Rapid, accurate and high-throughput identification of vector arthropods is of paramount importance in surveillance programmes that are becoming more common due to the changing geographic occurrence and extent of many arthropod-borne diseases. Protein profiling by MALDI-TOF mass spectrometry fulfils these requirements for identification, and reference databases have recently been established for several vector taxa, mostly with specimens from laboratory colonies.
Methods
We established and validated a reference database containing 20 phlebotomine sand fly (Diptera: Psychodidae, Phlebotominae) species by using specimens from colonies or field-collections that had been stored for various periods of time.
Results
Identical biomarker mass patterns (‘superspectra’) were obtained with colony- or field-derived specimens of the same species. In the validation study, high quality spectra (i.e. more than 30 evaluable masses) were obtained with all fresh insects from colonies, and with 55/59 insects deep-frozen (liquid nitrogen/-80 °C) for up to 25 years. In contrast, only 36/52 specimens stored in ethanol could be identified. This resulted in an overall sensitivity of 87 % (140/161); specificity was 100 %. Duration of storage impaired data counts in the high mass range, and thus cluster analyses of closely related specimens might reflect their storage conditions rather than phenotypic distinctness. A major drawback of MALDI-TOF MS is the restricted availability of in-house databases and the fact that mass spectrometers from 2 companies (Bruker, Shimadzu) are widely being used. We have analysed fingerprints of phlebotomine sand flies obtained by automatic routine procedure on a Bruker instrument by using our database and the software established on a Shimadzu system. The sensitivity with 312 specimens from 8 sand fly species from laboratory colonies when evaluating only high quality spectra was 98.3 %; the specificity was 100 %. The corresponding diagnostic values with 55 field-collected specimens from 4 species were 94.7 % and 97.4 %, respectively.
Conclusions
A centralized high-quality database (created by expert taxonomists and experienced users of mass spectrometers) that is easily amenable to customer-oriented identification services is a highly desirable resource. As shown in the present work, spectra obtained from different specimens with different instruments can be analysed using a centralized database, which should be available in the near future via an online platform in a cost-efficient manner.
The geographic occurrence and extent of arthropod-borne diseases is changing, due to globalisation and environmental alterations. Most spectacular is the emergence of invasive species, e.g. Aedes mosquitoes [1, 2], with associated new disease threats [3]. Other arthropod vectors such as ticks (Ixodida: Ixodidae) [4, 5], biting midges (Diptera: Ceratopogonidae) [6] and phlebotomine sand flies (Diptera: Psychodidae) [7–9] are gradually expanding their distribution ranges in Europe. Because these changes in vector distribution are associated with changes in the risk of exposure to the pathogens they transmit, monitoring the presence and abundances of arthropod vectors is of growing importance in many regions. Guidelines for surveillance and options for control have so far only been developed for mosquitoes, both native and invasive species [2, 10, 11]. Regularly updated distribution maps for Europe are provided by ECDC (www.ecdc.europa.eu) for a number of vectors (eight sand fly species, five Aedes mosquito species, four tick species).
Undoubtedly, reliable, rapid and cost-effective identification of vector arthropods is a key element of surveillance programmes. Morphological identification requires at least some degree of proficiency and can be time-consuming, e.g. requiring slide preparations and in-depth analysis of characteristics such as the morphology of pharynx and genitalia in the case of sand flies [12]. However, morphological identification can be difficult or impossible in many instances (e.g. due to specimens of sibling or cryptic species; damaged or incomplete specimens; life stages with few morphological features like eggs or larvae; poor preservation methods or damage during shipment). In the case of sand flies, which are the focus of this paper, morphological identification is sometimes hampered by the lack of comprehensive keys, minute species-distinctive characters in some subgenera and the existence of phenotypic plasticity among populations [13, 14]. PCR-based approaches are established in different formats for a number of phlebotomine species (compiled by [15, 16]), but their validity may be impaired due to genetic variability at the target locus [17, 18]. Further, these approaches are generally considered expensive and time-consuming.
As an alternative, protein profiling by matrix-assisted laser desorption/ionization time of flight mass spectrometry (MALDI-TOF MS), which is routinely used in clinical diagnostics of bacteria and fungi [19, 20] with high interlaboratory reproducibility [21], has recently been applied for the identification of a number of arthropods, including adult stages of vector taxa [15, 22–33]. In addition, protein profiles have been determined for larvae of holometabolous Culicoides biting midges and Culicidae [34, 35], and for eggs of nine aedine mosquito species [36]. MALDI-TOF MS was capable of identifying sister taxa and cryptic species [26, 28], and the method proved reliable for large scale species identification of Culicoides biting midges (correct identification of 98.9 % of 1,200 field-collected specimens) as well as in the surveillance of invasive mosquito species (identification of eggs from ovitraps; [28]).
