Literature DB >> 25062012

Molecular and morphological identification of mealybug species (Hemiptera: Pseudococcidae) in Brazilian vineyards.

Vitor C Pacheco da Silva1, Aline Bertin2, Aurélie Blin3, Jean-François Germain4, Daniel Bernardi2, Guylène Rignol3, Marcos Botton1, Thibaut Malausa3.   

Abstract

Mealybugs (Hemiptera: Pseudococcidae) are pests constraining the international trade of Brazilian table grapes. They damage grapes by transmitting viruses and toxins, causing defoliation, chlorosis, and vigor losses and favoring the development of sooty mold. Difficulties in mealybug identification remain an obstacle to the adequate management of these pests. In this study, our primary aim was to identify the principal mealybug species infesting the major table grape-producing regions in Brazil, by morphological and molecular characterization. Our secondary aim was to develop a rapid identification kit based on species-specific Polymerase Chain Reactions, to facilitate the routine identification of the most common pest species. We surveyed 40 sites infested with mealybugs and identified 17 species: Dysmicoccus brevipes (Cockerell), Dysmicoccus sylvarum Williams and Granara de Willink, Dysmicoccus texensis (Tinsley), Ferrisia cristinae Kaydan and Gullan, Ferrisia meridionalis Williams, Ferrisia terani Williams and Granara de Willink, Phenacoccus baccharidis Williams, Phenacoccus parvus Morrison, Phenacoccus solenopsis Tinsley, Planococcus citri (Risso), Pseudococcus viburni (Signoret), Pseudococcus cryptus Hempel, four taxa closely related each of to Pseudococcus viburni, Pseudococcus sociabilis Hambleton, Pseudococcus maritimus (Ehrhorn) and Pseudococcus meridionalis Prado, and one specimen from the genus Pseudococcus Westwood. The PCR method developed effectively identified five mealybug species of economic interest on grape in Brazil: D. brevipes, Pl. citri, Ps. viburni, Ph. solenopsis and Planococcus ficus (Signoret). Nevertheless, it is not possible to assure that this procedure is reliable for taxa that have not been sampled already and might be very closely related to the target species.

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Year:  2014        PMID: 25062012      PMCID: PMC4111580          DOI: 10.1371/journal.pone.0103267

Source DB:  PubMed          Journal:  PLoS One        ISSN: 1932-6203            Impact factor:   3.240


