Literature DB >> 27563274

Molecular phylogeny of the forensically important genus Cochliomyia (Diptera: Calliphoridae).

Sohath Yusseff-Vanegas1, Ingi Agnarsson1.   

Abstract

Cochliomyia Townsend includes several abundant and one of the most broadly distributed, blow flies in the Americas, and is of significant economic and forensic importance. For decades, Cochliomyia hominivorax (Coquerel) and Cochliomyia macellaria (Fabricius) have received attention as livestock parasites and primary indicator species in forensic entomology. However, Cochliomyia minima Shannon and Cochliomyia aldrichi Del Ponte have only been subject to basic taxonomy and faunistic studies. Here we present the first complete phylogeny of Cochliomyia including numerous specimens per species, collected from 13 localities in the Caribbean. Four genes, the mitochondrial COI and the nuclear EF-1α, 28S rRNA, and ITS2, were analyzed. While we found some differences among gene trees, a concatenated gene matrix recovered a robustly supported monophyletic Cochliomyia with Compsomyiops Townsend as its sister group and recovered the monophyly of Cochliomyia hominivorax, Cochliomyia macellaria and Cochliomyia minima. Our results support a close relationship between Cochliomyia minima and Cochliomyia aldrichi. However, we found Cochliomyia aldrichi containing Cochliomyia minima, indicating recent speciation, or issues with the taxonomy of the group. We provide basic information on habitat preference, distribution and feeding habits of Cochliomyia minima and Cochliomyia aldrichi that will be useful for future forensic studies in the Caribbean.

Entities:  

Keywords:  Caribbean region; Cochliomyia hominivorax; Cochliomyia macellaria; Cochliomyia minima; Cochlioyia aldrichi; Forensic entomology; habitat preferences

Year:  2016        PMID: 27563274      PMCID: PMC4984421          DOI: 10.3897/zookeys.609.8638

Source DB:  PubMed          Journal:  Zookeys        ISSN: 1313-2970            Impact factor:   1.546


Introduction

Townsend is endemic to the Americas and includes only four species: Shannon, Del Ponte, (Fabricius) and (Coquerel). All of them are flesh eaters during their larval stage and are locally abundant. In particular, is one of the most broadly distributed blow flies in the New World (Whitworth 2010). These species vary in habitat preference, feeding habits, dispersal abilities, and morphology among the species (Hall 1948, Whitworth 2010). For instance, , and are primarily carrion feeders, while, is an obligate parasite of mammals (Hall 1948, Stevens and Wallman 2006, McDonagh et al. 2009, McDonagh and Stevens 2011). and have been intensely studied due to their commercial and forensic importance. is one of the most forensically important species commonly found on decomposing remains. This species is considered important for post mortem interval estimations (Smith 1986, Byrd and Castner 2010) being among the first species to colonize corpses. In contrast, is an obligate parasite with its larvae producing myiasis and feeding on living tissue (Hall 1948, Guimaraes et al. 1983). This species is one of the most important insect pests of livestock in the Neotropics causing economic losses of billions of dollars every year (Vargas-Terán et al. 2005). Both species are common throughout the year in tropical, warm and humid areas (Hall 1948). can be found in temperate climates from Canada to Argentina during the summer months (Whitworth 2010). initially ranged from southern United States to northern Argentina (Guimaraes et al. 1983) but has been eradicated from North America, Central America, Puerto Rico and the Virgin Islands (Vargas-Terán et al. 2005). It is worth noting that in 1988 this species was introduced in Libya and it was successfully eradicated in 1992 based on the . This was the major international effort and avoid a major disaster for the livestock industry of Africa and Southern Europe (Lindquist et al. 1992). Despite those successfully eradications continues to be an economically important pest in South America and parts of the Caribbean (Vargas-Terán et al. 2005). sterile insect technique The other two congeners, and , are poorly known and research has been limited to descriptive morphology and faunistics (Hall 1948, Dear 1985, Whitworth 2010). These two species are restricted to the West Indies and has been reported in the Florida Keys (Whitworth 2010). Dear (1985) listed for the Florida Keys, however Whitworth (2010) concluded that Dear mistakenly identified one specimen as . Forensically important insects in the Caribbean are generally understudied and these two species have not played an important role in forensic entomology. Yet, due to their abundance and broad distribution in this region, including Cuba, Dominican Republic, Jamaica, Puerto Rico, Virgin Islands, Bahamas and Cayman Islands (Hall 1948, Dear 1985, Whitworth 2010) they have an enormous forensic potential. For example, recent studies conducted in PageBreakPuerto Rico showed that is abundant and widely distributed on the island, and that adults are attracted to, and feed on, carrion (Yusseff-Vanegas 2014). Although the adult morphology of the four species is well known (Hall 1948, Dear 1985, Whitworth 2010), studies on the relationship among species have not been conducted yet. Morphological studies have provided synapomorphies of that clearly diagnose it from all other (Hall 1948; Dear 1985; Whitworth 2010). These include short and filiform palpus and phallus with extremely elongated paraphallus and a complex distiphallus (Dear 1985, Figs 37–44). Prior studies on the relationships among (Stevens 2003, Harvey et al. 2008, McDonagh and Stevens 2011) and the subfamily (Singh and Wells 2011), including and , supported monophyly, and placed it as sister to Townsend. However, the monophyly of the genus has not been formally tested with thorough sampling of all species, and the relationships among its species remain unknown. Furthermore, DNA-based methods can provide reliable identification of specimens by non-experts and will be particularly important for the identification of larval stages of and that remain poorly known. For example, only the third instar of has been described (Yusseff-Vanegas 2014). Here we provide a robust phylogenetic hypothesis of based on four genes sequenced from 38 individuals collected throughout the Caribbean, including for the first time molecular data about and . Our main goals are to test the monophyly of this genus and the validity of, and relationships among, its species.

