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Development of Reference Transcriptomes for the Major Field Insect Pests of Cowpea: A Toolbox for Insect Pest Management Approaches in West Africa

  • Tolulope A. Agunbiade ,

    agunbia1@illinois.edu

    Affiliation Department of Entomology, University of Illinois at Urbana-Champaign, Urbana, Illinois, United States of America

  • Weilin Sun,

    Affiliation Department of Entomology, University of Illinois at Urbana-Champaign, Urbana, Illinois, United States of America

  • Brad S. Coates,

    Affiliation Corn Insects and Crop Genetics Research Unit, United States Department of Agriculture, Agricultural Research Service, Ames, Iowa, United States of America

  • Rousseau Djouaka,

    Affiliation International Institute of Tropical Agriculture, Cotonou, Benin

  • Manuele Tamò,

    Affiliation International Institute of Tropical Agriculture, Cotonou, Benin

  • Malick N. Ba,

    Affiliation Institut de l’Environnement et de Recherches Agricoles, Ouagadougou, Burkina Faso

  • Clementine Binso-Dabire,

    Affiliation Institut de l’Environnement et de Recherches Agricoles, Ouagadougou, Burkina Faso

  • Ibrahim Baoua,

    Affiliation Institut National de la Recherche Agronomique du Niger, Maradi, Niger

  • Brett P. Olds,

    Affiliation Department of Animal Biology, University of Illinois at Urbana-Champaign, Urbana, Illinois, United States of America

  • Barry R. Pittendrigh

    Affiliation Department of Entomology, University of Illinois at Urbana-Champaign, Urbana, Illinois, United States of America

Abstract

Cowpea is a widely cultivated and major nutritional source of protein for many people that live in West Africa. Annual yields and longevity of grain storage is greatly reduced by feeding damage caused by a complex of insect pests that include the pod sucking bugs, Anoplocnemis curvipes Fabricius (Hemiptera: Coreidae) and Clavigralla tomentosicollis Stål (Hemiptera: Coreidae); as well as phloem-feeding cowpea aphids, Aphis craccivora Koch (Hemiptera: Aphididae) and flower thrips, Megalurothrips sjostedti Trybom (Thysanoptera: Thripidae). Efforts to control these pests remain a challenge and there is a need to understand the structure and movement of these pest populations in order to facilitate the development of integrated pest management strategies (IPM). Molecular tools have the potential to help facilitate a better understanding of pest populations. Towards this goal, we used 454 pyrosequencing technology to generate 319,126, 176,262, 320,722 and 227,882 raw reads from A. curvipes, A. craccivora, C. tomentosicollis and M. sjostedti, respectively. The reads were de novo assembled into 11,687, 7,647, 10,652 and 7,348 transcripts for A. curvipes, A. craccivora, C. tomentosicollis and M. sjostedti, respectively. Functional annotation of the resulting transcripts identified genes putatively involved in insecticide resistance, pathogen defense and immunity. Additionally, sequences that matched the primary aphid endosymbiont, Buchnera aphidicola, were identified among A. craccivora transcripts. Furthermore, 742, 97, 607 and 180 single nucleotide polymorphisms (SNPs) were respectively predicted among A. curvipes, A. craccivora, C. tomentosicollis and M. sjostedti transcripts, and will likely be valuable tools for future molecular genetic marker development. These results demonstrate that Roche 454-based transcriptome sequencing could be useful for the development of genomic resources for cowpea pest insects in West Africa.

Introduction

Crops of cowpea (Vigna Unguiculata (L). Walp) provide a major nutritional source of protein for about 200 million people in sub-Saharan Africa [1]. Cowpea production is highest in the West African countries of Nigeria, Niger and Burkina Faso, where insect feeding damage by over 100 pest species is a major constraint on field production and in grain storage [1]. Yield is most dramatically affected by insect pests that occur during the flowering and seed pod stages. These include flower and pod feeding insects such as flower thrips, Megalurothrips sjostedti Trybom (Thysanoptera: Thripidae); legume pod borer, Maruca vitrata Fabricius (Lepidoptera: Crambidae); pod sucking insects, Clavigralla tomentosicollis Stål (Hemiptera: Coreidae) [2] and Anoplocnemis curvipes Fabricius (Hemiptera: Coreidae); and phloem-feeding cowpea aphids, Aphis craccivora Koch (Hemiptera: Aphididae). Crop damage by these insect pests can be as high as 60 to 100% in the field [35]. Aphis craccivora can cause significant damage even at low population densities due to its ability to transmit at least 14 viruses including the potyviruses, the cowpea aphid-borne mosaic virus (CABMV) [6,7] and the blackeye cowpea mosaic virus (BICMV) [8]. These viruses produce severe cowpea mottling, chlorosis, and seed shriveling [9] which severely reduce yields [10,11]. In contrast to most plant viruses, which fail to cross into developing embryos from infected maternal tissues [12], CABMV and BICMV appear to propagate via vertical transmission from parent to progeny seed [13,14] and is exacerbated by horizontal transmissions by aphid vectors.

Much research has been directed towards developing strategies to control the feeding of the legume pod borer, M. vitrata on cowpea crops. Past use of chemical insecticides has resulted in increased frequencies of resistance in M. vitrata to three classes of insecticides in Nigeria [15], and unfortunately fits within the paradigm where selection pressures imposed by widespread application of a chemical control agent can oftentimes lead to the evolution of insecticide resistance within targeted pest insect populations [16,17]. Additionally, chemical insecticides are often financially inaccessible to smallholder farmers in West Africa, and pose serious health and environmental risks when used indiscriminately by untrained applicators [18,19]. Therefore, recent shifts toward the use of affordable and sustainable biocontrol measures have been initiated within West Africa [2,20]. Some of these potential M. vitrata control strategies have included the deployment of bio-pesticides [21,22] and the development of a transgenic cowpea that expresses Bacillus thuringiensis (Bt) toxins [23]. Additionally, traps baited with the female M. vitrata sex pheromone blends, in a 100:5:5 ratio of (E, E)-10,12-hexadecadienal, (E, E)-10,12-hexadecadienol and (E)-10-hexadecenal, have been distributed to farmers in Benin and used as a successful early warning tool [24]. These baited traps have the potential for monitoring seasonal northward M. vitrata migrations during the rainy season, but the fidelity of pheromone blend, and trap position and design can affect the accuracy of resulting estimates of population size and route of migration [2527]. The population genetic structure of M. vitrata has been described through the application of next generation sequencing (NGS) and high throughput single nucleotide polymorphism (SNP) genotyping technologies [28] as well as microsatellite loci [29]. In these aforementioned studies, M. vitrata population structure and estimates of gene flow (migration) within West African cowpea production area were assessed. The results of these studies have the potential to enhance integrated pest management (IPM) programs to determine the logical locations of natural enemy releases. This prior research on M. vitrata serves as a model for the application of genome-based approaches to increase the effectiveness of strategies used to control pest insect populations.

Since transgenic cowpea that express Bacillus thuringiensis (Bt) Cry1Ab toxin shows no toxicity towards non-lepidopteran insects and a majority of biocontrol strategies for M. vitrata are species-specific, cowpea crops remain susceptible to continued feeding and plant disease transmission by thrips, aphids and pod sucking pests. Thus, the only method widely available to date for the control of A. craccivora, A. curvipes, C. tomentosicollis and M. sjostedti by indigenous farmers in West Africa has been the application of chemical insecticides. Since insecticide resistance had evolved within M. vitrata populations [15], the establishment of effective insect resistance management (IRM) plans for A. craccivora, A. curvipes, C. tomentosicollis and M. sjostedti may be critical for delaying the evolution of resistance. The absence of population genetic data for these species hinders the estimation of movement patterns of these insects within their endemic range such that the regional scales necessary for IRM programs to remain effective are difficult to devise. NGS technologies that include Roche 454 GS FLX, Solexa/Illumina Genome Analyzer, ABI/SOLiD Gene Sequencers and Helicos Genetic Analysis System platforms use massively parallel pyrosequencing technologies to collect millions of nucleotide sequences in very short time frames [30-34]. Moreover, NGS technologies provide a rapid and cost-effective way to obtain large amounts of DNA sequence data from organisms where no prior information had existed [28]. De novo transcriptome analysis has proven to be a valuable first step to obtaining sequence information and expression levels of genes involved in developmental and metabolic pathways, insecticide resistance, and to discover single nucleotide polymorphisms (SNPs) in all kinds of model and non-model organisms [35-38]. SNPs are changes of a single nucleotide at a specific location within the genome of a species, and high-throughput assays have been developed for their detection and application as genetic markers [39-43]. Estimation of allelic frequency variation at SNP loci are effective for describing population demographics [44] and are increasingly becoming the marker of choice in population genetic analysis.

