans and D. sechellia. Genetics. 171:1789–1798. Gleason JM, James RA, Wicker-Thomas C, Ritchie MG. 2009. Identification of quantitative trait loci function through analysis of multiple cuticular hydrocarbons differing between Drosophila simulans and Drosophila sechellia females. Heredity (Edinb). 103:416–424. Gleason JM, Nuzhdin SV, Ritchie MG. 2002. Quantitative trait loci affecting a courtship signal in Drosophila melanogaster. Heredity (Edinb). 89:1–6. Gompert Z, Comeault AA, Farkas TE, Feder JL, Parchman TL, Buerkle CA, Nosil P. 2014. Experimental evidence for ecological selection on genome variation in the wild. Ecol Lett. 17:369–379. Kang EY, Han B, Furlotte N, Joo JW, Shih D, Davis RC, Lusis AJ, Eskin E. 2014. Meta-analysis identifies gene-by-environment interactions as demonstrated in a study of 4,965 mice. PLoS Genet. 10:e1004022. Kaufman D. 1974. Adaptive coloration in Peromyscus polionotus: experimental selection by owls. J Mammal. 55:271–283. Knowles LL, Markow TA. 2001. Sexually antagonistic coevolution of a postmating-prezygotic reproductive character in desert Drosophila. Proc Natl Acad Sci USA. 98:8692–8696. Leips J, Mackay TF. 2000. Quantitative trait loci for life span in Drosophila melanogaster: interactions with genetic background and larval density. Genetics. 155:1773–1788. Lewontin RC. 1991. Biology as ideology: The doctrine of DNA. New York: HarperCollins. Lewontin RC. 2000. The triple helix: gene, organism, and environment. Cambridge: Harvard University Press. Linnen CR, Poh YP, Peterson BK, Barrett RD, Larson JG, Jensen JD, Hoekstra HE. 2013. Adaptive evolution of multiple traits through multiple mutations at a single gene. Science. 339:1312–1316. Machado CA, Matzkin LM, Reed LK, Markow TA. 2007. Multilocus nuclear sequences reveal intra- and interspecific relationships among chromosomally polymorphic species of cactophilic Drosophila. Mol Ecol. 16:3009–3024. Mackay TFC. 2014. Epistasis and quantitative traits: using model organisms to study gene-gene interactions. Nat Rev Genet. 15:22–33. Greenfield MD. 2002. Signalers and receivers: mechanisms and evolution of arthropod communication. New York: Oxford Univ. Press. Mackay TFC, Anholt RRH. 2007. Ain’t misbehavin’? Genotype-environment interactions and the genetics of behavior. Trends in Genet. 23:311–314. Greenspan RJ, Ferveur JF. 2000. Courtship in Drosophila. Annu Rev Genet. 34:205–232. Majerus MEN. 1998. Melanism: evolution in action. Oxford: Oxford University Press. Grishkevich V, Yanai I. 2013. The genomic determinants of genotype × environment interactions in gene expression. Trends Genet. 29:479–487. Mallet J, Dasmahapatra KK. 2012. Hybrid zones and the speciation continuum in Heliconius butterflies. Mol Ecol. 21:5643–5645. Gurganus MC, Fry JD, Nuzhdin SV, Pasyukova EG, Lyman RF, Mackay TF. 1998. Genotype-environment interaction at quantitative trait loci affecting sensory bristle number in Drosophila melanogaster. Genetics. 149:1883–1898. Malone JH, Oliver B. 2011. Microarrays, deep sequencing and the true measure of the transcriptome. BMC Biol. 9:34. Havens JA, Orzack SH, Etges WJ. 2011. Mate choice opportunity leads to shorter offspring development time in a desert insect. J Evol Biol. 24:1317–1324. Hawthorne DJ, Via S. 2001. Genetic linkage of ecological specialization and reproductive isolation in pea aphids. Nature. 