Methods

Specimens and DNA extraction

A total of 44 specimens were included in this study, 38 representing the ingroup plus six outgroup species [ (Fabricius), (Macquart), sp., (Wiedemann), (Robineau-Desvoidy) and (Bigot)]. All sequences used here are new except for and (Table 1). The specimens were collected in the Caribbean (Jamaica, Cuba, Dominican Republic, Puerto Rico, Saint Barts Martinique and Dominica) from 2011 to 2013 and in the following countries, Colombia (2014), Florida (2013) and Mexico (2010 and 2012) (Table 1). All specimens were killed and preserved in 95% ethanol and stored at -20 °C. The adults were examined with a Leica MZ16 stereomicroscope and identified using the Whitworth (2010) keys. The DNA was isolated from thoracic muscle or two legs of each individual with the QIAGEN DNeasy Tissue Kit (Qiagen, Inc., Valencia, CA). Voucher specimens were deposited at the UVM Natural History Museum (in the Zadock Thompson Zoological Collections) and sequences were submitted to GenBank.
Table 1.

Specimen details, collection information and GenBank accession numbers.

Species name – Voucher NumberLocation CO1 EF-1α ITS2 28S rRNA
Cochliomyia macellaria CO002 Colombia, El refugio Dry Forest KX529522 KX529616 KX529574 KX529487
Cochliomyia macellaria CO010 Colombia, Choco, Jardín botánico del Pacífico KX529545 KX529617 KX529575 KX529488
Cochliomyia macellaria CO017 Colombia, Santander, Chipatá, Finca el Castillo KX529543 KX529618 KX529576 KX529489
Cochliomyia macellaria ME015*Mexico, Torreon, Coahuila KX529546 KX529629 KX529588 KX529492
Cochliomyia macellaria FL006 USA, Florida, Everglades National Park, Northeast KX529535 KX529623 KX529581 KX529503
Cochliomyia macellaria JA002 Jamaica, Marshall’s Pen House KX529538 KX529624 KX529582 KX529502
Cochliomyia macellaria CU018 Cuba, Pinar del Rio, Viñales Nacional Park KX529526 KX529620 KX529578 KX529499
Cochliomyia macellaria CU014 Cuba, Pinar del Rio, Viñales Nacional Park KX529541 KX529619 KX529577 KX529497
Cochliomyia macellaria DR134 Dominican Republic, Puerto Plata KX529527 KX529622 KX529580 KX529504
Cochliomyia macellaria DR010 Dominican Republic, El Morro, Monte Cristi KX529536 KX529621 KX529579 KX529496
Cochliomyia macellaria PR129 Puerto Rico, Vieques, Monte Pirata KX529542 - KX529591 KX529501
Cochliomyia macellaria PR128 Puerto Rico, Vieques, Monte Pirata KX529540 - KX529590 KX529494
Cochliomyia macellaria PR121 Puerto Rico, Trujillo Alto, Ciudad Universitaria KX529544 KX529630 KX529589 KX529500
Cochliomyia macellaria M112 Puerto Rico, Isla de Mona, Los Caobos KX529528 - KX529587 KX529493
Cochliomyia macellaria M081 Puerto Rico, Isla de Mona, Los Caobos KX529537 KX529628 KX529586 KX529498
Cochliomyia macellaria M077 Puerto Rico, Isla de Mona, Bajuras - Cerezos KX529539 KX529627 KX529585 KX529495
Cochliomyia macellaria LA142 Saint Barts, Colombier Deciduos Dry Forest KX529523 KX529631 KX529592 -