In this study, we applied Roche 454 sequencing technology to generate and subsequently assemble contigs from DNA sequencing reads from independent normalized cDNA libraries for A. curvipes, A. craccivora, C. tomentosicollis and M. sjostedti. Annotations of individual gene transcripts were used to identify candidate genes putatively involved in insecticide resistance, regulation of insect growth and response to disease transmission. This is the first report of genomic data for these insect pests and provides valuable tool for understanding molecular gene functions of several major field insect pests in cowpea cropping systems of West Africa. The application of this genomics data might ultimately lead to a better understanding of the pest populations, with the long-term potential to improve the effectiveness of IPM programs by better defining pest-pathogen interactions, and pest population dynamics prior to deployment of biocontrol agents.

Materials and Methods

Ethics Statement

For all the insect samples used in the study, no permission was required for the insect sampling and collection. Insect sampling and collection in Benin was performed with our collaborators at the International Institute of Tropical Agriculture (IITA). Permission was not required because the insects used for the study are common insect pests on legumes, and IITA Benin has a Memorandum of Understanding (MOU) with the government of Benin for conducting research on these insect pests. In Burkina Faso and Niger, insect sampling and collection were also carried out with our collaborators at the Institut de l’Environnement et de Recherches Agricoles (INERA) and the Institut National de la Recherche Agronomique du Niger (INRAN), respectively. Both INERA and INRAN are national government agencies in their respective countries and therefore have the mandate to work on these insect pests from their respective governments. The insects used for this study are not endangered species.

Development of Reference Transcriptome Sequence Assemblies

Insect samples were collected during the summer through fall of 2011 at 7, 11 and 9 locations in Benin, Burkina Faso and Niger respectively for A. craccivora, A. curvipes, C. tomentosicollis and M. sjostedti (Figure 1). A total of 79, 1,920, 364 and 740 individual insect samples were collected respectively for A. craccivora, A. curvipes, C. tomentosicollis and M. sjostedti from these locations. Both the larval and adult life stages were sampled for all species and stored in RNAlater (Ambion, TX, USA) immediately after collection in the field. All samples from each species, from a single location, were pooled and total RNA was extracted from the insect samples at IITA Benin and INERA Burkina Faso using QIAGEN RNeasy RNA extraction kits (CA, USA) and following the manufacturer's instructions. The RNA was shipped to University of Illinois at Urbana-Champaign (UIUC), USA in 70% ethanol where it was resuspended in water and quantified by measuring the absorbance at 260 nm using a NanoDrop spectrophotometer (Thermo Scientific, DE, USA). The samples were then stored in an ultra-low temperature freezer (-80°C).

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Figure 1. Map of Benin, Burkina Faso, and Niger showing the sites from which A. curvipes, A. craccivora, C. tomentosicollis and M. sjostedti were collected.

https://doi.org/10.1371/journal.pone.0079929.g001

Four normalized cDNA libraries were constructed and sequenced on a Roche 454 GS-FLX at the W.M. Keck Center for Comparative and Functional Genomics, Roy J. Carver Biotechnology Center, UIUC. Briefly, messenger RNA (mRNA) was isolated from 10μg of total RNA with the Oligotex kit (Qiagen, Valencia, CA). The mRNA-enriched fraction was converted to 454 barcoded cDNA libraries and normalized [45]. The barcoded libraries were pooled in equimolar concentration based on average fragment length and concentration. After library construction, the pooled libraries were quantified using a Qubit fluorometer (Invitrogen, CA, USA) and average fragment sizes were determined by analyzing 1µl of the samples on the Bioanalyzer (Agilent, CA, USA) using a DNA 7500 chip. The pooled library was diluted to 1 x 106 molecules/µl. Emulsion-based clonal amplification and sequencing on a full plate on the 454 Genome Sequencer FLX+ system was performed according to the manufacturer’s instructions (454 Life Sciences, CT, USA). Signal processing and base calling were performed using the bundled 454 Data Analysis Software v2.6.

The raw sequence read data from the four insect pests were analyzed using the CLC Genomics Workbench 6.0.1 (Cambridge, MA, USA). Pre-processing of the raw reads from each of the four insect samples involved trimming each 454 read using a Phred quality score of 20 and also removing nucleotides < 50 bp from the ends. The adapter sequences were also trimmed from the raw reads. The processed read data from each of the four insect samples were assembled into contiguous sequences using parameters: mismatch cost = 2, insertion and deletion cost = 3, length fraction = 60% and similarity = 90%. After assembly, the vector contamination were removed using the UniVec database and also after assembly, human, bacterial, fish (Danio rerio), mouse (Mus musculus), Salmonella enterica, archeal and viral contamination were removed using a web-based version of DeConSeq [46] using a coverage of 90% and a sequence identity threshold of 94%. The clean transcriptomes, with the contaminations removed, were then deposited at DDBJ/EMBL/GenBank for each of the four insect species.

Functional Gene Annotation

Open reading frames (ORFs) were predicted from assembled contigs using the ORF-Predictor server [47] using all 6 possible reading frames for prediction. The assembled transcripts were used as queries to search against NCBI’s non-redundant (nr) database using the BLASTx algorithm [48], with a cut-off E-value of ≤ 10-6 and a high scoring segment pairs (HSP) length cut-off of 33. The Blast2GO software package v2.6.5 [49] was used for automating BLASTx searches as well as to retrieve associated gene ontology (GO) terms that allowed the prediction of transcript functions [49,50]. The contigs with significant GO terms were determined with an E-value hit filter of ≤ 1 x 10-6 and an annotation cut off of 55. Gene ontologies were categorized with respect to molecular function, biological process and cellular component.

Annotations for A. craccivora, A. curvipes, C. tomentosicollis and M. sjostedti gene functions were manually searched for those putatively involved in the expression of insecticide resistance traits, and pathogen defense and immunity, using each gene function as keywords to search GO terms. Prediction of candidate gene function was also obtained using InterProScan [51,52] and Kyoto Encyclodepia of Genes and Genomes (KEGG) pathway analyses [53] using Blast2GO v2.6.5 [49].

Prediction of Putative SNPs

The associated SNP detection software on the CLC Workbench 6.0.1 was used for putative SNP discovery among Roche 454 reads for all species. Attempts to reduce the rate of false SNP discovery included applying a read coverage cut-off of ≥ 35-fold and reporting SNPs that were present in ≥ 35% of the aligned reads. These criteria might reduce the false SNP discovery rate by potentially eliminating sequencing errors from the prediction. However, such stringent criteria likely increases type II error, therefore we also performed a comparative prediction of putative SNPs using a reduced coverage cut off of ≥ 10%. All putative indels and nucleotide variants involving > 2 nucleotides were excluded. Lastly, only SNPs located in an ORF were extracted and reported in this study. We checked whether SNPs introduced an amino acid change to differentiate non-synonymous and synonymous SNPs by using the open reading frames of each of the contigs with SNPs, identifying the codons containing the SNPs and then translating and comparing the amino acids for each allele on CLC Workbench 6.0.1. We also checked the type of substitution, whether transition or transversion, using the CLC Workbench 6.0.1.

Metagenomic Identification of Endosymbiont and Pathogen Transcripts

The bacterial endosymbiont, Buchnera aphidicola, was identified from a BLASTn search against Buchnera (Taxid: 32199) in NCBI using the assembled A. craccivora contigs as queries. The A. craccivora contigs with relevant hits to Buchnera were extracted and further confirmatory analysis was performed using InterProScan on Blast2GO v2.6.5, and the associated KEGG pathways were investigated also using Blast2GO v2.6.5.

Data Deposition

The raw Roche 454 sequence data were submitted to the National Center for Biotechnology Information (NCBI) Sequence Read Archive (SRA) with accession numbers of SRR768514, SRR768515, SRR768524 and SRR768525 for A. curvipes, A. craccivora, C. tomentosicollis and M. sjostedti, respectively. The Transcriptome Shotgun Assembly project for the four insect species were submitted to DDBJ/EMBL/GenBank under the accession numbers of GAJV00000000, GAJW00000000, GAJX00000000 and GAJY00000000 for A. curvipes, A. craccivora, C. tomentosicollis and M. sjostedti, respectively. The version of the TSA accession numbers described in this paper is the first version for each of the four species.

Results

Development of Reference Transcriptome Sequence Assemblies

Normalized species-specific libraries were successfully constructed from mRNA isolated from pooled samples of all tissues and pooled adult and larval life stages. A total of 319,126, 176,262, 320,722 and 227,882 raw reads were respectively obtained from these A. curvipes, A. craccivora, C. tomentosicollis and M. sjostedti libraries. The bacterial and human contaminants discovered by DeConSeq were negligible across the four insect species. Seventeen, 2, 11 and 37 contigs were identified by DeConSeq as contaminants in A. curvipes, A. craccivora, C. tomentosicollis and M. sjostedti, respectively and were also subsequently removed from the transcripts. The remaining statistics for sequence and contig assemblies are reported in Table 1. After assembly and decontamination, the mean contig length ranged from 669.8 to 688.1, from which ORFs with a mean length of between 498.5 and 524.5 bp was predicted (Table 1).