412:904–907. Heed WB. 1978. Ecology and genetics of Sonoran Desert Drosophila. In: Brussard PF, editor. Ecological genetics: the interface. New York: SpringerVerlag. p. 109–126. Heed WB. 1981. Central and marginal populations revisited. Dros. Inform. Serv. 56:60–61. Heed WB. 1982. The origin of Drosophila in the Sonoran Desert. In: Barker JSF, Starmer WT, editors. Ecological genetics and evolution: the CactusYeast-Drosophila Model System. Sydney: Academic Press. p. 65–80. Heed WB, Mangan RL. 1986. Community ecology of the Sonoran Desert Drosophila. In: Ashburner M, Carson HL, Thompson JN, editors. The 768 Markow TA. 1991. Sexual isolation among populations of Drosophila mojavensis. Evolution. 45:1525–1529. Markow TA, Fogleman JC, Heed WB. 1983. Reproductive isolation in Sonoran Desert Drosophila. Evolution. 37:649–652. Markow TA, Toolson EC. 1990. Temperature effects on epicuticular hydrocarbons and sexual isolation in Drosophila mojavensis. In: Barker JSF, Starmer WT, MacIntyre RJ, editors. Ecological and evolutionary genetics of Drosophila: monographs in evolutionary biology. New York: Plenum. p. 315–331. Massie KR, Markow TA. 2005. Sympatry, allopatry and sexual isolation between Drosophila mojavensis and D. arizonae. Hereditas. 142:51–55. Matzkin LM, Eanes WF. 2003. Sequence variation of alcohol dehydrogenase (Adh) paralogs in cactophilic Drosophila. Genetics. 163:181–194. Mettler LE. 1957. Studies on experimental populations of Drosophila arizonensis and Drosophila mojavensis. Univ Tex Publ 5721:157–181. Mettler LE, Nagle JJ. 1966. Corroboratory evidence for the concept of the sympatric origin of isolating mechanisms. DIS. 41:76. Etges • Genetics, Environments, and Speciation Michaelson JJ, Loguercio S, Beyer A. 2009. Detection and interpretation of expression quantitative trait loci (eQTL). Methods. 48:265–276. SAS-Institute. 2004. SAS/STAT 9.1.2. Cary (NC): SAS Institute, Inc. Mills LE, Batterham P, Alegre J, Starmer WT, Sullivan. DT. 1986. Molecular genetics characterization of a locus that contains duplicate Adh genes in Drosophila mojavensis and related species. Genetics. 112:295–310. Schwarz D, Robertson HM, Feder JL, Varala K, Hudson ME, Ragland GJ, Hahn DA, Berlocher SH. 2009. Sympatric ecological speciation meets pyrosequencing: sampling the transcriptome of the apple maggot Rhagoletis pomonella. BMC Genomics. 10:633. Nachman MW, Hoekstra HE, D’Agostino SL. 2003. The genetic basis of adaptive melanism in pocket mice. Proc Natl Acad Sci USA. 100:5268–5273. Seehausen O, vanAlphen JJM, Witte F. 1997. Cichlid fish diversity threatened by eutrophication that curbs sexual selection. Science. 277:1808–1811. Naisbit RE, Jiggins CD, Mallet J. 2003. Mimicry: developmental genes that contribute to speciation. Evol Dev. 5:269–280. Shaw KL, Mullen SP. 2011. Genes versus phenotypes in the study of speciation. Genetica. 139:649–661. Nosil P. 2012. Ecological speciation. Oxford: Oxford University Press. Shaw KL, Parsons YM. 2002. Divergence of mate recognition behavior and its consequences for genetic architectures of speciation. Am Nat. 159(Suppl 3):S61–S75. Nosil P, Parchman TL, Feder JL, Gompert Z. 2012. Do highly divergent loci reside in genomic regions affecting reproductive isolation? A test using next-generation sequence data in Timema stick insects. BMC Evol Biol. 12:164. Nosil P, Vines TH, Funk DJ. 2005. Perspective: reproductive isolation caused by natural selection against immigrants from divergent habitats. Evolution. 