Introduction

Grapevines cover an area of approximately 82,000 hectares in Brazil, with an annual yield ranging from 1,300,000 to 1,450,000 t [1]. The cultivation of this crop has expanded throughout Brazil, with Rio Grande do Sul state producing the largest amounts, followed by Pernambuco, São Paulo and Paraná. Nationally, 57% of grape production is destined for consumption as table grapes and 43% is used for juice and wine production [1], [2]. Brazilian production levels increased in recent decades, largely due to expansion of the export of table grapes, mostly produced in the northern regions of Brazil, especially the São Francisco Valley, which is responsible for producing 90% of the grapes exported from Brazil [2], [4]. The cities of Petrolina (in Pernambuco) and Juazeiro (in Bahia) are the main grape exporters, and the industry is of utmost importance for the socioeconomic growth of the region [3], [4]. One of the key factors limiting the export of Brazilian grapes is the presence of mealybugs Hemiptera: Pseudococcidae). Mealybugs are small phloem-sucking insects, the nymphs and adult females of which feed by sucking sap from the trunk, roots, leaves, rachis and fruits of grapevines, causing direct and indirect damage, depending on the species and the site used for feeding [5]–[9]. The mere presence of these pests in the harvested and shipped fruits is a major cause of quarantine rejections [8], [10]. Moreover, dense populations of mealybugs may decrease plant vigor, cause defoliation and introduce toxic substances into the leaves, triggering chlorosis. Furthermore, the chief damage inflicted by these pests results from their transmission of viruses affecting final product quality and vineyard longevity [11]–[15]. In addition to all these other types of damage, mealybugs reduce the marketability of table grapes by excreting honeydew, which promotes the development of sooty mold on fruits. Daane et al. [9] reviewed the complex of vineyard mealybugs worldwide, five species of which are important in Brazil: the citrus mealybug Planococcus citri (Risso), the pineapple mealybug Dysmicoccus brevipes (Cockerell), the vine mealybug Pseudococcus viburni (Signoret), the grape mealybug Pseudococcus maritimus (Ehrhorn) and the passionvine mealybug Planococcus minor Maskell. These mealybugs are morphologically very similar and are therefore difficult to tell apart, particularly for non specialists. Current methods for distinguishing between mealybug species are based on observations of the morphological characteristics of adult female specimens under the microscope. This method is particularly time-consuming, impracticable for males and nymphs, and may be inconclusive, particularly for very closely related species [15]–[17]. This is particularly problematic because difficulties in identification may jeopardize the use of control and management methods specific to certain target species, which are currently favored over the use of broad-spectrum pesticides. For example, biological control methods based on the release of natural enemies (e.g. hymenopteran parasitoids) or pheromone trapping systems are mostly species-specific and require correct pest identification [18]. Moreover, different mealybug species cause greatly different degrees of damage and not all species are considered to be quarantine species, depending on the market to which fruits are exported. Given the difficulties involved in identifying mealybugs morphologically and the importance of correct identification, the association of DNA sequencing with morphological identification is particularly useful, making identification quicker, cheaper and more reliable. Several genomic regions have successfully been used for the identification of mealybugs and other scale insects. These regions include 28S-D2 and internal transcribed spacer 2 (ITS2) in the nuclear DNA, the mitochondrial cytochrome oxidase subunit I (COI) gene, and the leuA-16S region located in the DNA of the primary endosymbionts of most Pseudococcidae, Tremblaya princeps [17]–[26]. Furthermore, the DNA sequencing data obtained can be used to develop species-specific Polymerase Chain Reactions (PCR), making it possible to identify species molecularly, on the basis of the size of the sequence amplified [18], [27]–[29]. We used a combination of DNA sequencing at five loci and morphological characterization to survey the mealybug species infesting 40 Brazilian vineyards located in three major grape-producing regions, based on the methods described by Malausa et al. [24] and Abd-Rabou et al. [18]. We then designed a multiplex PCR method for rapid identification of the five mealybug species most commonly found or considered to be a major threat to Brazilian vineyards.

Materials and Methods

Sample collections

Forty-eight samples, each containing one to 20 mealybug individuals, were collected from Brazilian table grapes vineyards (from vines or other plants in the immediate vicinity of vines within the vineyards) during 2008 and 2009. Mealybugs were collected from the aerial parts of the plants or from the roots. Samples were collected from 40 sites in the states of Rio Grande do Sul, Pernambuco and Paraná, in order to carry out collections in major grape-producing regions of Brazil. The number of sites is smaller than the number of samples, because mealybugs collected from different plants within the same vineyard were considered to constitute different samples. Specimens were stored in ethanol (95%) at −20°C for identification and molecular analyses. GPS coordinates, host plants and the mealybug identifications are present in Table 1.
Table 1

List of populations sampled: Population code, geographic origin and host origin of the samples.