A. curvipesA. craccivoraC. tomentosicollisM. sjostedti
Putative SNPs identified74297607180
Contigs with SNPs2563022563
Transition50565423116
Transversion2373218464
Transition/Transversion Ratio2.12.02.31.8
SNPs per Kilobase0.090.020.080.04
Synonymous SNPs4257241997
Non-synonymous SNPs3172518883
Mean read depth of SNPs97.566.6115.574.9

Table 1. Statistics from Roche 454 sequencing of A. curvipes, A. craccivora, C. tomentosicollis and M. sjostedti cDNA libraries generated from pools of all tissues and the larval and adult life stages.

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Functional Gene Annotation

ORFs were predicted from ≥ 98% of A. curvipes, A. craccivora, C. tomentosicollis and M. sjostedti transcripts, and respectively showed mean lengths of 498.5, 514.3, 524.5 and 508.8 bp (Table 1). Blast2GO output indicated that BLASTx hits were obtained for 6,430 (55%), 7,647 (79.9%), 6,839 (64.2%) and 4,292 (58.4%) contigs in A. curvipes, A. craccivora, C. tomentosicollis and M. sjostedti, respectively. The contigs with significant BLASTx matches were assigned GO terms into molecular function, biological process, and cellular components (Tables S1a to S1d). The functional classification based on molecular function, biological process and cellular component are represented in Figures 2a to 2d. In the molecular function category, the most highly represented were assigned to binding (13.7% for A. curvipes, 13.6% for A. craccivora, 13.4% for C. tomentosicollis and 13.5% for M. sjostedti) and catalytic activity (14.4% for A. curvipes, 13.1% for A. craccivora, 14.9% for C. tomentosicollis and 13.5% for M. sjostedti). In the biological process category, the most highly represented were assigned to cellular process (4.7% for A. curvipes, 4.7% for A. craccivora, 4.7% for C. tomentosicollis and 4.7% for M. sjostedti) and metabolic process (5.4% for A. curvipes, 5.4% for A. craccivora, 5.8% for C. tomentosicollis and 5.6% for M. sjostedti) while in the cellular component category, the most highly represented were assigned to cell (9.3% for A. curvipes, 9.1% for A. craccivora, 9.5% for C. tomentosicollis and 9% for M. sjostedti) and cell part (8.2% for A. curvipes, 8% for A. craccivora, 8.3% for C. tomentosicollis and 8.2% for M. sjostedti) (Tables S1a to S1d).

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Figure 2. Gene ontology classification into biological process, cellular component and molecular function.

Gene ontology terms were determined using an e-value of ≤ 1.0 e-6 sorted based on level 2 classifications in all the contigs of (a) A. curvipes, (b) A. craccivora, (c) C. tomentosicollis, (d) M. sjostedti.

https://doi.org/10.1371/journal.pone.0079929.g002

The majority of the top BLASTx hits in the four insect species were from insects. In A. curvipes, the most common were from Hemiptera [Riptortus pedestris (23.6%)], Coleoptera [Tribolium castaneum (7.1%)], Phthiraptera [Pediculus humanus (6.7%)] and another Hemiptera [Acryrthosiphon pisum (6%)] (Figure S1a). The most frequent hits from A. craccivora were from Hemiptera [A. pisum (83.7%)], two fungi species [Rhizopus delemar (1.5%); Batrachochytrium dendrobatidis (0.7%)] and Phthiraptera [P. humanus (0.5%)] (Figure S1b). The most frequent in C. tomentosicollis were from Hemiptera [R. pedestris (27.7%)], Coleoptera [T. castaneum (7.7%)], another Hemiptera [A. pisum (7%)] and Phthiraptera [P. humanus (6.7%)] and (Figure S1c) while the most frequent in M. sjostedti transcripts were from Coleoptera [T. castaneum (9.7%)], Phthiraptera [P. humanus (8.4%)], Lepidoptera [Danaus plexippus (6.5%)] and Hymenoptera [Nasonia vitripennis (5.6%)] (Figure S1d). BLASTx hits also revealed matches to other fungi species, bacteria, and a plant among A. craccivora contigs (Figure S1b), but these were not analogously observed within libraries from the other three insects.

Within the libraries constructed from A. curvipes, A. craccivora, C. tomentosicollis and M. sjostedti cDNA, a combined total of 23 candidate genes for detoxification, immunity and pathogen defense, development and communication were identified including cytochrome P450, glutathione s-transferase, esterase, cathepsin, heat shock protein, chitinase, defensin, c-Jun NH (2)-terminal kinase (jnk) stimulatory phosphatase, down syndrome critical region protein, epidermal growth factor, lysozyme, nimrod, nitric acid synthase, prophenol oxidase, ubiquinol cytochrome c reductase, peptidoglycan recognition protein, toll protein, chemosensory protein, juvenile hormone inducible protein, juvenile hormone esterase and juvenile hormone epoxide hydrolase, chemosensory binding protein as well as odorant binding protein (Figures 3a to 3d).

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Figure 3. Transcripts putatively involved in responses to xenobiotic (e.g., insecticide resistance) and disease transmission in (a) A. curvipes, (b) A. craccivora, (c) C. tomentosicollis, (d) M. sjostedti.

https://doi.org/10.1371/journal.pone.0079929.g003

Metagenomic Identification of Endosymbiont- and Pathogen-Derived Transcripts

Thirty six BLASTn hits to the NCBI nr protein database were identical to the primary endosymbiont of aphids, B. aphidicola, when transcripts from A. craccivora were used as queries of which 23 unique transcripts retrieved InterProScan annotations (Table S2) and nine were predicted to be involved in nine different bacterial biochemical pathways (Table 2). Transcripts from six different fungi species were also predicted among A. craccivora transcripts, including Rhizopus delemar and Batrachochytrium dendrobatidis (Figure S1b).

Contig IDOrthologous B. aphidicola gene B. aphidicola protein (EC)
Aphis 1561 D-fructose-6-phosphate amidotransferase (glmS)BAB12753.1 (EC 2.6.1.16)
Aphis 5691 UDP-N-acetylglucosamine pyrophosphorylase (glmU)BAB12754.1 (EC 2.7.7.23)
Aphis 5225 S-adenosylmethionine synthetase (metK)BAB13109.1 (EC 2.5.1.6)
Aphis 7020 acetolactate synthase small subunit (ilvH)BAB12941.1 (EC 2.2.1.6)
Aphis 6159 2-oxoglutarate dehydrogenase e1 component (sucA) BAB13011.1 (EC 1.2.4.2)
Aphis 5021 ABC transporter ATP-binding protein (uup)BAB13068.1
Aphis 376  Spermidine synthase (speE)BAB12926.1 (EC 2.5.1.16)
Aphis 3768 6-phsphoglucanate dehydrogenase (gnd)BAB12826.1 (EC 1.1.1.44)
Aphis 3870 Hypothetical GTP-binding protein (yfgK)BAB13291.1 

Table 2. The orthologs of A. craccivora contigs derived from the genome of the primary aphid endosymbiont, B. aphidicola (identified in GenBank accession BA000003.2.).

Information regarding protein function can be retrieved from SwissProt database (http://enzyme.expasy.org/) by searches for EC number (not available for all B. aphidicola genes).
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Prediction of Putative SNPs

All A. curvipes, A. craccivora, C. tomentosicollis and M. sjostedti contigs, that contained a putative ORF, were included in the SNP prediction pipeline (Tables S3a to S3d; Tables S4a to S4d). From these predictions, 256, 30, 225 and 63 contigs respectively from A. curvipes, A. craccivora, C. tomentosicollis and M. sjostedti had putative SNPs, which respectively contained a total of 742, 97, 607 and 180 putative SNPs (Tables S3a to S3d; Tables S4a to S4d). The mean depth of reads aligned to the reference transcripts depth for all putative SNPs was > 60 across all species (Table 3). The density of SNPs within transcripts was measured by estimates of mean number of putative SNPs per kilobase, and were all less than 1 (0.09, 0.02, 0.08 and 0.04 respectively among A. curvipes, A. craccivora, C. tomentosicollis and M. sjostedti contigs) (Table 3). The alternate ≥ 10% coverage cut off we used comparatively predicted 2,703, 340, 2,087 and 780 putative SNPs for A. curvipes, A. craccivora, C. tomentosicollis and M. sjostedti, respectively. As a consequence of 454-based sequence by synthesis methods used, resulting reads are prone to sequencing errors known as homopolymers which comprise imprecise nucleotide numbers in long arrays of the same nucleotide. These errors can cause misalignment within contig assemblies such that incorrect SNP predictions can result in sequence regions flanking the homopolymer stretch. To compensate for these errors, the assembled contigs were filtered for 454/Ion homopolymer INDELS in the SNP detection software in the CLC Genomics Workbench before performing the SNPs prediction. To understand the effects of SNP mutations and associate them to the different transcripts obtained in our study, we differentiated synonymous SNPs from non-synonymous SNPs. Of the total number of SNPs obtained in the four insect species, there were 425, 72, 419 and 97 synonymous SNPs respectively in A. curvipes, A. craccivora, C. tomentosicollis and M. sjostedti and respectively 317, 25, 188 and 83 non-synonymous SNPs. In all four species, transitions were more frequent than transversions (Ts/Tv > 1) (Table 3).