59:705–719. Nuzhdin SV, Friesen ML, McIntyre LM. 2012. Genotype-phenotype mapping in a post-GWAS world. Trends Genet. 28:421–426. Oliveira DC, Almeida FC, O’Grady PM, Armella MA, DeSalle R, Etges WJ. 2012. Monophyly, divergence times, and evolution of host plant use inferred from a revised phylogeny of the Drosophila repleta species group. Mol Phylogenet Evol. 64:533–544. Orr HA, Masly JP, Presgraves DC. 2004. Speciation genes. Curr Opin Genet Dev. 14:675–679. Oshlack A, Robinson MD, Young MD. 2010. From RNA-seq reads to differential expression results. Genome Biol. 11:220. Pavey SA, Bernatchez L, Aubin-Horth N, Landry CR. 2012. What is needed for next-generation ecological and evolutionary genomics? Trends Ecol Evol. 27:673–678. Peixoto AA, Hall JC. 1998. Analysis of temperature-sensitive mutants reveals new genes involved in the courtship song of Drosophila. Genetics. 148:827–838. Pritchard VL, Dimond L, Harrison JS, S Velázquez CC, Zieba JT, Burton RS, Edmands S. 2011. Interpopulation hybridization results in widespread viability selection across the genome in Tigriopus californicus. BMC Genet. 12:54. Quackenbush J. 2001. Computational analysis of microarray data. Nat Rev Genet. 2:418–427. Rajpurohit S, Oliveira CC, Etges WJ, Gibbs AG. 2013. Functional genomic and phenotypic responses to desiccation in natural populations of a desert drosophilid. Mol Ecol. 22:2698–2715. Reed LK, Nyboer M, Markow TA. 2007. Evolutionary relationships of Drosophila mojavensis geographic host races and their sister species Drosophila arizonae. Mol Ecol. 16:1007–1022. Rodríguez RL, Sullivan LM, Snyder RL, Cocroft RB. 2008. Host shifts and the beginning of signal divergence. Evolution. 62:12–20. Rosenblum EB, Hoekstra HE, Nachman MW. 2004. Adaptive reptile color variation and the evolution of the Mc1r gene. Evolution. 58:1794–1808. Ross CL, Markow TA. 2006. Microsatellite variation among diverging populations of Drosophila mojavensis. J Evol Biol. 19:1691–1700. Singer MC, McBride CS. 2010. Multitrait, host-associated divergence among sets of butterfly populations: implications for reproductive isolation and ecological speciation. Evolution. 64:921–933. Smith G, Fang Y, Liu X, Kenny J, Cossins AR, de Oliveira CC, Etges WJ, Ritchie MG. 2013. Transcriptome-wide expression variation associated with environmental plasticity and mating success in cactophilic Drosophila mojavensis. Evolution. 67:1950–1963. Smith G, Lohse K, Etges WJ, Ritchie MG. 2012. Model-based comparisons of phylogeographic scenarios resolve the intraspecific divergence of cactophilic Drosophila mojavensis. Mol Ecol. 21:3293–3307. Starmer WT, Heed WB, Miranda M, Miller MW, Phaff HJ. 1976. The ecology of yeast flora associated with cactiphilic Drosophila and their host plants in the Sonoran Desert. Microb Ecol. 3:11–30. Starmer WT, Heed WB, Rockwood-Sluss ES. 1977. Extension of longevity in Drosophila mojavensis by environmental ethanol: differences between subraces. Proc Nat Acad Sci USA. 74:387–391. Stranger BE, Stahl EA, Raj T. 2011. Progress and promise of genomewide association studies for human complex trait genetics. Genetics. 