Literature DB >> 31641487

Molecular biogeography and host relations of a parasitoid fly.

David A Gray1, Henry D Kunerth2,3, Marlene Zuk3, William H Cade4, Susan L Balenger5.   

Abstract

Successful geographic range expansion by parasites and parasitoids may also require host range expansion. Thus, the evolutionary advantages of host specialization may trade off against the ability to exploit new host species encountered in new geographic regions. Here, we use molecular techniques and confirmed host records to examine biogeography, population divergence, and host flexibility of the parasitoid fly, Ormia ochracea (Bigot). Gravid females of this fly find their cricket hosts acoustically by eavesdropping on male cricket calling songs; these songs vary greatly among the known host species of crickets. Using both nuclear and mitochondrial genetic markers, we (a) describe the geographical distribution and subdivision of genetic variation in O. ochracea from across the continental United States, the Mexican states of Sonora and Oaxaca, and populations introduced to Hawaii; (b) demonstrate that the distribution of genetic variation among fly populations is consistent with a single widespread species with regional host specialization, rather than locally differentiated cryptic species; (c) identify the more-probable source populations for the flies introduced to the Hawaiian islands; (d) examine genetic variation and substructure within Hawaii; (e) show that among-population geographic, genetic, and host song distances are all correlated; and (f) discuss specialization and lability in host-finding behavior in light of the diversity of cricket songs serving as host cues in different geographically separate populations.
© 2019 The Authors. Ecology and Evolution published by John Wiley & Sons Ltd.

Entities:  

Keywords:  Gryllus; Ormia; Teleogryllus; host specialization; parasitoid; range expansion; song distance matrix

Year:  2019        PMID: 31641487      PMCID: PMC6802024          DOI: 10.1002/ece3.5649

Source DB:  PubMed          Journal:  Ecol Evol        ISSN: 2045-7758            Impact factor:   2.912


INTRODUCTION

Evolutionary specialization is often viewed as a double‐edged sword: Specialization may facilitate efficient exploitation of favored resources, but may also inhibit exploitation of novel resources. Specialization has often been viewed as an evolutionary “dead end” (Jaenike, 1990; Kelley & Farrell, 1998; Raia & Fortelius, 2013), although recent research has revealed considerable flexibility among specialist lineages and occasional “reversals” from specialized to more generalized niches (Gompert et al., 2015; Vamosi, Armbruster, & Renner, 2014). The retention of evolutionary lability may be especially relevant for geographic range expansion; indeed, “generalist” species are often among the most invasive (Romanuk et al., 2009)—a pattern found among plants, arthropods, mammals, and birds (Blackburn & Duncan, 2001; González‐Suárez, Bacher, & Jeschke, 2015; Higgins & Richardson, 2014; Snyder & Evans, 2006). For specialist species to expand their geographic range, they must readily encounter suitable resources, exhibit phenotypic plasticity enabling adoption of novel resources, and/or show rapid evolutionary adaptation. Parasitoid insects, especially Ichneumonid and Braconid wasps (Hymenoptera) and Tachinid flies (Diptera), are especially illuminating for studies of host specialization, ranging from extreme generalists to extreme specialists (Quicke, 2014; Stireman, O'Hara, & Wood, 2006). Some species are sufficiently host‐specific to be used for classical biological control of pests (Parkman, Frank, Walker, & Schuster, 1996; Vargas, Leblanc, Putoa, & Eitam, 2007), others routinely utilize a broad range of hosts (Arnaud, 1978; Stireman, 2005; Tschorsnig, 2017), and in other cases, presumed generalists are later revealed to be complexes of cryptic specialists (Smith et al., 2008). Within the ca. 9,000 species of Tachinids, the Ormiini tribe represents a small group (ca. 68 described species) of highly specialized flies (Lehmann, 2003; Sabrosky, 1953a, 1953b). Several specializations are noteworthy for the entire group (so far as is known): All are parasitoids of crickets or katydids (Ensifera, Orthoptera); all locate their (principally male) hosts using a specialized ear (Edgecomb, Robert, Read, & Hoy, 1995; Hedwig & Robert, 2014) to eavesdrop on their male host's mating song (Allen, 1995; Cade, 1975; Lehmann, 2003); and all have sclerotized planidiform larvae which are somewhat mobile and actively burrow into the host (Adamo, Robert, Perez, & Hoy, 1995; Cantrell, 1988). Within this group, all genera with known hosts parasitize katydids (Tettigoniidae); in the genus Ormia, most species parasitize katydids but three species attack crickets and mole crickets (Gryllidae and Gryllotalpidae; Lehmann, 2003). The shift from katydids to crickets and mole crickets represents a significant shift in female fly hearing toward lower frequency sounds (ca. 4–5 kHz in crickets and ca. 2–3 kHz in mole crickets) than are typical of most katydids (often >> 10 kHz). Utilization of katydids with relatively low frequency calls may have facilitated the evolutionary transition to crickets and mole crickets. For example, certain katydid hosts of Ormiines have relatively low frequency calls, for example, ca. 5–6 kHz in Sciarasaga quadrata (host of Homotrixa alleni; Allen, Kamien, Berry, Byrne, & Hunt, 1999); ca. 7 kHz in Neoconocephalus robustus (host of O. brevicornis; Nutting, 1953); and ca. 8 kHz in Orchelimum pulchellum (one of several hosts of O. lineifrons; Shapiro, 1995). Within Ormia, O. ochracea has been most extensively studied. Peak sensitivity of female fly hearing closely matches or is at slightly higher frequencies than typical male host calling song (Robert, Amoroso, & Hoy, 1992). The current geographic range attributed to this species extends from Florida (Walker & Wineriter, 1991), across the southern Gulf States (Henne & Johnson, 2001), into Texas (Cade, 1975), Arizona (Sakaguchi & Gray, 2011), California (Wagner, 1996), and Mexico (Sabrosky, 1953b); throughout this range, it parasitizes various species of Gryllus field crickets (see below). In addition, O. ochracea was introduced to Hawaii by at least 1989 (Evenhuis, 2003), where it parasitizes Teleogryllus oceanicus, itself introduced to Hawaii from Australia via Oceania by at least 1877 (Kevan, 1990) and possibly earlier, perhaps facilitated by Polynesian settlement (Tinghitella, Zuk, Beveridge, & Simmons, 2011). Localized populations of O. ochracea show varying degrees of host specialization: Flies in Florida almost exclusively parasitize Gryllus rubens (Walker, 1993; Walker & Wineriter, 1991); flies in Texas primarily parasitize G. texensis (Cade, 1975); flies in Arizona regularly parasitize multiple Gryllus species (Sakaguchi & Gray, 2011); flies in southern California primarily parasitize G. lineaticeps (Wagner, 1996; Wagner & Basolo, 2007); and as noted above, Hawaiian flies parasitize T. oceanicus. Remarkably, playback experiments in Florida, Texas, California, and Hawaii, which simultaneously presented the songs of G. rubens, G. texensis, G. lineaticeps, and T. oceanicus, revealed that each fly population showed a significant (but not exclusive) preference for the song of its primary local host species of cricket (Gray, Banuelos, Walker, Cade, & Zuk, 2007). This suggests an even further degree of host specialization in these flies—possibly indicative of cryptic host races or species as has been found in other Tachinids (Smith et al., 2008; Smith, Woodley, Janzen, Hallwachs, & Hebert, 2006). Determining the extent to which geographic and host range subdivision is coupled with genetic subdivision is thus one of the goals of this study. Successful establishment of O. ochracea in Hawaii represents a significant expansion of both the geographic and host range of the fly. How can such a specialist invade switch to a novel host with a strongly divergent song structure, and in the course of a few decades come to prefer that novel host's song to the songs of ancestral hosts? Two of our aims in this paper are to use mitochondrial and nuclear markers both to examine genetic variation within Hawaii and to identify the more‐likely continental source population(s) of those Hawaiian flies, and thereby the most likely types of recent ancestral host songs. This necessitates broad sampling of continental populations, and we therefore expand upon the previous work in the United States and include flies from populations in both northern and southern Mexico, as well as catalog the confirmed host species and their songs in each of these areas. We apply standard phylogeographic analyses to mitochondrial DNA sequence data, including outgroup species of Ormia, and we adopt a population genetic approach to analysis of microsatellite nuclear markers.