Cochliomyia macellaria LA096 Martinique, Cap de Macré Coastal Forest KX529524 KX529626 KX529584 KX529491
Cochliomyia macellaria LA071 Dominica, Middleham Falls Trail KX529525 KX529625 KX529583 KX529490
Cochliomyia aldrichi M080 Puerto Rico, Isla de Mona, Near Cueva Portugues KX529529 KX529605 KX529563 KX529513
Cochliomyia aldrichi M085 Puerto Rico, Isla de Mona, Los Caobos KX529530 KX529606 KX529564 KX529515
Cochliomyia aldrichi M086 Puerto Rico, Isla de Mona, Camino del Indio KX529531 KX529607 KX529565 KX529514
Cochliomyia aldrichi M103 Puerto Rico, Isla de Mona, Los Caobos KX529532 KX529608 KX529566 KX529516
Cochliomyia aldrichi M105 Puerto Rico, Isla de Mona, Near Cueva Portugues KX529533 KX529609 KX529567 KX529518
Cochliomyia aldrichi M107 Puerto Rico, Isla de Mona, Near Cueva Portugues KX529534 KX529610 KX529568 KX529517
Cochliomyia minima CU046 Cuba, Guantanamo, Alejandro de Humboldt National Park KX529547 KX529633 KX529595 KX529510
Cochliomyia minima CU022 Cuba, Pinar del Rio, Viñales National Park KX529549 KX529632 KX529593 KX529511
Cochliomyia minima CU023 Cuba, Pinar del Rio, Viñales National Park KX529550 - KX529594 KX529508
Cochliomyia minima DR136 Dominican Republic, Puerto Plata KX529548 KX529635 KX529597 KX529509
Cochliomyia minima DR055 Dominican Republic, Haitises National Park KX529552 KX529634 KX529596 KX529507
Cochliomyia minima PR141 Puerto Rico, Loiza, Mangrove area KX529551 - KX529600 KX529512
Cochliomyia minima PR132 Puerto Rico, Loiza, Mangrove area KX529553 KX529636 KX529598 -
Cochliomyia minima PR133 Puerto Rico, Vieques, Monte Pirata KX529554 KX529637 KX529599 KX529506
Cochliomyia hominivorax CO001 Colombia, El refugio Dry Forest- KX529611 KX529569 KX529482
Cochliomyia hominivorax CU020 Cuba, Pinar del Rio, Viñales Nacional Park- KX529612 KX529570 KX529483
Cochliomyia hominivorax CU033 Cuba, Pinar del Rio, Viñales Nacional Park KX529556 KX529613 KX529571 KX529484
Cochliomyia hominivorax DR042 Dominican Republic, Rabo de Gato KX529557 KX529614 KX529572 KX529485
Cochliomyia hominivorax DR105 Dominican Republic, East National Park, Yuma KX529558 KX529615 KX529573 KX529486
Chrysomya megacephala FL003 USA, Florida, Everglades National Park, Northeast KX529521 KX529603 KX529561 KX529480
Chrysomya rufifacies CU004 Cuba, Granma: Turquino National Park KX529555 KX529604 KX529562 KX529481
Hemilucilia sp. CO018 Colombia, Santander, Chipatá, Finca el Castillo KX529560 KX529638 KX529601 KX529519
Lucilia cuprina PR073 Puerto Rico, Trujillo Alto, Ciudad Universitaria KX529559 KX529639 KX529602 KX529520
Compsomyiops fulvicrura As Published (Kutty et al. 2008) FJ025607 FJ025667 - FJ025504
Compsomyiops callipes As Published (Wells and Sperling 2001) AF295549 ---

*The sample from Mexico was collected by Fabián García Espinoza from Universidad Antonio Narro Unidad Laguna.