This paper elaborates on the suitability of MALDI-TOF MS to identify adult phlebotomine sand flies, the biological vectors of a number of important protozoan and viral pathogens of medical or veterinary importance [7, 37, 38], extending the method from identifying specimens from laboratory colonies [15] to identifying specimens collected in the field and stored for a prolonged period of time. In addition, we evaluated whether raw mass spectra obtained with the instrument of one company (Ultraflex III, Bruker, Germany) allow species identification by using the software and the reference database established on an instrument of another company (Axima Confidence, Shimadzu, Japan), whereby the two most widespread instrument series were involved. The ability to cross-reference specimens with non-parent databases would strongly enhance the value and availability of in-house reference databases established at different institutions.
Methods
Sand fly collection and morphological identification
Mass spectra were determined from sand fly specimens of 20 species obtained from field collections (9 species), colonies (7) or both (4) (see Table 1 for origin, year of collection). Sand flies were captured using CDC miniature light traps (John W. Hock Co. FL, USA) or sticky papers. Specimens were killed using carbon dioxide or liquid nitrogen and stored as described in Table 1. For morphological identification, head and genitalia of each specimen were processed and mounted on slides following traditional procedures [39] and the species determined using standard keys [40–42]. The taxonomic abbreviations used are as described [43].
Table 1
Features of the phlebotomine sand flies investigated in the experimental part of the study
2Used for calculating alternative reference database (replacing spectra from colony insects, see also Fig. 2)
3Colonies maintained at Department of Parasitology, Charles University, Prague, Czech Republic [15]
4-80 °C since 2012
Generation of MALDI-TOF MS biomarker mass sets, validation study
Thoraxes with wings and legs were manually homogenized, mixed with matrix and spotted on steel target plates as described [26]. Protein mass fingerprints were obtained using a MALDI-TOF Mass Spectrometry Axima™ Confidence machine (Shimadzu-Biotech Corp., Kyoto, Japan) and analysed with SARAMIS™ Premium software (spectral archive and microbial identification system, AnagnosTec, Potsdam-Golm, Germany) as described elsewhere [36]. Biomarker mass patterns, called ‘superspectra’, were calculated using the SARAMIS™ SuperSpectra™ tool with 5 specimens per species (Table 1) with 4 technical replicates each (quadruplicates). For SuperSpectra™ validation, 161 specimens (Table 1) were analysed (also in quadruplicates), and the generated mass fingerprints were imported into SARAMIS™ software for automated identification with SuperSpectra™. The threshold for identification was set at 75 % biomarker matches based on the reference data set, according to the SARAMIS™ user guideline. Spectra containing less than 30 data counts were considered low quality. A dendrogram was produced as described [27].
Analyses of raw data mass spectra obtained on Bruker mass spectrometer with Shimadzu software
Mass fingerprints generated using automatic routine procedures on an Ultraflex III MALDI TOF mass spectrometer (Bruker Daltonics, Bremen, Germany) [15] were analysed in a blinded manner with the SARAMIS™ Premium software. Bruker mass lists were exported as mzXml files, adapted to the SARAMIS™ Premium file format by use of an in-house phyton script and imported for automated identification. Mass lists obtained with insect thoraxes were available for 312 specimens of Phlebotomus arabicus (n = 13), Ph. argentipes (n = 20), Ph. duboscqi (n = 10), Ph. orientalis (n = 10), Ph. papatasi (n = 84), Ph. perniciosus (n = 94), Ph. sergenti (n = 22), Ph. tobbi (n = 59) (from colonies maintained in Prague and analysed after storage in 70 % EtOH overnight [15]) and from 55 field-collected (Karpathos island, Greece, stored in 70 % EtOH for several weeks) Ph. neglectus (n = 44); Ph. similis (n = 8); Ph. alexandri (n = 1), Ph. galilaeus (n = 2) (total 367 specimens).
Genetic analyses
DNA was isolated from the remains of the abdomens with a kit (Qiamp DNA mini kit, Qiagen, Hildesheim, Germany) according to the manufacturer’s instruction and after mechanical homogenization as previously described [44]. Genetic characterisation by PCR/sequencing was mainly done at the mitochondrial cytochrome b gene (cyt b). The primers CB3_PDRmod (5’-CTC CYC ATA TYC AAC CWG AAT G-3’) and CB_R06mod (TAT CTA ATG KTT TCA AAA CAA TTG C-3’) were modified from described ones [45,46]. Species for which no corresponding cyt b sequence was available in GenBank were characterized at the mitochondrial cytochrome c oxidase subunit I gene (COI) using primers LCO1490/HCO2198 [47] or at the small subunit nuclear ribosomal RNA gene using forward primer F2 [48] and the new reverse primer R2_new (5’-GTC CTA TTC CAT TAT TCC ATG C-3’). Direct sequencing of the amplicons was performed by a private company (Synergene, Schlieren, Switzerland).