METHODS

Fly collection

We collected flies at mesh screen and/or bottle traps using playbacks of cricket songs (Walker, 1989). The songs played to attract flies varied among populations and across years, but for mainland sites always included songs of 2–4 species of crickets at least one of which was a known local host; for Hawaiian sites, some collections (WHC, 2003) were made with playbacks of four cricket songs (see Gray et al., 2007), whereas later collections used T. oceanicus song (the only Hawaiian host). We also collected a small number of flies at lights or as they emerged from field‐collected crickets. Table 1 provides details of locations and dates of sampling. Collected flies were preserved in ethanol until DNA extraction and further analysis. We extracted DNA using a Qiagen DNeasy tissue kit according to the manufacturer's instructions. We used entire flies as source tissue for all of the mainland and 13 of the Hawaiian flies, and head and thorax tissue for the remainder of the Hawaiian flies. In theory, the whole tissue extractions could include DNA from larvae, although the amounts of such DNA would be trivial compared to maternal DNA. We quantified DNA using a NanoDrop system and adjusted concentrations to between 20 and 75 ng/μl.
Table 1

Sample collection data; not all specimens were used in all analyses

RegionLocalityDates N Collector(s)
FloridaGainesville, FLAugust 200241DAG
TexasSan Antonio, TXSeptember 20025WHC
Austin, TXSeptember 2002, 200429WHC and S. Walker 2002; DAG 2004
Huntsville, TXSeptember 20021S. Walker
ArizonaSedona, AZAugust 200412DAG
Oak Creek, AZAugust 20046DAG
Holbrook, AZAugust 20021DAG
Verde River, AZAugust 20043DAG
Madera Canyon, AZAugust 200410DAG
KOFA, AZSeptember 20052DAG
Yuma, AZNovember 20032A. Izzo
Parker Canyon, AZAugust 20042DAG
Petroglyph, AZSeptember 200616DAG
Pinery Canyon, AZSeptember 20045DAG
Portal, AZAugust 20031DAG
SonoraAlamos, Sonora, MXJuly 200617DAG
OaxacaSan Pablo Etla, Oaxaca, MXNovember 201413DAG
CaliforniaMalibu Creek, CASeptember and October 2003, 200422DAG
Stunt Ranch, CASeptember 200210DAG
Santa Margarita Reserve, CASeptember 20035DAG
HawaiiKauai, HIFebruary and August 201424MZ and SLB
Hilo, HIMarch 2003; February and August 201433WHC 2003; MZ and SLB 2014
Oahu, HIFebruary 20144MZ and SLB
Outgroups
Ormia depleta Gainesville, FLDecember 20032H. Frank, via T. J. Walker
Ormia lineifrons Gainesville, FLDecember 20032H. Frank, via T. J. Walker
Sample collection data; not all specimens were used in all analyses