Specimen details, collection information and GenBank accession numbers. *The sample from Mexico was collected by Fabián García Espinoza from Universidad Antonio Narro Unidad Laguna.

PCR amplification and sequencing

We amplified regions of three nuclear loci: the protein coding , the ribosomal 28S, and , plus the mitochondrial protein coding . The primer sequences are listed in Table 2. Protocols for COI reactions included an initial denaturation step of 95 °C for 2 min, followed by 35 cycles of 95 °C for 30 s, 44 °C for 45 s and 72 °C for 45 s, and a final elongation step of 72 °C for 10 min (Agnarsson et al. 2007). For ITS2 an initial denaturation step of 94 °C for 2 min was followed by 38 cycles of 94 °C for 30 s, 44 °C for 35 s and 72 °C for 30 s, and a final elongation step of 72 °C for 3 min (Agnarsson 2010). For EF-1α an initial denaturation of 95 °C for 5 min was followed by 35 cycles of 94 °C for 30 s, 55 °C for 35 s and 72 °C for 1 min, and a final elongation step of 72 °C for 10 min (McDonagh et al. 2009). For 28S rRNA initial denaturation of 94 °C for 5 min was PageBreakfollowed by 35 cycles of 93 °C for 1 min, 60 °C for 1 min and 72 °C for 2 min, and a final elongation step of 72 °C for 3 min (Friedrich and Tautz 1997). Amplified fragments were sequenced in both directions by University of Arizona Genetics Core. Sequences were interpreted from chromatograms using Phred (Green and Ewing 2002) and Phrap (Green 1999, Green and Ewing 2002) using the Chromaseq module (Maddison and Maddison 2010a) in the evolutionary analysis program Mesquite 3.03 (Maddison and Maddison 2010b) with default parameters. The sequences were then proofread by examining chromatograms by eye. Alignments were done using MAFFT (Katoh et al. 2002) through the online portal EMBL-EBI. The gene matrices were then concatenated in Mesquite 3.03 (Maddison and Maddison 2010b) and the full aligned data set is 3368 bp.
Table 2.

PCR primers use in this study.

GenePrimer nameSequence (5’ to 3’)Source
COI LCO1490GGTCAACAAATCATAAAGATATTGG Folmer et al. (1994)
CI-N-2776GGATAATCAGAATATCGTCGAGG Hedin and Maddison (2001)
EF-1α B1CCCATYTCCGGHTGGCACGG McDonagh et al. (2009)
C1CTCTCATGTCACGDACRGCG McDonagh et al. (2009)
28SD1.FCCCCCTGAATTTAAGCATAT Friedrich and Tautz (1997)
D35.486.RTCGGAAGGAACCAGCTACTA Friedrich and Tautz (1997)
ITSITS4TCCTCCGCTTATTGATATGC White et al. (1990)
ITS5.8GGGACGATGAAGAACGCAGC Agnarsson (2010)
elongation factor-1 alpha internal transcribed spacer 2 cytochrome oxidase I PCR primers use in this study.

Phylogenetic analysis

We partitioned each gene and codon position for a total of eight partitions that were exported from Mesquite for model choice and the appropriate models were chosen using jModeltest v2.1.4 (Posada and Crandall 1998), and the AIC criterion (Posada and Buckley 2004). The corresponding model of evolution was used for the Bayesian analysis: GTR + Γ + I for 28S, ITS2 and COI3rd, GTR + Γ for COI1st, COI2nd, EF-1α3rd, HKY + Γ for EF-1α2nd and F81 for EF-1α1st. We ran the MC3 (Metropolis Coupled Markov Chain Monte Carlo) chain in MrBayes v3.2.3 (Huelsenbeck and Ronquist 2001) through the online portal Cipres Science Gateway v3.3 (Miller et al. 2010). The analysis was run for 30.000.000 generations, sampling every 1000 generations. Chain stationary, ESS, and appropriate burnin was verified using Tracer 1.6 (Rambaut and Drummond 2009). analysis of the concatenated matrix was done in Garli (Zwickl 2006) using the same partitioning scheme and models. Maximum likelihood

Results

The phylogenetic analyses of the concatenated matrix, either using Bayesian or maximum likelihood approaches, recovered a generally well supported monophyletic (Fig. 1). , and were recovered as monophyletic, while was recovered as paraphyletic.
Figure 1.