A. curvipesA. craccivoraC. tomentosicollisM. sjostedti
NormalizationNormalizedNormalizedNormalizedNormalized
Total number of raw reads319,126176,262320,722227,882
Mean raw read lengths (bp)382.7402.1389.6391.5
Total number of processed reads after trimming304,110166,565306,666211,626
Mean trimmed read length (bp)315.5356.5327.1340.9
Final processed number of assembled contigs11,6877,64710,6527,348
Mean length of assembled contig (bp)688.1669.8685.8683.7
Total number of singletons219211180115
Mean ORF length (bp)498.5514.3524.5508.8
Total number of contigs with BLASTx hits6,4306,1136,8394,292

Table 3. Summary of the putative single nucleotide polymorphism (SNP) predictions from reads mapped to reference A. curvipes, A. craccivora, C. tomentosicollis and M. sjostedti transcripts.

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Discussion

Development of Reference Transcriptome Sequence Assemblies

Next generation sequencing technologies offer a rapid entry point into genomic research [44] and can generate valuable molecular resources for non-model species [35,54] that are a foundation from which a diversity of research questions can be addressed [54,55]. In the absence of complete genome sequences, transcriptome sequencing remain a useful molecular resource that can be applied to the identification of candidate insecticide resistance genes and mutations that can be developed into genetic markers for population genetic studies [28], as well as the identification of potential targets for RNAi knockdown. The Roche 454 platform provides long sequence read lengths that may better allow the assembly of de novo transcriptomes [54], but remain susceptible to sequencing errors in homopolymer regions. The Roche 454 transcriptome data presented in this study from A. curvipes, A. craccivora, C. tomentosicollis and M. sjostedti had a high median length (≥ 680 bp), and a majority of resulting contigs encoded a predicted ORF (= protein coding sequence, CDS). Despite this, a high number of contigs (> 35%) had ORFs with no amino acid similarity to known proteins within the NCBI nr database and was especially the case for A. curvipes, C. tomentosicollis and M. sjostedti transcripts. However, only 20.06% of the A. craccivora contigs had no similarity to known proteins in the NCBI nr database. Annotation of previous transcriptome assemblies have similarly revealed a high number of contigs with genes of unknown function [56-59] which may represent novel uncharacterized genes and reflect the limitation of inferring transcript functions by comparison to model species that have long evolutionary distances to the non-model species in question [60]. Even within whole genome sequence assemblies, species-specific genes can comprise a high percentage of predicted ORFs [61]. The presence of these genes of unknown function could similarly suggest these proteins may be species-specific and, that de novo transcriptome assemblies from non-model insect pest species are useful for phylogenetic novel gene discovery. Furthermore, the resulting assembly of sequence data allow for the identification of novel gene pathways that have potentials for RNAi targeting within a suite of species-specific control tactics.

Functional Annotation

Functional annotations of assembled A. curvipes, A. craccivora, C. tomentosicollis and M. sjostedti transcripts allowed for the identification of candidate genes encoding proteins putatively involved in insecticide resistance, and pathogen defense and immunity. Transcriptomic approaches are powerful tools to identify new genes and gene functions and have been successfully applied to many organisms. In this study, we have identified genes putatively involved in the response to and the detoxification of xenobiotics in the four insect pests. Some of these xenobiotic response/detoxification genes will likely be useful for the study of chemical insecticide resistance traits as well the role in detoxification following exposure to plant allelochemicals. For example, strains of A. craccivora have elevated esterase activities that were linked to increased resistance to the nicotinic acetylecholine receptor agonist, dinotefuran, which belongs to the third generation of neonicotinoids [62]. Our results will provide a foundation that makes the future study of the involvement of these candidate genes in field-observed insecticide resistance traits in these insects more likely, and may also represent genetic markers that can be used to screen field populations (and compare resistant vs. susceptible individuals) to determine linkage (or not) of the locus to the resistant phenotype trait.

Our current understanding of insect immunity and stress responses comes from holometabolous insects and includes flies, butterflies, beetles and bees [63]. The four insect pests under study in this paper are all hemimetabolous insects with three of them (A. curvipes, A. craccivora and C. tomentosicollis) falling into the same insect order of Hemiptera and the fourth insect M. sjostedti falling into the insect order, Thysanoptera. Because all studied species exhibit incomplete development, comparison with the genome of a hemimetabolous insect (i.e., pea aphid, A. pisum) may provide insights into immunity and defense mechanisms in these pest insects. It is also interesting to note that while the four insect species included in this study were not intentionally immunologically challenged, we still observed some transcripts putatively involved in insect defense and immunity based on studies conducted on other insects such as A. pisum. We did not observe as many immunity and defense transcripts in both A. craccivora and M. sjostedti as we observed in A. curvipes and C. tomentosicollis. The immune genes observed in this study include most genes involved in the IMD pathway in insects and includes chitinase, defensin, down syndrome critical region protein, epidermal growth factor receptor, jnk stimulatory phosphatase, lysozyme, nimrod, nitric oxide synthase, odorant binding protein, peptidoglycan-recognition protein and pro-phenol oxidase. We also observed genes involved in toll signaling pathway. It is interesting to note that none of these genes are represented across all the four insect pests. Some insects have particular genes that others lack, and vice versa. For example, A. craccivora appears to be missing the defensin gene, however, a lack of such a gene would have to be verified in the future if a genomic project were to occur for this species. This is consistent with studies conducted on A. pisum, which shows the pea aphid is lacking many of the antimicrobial peptides, such as defensin, common to other insects [64]. The reduced humoral immune system in A. pisum, including an apparently non-functional IMD signaling pathway and absence of PGRPs, has been suggested to be an adaptation for the symbiosis with the bacterium B. aphidicola [65]. The presence of defensin in the human louse, P. humanus and in the ancient apterygote insect, the fire brat, Thermobia domestica [66], suggests that defensins may have been lost during aphid evolution.

Prediction of Putative SNPs

Single nucleotide polymorphisms are rapidly becoming the marker of choice for many applications in population ecology, evolution and conservation genetics, because of the potential for high genotyping efficiency, data quality, genome-wide coverage and analytical simplicity (e.g. in modeling mutational dynamics) [42]. Transcriptome-derived SNPs have several advantages over those developed from genomic sequences [6769], including acquisition of actual gene sequences that allow for direct mapping and comparative genome studies among organisms ([70] and references therein). SNPs derived from transcriptomes are also a source of candidate polymorphisms underlying important traits that can lead to the identification of quantitative trait nucleotides (QTN) [71] linked to ecologically relevant genes. The applicability of SNPs from sequence data for marker development has been previously reported [7274] and has been applied for the genetic mapping of insect orders such as Lepidoptera (Bombyx mori [75]), and for population genetics of the Glanville fritillary butterfly, Melitaea cinxia [76]. The current study provides a set of at least 742, 97, 607 and 180 putative SNPs respectively for A. curvipes, A. craccivora, C. tomentosicollis and M. sjostedti (predicted using the criteria that SNPs be present in ≥ 35% of aligned reads), and the segregating mutations that can be developed into molecular genetic markers for the study of the population genetic structure of these insect pests. Although a greater number of putative SNPs were predicted using a more lenient coverage cut off value of 10%, these loci may be prone to type I error and secondary validation methods may likely be required to distinguish these from sequencing errors.

The frequency of SNPs in laboratory strains of Drosophila was reported at 5 SNP per kilobase [77] and at 1.3 SNPs per kilobase in the inbred Dazao strain of Bombyx mori [78]. Similarly, laboratory strains of the malaria mosquito, Anopheles funestus, were reported to have 7.2 SNPs per kilobase [79], and 8.0 SNPs per kilobase in An. gambiae [80]. Compared to the results obtained from the above studies, we did observe a lower amount of SNPs per kilobase in the present study. Although laboratory strains were used in those studies, we used field-collected insects in our study and usually a reduced SNP frequency is reported in laboratory strains because homozygosity may be increased by the effects of inbreeding or random genetic drift. Non-synonymous SNPs have commonly been reported to occur less frequently than synonymous SNPs, and is presumably due to the evolutionary constraints of negative selection that may eliminate deleterious substitutions from the population [81]. Non-synonymous SNPs are of particular interest because they are more likely to affect the function of the encoded protein and may influence phenotype. It has been estimated that 20–30% of non-synonymous SNPs affect protein function [82,83]. In our study, we did observe a higher number of synonymous SNPs than non-synonymous SNPs across transcripts from all the four insect species. In metazoan DNA sequences, an excess of transition vs. transversion mutations is often observed. This may be partly due to the relatively high rate of change of methylated cytosines to thymine, as well as post-mutation processes of selection on codon-usage bias within coding regions [84]. The role of population genetic and biochemical effects on the rate and direction of nucleotide changes remains unknown, but are likely factors that affect the observed level of SNP allele frequencies within natural populations.