Genetic markers and analysis

We analyzed population structure using both mitochondrial and nuclear markers. For mtDNA, we analyzed a section of Cytochrome C Oxidase subunit I (hereafter COI) PCR amplified in two overlapping fragments with “universal” primer pairs Jerry‐Pat and Ron‐Nancy (Simon et al., 1994), resulting in 1,111 bp after alignment. In addition, we developed nuclear microsatellite markers de novo for this project. Marker discovery was performed by 454 sequencing at the Cornell University Life Sciences Core Laboratories Center with further validation done by SLB and HDK. We identified and tested 17 msat markers from this dataset consisting of 3, 4, and 6 bp repeats. PCR conditions followed a “touchdown” protocol of 95° for 40 s, 66° for 45 s, and 72° for 45 s. The annealing step was reduced by one degree every cycle for the first seven cycles. Cycles 8–35 followed a pattern of 95° for 40 s, 58° for 45 s, and 72° for 45 s. PCR products were stored at −20°C until genotyped. Individuals were genotyped at microsatellite loci by the University of Minnesota Genomics Center on an Applied Biosystems 3730xl DNA Analyzer. We scored alleles for fragment size manually using Peak Scanner 2.0 software. Multiple independent analysts scored the same products to assure veracity of the calls. If no clear designation could be made or alleles did not amplify, we scored the data as missing.

Population genetics analyses

Prior to analysis of microsatellite fragments, we filtered individuals and loci for missing data. A strict cutoff of >25% missing data led to the exclusion of six loci. Following this filter, we excluded any individuals with missing data at three or more loci, resulting in the removal of 52 samples. The final dataset included 274 individuals genotyped at 11 loci with between 6 and 17 alleles per locus (Table 2); analyses were repeated after exclusion of three loci (see below). To estimate allelic richness and the number of private alleles accurately given unequal sample sizes per population, we performed a rarefaction analysis using HP‐Rare (Kalinowski, 2005) using the population with the smallest sample size (Oaxaca, 13 samples) to calculate adjusted values.
Table 2

Locus primer and allelic richness statistics

LocusPrimer sequence 5′‐3′Repeat locusMean number of alleles
MotifNo.Size (bp)PoolDyeHI(K)HI(O)HI(H)CAAZSONOAXTXFL
Oo002 F: GTGTGTGAGCGTCTGATCTTCCCAGC11191AVIC2.653.573.17 *3.644.764.224.024.49 *5.58
R: ATCAGCCACATTTACACTTTCCC
Oo007 F: TTCCTTTACTATCGTATTGGCGCTTG8286A6‐FAM1.992.412.205.275.465.116.734.69 *4.68 *
R: AGGAAGGAAGACAAACAAACAGC
Oo011 F: CTGCCCTTTCACTCTTACTTGACAACGAC14395APET3.893.333.39 *4.775.335.684.057.297.02
R: GAGCTCCCTTGGCAAGTTAAATG
Oo017 F: TCAAATATGGGCTGGTTTGGATGTGGA10164A6‐FAM2.002.001.99 *3.364.975.496.445.05 *6.01
R: TGTCATGATGCAGCATAAACAAC
Oo022 F: AAAGGTGTTAGAAGATGTTGGCGGGAT9348B6‐FAM3.612.562.58 †6.29 *7.976.51 *8.407.73 *7.34 †
R: GATAATAGCGCTCGTAGTTGCAG
Oo024 F: TATGACGTGCAGCAATATGAGTGTTG15164BPET2.542.242.22 †2.89 †3.77 *3.93 *3.523.48 *3.69 *
R: GTGACGTACGTTTGAAATGCTC
Oo028 F: TCTTGTGGGTAATGGCAATTGTGTAG12333BNED2.002.412.18 *4.695.977.046.685.305.76
R: ATTTAATACGCAGCAATCCCAGG
Oo031 F: ACATATGGTGAGTAGTGGATCCCAAC11387BVIC2.702.432.31 *4.145.16 *5.256.545.776.91
R: ACCAGAAGCTGTCATATAGGGAG
Oo032 F: TGAAGTGTGACAGTTTCTTGACGTTG12416AVIC2.943.213.365.79 *5.864.476.287.096.34
R: ACTGTCAAGGATGTTAAACTGGC
Oo034 F: TTCGACCAAACCCATTATGTGACACA12182ANED1.921.831.901.902.783.023.593.343.25
R: TCCGGACTATCGAGATTGTACTG
Oo035 F: ATTTGCGGTGTTACTTCATTTGCGTT10190APET1.332.061.43 *2.64 *4.72 *6.146.08 *6.28 *6.98 †
R: TTGCTTACCACTGTTCGCTAATC
 Mean2.512.552.434.125.165.175.675.505.78
SD 0.730.550.601.321.251.131.531.421.32

Loci that significantly deviate from Hardy–Weinberg expectations in a population are marked with an *(if p < .05) or an †(if p < .001) for that population; the three Hawaiian islands were pooled for HWE testing.