187:367–383. Taylor EB, Boughman JW, Groenenboom M, Sniatynski M, Schluter D, Gow JL. 2006. Speciation in reverse: morphological and genetic evidence of the collapse of a three-spined stickleback (Gasterosteus aculeatus) species pair. Mol Ecol. 15:343–355. Ting CT, Tsaur SC, Sun S, Browne WE, Chen YC, Patel NH, Wu CI. 2004. Gene duplication and speciation in Drosophila: evidence from the Odysseus locus. Proc Natl Acad Sci USA. 101:12232–12235. Toolson EC. 1982. Effects of rearing temperature on cuticle permeability and epicuticular lipid composition in Drosophila pseudoobscura. J Exp Zool. 222:249–253. Turelli M, Lipkowitz JR, Brandvain Y. 2014. On the Coyne and Orr-igin of species: effects of intrinsic postzygotic isolation, ecological differentiation, x chromosome size, and sympatry on Drosophila speciation. Evolution. 68:1176–1187. Turner JRG. 1977. Butterfly mimicry: the genetical evolution of an adaptation. Evol Biol. 10:163–206. Tweedie S, Ashburner M, Falls K, Leyland P, McQuilton P, Marygold S, Millburn G, Osumi-Sutherland D, Schroeder A, Seal R, et al.; FlyBase Consortium. 2009. FlyBase: enhancing Drosophila Gene Ontology annotations. Nucleic Acids Res. 37:D555–D559. Ruiz A, Heed WB, Wasserman M. 1990. Evolution of the mojavensis cluster of cactophilic Drosophila with descriptions of two new species. J Hered. 81:30–42. Van Devender TR. 1990. Late quarternary vegetation and climate of the Sonoran Desert, United States and Mexico. In: Betancourt JL, Van Devender TR, Martin PS, editors. Packrat middens: the last 40,000 years of biotic change. Tucson: Univ. Arizona Press. p. 134–165. Ryner LC, Goodwin SF, Castrillon DH, Anand A, Villella A, Baker BS, Hall JC, Taylor BJ, Wasserman SA. 1996. Control of male sexual behavior and sexual orientation in Drosophila by the fruitless gene. Cell. 87:1079–1089. Wasserman M. 1962. Cytological studies of the repleta group of the genus Drosophila. V. The mulleri subgroup. Univ Texas Publ. 6205:85–117. Ruiz A, Heed WB. 1988. Host-plant specificity in the cactophilic Drosophila mulleri species complex. J Anim Ecol. 57:237–249. Via S. 2009. Natural selection in action during speciation. Proc Natl Acad Sci USA. 106(Suppl 1):9939–9946. 769 Journal of Heredity Wasserman M. 1992. Cytological evolution of the Drosophila repleta species group. In: Krimbas CB, Powell JR, editors. Drosophila inversion polymorphism. Boca Raton: CRC Press. p. 455–552. Yukilevich R. 2014. The rate test of speciation: estimating the likelihood of non-allopatric speciation from reproductive isolation rates in Drosophila. Evolution. 68:1150–1162. Wasserman M, Koepfer HR. 1977. Character displacement for sexual isolation between Drosophila mojavensis and Drosophila arizonensis. Evolution. 31:812–823. Zouros E, d’Entremont CJ. 1974. Sexual isolation among populations of Drosophila mojavensis race B. Dros Inf Serv. 51:112. Zouros E, d’Entremont CJ. 1980. Sexual isolation among populations of Drosophila mojavensis: response to pressure from a related species. Evolution. 34:421–430. Williams GC. 1966. Adaptation and natural selection: a critique of some current evolutionary thought. Princeton (NJ): Princeton University Press. Wray GA. 2013. Genomics and the evolution of phenotypic traits. Ann Rev Ecol Evol Syst. 44:51–72. Young DJ, Vacek DC, Heed WB. 1981. The facultatively anaerobic bacteria as a source of alcohols in three breeding substrates of cactophilic Drosophila. Dros Infor Serv. 56:165–166. 770 Received January 16, 2014; First decision March 5, 2014; Accepted May 31, 2014 Corresponding Editor: Kerry Shaw