Metagenomic Identification of Endosymbiont- and Pathogen-Derived Transcripts

Aphids are sap-feeding insects that infest a wide range of plant species. Although sap fluids from plant phloem contain high concentrations of carbohydrates, they are deficient in nitrogenous nutrients such as specific amino acids [85,86]. To overcome these nutritional deficiencies, species within Aphidoidea have established mutualistic relationships with the obligate intracellular endosymbiont, B. aphidicola [87,88]. Buchnera endosymbionts produce essential amino acids that cannot be synthesized by aphids or obtained in sufficient quantities from plant saps [65,87]. In return, aphids provide Buchnera with other nutrients required to survive [89]. Relationships between these two groups have existed for approximately 150 to 200 million years [90] resulting in drastic Buchnera genome reductions due to the loss of many genes needed for independent life and has led to the inability to survive outside host cells [91]. Therefore, aphids and associated Buchnera symbionts may be inseparable mutualistic partners. We observed 36 B. aphidicola transcripts among BLASTn hits to our A. craccivora transcripts. These 36 B. aphidicola transcripts were annotated from twelve different strains of B. aphidicola. We also observed ubiquinone in the BLASTx search of A. craccivora. Symbiotic B. aphidicola are aerobic bacterium which, due to gene reduction in metabolic pathways, cannot carry out respiration without obtaining gene products from the host [92]. The electron transport chain consists of a primary dehydrogenase and a terminal reductase, which are linked by ubiquinone [93]. Ubiquinone is an essential redox component of the aerobic respiration of bacteria and mitochondria [94], and participates in the transfer of electrons and hydrogen between flavoproteins and cytochrome b in the respiratory chain. Also, one of the 36 A. craccivora contigs with hits to B. aphidicola was annotated as the gene symbionin, which has been reported to increase the transmission of plant viruses by binding to the read-through domain of the viral coat protein [95]. Further study of these genes may likely lead to a better understanding of symbiosis and plant disease transmission by A. craccivora, and may lead to potential tactics to reduce or eliminate the disease vectoring capacity of A. craccivora.

Additionally, we observed BLASTx hits to six fungi species among A. craccivora sequences. Rhizopus oryzae (R. oryzae has been reclassified to include R. oryzae and R. delemar [96]. Rhizopus delemar was observed in the BLASTx hits in this study) was previously reported to be an entomopathogenic fungal species [97]. Batrachochytrium dendrobatidis causes chytridiomycosis and is a major cause of amphibian population decline worldwide [98] and the sequences within our aphid transcripts may be derived from a related fungal species that is capable of infecting A. craccivora in West Africa. In contrast, Melampsora larici-populina is a cause of rust in poplar trees [99]. These may have resulted from environmental contamination or were present within gut contents of whole aphids that were used for library preparations. These results suggest that application of NGS may be used for the metagenomic identification of putative pathogen species, which in turn may be useful for the biological control of pest insect species.

Conclusion

With the exception of prior studies that focused on M. vitrata, this study represents the first attempt to develop transcriptomic and molecular marker data for field insect pests of cowpea in West Africa.  Although the sequence data, and biological functions of these genes, may be of interest and importance to molecular biologists, the molecular markers are potentially of much greater near-term pragmatic importance for those interested in controlling these pests. Previous studies have already demonstrated that such molecular markers can give us important insights into pest movement patterns that ultimately will impact how pest control strategies for M. vitrata need to be developed in different agro-ecological zones in West Africa [28,29]. For example, M. vitrata is an endemic pest in the southern part of the selected West African countries and migratory in the northern part; thus biocontrol agents need to be released in the south and spraying of pesticides or biopesticides [22] may be a better solution in areas where these insects are not endemic. This understanding has emerged from a combination of studies on the biology of this pest and through the use of molecular markers. We term this approach, combining traditional IPM strategies with knowledge that emerges from population genetics/genomics tools, IPM-omics [100].  This study lays the foundation for research in other pest species, with the long-term goal to develop a comprehensive program that integrates genomics datasets into IPM and IRM programs in order to minimize the crop damage inflicted by pest insect species of cowpea in West Africa.

Supporting Information

Figure S1.

Species distribution of the top BLASTx hits in (a) A. curvipes, (b) A. craccivora, (c) C. tomentosicollis, (d) M. sjostedti.

https://doi.org/10.1371/journal.pone.0079929.s001

(TIF)

Table S1.

a. Counts of all the genes identified in the gene ontology analysis of all the contigs present in A. curvipes. b. Counts of all the genes identified in the gene ontology analysis of all the contigs present in A. craccivora. c. Counts of all the genes identified in the gene ontology analysis of all the contigs present in C. tomentosicollis. d. Counts of all the genes identified in the gene ontology analysis of all the contigs present in M. sjostedti.

https://doi.org/10.1371/journal.pone.0079929.s002

(DOCX)

Table S2.

InterproScan results from A. craccivora contigs that showed BLASTn hits to B. aphidicola.

https://doi.org/10.1371/journal.pone.0079929.s003

(DOCX)

Table S3.

a. Summary of all SNPs detected in contigs in A. curvipes, including sequence description, length, organism, minimum e-value, number of GOs and number of SNPs associated with each contig. b. Summary of all SNPs detected in contigs in A. craccivora, including sequence description, length, organism, minimum e-value, number of GOs and number of SNPs associated with each contig. c. Summary of all SNPs detected in contigs in C. tomentosicollis, including sequence description, length, organism, minimum e-value, number of GOs and number of SNPs associated with each contig. d. Summary of all SNPs detected in contigs in M. sjostedti, including sequence description, length, organism, minimum e-value, number of GOs and number of SNPs associated with each contig.

https://doi.org/10.1371/journal.pone.0079929.s004

(DOCX)

Table S4.

a. List of all SNPs detected in A. curvipes, including consensus positions on contigs, alleles, coverage, frequency and contig sequences. b. List of all SNPs detected in A. craccivora, including consensus positions on contigs, alleles, coverage, frequency and contig sequences. c. List of all SNPs detected in C. tomentosicollis, including consensus positions on contigs, alleles, coverage, frequency and contig sequences. d. List of all SNPs detected in M. sjostedti, including consensus positions on contigs, alleles, coverage, frequency and contig sequences.

https://doi.org/10.1371/journal.pone.0079929.s005

(XLSX)

Acknowledgments

We thank the technicians at IITA Benin, INERA Burkina Faso and INRAN Niger for the collection of the insects used in this study. We also thank the Plant Genetics and Biotechnology Laboratory at INERA, Burkina Faso and the Agro-eco-health laboratory at IITA, Benin for providing facilities for RNA extraction. We thank Susan Balfe for help in preparing Figure 1.

Author Contributions

Conceived and designed the experiments: TAA BRP. Performed the experiments: TAA WS BSC RD MT MNB CBD IB BPO. Analyzed the data: TAA WS BSC RD MT MNB CBD IB BPO BRP. Contributed reagents/materials/analysis tools: TAA WS BSC RD MT MNB CBD IB BPO BRP. Wrote the manuscript: TAA BSC BRP.