Results
Reference database
Biomarker mass patterns (‘superspectra’) were calculated for 20 sand fly species, by using 5 insects per species. Specimens from colonies (10 species) and insects collected in the field (10 species) were used (Table 1). Reference mass peaks were in the range of 4000 and, depending on the species, 9800 to 11400 Da. Identification of the field-collected species could be confirmed by PCR/sequencing with 1 specimen per species for 8 of these 10 species. The two remaining species were Ph. barguesae and Psathyromyia aragaoi. In the case of Ph. barguesae, the partial (around 570 bp) sequence of the COI gene obtained from the field-collected specimens best matched with the two GenBank sequences ascribed to this species (acc. nos. FJ348734-5), but differed by 7 %. Another 5 specimens morphologically attributed to this species were then genetically characterized, yielding identical sequences. No single sequence was available in GenBank for Ps. aragaoi, and partial cyt b and COI gene sequences have been deposited [GenBank: KP763471, GenBank: KP763472].
Superspectra were calculated for the species Ph. perniciosus and Ph. tobbi with 5 specimens each from either colonies or the field (Table 1), yielding identical masses.
Validation
The reference database was validated with 161 specimens from 19 species (Table 1). Eighty-four specimens were field-collected and stored in various media, 50 specimens were fresh from ongoing colonies of 10 species (that were also used to create the reference database), and 27 specimens were stored deep-frozen from earlier colonies. Altogether, 140 insects were correctly identified, including 77 specimens from colonies. Poor quality spectra (less than 30 data counts) were obtained with 20 field-collected specimens, of which 17 yielded no result upon automated identification with SuperSpectra™. The analyses of the other 3 of these 20 low data count specimens produced discrepant identifications (in 2 of the 4 technical replicates, no identification in the other two) as compared to morphological and genetic identification. Further, 2 insects probably were mislabelled as Ph. perniciosus, as both mass spectrometry and DNA sequencing identified them as Ph. ariasi, and specimens of this species had been obtained from the same source. Finally, one specimen yielded a novel spectrum but was identified by morphology as Ph. perfiliewi, which is included in the database, and as belonging to the Ph. perfiliewi complex by DNA analyses.
Thus, overall sensitivity of MALDI-TOF MS was 87 % (140/161); specificity (defined as 100 minus percentage of wrong identifications as compared to morphological identification, all specimens considered that yielded an MS identification) was 97 % (139/144) or 100 % (when consequently omitting low data count specimens and considering the probable mislabelling in 2 cases).
In addition to the specimens with discrepant identification, 22 arbitrarily chosen specimens were genetically analysed, confirming morphological and MALDI-based identification. The specimen with inconclusive morphological identification (Table 1) was among the specimens with low data count but turned out to belong to the Ph. perfiliewi complex based on DNA sequence analysis.
High quality spectra (i.e., equal to or more than 30 data counts) were obtained with all (n = 50) fresh insects from colonies, and with 55/59 insects from colonies or the field and stored deep-frozen (liquid nitrogen/-80 °C) for up to 25 years. In contrast, only 36/52 specimens stored in EtOH (70 or 95 %; room temperature or −20 °C) for only a few years could be identified (Table 1). Duration of storage impaired data counts in the high mass range as exemplified in Fig. 1.
Fig. 1
Matrix-assisted laser desorption/ionization time of flight (MALDI-TOF) mass spectra of Phlebotomus perniciosus. (a) Fresh specimen from colony. (b) Field specimen stored in 70 % EtOH, −20 °C for 3 years. (c) Field specimen stored in N2 then −80 °C since 1991. (d) Field specimen stored in N2 then −80 °C, since 1989. Note different scale of magnification (10 ×) for the higher mass range (10–20 kDa)
Different batches of sand fly specimens (colony, wild catches from different geographical origins and stored under different conditions and/or for different periods of time) were available for a few species. For example, a dendrogram of Ph. perniciosus groups is given in Fig. 2. The spectra from colony insects (originally from Spain) form a distinct cluster, whereas spectra of specimens from two geographical origins (Italy, Malta) and stored under comparable conditions do not. A single spectrum available from a more recently collected Ph. perniciosus from France, which was stored differently, is placed on a distinct branch, separated from both the colony- but also the other field-derived spectra.