Locus primer and allelic richness statistics Loci that significantly deviate from Hardy–Weinberg expectations in a population are marked with an *(if p < .05) or an †(if p < .001) for that population; the three Hawaiian islands were pooled for HWE testing. We visualized population genetic variation using a discriminant function analysis of principal components (DAPC) with 80 principal components and four discriminant functions using the adegenet (Jombart, 2008; Jombart & Ahmed, 2011) and pegas (Paradis, 2010) packages in R. To visualize genetic structure, we implemented the Bayesian analysis program STRUCTURE v2.3.4 using an admixture model with correlated allele frequencies and without using source population as a prior. We used a burn‐in of 50,000 steps and 100,000 MCMC iterations. We conducted separate runs for the full dataset, a mainland dataset with the Hawaiian samples excluded, and a dataset of Hawaiian samples only. For the 8‐locus dataset, we performed 20 runs each for k = 1–9; for the 11‐locus dataset, we performed five runs each for k = 2–9. To infer the likely number of genetic clusters, we used both the Ln estimated probability of the data from STRUCTURE and the Evanno method utilizing Δk (Evanno, Regnaut, & Goudet, 2005). We calculated pairwise estimates of F ST (Weir & Cockerham, 1984) and Nei's genetic distance between populations using the R packages adegenet and ade4 (Chessel, Dufour, & Thioulouse, 2004), and we calculated expected and observed heterozygosity using adegenet. We tested if loci met Hardy–Weinberg expectations within each population (Hawaiian islands pooled) using an exact permutation test (Table 2). To test for bottlenecks during a potential range expansion, we calculated the Garza and Williamson's M (Garza & Williamson, 2001) statistic for each population, with the three Hawaiian islands grouped as a single population. We built a mitochondrial haplotype network using 55 haplotypes from 1,111 bp of COI sequences from 275 individuals using the R package pegas (Paradis, 2010) with default parameters.

Host ranges and songs

To provide context for understanding the degree of host specialization, we present in this paper the songs of confirmed hosts in each of the geographic regions studied. We present only hosts confirmed to be naturally parasitized by the development of O. ochracea from field‐collected crickets. We suspect that a few additional host species will be confirmed in the United States, especially if the species is only occasionally parasitized, and we expect that many more species are parasitized in southern and central Mexico; this reflects the status of current knowledge of Gryllus systematics and the extent of field sampling. Many of the confirmed host species are not yet officially described (Weissman and Gray, in press); to provide continuity within the literature, we use provisional manuscript names here and note that the names are disclaimed as unavailable per Article 8.3 of the ICZN. Songs from field caught males were recorded in the laboratory, directly to computer at 44.1 kHz 16 bit sampling. In early work, we used CoolEdit 2000 and later switched to using Audacity (various versions over several years, currently v. 2.2.1). In an attempt to quantify relative song differences, we created a Euclidean song distance matrix using matrix <‐ dist(songdata) function in R. Song variables were dominant frequency (kHz), pulse rate, pulses per chirp or trill (ln‐transformed), pulse duty cycle, song type (chirp, trill, stutter‐trill, complex stutter‐trill), and chirps per trill (for stutter‐trillers), as well as introductory pulses per trill and introductory pulse rate (for complex stutter‐trillers). Prior to matrix calculation, the raw song data were normalized as z‐scores (see data and matrix in the accompanying data deposited in Dryad). The resulting song distance matrix has the advantage of objectively showing unit‐less quantitative differences among cricket host species, but has the disadvantage that the different song features are not weighted by their perceptual importance to O. ochracea, which would be preferable but is not currently possible. Our coding of song characters is only one of many possible coding schemes; our goal was to capture the major structural differences among cricket songs (Alexander, 1962) while attempting to have song features coded in such a way that comparisons across species represent “homologous” traits in song space, see Desutter‐Grandcolas and Robillard (2003). We used Mantel tests implemented in the R package ecodist (Goslee & Urban, 2007) to relate the cricket host song distances among the different fly populations to the geographic and genetic distances among the fly populations. Geographic distances were measured from Google Earth as terrestrial linear distances (i.e., avoiding crossing the Gulf of Mexico). We used Nei's genetic distances, both including and excluding three loci identified as deviating from Hardy–Weinberg expectations in five or more populations (see Section 3). We used the among‐cricket‐species song distance matrix (described above) to generate an among‐fly‐populations song distance matrix. This is a complicated endeavor because several fly populations regularly utilize multiple cricket hosts, so the song differences among the fly populations represent the song differences among an assemblage of cricket host species, not between the songs of single species of crickets. We could not settle on an a priori “best” way to do this, so we tried three approaches: (a) pairwise average song distance between fly populations for commonly utilized host species, (b) pairwise minimum song distance between fly populations for commonly utilized host species, and (c) pairwise minimum song distance between fly populations for all known host species. Method (i), the average song distance between the commonly utilized hosts conceptually represents how different are the suite of host cues for the host species most relevant to the evolutionary fitness of the flies. Method (ii), the minimum song distance between the commonly utilized hosts conceptually represents the minimum difference in recognition of host cues necessary for the fly to establish a population within a new geographic area with a particular assemblage of potential hosts and have high fitness with at least one host. Method (iii), minimum song distance for all known hosts conceptually represents the minimum difference in recognition of host cues necessary for the fly to have any fitness within a new assemblage of potential host species. The “commonly utilized host species” per population was determined based on prior fieldwork (Gray et al., 2007; Hedrick & Kortet, 2006; Sakaguchi & Gray, 2011; Walker & Wineriter, 1991; Weissman & Gray, in press) and was as follows: Florida G. rubens; Texas G. texensis; Arizona G. “longicercus,” G. “staccato,” G. “regularis,” G. armatus, and G. cohni; Sonora G. “staccato,” G. “regularis,” G. armatus, and G. cohni; Oaxaca G. assimilis; California G. lineaticeps and G. integer; and Hawaii T. oceanicus.