Phylogenetic relationship within (ingroup) based on partitioned Bayesian analysis of the combined gene (COI, EF-1α, 28S rRNA and ITS2) data set. Branch support values: normal fond, Bayesian posterior probability; bold-italic font, maximum likelihood percentage bootstrap. Each color represents different species.

Phylogenetic relationship within (ingroup) based on partitioned Bayesian analysis of the combined gene (COI, EF-1α, 28S rRNA and ITS2) data set. Branch support values: normal fond, Bayesian posterior probability; bold-italic font, maximum likelihood percentage bootstrap. Each color represents different species. Independent analyses of 28S and ITS2 supported the monophyly of , while COI and EF-1α recovered it as a paraphyletic group (Suppl. material 1). At the species level, EF-1α and 28S had limited signal and did not distinguish between and . COI recovered the monophyly of , but did not resolve relationships among and . ITS2 fully resolved the relationships within , and is the only gene that recovered the monophyly of . Despite of the incongruence detected among the four gene trees, they all recovered monophyletic and three of the four genes (COI, 28S and ITS2) strongly supported a monophyletic as sister to the other three species. The concatenated dataset yielded a topology supporting a close relationship between and which is congruent with the current taxonomy and indicates as the sister lineage of these two.

Discussion

We present the first species complete phylogeny of the genus including samples collected throughout the Caribbean from 13 different localities (Table 1). The concatenated matrix recovered a monophyletic , partially resolved relationships among its species and recovered as its sister group (Fig. 1), in congruence with prior studies (McDonagh and Stevens 2011, Singh and Wells 2011). Independent gene trees did not yield fully congruent relationships among species, unsurprising as genes have independent histories. Two nuclear genes, 28S and ITS2 (adjacent loci), strongly supported the monophyly of while the other two genes, COI and EF-1α did not. These results differ from McDonagh (2009), where EF-1α and COI strongly supported the monophyly of , while 28S recovered as paraphyletic. However, McDonagh (2009) included only two of the species of represented by one specimen each. The differences between the studies could be due to a variety of taxon sampling issues, where our sampling was designed specifically to test monophyly and relationships among species. The monophyly of is supported in all analyses, however, independent gene trees were not congruent with regards to other species. The relatively slowly evolving nuclear genes EF-1α and 28S supported but failed to distinguish between and . The relatively rapidly evolving COI “DNA barcode” was found suitable for species identification and delineation (Hebert et al. 2003). COI was the only gene that recovered the monophyly of , however, COI did not resolve relationships among specimens of and . This is surprising as these species are clearly identifiable based on morphological characteristics (Hall 1948, Whitworth 2010). Other studies also reported similar results where COI failed to distinguish among some closely related calliphorids (Wallman and Donnellan 2001, Nelson et al. 2007, Whitworth et al. 2007, Harvey et al. 2008, DeBry et al. 2013, Whitworth 2014), a result that has been attributed to incomplete lineage sorting. Results from COI, EF-1α, and 28S combined suggested as sister to , instead of to as we would expect based on morphological characteristics. Based on these results we opted to add the rapidly evolving nuclear marker, ITS2 to help resolve species level relationships (Nelson et al. 2007, Agnarsson 2010). ITS2 was the only gene that recovered as a monophyletic group and supported as its sister lineage. Despite the incongruence detected between the four genes, a concatenate matrix recovered the monophyly of , and , and supported the monophyly of plus , mostly congruent with the current taxonomy. However, we found that is nested within . That one species is paraphyletic with respect to another is not unexpected and does not necessarily refute their species status. The non-monophyly of is surprising in that all specimens included in this study were collected from the tiny Mona Island (22 square miles). This indicates incomplete lineage sorting, or possibly recent speciation, rather than other processes like gene flow among species (given Mona’s isolation, expectation of panmixia among on the tiny island, and absence of from other islands sampled). In contrast, and are present on most of the islands (Table 1) and the populations in different islands do not show any geographic structure (Fig. 1), indicating a constant gene flow among populations through migration. The variability in feeding habits, habitat preference and morphology within is considerable (Fig. 2). In feeding habits, , and share similar behaviors. They are primarily carrion feeders, commonly found on PageBreakdecomposing cadavers. However, they are also capable of producing myiasis in open wounds as secondary facultative parasites under certain conditions or as primary facultative parasites as in the case of , (Hall 1948, Dear 1985). In contrast, is an obligate parasite of mammals never found in decaying meats (Hall 1948, Stevens and Wallman 2006, McDonagh et al. 2009, McDonagh and Stevens 2011, but see Brody and Knipling 1943). Several authors have studied the evolution of parasitism within and have concluded that the parasitic behavior in this family evolved independently several times (Stevens and Wallman 2006, McDonagh and Stevens 2011, Singh and Wells 2011). Within , we conclude that parasitism evolved once in , since the congeners are carrion feeders, as are members of the sister group, (Fig. 2).
Figure 2.