Fig. 2
Dendrogram of matrix-assisted laser desorption/ionization time of flight (MALDI-TOF) mass spectra (paired-group dice algorithm) of Phlebotomus perniciosus specimens from different groups (colony, geographical origin of field specimens; for conditions and time of storage, see Table 1)
Analyses of mass lists obtained on a Bruker instrument with a reference database (SARAMIS™) and reference spectra acquired on a Shimadzu instrument
Raw data from a total of 312 specimens from 8 sand fly species from laboratory colonies were analysed, resulting in the correct identification of 297 individuals. No identification was obtained for 15 specimens, of which 10 had low data count spectra (less than 30). Five spectra with a sufficient number of data counts (30 or more) could not be identified. No misidentification occurred (overall sensitivity 95.2; sensitivity considering only high quality spectra 98.3 %; specificity 100 %). Thirty-six of the 55 field-collected specimens from 4 species were identified in concordance with the morphological identification. The single specimen of Ph. alexandri had a high quality spectrum (data count of 57), but yielded no identification as this species was not included in the database. Seventeen spectra contained insufficient data counts and were not identified. One specimen morphologically identified as Ph. galilaeus yielded a spectrum identified as Ph. perniciosus. Thus, diagnostic parameters with the field-collected specimens differed slightly from laboratory collections (sensitivity considering only high quality spectra 94.7 %; specificity 97.4 %).
Discussion
MALDI-TOF MS reference database and validation
A MALDI-TOF MS database was established with 20 phlebotomine species. In selecting our study species, we took into account i) their vectorial role - in order to include many species which are proven vectors of Leishmania spp., and ii) their taxonomic position - in order to compare closely related species and species belonging to different genera (Table 1). An evaluation of the database with 161 specimens revealed a robust sensitivity and a very high specificity of this approach. Twenty specimens were not (n = 17) or incorrectly (n = 3) identified due to low spectra quality (data count below 30). Thus, a threshold of 30 data counts, based on our experience with mass spectrometry analyses of Ceratopogonidae biting midges [26, 27], seems a useful criterion to exclude spectra from future analyses.
The major factor impairing mass spectrum quality seems to be the way the insects were stored rather than the duration of storage, though this aspect has not systematically been addressed in the present study. Thus, e.g. 22/23 specimens of Ph. perniciosus stored for 25 years in liquid nitrogen/-80 °C could be identified, but only 3/6 insects of the same species stored since 2011 in 70 % EtOH at −20 °C could be identified. This confirms earlier findings that freezing is superior to EtOH as a storage medium, with EtOH at a concentration of 70 % being more suitable than higher concentrations, as experimentally determined with sand flies stored up to 75 days [15]. Thus, this ‘storage constraint’ limits the value of mass spectrometry for the identification of insects, as ethanol is the widely preferred storage medium. However, a high reliability of mass spectrometry (98.9 % good quality spectra) was found with 1,200 field-collected Culicoides specimens stored in 70 % EtOH at 4 °C for one year [49]. Most other studies on mass spectrometry as a tool for the identification of arthropods relied on fresh colony-derived specimens. Successful identification by MALDI-TOF MS with field-collected specimens was reported with ticks (stored in liquid nitrogen, [25]), tsetse flies (using air-dried wings, [50]; and mosquitoes (analysis of legs, storage conditions not described, [31]).
As also shown in our study, storage reduces the higher weight masses (Fig. 1). Identification to species level is unaffected by this constraint as reference masses are in the lower mass range. Identification of specimens from different geographic origins (given they were properly stored) was equally reliable by using superspectra derived with either insects fresh from colonies or wild-catches from storage (Table 1). However, higher resolution (e.g., ‘fine typing’ with regard to geographical origin of specimens or lower taxonomic levels) might be critical as the topography of a dendrogram created in cluster analyses could reflect the storage conditions of the analysed specimens rather than phenotypic distinctness (see also Fig. 2). The identification of cryptic insect species (Anopheles spp.) and even the classification of specimens from different laboratory colonies were possible with a standardized approach (fresh specimens, same feed etc.) [28], but seem improbable with field-collected specimens. Thus, care should be taken not to over-interpret cluster analyses of mass spectra obtained from field-collected and stored specimens.
A novel spectrum was obtained for a specimen that morphologically was identified as a species (Ph. perfiliewi) that is included in the database. This species is known to exist as a complex of species [12] which might explain variability in mass spectra. All morphologically identified Ph. barguesae specimens had considerable genetic differences at the barcoding locus from corresponding GenBank entries. Genetic variability of this species, which is characterized by a unique morphology of the female spermathecae [51], has been observed among populations from different caves (Depaquit, unpublished). Further studies employing mass spectrometry to different populations of freshly collected specimens and the comparison with results of DNA-based molecular approaches might contribute to elucidate taxonomic relationships. This technique shall be especially considered when dealing with species complexes like Ph. perfiliewi or Ph. major which are incriminated in transmission of medically important Leishmania species and represent a taxonomic challenge.