RESULTS

Nuclear and mitochondrial genetics

Three loci (Oo022, Oo024, and Oo035) showed significant departure from Hardy–Weinberg expectations in five or more populations (Table 2); subsequent analyses were done both including and excluding these three loci. Following filtration at missing data cutoffs, 274 individuals and either 11 or 8 loci (see above) were included in the final msat dataset, with 1.86% data missing. Heterozygosity across all individuals was 50.9% (11 loci) or 56.0% (8 loci). The Hawaiian populations showed a drastic decrease in heterozygosity (Table 3). The rarefaction analysis also suggested a substantial decrease in both total and private allelic diversity within the Hawaiian populations (Table 2).
Table 3

Population sample sizes and heterozygosity for nuclear msat loci

PopulationSample sizeNo. allelesHeterozygosity (expected)Heterozygosity (observed)
Kauai2029 (21)0.437 (0.480)0.367 (0.460)
Oahu2831 (22)0.438 (0.479)0.367 (0.450)
Hilo3234 (26)0.401 (0.449)0.321 (0.400)
California3262 (47)0.588 (0.591)0.478 (0.528)
Arizona5795 (71)0.667 (0.665)0.612 (0.625)
Sonora1770 (52)0.677 (0.658)0.588 (0.648)
Oaxaca1370 (53)0.724 (0.723)0.607 (0.604)
Texas3591 (67)0.714 (0.709)0.604 (0.636)
Florida4095 (70)0.741 (0.730)0.638 (0.693)

Values are given for the full dataset of 11 loci with values in parentheses for the reduced set of eight loci.

Population sample sizes and heterozygosity for nuclear msat loci Values are given for the full dataset of 11 loci with values in parentheses for the reduced set of eight loci. Analysis of Nei's genetic distances documented a clear split between Hawaiian and mainland populations (Table 4), with Hawaiian populations more similar to western mainland populations. Longitude explained the primary axis of variation among the mainland populations, with a clear east–west gradient evident in both the DAPC and mtDNA haplotype network (Figure 1). Pairwise comparisons of Fst demonstrated a similar east–west pattern for mainland populations, but did not show a clear pattern between Hawaiian and mainland populations (Table 4).
Table 4

Pairwise F ST (above diagonal) and Nei's genetic distance (below diagonal) by population

 KauaiOahuHiloCaliforniaArizonaSonoraOaxacaTexasFlorida
Kauai 0.027 (0.029)0.057 (0.066)0.092 (0.102)0.071 (0.080)0.105 (0.099)0.109 (0.108)0.091 (0.086)0.087 (0.083)
Oahu0.044 (0.033)0.047 (0.056)0.088 (0.089)0.079 (0.084)0.099 (0.087)0.095 (0.090)0.100 (0.093)0.098 (0.091)
Hilo0.096 (0.063)0.073 (0.055)0.114 (0.115)0.097 (0.100)0.124 (0.110)0.118 (0.111)0.127 (0.117)0.122 (0.113)
California0.263 (0.327)0.229 (0.299)0.279 (0.310)0.024 (0.028)0.034 (0.030)0.049 (0.056)0.055 (0.059)0.060 (0.065)
Arizona0.282 (0.395)0.267 (0.378)0.291 (0.369)0.088 (0.132)0.011 (0.008)0.019 (0.023)0.031 (0.035)0.035 (0.038)
Sonora0.290 (0.365)0.286 (0.359)0.344 (0.375)0.127 (0.163)0.067 (0.089)0.032 (0.037)0.026 (0.028)0.026 (0.031)
Oaxaca0.327 (0.443)0.305 (0.451)0.365 (0.456)0.235 (0.293)0.151 (0.197)0.169 (0.189)0.022 (0.027)0.021 (0.024)
Texas0.331 (0.427)0.332 (0.450)0.394 (0.454)0.231 (0.263)0.165 (0.171)0.149 (0.167)0.158 (0.205)0.008 (0.006)
Florida0.337 (0.442)0.336 (0.451)0.388 (0.461)0.273 (0.303)0.187 (0.190)0.167 (0.202)0.171 (0.211)0.045 (0.058)

Values are given for the full dataset of 11 loci with values in parentheses for the reduced set of eight loci.

Figure 1

(a) DAPC clustering analysis. Individuals are marked as points with ellipses representing 75% of the observed data. (b) Haplotype network of 55 haplotypes of 1,111 bp of mitochondrial COI gene sequences. (c) Map of collection sites

Pairwise F ST (above diagonal) and Nei's genetic distance (below diagonal) by population Values are given for the full dataset of 11 loci with values in parentheses for the reduced set of eight loci. (a) DAPC clustering analysis. Individuals are marked as points with ellipses representing 75% of the observed data. (b) Haplotype network of 55 haplotypes of 1,111 bp of mitochondrial COI gene sequences. (c) Map of collection sites For the 8‐locus dataset, with all samples, STRUCTURE analyses indicated the strongest support for k = 2 genetic clusters (mean LnP(K) = −6286.49) separating Hawaiian from mainland populations (Figure 2); however, support for k = 3 clusters was also high (mean LnP(K) = −6028.0), which further divided the mainland populations into eastern and western subsets (Figure 2). The Evanno method indicated the strongest support for k = 2 clusters (Table S1). STRUCTURE plots for within Hawaii (k = 2 and k = 3) and mainland (k = 2, k = 3, and k = 6) are in Figures S1 and S2. Analysis of the 11‐locus dataset (5 runs, k = 2–9) gave qualitatively the same results: strongest support for K = 2 genetic clusters (mean LnP(K) = −8386.5, Delta K = 131.43), though support for K = 3 clusters was also high (mean LnP(K) = −8082.08, Delta K = 68.13).
Figure 2

Bayesian clustering analysis implemented by STRUCTURE software (Pritchard, Stephens, & Donnelly, 2000). Top panel shows clustering into two genetic groups (K = 2), and the bottom panel shows clustering into three genetic groups (K = 3)