Variability in feeding habits, habitat preference and morphology within . * has been reported in the Florida Keys Islands. **We refer to temperatures around 10–15 °C. ● Carrion feeder; ▴ primary facultative parasite; ■ secondary facultative parasite; ★ obligate parasite.

Variability in feeding habits, habitat preference and morphology within . * has been reported in the Florida Keys Islands. **We refer to temperatures around 10–15 °C. ● Carrion feeder; ▴ primary facultative parasite; ■ secondary facultative parasite; ★ obligate parasite. The habitat preferences of and are largely known (Hall 1948, Greenberg 1971, Smith 1986, Wells and Greenberg 1992, Byrd and Butler 1996, Byrd and Castner 2010, Koller et al. 2011), however, little is known about and . In recent studies of in Puerto Rico, Yusseff-Vanegas (2014) reported that prefer highly humid areas and can tolerate relatively cool conditions at altitudes >800m, while this species is absent from extremely dry and hot areas. Similar results were found in Dominican Republic and Cuba where was found abundantly in tropical and subtropical rain/moist forest even at altitudes >1300m, but absent from dry forest (unpublished data). These results supported the assumption that prefer humid cool areas, however, more studies are needed to understand its habitat preferences. In contrast, seems to prefer hot dry areas, different from what we expected given the apparent recent divergence between and . This is the case of recently divergent species like (Meigen) and Wiedemann, and Macquart and Macquart that have similar habitat preferences PageBreak(Stevens and Wall 1996, 1997, Whitworth 2006, Byrd and Castner 2010, Whitworth 2010, 2014). However, was found only on Mona Island, a subtropical dry forest with an average annual temperature of 27 °C (National Oceanic and Atmospheric Administration - NOAA) and low humidity through the year, strikingly different from . Yet, similar results have been reported before for closely related species like and (Singh et al. 2011) which are characterized by very different habitat preferences (Kurahashi 1981, 1991). Despite we have extensively collected in Florida (Everglades and the Keys), Cuba, Puerto Rico and the Bahamas, where was previously reported (Whitworth 2010), we did not find this species. This could be explained by sampling bias as we only collected during the summer when precipitation and relative humidity are very high in the Caribbean. It is possible, for example, that may be seasonal, being present during the winter when conditions are generally drier and cooler in the Caribbean. Alternatively, our sampling might indicate the recent extinction of this species from areas outside Mona, nevertheless, further studies are necessary to test these alternative hypotheses. Two of the four species, and are Caribbean endemics while the other two are widespread (Figs 1–2). It is difficult to assess the biogeographical history of widespread species, however, we can conclude from our data that divergence between and probably occurred in the Caribbean after the area was colonized. Island colonization is sometimes accompanied by a reduction in dispersal abilities and such processes may have led to reduced gene flow among islands, and promoted the formation of the Caribbean endemics. Further phylogeographic/phylogenomic studies including more taxa from the Caribbean and the continents are necessary to assess the colonization history of the genus and the possible secondary loss of dispersal ability in this group.

Conclusions

We provide the first complete phylogeny of , supporting its monophyly and placement within the subfamily . Given incongruence among gene trees and low level of information at the species level for slowly evolving genes, the resolution of the outstanding questions in phylogeny will require more data rich approaches, such as those offered by NGS methods. Nevertheless, we advance knowledge on the phylogeny, distribution, and life history of these species that should prove useful in future research and in realizing the potential of these species as forensic insects.
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