Analyses of mass lists obtained on a Bruker instrument with a reference database (SARAMIS™) and reference spectra acquired on a Shimadzu instrument
Comparative studies have shown that the performance of the two systems (Shimadzu, Bruker) for the identification of microorganisms in clinical laboratories is comparable [52, 53]. Exchangeability of data obtained on the two different instruments, however, has to the best of our knowledge not been reported so far. Here, we show that fingerprints of phlebotomine sand flies obtained by automatic routine procedure on a Bruker instrument allow for reliable (high values of diagnostic parameters) determination of species by using the database and the software (SARAMIS™) established on a Shimadzu instrument. The sensitivity of this analysis was high despite slight differences in sample preparation [15] and mass ranges considered (Bruker: 2–25 kDa; Shimadzu: 3–20 kDa). Non-identifiable spectra mostly contained few data counts (n = 10) or low intensity peaks (n = 3), and these spectra could not be identified with the Bruker Biotyper software either. Two spectra of good quality did not have sufficient matches for automated identification with superspectra, though their identification (Ph. argentipes, Ph. perniciosus) was possible with manual full comparison.
Conclusions
The power of mass spectrometric identification of organisms depends on the quality of the available database (i.e., reference quality, taxonomic coverage) and its accessibility. The first aspect requires the participation of expert taxonomists, particularly when dealing with closely related species, and experienced users of mass spectrometers who keep a high quality standard for generating the spectra. It further advocates for a centralized, comprehensive database, rather than scattered in-house ones. Accessibility (i.e., the analysis of specimens by third parties) might be an issue at scientific institutions where capacity for analysis, availability and willingness of an operator could be limiting factors. Therefore, a centralized database and analyses at a private company, which provides a customer-oriented service, is a valuable alternative for greater sustainability. As shown in the present work, spectra obtained with different instruments can be analysed using such a centralized database, and this should be possible in the near future via an online platform in a cost-efficient manner.
Declarations
Acknowledgments
We thank Jeannine Hauri for excellent technical support, and greatly acknowledge the Swiss Food Safety and Veterinary Office as sponsor of the Swiss National Centre for Vector Entomology. We also thank Bernard Pesson and Mohammad Akhoundi for providing us many specimens. The work of AM, VD, HT, CK and FS was done under the frame of EurNegVec COST Action TD1303. The work of VD, PH, PV and KH was supported by the Czech Science Foundation (project GACR 15-04329S). The work of PH was also supported by the Institutional Research Project of the Institute of Microbiology (RVO61388971). The work of ALB, JP and DS has been supported by the EDENext project (reference nr. EDENext329). We are also grateful to the PhDB group of Montpellier for the field collection.
Authors’ Affiliations
(1)
Swiss National Centre for Vector Entomology, Institute of Parasitology, University of Zürich
(2)
Université de Reims Champagne-Ardenne, ANSES, EA4688 - USC “transmission vectorielle et épidémiosurveillance de maladies parasitaires (VECPAR)”
(3)
Department of Parasitology, Faculty of Sciences, Charles University in Prague
(4)
MIVEGEC, UMR CNRS-IRD-Université de Montpellier Centre IRD
(5)
Laboratory of Molecular Structure Characterization, Institute of Microbiology, The Czech Academy of Sciences
(6)
Instituto de Microbiología, Universidad San Francisco de Quito
(7)
Mabritec SA, Lörracherstrasse 50
(8)
Avia-GIS, Risschotlei 33
(9)
Current address: NSF Center for Integrated Pest Management
References
Schaffner F, Kaufmann C, Hegglin D, Mathis A. The invasive mosquito Aedes japonicus in central Europe. Med Vet Entomol. 2009;23:448–51.View ArticlePubMedGoogle Scholar
Medlock JM, Hansford KM, Schaffner F, Versteirt V, Hendrickx G, Zeller H, et al. A review of the invasive mosquitoes in Europe: ecology, public health risks, and control options. Vector Borne Zoonotic Dis. 2012;12:435–47.View ArticlePubMed CentralPubMedGoogle Scholar