Bayesian clustering analysis implemented by STRUCTURE software (Pritchard, Stephens, & Donnelly, 2000). Top panel shows clustering into two genetic groups (K = 2), and the bottom panel shows clustering into three genetic groups (K = 3) The mtDNA haplotype network (Figure 1b) also showed (a) low genetic variation within Hawaii, (b) affinity of the Hawaiian sequences for the western mainland (i.e., California) sequences, and (c) a longitudinal geographic structure within the mainland populations. Oaxaca had a high diversity of haplotypes shared with all other mainland populations. Neighbor‐joining analysis of populations based on Nei's genetic distance (eight loci) also shows affinity of California and Hawaii (Figure 3).
Figure 3

Unrooted neighbor‐joining of populations based on multilocus microsatellite genetic distances (Nei's distances, 8 loci)

Unrooted neighbor‐joining of populations based on multilocus microsatellite genetic distances (Nei's distances, 8 loci) Given the apparent distinctness of the Hawaiian populations, it is important to emphasize that these patterns reflect founder effects, and concomitant change in allele frequency in Hawaii, not the development of novel genetic variation in Hawaii. This is most easily seen in allele frequency histograms which show that the Hawaiian genetic variation is effectively a simple subset of the genetic variation found in western mainland populations, themselves a simple subset of the genetic variation found in Florida, Texas, and Mexico populations (see Figure 4 for a representative locus; figures for all other loci show similar patterns and are presented as Figures S3–S12). The Garza and Williamson's M statistic also provided support for bottlenecks due to founder effects in the Hawaiian populations (Figure 5) and a more modest reduction in population size as the range expanded westward (e.g., California).
Figure 4

Allele frequency histograms for msat locus 35 for each population

Figure 5

Garza and Williamson's M for each population, suggesting genetic bottlenecks associated with reductions in population size, especially for California and Hawaii

Allele frequency histograms for msat locus 35 for each population Garza and Williamson's M for each population, suggesting genetic bottlenecks associated with reductions in population size, especially for California and Hawaii

Host range and song structures

Confirmed host species, geographic range information, and host calling song type, frequency, pulse rate, and pulses/chirp are presented in Table 5. Songs of confirmed host species vary dramatically, from simple chirps to complex trills; see waveform oscillograms and frequency spectrograms in Figures 6 and 7, respectively (prepared using the R package seewave).
Table 5

Confirmed hosts of Ormia ochracea

Host speciesConfirmed as host inSong typeDominant frequency (kHz)Pulse rate (p/s)a Pulses per chirp or trillb References for host status and song data
G. rubens FloridaTrill4.750–55100–200Blankers, Hennig, and Gray (2015), Izzo and Gray (2004), Vélez and Brockmann (2006), and Walker and Wineriter (1991)
G. firmus Florida, TexasChirp4.2163–5Doherty and Storz (1992), Walker and Wineriter (1991), and D. Weissman personal communication
G. texensis Texas, Oklahoma, CoahuilaTrill5.275–8025–65Blankers et al. (2015), Cade (1975, 1981), Cade, Ciceran, and Murray (1996), Gray and Cade (1999), Izzo and Gray (2004), DAG, and D. Weissman personal communication
G. assimilis Texas, Oaxaca, Nuevo LeonChirp3.7856–9DAG; D. Weissman personal communication (Weissman, Walker, & Gray, 2009)
G. personatus Arizona, CoahuilaChirp4.0576–8DAG; D. Weissman personal communication (Gray, Gutierrez, et al., 2016)
G. vocalis a.k.a. Regular stutter‐trillerArizonaFast chirp4.8333–4D. Weissman personal communication (Sakaguchi & Gray, 2011; Weissman, Rentz, Alexander, & Loher, 1980)
G. “staccato” a.k.a. G#15Arizona, SonoraChirp5.2736–8Gray, Gutierrez, et al. (2016), Sakaguchi and Gray (2011), and DAG
G. armatus ArizonaStutter‐trill3.6582, 15–20Hedrick and Kortet (2006), and DAG
G. “montis” ArizonaChirp3.8224–5DAG
G. “longicercus” a.k.a. G#13ArizonaChirp4.5104–6DAG; D. Weissman personal communication (Gray, Gabel, Blankers, & Hennig, 2016)
G. “lightfooti” ArizonaChirp4.5204–6DAG; D. Weissman personal communication
G. multipulsator Arizona, Sonora, Jalisco, Zacatecas, Sinaloa, Baja California SurChirp4.17012–16A. Izzo; DAG; D. Weissman personal communication (Weissman et al., 2009)
G. “regularis” a.k.a. G#14, Arizona trillerArizonaTrill4.53820–80Blankers et al. (2015), Sakaguchi and Gray (2011), and DAG
G. cohni a.k.a. G#20, Arizona stutter‐trillerArizona, SonoraStutter‐trill4.8252–8, 1–6Sakaguchi and Gray (2011), and DAG
G. “saxatilis” a.k.a. G#2California, Baja California NorteChirp4.1203–4DAG; D. Weissman personal communication
G. lineaticeps CaliforniaChirp5.1556–8Gray, Gutierrez, et al. (2016), Wagner (1996), Wagner and Basolo (2007), and DAG
G. integer CaliforniaStutter‐trill4.5602–3, 15–80Hedrick and Kortet (2006), Hedrick and Weber (1998), Paur and Gray (2011a) and Weissman et al. (1980)
Teleogryllus oceanicus HawaiiComplex 2‐part trill// stutter‐trillc 4.614//246−8//2, 8–10Zuk, Simmons, and Cupp (1993) and Zuk, Simmons, and Rotenberry (1995)

Pulse rates approximate the average at 25°C.

For stutter‐trillers, numbers are given as pulses per chirp, chirps per trill.

For the T. oceanicus 2‐part song, numbers are given as trill part 1//stutter‐trill part 2.