References

  1. 1. Cork A, Dobson H, Grzywacz D, Hodges R, Orr A et al. (2009) Review of pre- and post-harvest pest management for pulses with special reference to Eastern and Southern Africa. Natural Resources Institute, University of Greenwich, Central Avenue, Chatham Maritime, Kent ME4 4TB, UK. Prepared for and Funded by McKnight Foundation. Collaborative Crops Research Program.
  2. 2. Adati T, Tamò M, Yusuf SR, Downham MCA, Singh BB et al. (2007) Integrated pest management for cowpea–cereal cropping systems in the West African savannah. International Journal of Tropical Insect Science 27: 123-137. doi:https://doi.org/10.1017/S1742758407883172.
  3. 3. Singh SR, Allen DJ (1980) Pests, diseases, resistance and protection in cowpeas. In: R. J. SummerfieldA. H. Bunting. Advances in Legume Science, Royal Botanical Gardens, Kew. pp. 419–443.
  4. 4. Jackai LEN, Daoust RA (1986) Insect pests of cowpeas. Annual Review of Entomology 31: 95–119. doi:https://doi.org/10.1146/annurev.en.31.010186.000523.
  5. 5. Dugje IY, Omoigui LO, Ekeleme F, Kamara AY, Ajeigbe H (2009) Farmers’ Guide to Cowpea Production in West Africa. IITA, Ibadan, Nigeria. 20 pp.
  6. 6. Thottappilly G, Rossel HW (1985) Virus Diseases of Important Food Crops in Tropical Africa. Ibadan, Nigeria, International Institute of Tropical Agriculture. p. 35.
  7. 7. Atiri GI, Enobakhare DA, Thottappilly A (1986) The importance of colonizing and non-colonizing aphid vectors in the spread of cowpea aphid-borne mosaic virus in cowpea. Crop Protection 5: 406-410. doi:https://doi.org/10.1016/0261-2194(86)90073-6.
  8. 8. Dijkstra J, Bos L, Bouwmeester HJ, Hadiastono T, Lohuis H (1987) Identification of blackeye cowpea mosaic virus from germplasm of yard-long bean and from soybean, and the relationships between blackeye cowpea mosaic virus and cowpea aphid-borne mosaic virus. Netherlands Journal of Plant Pathology 93(3): 115-133. doi:https://doi.org/10.1007/BF02000562.
  9. 9. Brunt A, Crabtree K, Gibbs A (1990) Viruses of Tropical Plants. C.A.B. International, Wallingford, UK. pp. 97-102.
  10. 10. Bock KR, Conti M (1974) Cowpea aphid-borne mosaic virus, descriptions of plant viruses, No. 134. . Commonwealth Mycological Institute and Association of Applied Biologists.Kew, Surrey, UK. 4pp.
  11. 11. Singh SR, Van Emden HF (1979) Insect pests of grain legumes. Annual Review of. Entomology 24: 255–278. doi:https://doi.org/10.1146/annurev.en.24.010179.001351.
  12. 12. Bennett CW (1969) Seed transmission of plant viruses. Adv Virus Res 14: 221–262. doi:https://doi.org/10.1016/S0065-3527(08)60561-8. PubMed: 4886836.
  13. 13. Gillaspie AG Jr, Hopkins MS, Pinnow DL (1993) Relationship of cowpea seed-part infection and seed transmission of blackeye cowpea mosaic potyvirus in cowpea. Plant Disease 77(9): 875-877. doi:https://doi.org/10.1094/PD-77-0875.
  14. 14. Bashir M, Hampton RO (1996) Detection and identification of seed-borne viruses from cowpea (Vigna unguiculata (L.) Walp.) germplasm. Plant Pathology. 4: 54-58.
  15. 15. Ekesi S (1999) Insecticide resistance in field populations of the legume pod-borer, Maruca vitrata Fabricius (Lepidoptera: Pyralidae), on cowpea, Vigna unguiculata (L.) Walp in Nigeria. International Journal of Pest Management. 45:57-59.
  16. 16. Champ BR, Dyte CE (1976) Report of the FAO global survey of pesticide susceptibility of stored grain pests. FAO Plant Production Project. Paper No. 5. FAO/UN, Rome.
  17. 17. Georghiou GP, Lagunes-Tejeda A (1991) The Occurrence of Resistance to Pesticides in Arthropods. FAO, Rome.
  18. 18. Kamara AY, Chikoye D, Omoigui LO, Dugje IY (2007) Cultivar and insecticide spraying regimes effects on insect pests and grain yield of cowpea in the dry savannas of north-eastern Nigeria. African Crop Science Conference Proceedings 8. pp. 179-184.
  19. 19. Oparaeke AM (2007) Toxicity and spraying schedules of a biopesticide prepared from Piper guineense against two cowpea pests. Plant Protect Sci 43: 103–108.
  20. 20. Amevoin K, Sanon A, Apossaba M, Glitho IA (2007) Biological control of bruchids infesting cowpea by the introduction of Dinarmus basalis (Rondani) (Hymenoptera: Pteromalidae) adults into farmers’ stores in West Africa. Journal of Stored Products Research 43(3): 240–247. doi:https://doi.org/10.1016/j.jspr.2006.06.004.
  21. 21. Oparaeke AM (2006) The potential for controlling Maruca vitrata Fab. And Clavigralla tomentosicollis Stal. Using different concentrations and spraying schedules of Syzigium aromaticum (L.) Merr and Perr on cowpea plants. J. Plant Sci. 1:132–137.
  22. 22. Tamò M, Srinivasan R, Dannon E, Agboton C, Datinon B et al. (2012) Biological Control: a Major Component for the Long-Term Cowpea Pest Management Strategy. In: O. BoukarO. CoulibalyC. FatokunK. LopezM. Tamò. Improving livelihoods in the cowpea value chain through advancements in science. Proceedings of the 5th World Cowpea Research Conference. pp. 249-259.
  23. 23. Bean. , Cowpea CRSP (2001) The Dakar Symposium/Workshop on the Genetic Improvement of Cowpea. JAN. 8-12.
  24. 24. Downham MCA, Tamò M, Hall DR, Datinon B, Adetonah S et al. (2003) Developing pheromone traps and lures for Maruca vitrata in Benin, West Aftrica. Entomologia Experimentalis et Applicata. 110(2): 151-158.
  25. 25. Bartels DW, Hutchison WD, Udayagiri S (1997) Pheromone trap monitoring of Z-strain European corn borer (Lepidoptera: Pyralidae): optimum pheromone blend, comparison with black light trap, and trap number requirements. J Econ Entomol 90: 449-457.
  26. 26. Bradshaw JWS, Baker R, Longhurst C, Edwards JC, Lisk JC (1983) Optimization of a monitoring system for the pine beauty moth, Panolis flammea (Denis & Schiffermüller), using sex attractants. Crop Protection 2: 63–73. doi:https://doi.org/10.1016/0261-2194(83)90026-1.
  27. 27. Lewis T, Macaulay EDM (1976) Design and elevation of sex attractant traps for pea moth, Cydia nigricana (Steph.) and the effect of plume shape on catches. Ecological Entomology 1: 175–187. doi:https://doi.org/10.1111/j.1365-2311.1976.tb01221.x.
  28. 28. Margam VM, Coates BS, Bayles DO, Hellmich RL, Agunbiade T et al. (2011) Transcriptome sequencing, and rapid development and application of SNP markers for the legume pod borer Maruca vitrata (Lepidoptera: Crambidae). PLOS ONE. 6(7): e21388. doi:https://doi.org/10.1371/journal.pone.0021388. PubMed: 21754987.
  29. 29. Agunbiade TA, Kim KS, Forgacs D, Margam VM, Murdock LL et al. (2012) The spatial genetic differentiation of the legume pod borer, Maruca vitrata F. (Lepidoptera: Crambidae) populations in West Africa. Bulletin of Entomological Research 102(5): 589-599. doi:https://doi.org/10.1017/S0007485312000156.
  30. 30. Margulies M, Egholm M, Altman WE, Attiya S, Bader JS et al. (2005) Genome sequencing in microfabricated high-density picolitre reactors. Nature 437: 376-380. PubMed: 16056220.
  31. 31. Moore MJ, Dhingra A, Soltis PS, Shaw R, Farmerie WG et al. (2006) Rapid and accurate pyrosequencing of angiosperm plastid genomes. BMC Plant Biol 6: 17. doi:https://doi.org/10.1186/1471-2229-6-17. PubMed: 16934154.
  32. 32. Wicker T, Schlagenhauf E, Graner A, Close TJ, Keller B et al. (2006) 454 sequencing put to the test using the complex genome of barley. BMC Genomics 7: 275. doi:https://doi.org/10.1186/1471-2164-7-275. PubMed: 17067373.
  33. 33. Huse SM, Huber JA, Morrison HG, Sogin ML, Welch DM (2007) Accuracy and quality of massively-parallel DNA pyrosequencing. Genome Biol. 8: R143 J. Med. Entomol. 42(1):36-41.
  34. 34. Weber APM, Weber KL, Carr K, Wilkerson C, Ohlrogge JB (2007) Sampling the Arabidopsis transcriptome with massively parallel pyrosequencing. Plant Physiol 144: 32-42. doi:https://doi.org/10.1104/pp.107.096677. PubMed: 17351049.