Schaffner F, Mathis A. Dengue and dengue vectors in the WHO European region: past, present, and scenarios for the future. Lancet Infect Dis. 2014;14:1271–80.View ArticlePubMedGoogle Scholar
Jaenson TGT, Jaenson DGE, Eisen L, Petersson E, Lindgren E. Changes in the geographical distribution and abundance of the tick Ixodes ricinus during the past 30 years in Sweden. Parasit Vectors. 2012;5:8.View ArticlePubMed CentralPubMedGoogle Scholar
Dergousoff SJ, Galloway TD, Lindsay LR, Curry PS, Chilton NB. Range expansion of Dermacentor variabilis and Dermacentor andersoni (Acari: Ixodidae) near their northern distributional limits. J Med Entomol. 2013;50:510–20.View ArticlePubMedGoogle Scholar
Nolan DV, Dallas JF, Piertney SB, Mordue Luntz AJ. Incursion and range expansion in the bluetongue vector Culicoides imicola in the Mediterranean basin: a phylogeographic analysis. Med Vet Entomol. 2008;22:340–51.View ArticlePubMedGoogle Scholar
Maroli M, Feliciangeli MD, Bichaud L, Charrel RN, Gradoni L. Phlebotomine sandflies and the spreading of leishmaniases and other diseases of public health concern. Med Vet Entomol. 2013;27:123–47.View ArticlePubMedGoogle Scholar
Poeppl W, Obwaller AG, Weiler M, Burgmann H, Mooseder G, Lorentz S, et al. Emergence of sandflies (Phlebotominae) in Austria, a Central European country. Parasitol Res. 2013;112(12):4231–7.View ArticlePubMed CentralPubMedGoogle Scholar
Medlock JM, Hansford KM, van Bortel W, Zeller H, Alten B. A summary of the evidence for the change in European distribution of phlebotomine sand flies (Diptera: Psychodidae) of public health importance. J Vector Ecol. 2014;39:72–7.View ArticlePubMedGoogle Scholar
Schaffner F, Bellini R, Petrić D, Scholte E-J, Zeller H, Marrama Rakotoarivony L. Development of guidelines for the surveillance of invasive mosquitoes in Europe. Parasit Vectors. 2013;6:209.View ArticlePubMed CentralPubMedGoogle Scholar
European Centre for Disease Prevention and Control: Guidelines for the surveillance of native mosquitoes in Europe. Stockholm: ECDC Technical Report; 2014. doi:https://doi.org/10.2900/37227
Depaquit J, Bounamous A, Akhoundi M, Augot D, Sauvage F, Dvorak V, et al. A taxonomic study of Phlebotomus (Larroussius) perfiliewi s. l. Infect Genet Evol. 2013;20:500–8.View ArticlePubMedGoogle Scholar
Prudhomme J, Gunay F, Rahola N, Ouanaimi F, Guernaoui S, Boumezzough A, et al. Wing size and shape variation of Phlebotomus papatasi (Diptera: Psychodidae) populations from the south and north slopes of the Atlas Mountains in Morocco. J Vector Ecol. 2012;37:137–47.View ArticlePubMedGoogle Scholar
Ready PD. Biology of phlebotomine sand flies as vectors of disease agents. Ann Rev Entomol. 2013;58:227–50.View ArticleGoogle Scholar
Dvorak V, Halada P, Hlavackova K, Dokianakis E, Antoniou M, Volf P. Identification of phlebotomine sand flies (Diptera: Psychodidae) by matrix-assisted laser desorption/ionization time of flight mass spectrometry. Parasit Vectors. 2014;7:21.View ArticlePubMed CentralPubMedGoogle Scholar
Depaquit J. Molecular systematics applied to Phlebotomine sandflies: Review and perspectives. Infect Genet Evol. 2014;28:744–56.View ArticlePubMedGoogle Scholar
Depaquit J, Ferte H, Leger N, Lefranc F, Alves-Pires C, Hanafi H, et al. ITS 2 sequences heterogeneity in Phlebotomus sergenti and Phlebotomus similis (Diptera, Psychodidae): possible consequences in their ability to transmit Leishmania tropica. Int J Parasitol. 2002;32:1123–31.View ArticlePubMedGoogle Scholar
Dvorak V, Votypka J, Aytekin A, Alten B, Volf P. Intraspecific variability of natural populations of Phlebotomus sergenti, the main vector of Leishmania tropica. J Vector Ecol. 2011;36:S49–57.View ArticlePubMedGoogle Scholar
Croxatto A, Prod'hom G, Greub G. Applications of MALDI-TOF mass spectrometry in clinical diagnostic microbiology. FEMS Microbiol Rev. 2012;36:380–407.View ArticlePubMedGoogle Scholar
Posteraro B, De Carolis E, Vella A, Sanguinetti M. MALDI-TOF mass spectrometry in the clinical mycology laboratory: identification of fungi and beyond. Expert Rev Proteomic. 2013;10:151–64.View ArticleGoogle Scholar
Mellmann A, Bimet F, Bizet C, Borovskaya AD, Drake RR, Eigner U, et al. High interlaboratory reproducibility of matrix-assisted laser desorption ionization-time of flight mass spectrometry-based species identification of nonfermenting bacteria. J Clin Microbiol. 2009;47:3732–4.View ArticlePubMed CentralPubMedGoogle Scholar