Figure 6

Waveform oscillograms of 3 s of song from confirmed host species showing overall song structure (chirps/trills)

Figure 7

Spectrogram representations of 0.2 s of song from confirmed host species showing fine‐scale song structure (pulses)

Confirmed hosts of Ormia ochracea Pulse rates approximate the average at 25°C. For stutter‐trillers, numbers are given as pulses per chirp, chirps per trill. For the T. oceanicus 2‐part song, numbers are given as trill part 1//stutter‐trill part 2. Waveform oscillograms of 3 s of song from confirmed host species showing overall song structure (chirps/trills) Spectrogram representations of 0.2 s of song from confirmed host species showing fine‐scale song structure (pulses) The song distance matrix shows nearly 30‐fold variation in pairwise interhost song distance comparisons (0.28 between G. “saxatilis” and G. firmus vs. 8.24 between G. rubens and T. oceanicus; Figure 8). Notably, the average distance of T. oceanicus song from each of the other songs was about double the average distances for the continental Gryllus species (7.75 vs. 3.85, Z = 7.4, p < .0001).
Figure 8

Euclidean pairwise interhost song distances with heatmap colors indicating similar songs (green) or strongly divergent songs (red)

Euclidean pairwise interhost song distances with heatmap colors indicating similar songs (green) or strongly divergent songs (red) Mantel tests showed strong associations between geographic, genetic, and song distances (Figures 9 and 10). To explore these patterns further, we repeated the analyses excluding the comparisons based on Hawaiian samples, that is, Mantel tests just for mainland population comparisons. Using average song distances among common hosts, song distance was correlated with genetic distance both when considering all comparisons and when considering only mainland comparisons (Figure 9c); the same was true when using minimum song distance among common hosts (Figure 10a), but not minimum song distance among any hosts (Figure 10b).
Figure 9

(a–c) Association between geographic, genetic, and song distances among populations

Figure 10

(a,b) Association between genetic and song distances among populations

(a–c) Association between geographic, genetic, and song distances among populations (a,b) Association between genetic and song distances among populations Partial Mantel tests gave somewhat inconsistent results (Table 6). Across all analyses, generally, it appears that the correlation between genetic and geographic distances persists even after conditioning on song distance. Song distance was significantly correlated with genetic distance, after conditioning on geographic distance, only for mainland comparisons using average song distance among commonly used hosts. The same pattern was not significant but somewhat suggested for all comparisons using average song distance among commonly used hosts, and for mainland comparisons using minimum song distance among commonly used hosts. Using minimum song distances among any hosts resulted in no relationship, or even a negative relationship, between song distance and genetic distance after conditioning on geographic distance.
Table 6

Results of partial Mantel tests of among‐population matrices of genetic (Nei), geographic (km), and host song distances

Population comparisonsSong distance methodM1 ~ M2 + M3All lociExcluding 3 loci
r p r p
All comparisonsAverage b/w common hostsGen ~ Geo + Song.60.0856.61.0812
Geo ~ Song + Gen.32.2167.34.1856
Gen ~ Song + Geo.51.0807.48.0866
Minimum b/w common hosts Gen ~ Geo + Song .67 .0084 .66 .0122
Geo ~ Song + Gen.39.1277.37.1305
Gen ~ Song + Geo.34.1506.38.1101
Minimum b/w any hosts Gen ~ Geo + Song .78 .0004 .78 .0007
Geo ~ Song + Gen.63.0621.63.0648
Gen ~ Song + Geo−.09.6518−.10.6562
Mainland onlyAverage b/w common hosts Gen ~ Geo + Song .63 .0236 .75 .0049
Geo ~ Song + Gen−.31.8273−.49.9538
Gen ~ Song + Geo .80 .0023 .84 .0001
Minimum b/w common hosts Gen ~ Geo + Song .57 .0354 .64 .0311
Geo ~ Song + Gen.13.3544.01.4571
Gen ~ Song + Geo.37.1632.45.0905
Minimum b/w any hosts Gen ~ Geo + Song .76 .0035 .79 .0013
Geo ~ Song + Gen .61 .0111 .59 .0193
Gen ~ Song + Geo−.49.982−.46.9032

Comparisons in bold are significant at p < .05.

Abbreviations: Gen, genetic distance (Nei); Geo, geographic distance (km); M1, response matrix; M2, explanatory matrix; M3, conditional matrix; Song, song distance.

Results of partial Mantel tests of among‐population matrices of genetic (Nei), geographic (km), and host song distances Comparisons in bold are significant at p < .05. Abbreviations: Gen, genetic distance (Nei); Geo, geographic distance (km); M1, response matrix; M2, explanatory matrix; M3, conditional matrix; Song, song distance.