  35. 35. Sloan DB, Keller SR, Berardi AE, Sanderson BJ, Karpovich JF et al. (2012) De novo transcriptome assembly and polymorphism detection in the flowering plant Silene vulgaris (Caryophyllaceae). Mol Ecol Resour 12: 333–343. doi:https://doi.org/10.1111/j.1755-0998.2011.03079.x. PubMed: 21999839.
  36. 36. Xue J, Bao Y-Y, Li B-l, Cheng Y-B, Peng Z-Y et al. (2010) Transcriptome Analysis of the Brown Planthopper Nilaparvata lugens. PLOS ONE 5: e14233. PubMed: 21151909.
  37. 37. Mittapalli O, Bai X, Mamidala P, Rajarapu SP, Bonello P et al. (2010) Tissue-Specific Transcriptomics of the Exotic Invasive Insect Pest Emerald Ash Borer (Agrilus planipennis). PLOS ONE 5: e13708. PubMed: 21060843.
  38. 38. Poelchau MF, Reynolds JA, Denlinger DL, Elsik CG, Armbruster PA (2011) A de novo transcriptome of the Asian tiger mosquito, Aedes albopictus, to identify candidate transcripts for diapause preparation. BMC Genomics 12: 619-. PubMed: 22185595.
  39. 39. Tang K, Fu DJ, Julien D, Braun A, Cantor CR et al. (1999) Chip-based genotyping by mass spectrometry. Proc Natl Acad Sci U S A 96: 10016–10020. doi:https://doi.org/10.1073/pnas.96.18.10016. PubMed: 10468554.
  40. 40. Vignal A, Milan D, SanCristobal M, Eggen A (2002) A review on SNP and other types of molecular markers and their use in animal genetics. Genet Sel Evol 34: 275-305. doi:https://doi.org/10.1186/1297-9686-34-3-275. PubMed: 12081799.
  41. 41. Brumfield RT, Beerli P, Nickerson DA, Edwards SV (2003) The utility of single nucleotide polymorphisms in inferences of population history. Trends Ecol Evol 18: 249-256. doi:https://doi.org/10.1016/S0169-5347(03)00018-1.
  42. 42. Morin PA, Luikart G, Wayne RK, SNP-Workshop_Grp (2004) SNPs in ecology, evolution and conservation. Trends in Ecology and Evolution 19: 208-216 doi:10.1016/j.tree.2004.01.009.
  43. 43. Schlötterer C (2004) The evolution of molecular markers – just a matter of fashion? Nat Rev Genet 5(1): 63-69. doi:https://doi.org/10.1038/nrg1249. PubMed: 14666112.
  44. 44. Coates BS, Bayles DO, Wanner KW, Robertson HM, Hellmich RL et al. (2011) The application and performance of single nucleotide polymorphism markers for population genetic analyses of Lepidoptera. Frontiers in Research 2 (38): 1 -10.
  45. 45. Lambert DJ, Yi Chan Xin, Spiecker B, Sweet HC (2010) Characterizing the embryonic transcriptome of the snail, Ilyanassa. Integr Comp Biol 50(5): 768-777. doi:https://doi.org/10.1093/icb/icq121. PubMed: 21558239.
  46. 46. Schmieder R, Edwards R (2011) Fast identification and removal of sequence contamination from genomic and metagenomic datasets. PLOS ONE 6: e17288. doi:https://doi.org/10.1371/journal.pone.0017288. PubMed: 21408061.
  47. 47. Min XJ, Butler G, Storms R, Tsang A (2005) OrfPredictor: predicting protein-coding regions in EST-derived sequences. Nucleic Acids Res 33: W677–W680. doi:https://doi.org/10.1093/nar/gki394. PubMed: 15980561.
  48. 48. Altschul SF, Warren G, Webb M, Eugene WM, David JL (1990) Basic Local Alignment Search Tool. J Mol Biol 215: 403-410. doi:https://doi.org/10.1016/S0022-2836(05)80360-2. PubMed: 2231712.
  49. 49. Ashburner M, Ball CA, Blake JA et al. (2000) Gene Ontology: tool for the unification of biology. Nat Genet 25: 25–29. doi:https://doi.org/10.1038/75556. PubMed: 10802651.
  50. 50. Shaw DR, Ashburner M, Blake J,. et al. (1999) Gene Ontology: a controlled vocabulary to describe the function, biological process and cellular location of gene products in genome databases. American Journal of Human Genetics 65: 1419.
  51. 51. Hunter S, Apweiler R, Attwood TK, Bairoch A, Bateman A et al. (2009) InterPro: the integrative protein signature database. Nucleic Acids Res 37: D211–D215. doi:https://doi.org/10.1093/nar/gkn785. PubMed: 18940856.
  52. 52. Quevillon E, Silventoinen V, Pillai S, Harte N, Mulder N et al. (2005) InterProScan: protein domains identifier. Nucleic Acids Res 33: W116–W120. doi:https://doi.org/10.1093/nar/gni118. PubMed: 15980438.
  53. 53. Kanehisa M, Goto S (2000) KEGG: Kyoto encyclopedia of genes and genomes. Nucleic Acids Res 28: 27–30. doi:https://doi.org/10.1093/nar/28.7.e27. PubMed: 10592173.
  54. 54. Harismendy O, Ng PC, Strausberg RL, Wang X, Stockwell TB et al. (2009) Evaluation of next generation sequencing platforms for population targeted sequencing studies. Genome Biol 10: R32. doi:https://doi.org/10.1186/gb-2009-10-3-r32. PubMed: 19327155.
  55. 55. Rothberg JM, Leamon JH (2008) The development and impact of 454 sequencing. Nat Biotechnol 26: 1117–1124. doi:https://doi.org/10.1038/nbt1485. PubMed: 18846085.
  56. 56. Karatolos N, Pauchet Y, Wilkinson P, Chauhan R, Denholm I et al. (2011) Pyrosequencing the transcriptome of the greenhouse whitefly, Trialeurodes vaporariorum reveals multiple transcripts encoding insecticide targets and detoxifying enzymes. BMC Genomics 12: 56. doi:https://doi.org/10.1186/1471-2164-12-56. PubMed: 21261962.
  57. 57. Bai X, Mamidala P, Rajarapu SP, Jones SC, Mittapalli O (2011) Transcriptomics of the Bed Bug (Cimex lectularius). PLOS ONE 6(1): e16336. doi:https://doi.org/10.1371/journal.pone.0016336. PubMed: 21283830.
  58. 58. Wang X-W, Luan J-B, Li J-M, Bao Y-Y, Zhang C-X et al. (2010) De novo characterization of a whitefly transcriptome and analysis of its gene expression during development. BMC Genomics 11: 400. doi:https://doi.org/10.1186/1471-2164-11-400. PubMed: 20573269.
  59. 59. Shen G-M, Dou W, Niu J-Z, Jiang H-B, Yang W-J et al. (2011) Transcriptome Analysis of the Oriental Fruit Fly (Bactrocera dorsalis). PLOS ONE 6: e29127. doi:https://doi.org/10.1371/journal.pone.0029127. PubMed: 22195006.
  60. 60. Coates BS, Sumerford DV, Hellmich RL, Lewis LC (2008) Mining an Ostrinia nubilalis midgut expressed sequence tag (EST) library for candidate genes and single nucleotide polymorphisms (SNPs). Insect Mol Biol 17: 607–620. doi:https://doi.org/10.1111/j.1365-2583.2008.00833.x. PubMed: 19133073.
  61. 61. Tribolium Genome Sequencing Consortium (2008) The genome of the model beetle and pest Tribolium castaneum. Nature 452: 949-955. doi:https://doi.org/10.1038/nature06784. PubMed: 18362917.
  62. 62. Mokbel ES, Mohamed AI (2009) Development of resistance in field strain of Aphis craccivora to the dinotefuran insecticides from the new class neonicotinoids and its effect on some enzymes. Egypt. Acad - J Biolog Sci 1(1): 65-69.
  63. 63. Gerardo NM, Altincicek B, Anselme C, Atamian H, Barribeau SM et al. (2010) Immunity and other defenses in pea aphids, Acyrthosiphon pisum. Genome Biol 11: R21. doi:https://doi.org/10.1186/1465-6906-11-S1-P21. PubMed: 20178569.
  64. 64. Zou Z, Evans JD, Lu Z, Zhao P, Williams M et al. (2007) Comparative genomic analysis of the Tribolium immune system. Genome Biol 8: R177. doi:https://doi.org/10.1186/gb-2007-8-8-r177. PubMed: 17727709.
  65. 65. Douglas AE (1998) Nutritional interactions in insect-microbe symbioses: aphids and their symbiotic bacteria Buchnera. Annu Rev Entomol 43: 17–37. doi:https://doi.org/10.1146/annurev.ento.43.1.17. PubMed: 15012383.
  66. 66. Altincicek B, Vilcinskas A (2007) Identification of immune-related genes from an apterygote insect, the firebrat Thermobia domestica. Insect Biochem Mol Biol 37: 726-731. doi:https://doi.org/10.1016/j.ibmb.2007.03.012. PubMed: 17550828.
  67. 67. Hayes J, Laerdahl JK, Lien S, Moen T, Berg P et al. (2007) An extensive resource of single nucleotide polymorphism markers associated with Atlantic salmon (Salmo salar) expressed sequences. Aquaculture 265 (1-4): 82 -90. doi:https://doi.org/10.1016/j.aquaculture.2007.01.037.