Campbell PM. Species differentiation of insects and other multicellular organisms using matrix-assisted laser desorption/ionization time of flight mass spectrometry protein profiling. Syst Entomol. 2005;30:186–90.View ArticleGoogle Scholar
Feltens R, Gorner R, Kalkhof S, Groger-Arndt H, von Bergen M. Discrimination of different species from the genus Drosophila by intact protein profiling using matrix-assisted laser desorption ionization mass spectrometry. BMC Evol Biol. 2010;10:95.View ArticlePubMed CentralPubMedGoogle Scholar
Hoppenheit A, Murugaiyan J, Bauer B, Steuber S, Clausen PH, Roesler U. Identification of Tsetse (Glossina spp.) using matrix-assisted laser desorption/ionisation time of flight mass spectrometry. PLoS Negl Trop Dis. 2013;7, e2305.View ArticlePubMed CentralPubMedGoogle Scholar
Karger A, Kampen H, Bettin B, Dautel H, Ziller M, Hoffmann B, et al. Species determination and characterization of developmental stages of ticks by whole-animal matrix-assisted laser desorption/ionization mass spectrometry. Ticks Tick Borne Dis. 2012;3:78–89.View ArticlePubMedGoogle Scholar
Kaufmann C, Schaffner F, Ziegler D, Pfluger V, Mathis A. Identification of field-caught Culicoides biting midges using matrix-assisted laser desorption/ionization time of flight mass spectrometry. Parasitology. 2012;139:248–58.View ArticlePubMedGoogle Scholar
Kaufmann C, Ziegler D, Schaffner F, Carpenter S, Pfluger V, Mathis A. Evaluation of matrix-assisted laser desorption/ionization time of flight mass spectrometry for characterization of Culicoides nubeculosus biting midges. Med Vet Entomol. 2011;25:32–8.View ArticlePubMedGoogle Scholar
Muller P, Pfluger V, Wittwer M, Ziegler D, Chandre F, Simard F, et al. Identification of cryptic Anopheles mosquito species by molecular protein profiling. PLoS One. 2013;8, e57486.View ArticlePubMed CentralPubMedGoogle Scholar
Perera MR, Vargas RDF, Jones MGK. Identification of aphid species using protein profiling and matrix-assisted laser desorption/ionization time-of-flight mass spectrometry. Entomol Exp Appl. 2005;117:243–7.View ArticleGoogle Scholar
Yssouf A, Flaudrops C, Drali R, Kernif T, Socolovschi C, Berenger JM, et al. Matrix-assisted laser desorption ionization-time of flight mass spectrometry for rapid identification of tick vectors. J Clin Microbiol. 2013;51:522–8.View ArticlePubMed CentralPubMedGoogle Scholar
Yssouf A, Socolovschi C, Flaudrops C, Ndiath MO, Sougoufara S, Dehecq JS, et al. Matrix-assisted laser desorption ionization–time of flight mass spectrometry: an emerging tool for the rapid identification of mosquito vectors. PLoS One. 2013;8:e72380.View ArticlePubMed CentralPubMedGoogle Scholar
Yssouf A, Socolovschi C, Leulmi H, Kernif T, Bitam I, Audoly G, et al. Identification of flea species using MALDI-TOF/MS. Comp Immunol Microbiol Infect Dis. 2014;37:153–7.View ArticlePubMedGoogle Scholar
Yssouf A, Parola P, Lindstrom A, Lilja T, LAmbert G, Bondesson U, et al. Identification of European mosquito species by MALDI-TOF MS. Parasitol Res. 2014;113:2375–8.View ArticlePubMedGoogle Scholar
Steinmann IC, Pfluger V, Schaffner F, Mathis A, Kaufmann C. Evaluation of matrix-assisted laser desorption/ionization time of flight mass spectrometry for the identification of ceratopogonid and culicid larvae. Parasitology. 2013;140:318–27.View ArticlePubMedGoogle Scholar
Dieme C, Yssouf A, Vega-Rúa A, Berenger J-M, Failloux A-B, Raoult D, et al. Accurate identification of Culicidae at aquatic developmental stages by MALDI–TOF MS profiling. Parasit Vectors. 2014;7:544.View ArticlePubMed CentralPubMedGoogle Scholar
Schaffner F, Kaufmann C, Pfluger V, Mathis A. Rapid protein profiling facilitates surveillance of invasive mosquito species. Parasit Vectors. 2014;7:142.View ArticlePubMed CentralPubMedGoogle Scholar
Alkan C, Bichaud L, de Lamballerie X, Alten B, Gould EA, Charrel RN. Sandfly-borne phleboviruses of Eurasia and Africa: epidemiology, genetic diversity, geographic range, control measures. Antiviral Res. 2013;100:54–74.View ArticlePubMedGoogle Scholar
Alvar J, Velez ID, Bern C, Herrero M, Desjeux P, Cano J, et al. WHO Leishmaniasis Control Team: Leishmaniasis worldwide and global estimates of its incidence. PLoS One. 2012;7, e35671.View ArticlePubMed CentralPubMedGoogle Scholar