DISCUSSION

Our results suggest the following: (a) O. ochracea is a single widespread species with regional host specialization, not a complex of cryptic species, (b) O. ochracea has spread geographically into northern Mexico (Sonora) and the western United States (Arizona and California) from source populations in southern Mexico (Oaxaca) and/or the southern US Gulf region (Florida, Texas), (c) Hawaiian flies were introduced from a western continental US population, most likely California, potentially consisting of as few as one gravid female fly, and (d) novel song types with highly divergent song structures do not inhibit novel host exploitation. We elaborate on these results below and discuss mechanisms of regional host song specialization. Studies of other Tachinid groups have sometimes revealed that what was considered a single generalist species actually consists of a complex of cryptic specialist species (Smith, Wood, Janzen, Hallwachs, & Hebert, 2007; Smith et al., 2006). The regional host specialization in O. ochracea documented previously (Gray et al., 2007) could have been consistent with either a widespread generalist with regional host preferences or with multiple cryptic host specialists. Both the mtDNA and msat variation suggest a single species. The mtDNA sequences, although showing clear east–west geographic structure, are relatively uniform and strongly divergent from O. depleta and O. lineifrons sequences (Figure S13). The msat data clearly show that populations strongly differentiated in host song preferences can nonetheless be genetically panmictic. Perhaps the best example of this involves flies from Florida and Texas: Gray et al. (2007) showed that Florida flies preferred G. rubens song over G. texensis song nearly 2:1 and that Texas flies preferred G. texensis song over G. rubens song 6:1. Nonetheless, the pairwise F ST of 0.008 for these populations (Table 4) and the DAPC (Figure 1a) show that these two populations are genetically rather homogenous. Both the mtDNA and msat data also inform the broader geographic history of the fly within North America. There is a clear east–west differentiation among samples, consistent with isolation by distance (Figure 9a). Moreover, the pattern of allelic variation in the msat loci (e.g., Figures 4 and S3–S12) suggests serial founder effects as flies colonized the western continental United States and then Hawaii; this interpretation is supported by Garza and Williamson's M (Figure 5). The mtDNA similarly suggests that the older fly lineages are to be found within the southeastern US populations (Figures 1b and S13). In this light, it is interesting to note that Florida is home to two Gryllus species, G. ovisopis and G. cayensis, which lack a normal calling song (Gray, Hormozi, Libby, & Cohen, 2018; Walker, 1974, 2001), possibly a consequence of a prolonged history of Ormia parasitism in that region. In contrast, there are no noncalling Gryllus in western North America. If the southeastern United States was an original source area for western North American populations, then the ancestral host songs were likely simple trills as in G. rubens and G. texensis. The introduction of O. ochracea to Hawaii appears virtually certain to have been from a western North American population. The dominant mtDNA haplotype in Hawaii is also found in California and Arizona (Figure 1b); locus by locus, the msat allelic variation in Hawaii is likewise a subset of the most common alleles in California and Arizona (Figures 4 and S3–S12); combining msat loci, a neighbor‐joining tree based on Nei's distances places Hawaii and California as sister populations (Figure 3). A single introduction seems likely; the levels of genetic variation in Hawaii do not preclude the possibility that the introduction could have consisted of as few as one gravid female, although it seems more plausible that multiple individuals were introduced, perhaps as pupae in soil. In other systems, experimental introductions have indicated that in some circumstances, introductions of a single gravid female can nonetheless establish a persistent population (Fauvergue, Malausa, Giuge, & Courchamp, 2007; Grevstad, 1999). Within Hawaii, our data are consistent with the spread of an introduced population among islands, rather than separate introductions on each island (Figure S1). Once in Hawaii, the adoption of T. oceanicus as a host represents a major shift within O. ochracea's repertoire of host song recognition. Quantitatively and qualitatively, T. oceanicus song is strikingly divergent from the songs of continental North American hosts (Figures 6, 7, 8). Even within mainland sites only, song divergence is associated with both geographic and genetic distances (Figures 9 and 10), demonstrating adoption of hosts with novel songs. Across the diversity of host songs, one could argue that the single essential song recognition feature is a dominant frequency in the 3–6 kHz range. This may be true in a strict sense, but frequency is clearly not the only song recognition feature. Multiple studies have shown that the temporal pattern of sound pulses is also important (Gray & Cade, 1999; Sakaguchi & Gray, 2011; Wagner, 1996; Wagner & Basolo, 2007; Walker, 1993). Moreover, fly populations prefer the temporal structure of their most common host species, even when dominant frequencies are similar (Gray et al., 2007). Perhaps most remarkably, Gray et al. (2007) showed that Hawaiian O. ochracea preferred T. oceanicus song over the songs of ancestral host species by a large margin (12 of 13 Hawaiian flies chose T. oceanicus song over the songs of G. rubens, G. texensis, and G. lineaticeps). Adoption of T. oceanicus as a host in Hawaii also required compatible host physiology for larval development. Although mostly confined to parasitism of adult males, O. ochracea can develop within a wide variety of crickets, including juveniles (Vincent & Bertram, 2009) and species not normally used as hosts (Adamo, Robert, & Hoy, 1995; Thomson, Vincent, & Bertram, 2012) including Acheta domesticus (Paur & Gray, 2011a, 2011b; Wineriter & Walker, 1990) which is more distantly related to Gryllus than is Teleogryllus (D. A. Gray, D. B. Weissman, E. M. Lemmon, A. R. Lemmon, unpublished data). This latitude probably results from the generalized nature of the cricket immune encapsulation response (Vinson, 1990), which is exploited by Ormiines to develop a respiratory spiracle. Given this latitude, we expect that physiological compatibility with T. oceanicus was unlikely to be a significant factor in terms of host suitability. Our results suggest that host specialization in O. ochracea is not at odds with rapid exploitation of novel hosts, as might be expected from evolutionary theory (Jaenike, 1990; Kelley & Farrell, 1998; Raia & Fortelius, 2013), despite associations between song divergence and genetic divergence independent of geography. But how can highly regional host song specificity (Gray et al., 2007), even to the point of flies having song preferences for certain intraspecific song variants (Gray & Cade, 1999; Sakaguchi & Gray, 2011; Wagner, 1996; Wagner & Basolo, 2007), be compatible with flexible and rapid adoption of novel hosts? We expect that behavioral plasticity coupled with local host learning (Paur & Gray, 2011a) may be the mechanism that enables flies to escape the “dead end” of specialization.

CONFLICT OF INTEREST

None declared.

AUTHOR CONTRIBUTIONS

DAG, SLB, MZ, and WHC conceived of the study and collected flies; DAG performed the mtDNA sequencing; SLB and HDK performed the msat amplification and analysis; and all authors contributed to the writing and editing of the manuscript. Click here for additional data file.
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