  68. 68. Akey JM, Zhang K, Xiong M, Jin L (2003) The effect of single nucleotide polymorphism identification strategies on estimates of linkage disequilibrium. Mol Biol Evol 20 (2): 232-242. doi:https://doi.org/10.1093/molbev/msg032. PubMed: 12598690.
  69. 69. Picoult-Newberg L, Ideker TE, Pohl MG, Taylor SL, Donaldson MA et al. (1999) Mining SNPs from EST databases. Genome Res 9: 167–174. PubMed: 10022981.
  70. 70. Wang S, Sha Z, Sonstegard TS, Liu H, Xu P, Somridhivej B et al. (2008) Quality assessment parameters for EST-derived SNPs from catfish. BMC Genomics 9: 450. doi:https://doi.org/10.1186/1471-2164-9-450. PubMed: 18826589.
  71. 71. Jalving R, van’t Slot R, van Oost BA (2004) Chicken single nucleotide polymorphism identification and selection for genetic mapping. Poult Sci 83(12): 1925-1931. PubMed: 15615001.
  72. 72. Novaes ED, Drost R, Farmerie WG, Pappas GJ, Grattapaglia D et al. (2008) High-throughput gene and SNP discovery in Eucalyptus grandis, an uncharacterized genome. BMC Genomics 9: 312. doi:https://doi.org/10.1186/1471-2164-9-312. PubMed: 18590545.
  73. 73. Wiedmann RT, Smith TPL, Nonneman DJ (2008) SNP discovery in swine by reduced representation and high throughput pyrosequencing. BMC Genet 9: 81. doi:https://doi.org/10.1186/1471-2156-9-81. PubMed: 19055830.
  74. 74. Williams LM, Ma X, Boyko AR, Bustamante CD, Oleksiak MF (2010) SNP identification, verification, and utility for population genetics in a non-model genus. BMC Genet 11: 32. doi:https://doi.org/10.1186/1471-2350-11-32. PubMed: 20433726.
  75. 75. Yamamoto K, Zhang P, Banno Y, Fujii H (2006) Identification of a sigma-class glutathione-S-transferase from the silkworm, Bombyx mori. J Appl Entomol 130: 515–522. doi:https://doi.org/10.1111/j.1439-0418.2006.01092.x.
  76. 76. Orsini L, Corander J, Alasentie A, Hanski I (2008) Genetic spatial structure in a butterfly metapopulation correlates better with past than present demographic structure. Mol Ecol 17: 2629–2642. doi:https://doi.org/10.1111/j.1365-294X.2008.03782.x. PubMed: 18466229.
  77. 77. Berger J, Suzuki T, Senti KA, Stubbs J, Schaffner G et al. (2001) Genetic mapping with SNP markers in Drosophila. Nat Genet 29(4): 475-481. doi:https://doi.org/10.1038/ng773. PubMed: 11726933.
  78. 78. Cheng TC, Xia QY, Qian JF, Liu C, Lin YZX et al. (2004) Mining single nucleotide polymorphisms from EST data of silkworm, Bombyx mori, inbred strain Dazao. Insect Biochem Mol Biol 34: 523-530. doi:https://doi.org/10.1016/j.ibmb.2004.02.004. PubMed: 15147754.
  79. 79. Wondji CS, Morgan J, Coetzee M, Hunt RH et al. (2007) Mapping a quantitative trait locus (QTL) conferring pyrethroid resistance in the African malaria vector Anopheles funestus. BMC Genomics 8: 34. PubMed: 17261170.
  80. 80. Morlais I, Ponçon N, Simard F, Cohuet A, Fontenille D (2004) Intraspecific nucleotide variation in Anopheles gambiae: new insights into the biology of malaria vectors. Am J Trop Med Hyg71(6): 795-802. PubMed: 15642974.
  81. 81. Cargill M, Altshuler D, Ireland J, Sklar P, Ardlie K et al. (1999) Characterization of single-nucleotide polymorphisms in coding regions of human genes. Nat Genet 22(3): 231-238. doi:https://doi.org/10.1038/10290. PubMed: 10391209.
  82. 82. Sunyaev S, Ramensky V, Koch I, Lathe W 3rd, Kondrashov AS et al. (2001) Prediction of deleterious human alleles. Hum Mol Genet 10(6): 591-597. doi:https://doi.org/10.1093/hmg/10.6.591. PubMed: 11230178.
  83. 83. Chasman D, Adams RM (2001) Predicting the functional consequences of non-synonymous single nucleotide polymorphisms: structure-based assessment of amino acid variation. J Mol Biol 307(2): 683-706. PubMed: 11254390.
  84. 84. Keller A, Zhuang H, Chi Q, Vosshall LB, Matsunami H et al. (2007) Genetic variation in a human odorant receptor alters odour perception. Nature 449: 468-472. doi:https://doi.org/10.1038/nature06162. PubMed: 17873857.
  85. 85. Sandström J, Moran NA (1999) How nutritionally imbalanced is phloem sap for aphids? Entomol Exp Appl 91(1): 203-210. doi:https://doi.org/10.1046/j.1570-7458.1999.00485.x.
  86. 86. Houk EJ, Griffiths GW (1980) Intracellular symbiotes of the Homoptera. Annual Review of Entomology. 25: 161–187. doi:https://doi.org/10.1146/annurev.en.25.010180.001113.
  87. 87. Lai CY, Baumann L, Baumann P (1994) Amplification of trpEG: adaptation of Buchnera aphidicola to an endosymbiotic association with aphids. Proc Natl Acad Sci U S A 91(9): 3819-3823. doi:https://doi.org/10.1073/pnas.91.9.3819. PubMed: 8170994.
  88. 88. Munson MA, Baumann P, Kinsey MG (1991) Buchnera gen. nov. and Buchnera aphidicola sp. Nov., a Taxon Consisting of the Mycetocyte-Associated, Primary Endosymbionts of Aphids. Int J Syst Bacteriol 41(4): 566-568. doi:https://doi.org/10.1099/00207713-41-4-566.
  89. 89. Wilkinson TL, Douglas AE (1995) Why Pea aphids (Acyrthosiphon pisum) Lacking Symbiotic Bacteria Have Elevated Levels of the Amino Acid Glutamine. J Insect Physiol 41(11): 921-927. doi:https://doi.org/10.1016/0022-1910(95)00063-Z.
  90. 90. Moran NA, Munson MA, Baumann P, Ishikawa H (1993) A molecular clock in endosymbiotic bacteria is calibrated usingthe insect hosts. Proc R Soc Lond B 253: 167–171. doi:https://doi.org/10.1098/rspb.1993.0098.
  91. 91. Shigenobu S, Watanabe H, Hattori M, Sakaki Y, Ishikawa H (2000) Genome sequence of the endocellular bacterial symbiont of aphids Buchnera sp. APS. Nature 407(6800): 81-86. doi:https://doi.org/10.1038/35024074. PubMed: 10993077.
  92. 92. Zientz E, Dandekar T, Gross R (2004) Metabolic Interdependence of Obligate Intracellular Bacteria and Their Insect Hosts. Microbiol Mol Biol Rev 68(4): 745-770. doi:https://doi.org/10.1128/MMBR.68.4.745-770.2004. PubMed: 15590782.
  93. 93. Unden G, Bongaerts J (1997) Alternative respiratory pathways of Escherichia coli: energetics and transcriptional regulation in response to electron acceptors. Biochim Biophys Acta 1320: 217–234. doi:https://doi.org/10.1016/S0005-2728(97)00034-0. PubMed: 9230919.
  94. 94. Søballe B, Poole RK (2000) Ubiquinone limits oxidative stress in Escherichia coli. Microbiology. 146: 787–796. PubMed: 10784036.
  95. 95. Banerjee S, Hess D, Majumder P, Roy D, Das S (2004) The Interactions of Allium sativum Leaf Agglutinin with a Chaperonin Group of Unique Receptor Protein Isolated from a Bacterial Endosymbiont of the Mustard Aphid. J Biol Chem 279(22): 23782–23789. doi:https://doi.org/10.1074/jbc.M401405200. PubMed: 15028723.
  96. 96. Abe A, Oda Y, Asano K, Sone T (2007) Rhizopus delemar is the proper name for Rhizopus oryzae fumaric-malic acid producers. Mycologia 99: 714–722. doi:https://doi.org/10.3852/mycologia.99.5.714. PubMed: 18268905.
  97. 97. Sharma A, Chandla VK, Thakur DR (2012) Biodiversity and Pathogenicity Potential of Mycoflora Associated with Brahmina coriacea in Potato Fields of North-Western Indian Hills. Journal of Entomology 9: 319-331. doi:https://doi.org/10.3923/je.2012.319.331.
  98. 98. Friesen LR, Kuhn RE (2012) Fluorescent Microscopy of Viable Batrachochytrium dendrobatidis. J Parasitol 98: (3): 509-512. doi:https://doi.org/10.1645/GE-2973.1. PubMed: 22257116.
  99. 99. Yu Z, Liang J, Cao Z, Guo Z, Dan J et al. (2009) Nuclear behavior in the life cycle of Melampsora larici-populina Kleb. Journal of Food, Agriculture and Environment 7 (3&4): 791-794.
  100. 100. Agunbiade T, Steele L, Coates B, Gassmann A, Margam V et al. (2012) IPM-omics: From Genomics to Extension for Integrated Pest Management of Cowpea. In: O. BoukarO. CoulibalyC. FatokunK. LopezM. Tamò. Improving livelihoods in the cowpea value chain through advancements in science. Proceedings of the 5th World Cowpea Research Conference. pp. 231 - 248.