Zapata S, Mejia L, Le Pont F, Leon R, Pesson B, Ravel C, et al. A study of a population of Nyssomyia trapidoi (Diptera: Psychodidae) caught on the Pacific coast of Ecuador. Parasit Vectors. 2012;5:144.View ArticlePubMedGoogle Scholar
Dedet JP, Addadi K, Belazzoug S. Les phlébotomes (Diptera, Psychodidae) d'Algérie. Cah ORSTOM, Sér Ent Méd Parasitol. 1984;22:99–127.Google Scholar
Lewis D. A taxonomic review of the genus Phlebotomus. Bull Brit Mus Nat Hist (Entomol). 1982;45:121–209.Google Scholar
Young DG, Duncan MA: Guide to the identification and geographic distribution of Lutzomyia sand flies in Mexico, the West Indies, Central and South America (Diptera: Psychodidae). Memoirs of the American Entomological Institute, vol. 54. Associated Publishers, Gainesville, Florida, USA; 1994, 881 pp. www.dtic.mil/dtic/tr/fulltext/u2/a285737.pdf
Marcondes CB. A proposal of generic and subgeneric abbreviations for Phlebotomine sandflies (Diptera: Psychodidae: Phlebotominae) of the World. Entomol News. 2007;118:351–6.View ArticleGoogle Scholar
Wenk C, Kaufmann C, Schaffner F, Mathis A. Molecular characterisation of Swiss Ceratopogonidae (Diptera) and evaluation of real-time PCR assays for the identification of Culicoides biting midges. Vet Parasitol. 2012;184:258–66.View ArticlePubMedGoogle Scholar
Esseghir S, Ready PD, Killick-Kendrick R, Ben-Ismail R. Mitochondrial haplotypes and phylogeography of Phlebotomus vectors of Leishmania major. Insect Mol Biol. 1997;6:211–25.View ArticlePubMedGoogle Scholar
Parvizi P, Ready PD. Molecular investigation of the population differentiation of Phlebotomus papatasi, important vector of Leishmania major, in different habitats and regions of Iran. Iranian Biomed J. 2006;10:69–77.Google Scholar
Folmer O, Black M, Hoeh W, Lutz R, Vrijenhoek R. DNA primers for amplification of mitochondrial cytochrome c oxidase subunit I from diverse metazoan invertebrates. Mol Mar Biol Biotech. 1994;3:294–9.Google Scholar
Aransay AM, Scoulica E, Tselentis Y, Ready PD. Phylogenetic relationships of phlebotomine sandflies inferred from small subunit nuclear ribosomal DNA. Insect Mol Biol. 2000;9:157–68.View ArticlePubMedGoogle Scholar
Kaufmann C, Steinmann IC, Hegglin D, Schaffner F, Mathis A. Spatio-temporal occurrence of Culicoides biting midges in the climatic regions of Switzerland, along with large scale species identification by MALDI-TOF mass spectrometry. Parasit Vectors. 2012;5:246.View ArticlePubMed CentralPubMedGoogle Scholar
Hoppenheit A, Murugaiyan J, Bauer B, Clausen P-H, Roesler U. Analysis of Glossina palpalis gambiensis and Glossina tachinoides from two distant locations in Burkina Faso using MALDI TOF MS. Parasitol Res. 2014;113:723–6.View ArticlePubMedGoogle Scholar
Depaquit J, Muller F, Léger N. Phlebotomus (Euphlebotomus) barguesae n. sp. from Thailand (Diptera-Psychodidae). Parasit Vectors. 2009;2:5.View ArticlePubMed CentralPubMedGoogle Scholar
Alby K, Gilligan PH, Miller MB. Comparison of matrix-assisted laser desorption ionization-time of flight (maldi-tof) mass spectrometry platforms for the identification of gram-negative rods from patients with cystic fibrosis. J Clin Microbiol. 2013;51:3852–4.View ArticlePubMed CentralPubMedGoogle Scholar
Lohmann C, Sabou M, Moussaoui W, Prevost G, Delarbre J-M, Candolfi E, et al. Comparison between the Biflex III-Biotyper and the Axima-SARAMIS systems for yeast identification by matrix-assisted laser desorption ionization-time of flight mass spectrometry. J Clin Microbiol. 2013;51:1231–6.View ArticlePubMed CentralPubMedGoogle Scholar
This is an Open Access article distributed under the terms of the Creative Commons Attribution License (http://creativecommons.org/licenses/by/4.0) which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly credited. The Creative Commons Public Domain Dedication waiver (http://creativecommons.org/publicdomain/zero/1.0/) applies to the data made available in this article, unless otherwise stated.
Comments
By submitting a comment you agree to abide by our Terms and Community Guidelines. If you find something abusive or that does not comply with our terms or guidelines please flag it as inappropriate.
Comments
By submitting a comment you agree to abide by our Terms and Community Guidelines. If you find something abusive or that does not comply with our terms or guidelines please flag it as inappropriate.