Population codeCityGPS coordinatesHost plantCollection dateIdentification
1Caxias do Sul29°09.964' S, 51°06.596′ W Vitis vinifera 29/04/2009 Pseudococcus viburni
2Caxias do Sul29°08.023′ S, 51°06.140′ W Vitis vinifera 06/05/2009 Pseudococcus viburni
3Caxias do Sul29°16.093′ S, 51°01.906′ W Vitis vinifera 29/04/2009 Pseudococcus nr. maritimus
4Caxias do Sul29°15.567′ S, 51°09.980′ W Vitis vinifera 07/05/2009 Dysmicoccus texensis
5Caxias do Sul29°15.376′ S, 51°10.684′ W Vitis vinifera 07/05/2009 Pseudococcus viburni
6Caxias do Sul29°09.964′ S, 51°06.596′ W Rumex sp.29/04/2009 Pseudococcus viburni, Pseudococcus nr. viburni, Dysmicoccus brevipes
7Caxias do Sul29°13.135′ S, 51°14.832′ W Rumex sp.21/05/2009 Dysmicoccus brevipes
8Caxias do Sul29°13.459′ S, 51°08.461′ W Rumex sp.06/05/2009 Dysmicoccus brevipes
9Caxias do Sul29°14.787′ S, 51°16.474′ W Rumex sp.21/05/2009 Dysmicoccus brevipes
10Caxias do Sul29°13.826′ S, 51°01.012′ W Rumex sp.29/04/2009 Dysmicoccus sylvarum
11Caxias do Sul29°16.093′ S, 51°01.906′ W Rumex sp.29/04/2009 Dysmicoccus sylvarum
12Caxias do Sul29°13.288′ S, 51°01.249′ W Vitis vinifera 29/04/2009 Pseudococcus viburni
13Caxias do Sul29°15.818′ S, 51°11.224′ W Vitis vinifera 05/06/2009 Pseudococcus viburni
14Bento Gonçalves29°09.853′ S, 51°31.777′ W Vitis vinifera 19/02/2009 Dysmicoccus brevipes
15Bento Gonçalves29°09.853′ S, 51°31.777′ W Sonchus oleraceus 07/01/2009 Pseudococcus viburni
16Caxias do Sul29°15.871′ S, 51°11.074′ W Vitis vinifera 09/10/2008 Pseudococcus sp.
17Caxias do Sul29°10.375′ S, 51°05.511′ W Vitis vinifera 29/04/2009 Pseudococcus viburni
18Caxias do Sul29°13.955′ S, 51°16.914′ W Vitis vinifera 21/05/2009 Pseudococcus viburni
19Marialva23°30.015' S, 51°49.628' W Vitis vinifera 22/07/2009 Planococcus citri
20Marialva23°30.856' S, 51°47.535' W Vitis vinifera 21/07/2009 Pseudococcus nr. sociabilis, Planococcus citri
21Sarandi23°21.520′ S, 51°48.561' W Bidens pilosa 22/07/2009 Planococcus citri
22Mandaguari23°31.784' S, 51°41.638' W Vitis vinifera 22/07/2009 Planococcus citri, Phenacoccus parvus
23Pinto Bandeira29°06.358′ S, 51°28.987′ W Vitis vinifera 28/04/2009 Dysmicoccus brevipes
24Sarandi23°26.775' S, 51°48.293' W Bidens pilosa 22/07/2009 Phenacoccus parvus
25Petrolina09°14.313' S, 40°27.475 W Vitis vinifera 10/04/2008 Planococcus citri, Phenacoccus solenopsis, Ferrisia meridionalis, Dysmicoccus brevipes
26Marialva23°30.149' S, 51°44.847' W Vitis vinifera 22/07/2009 Planococcus citri
27Marialva23°27.817' S, 51°47.297' W Vitis vinifera 22/07/2009 Planococcus citri
28Jandaia do Sul23°38.919' S, 51°37.881' W Vitis vinifera 21/07/2009 Planococcus citri
29Sarandi23°21.401' S, 51°48.476' W Vitis vinifera 22/07/2009 Planococcus citri, Pseudococcus nr. sociabilis, Ferrisia cristinae
30Caxias do Sul29°07.100′ S, 51°12.513′ W Vitis vinifera 28/05/2009 Ferrisia terani
31Caxias do Sul29°05.473′ S, 51°13.007′ W Vitis vinifera 28/05/2009 Pseudococcus viburni
32Marialva23°30.558' S, 51°48.963' W Vitis vinifera 22/07/2009 Planococcus citri, Pseudococcus cryptus
33Caxias do Sul29°07.562′ S, 51°13.695′ W Vitis vinifera 20/05/2009 Ferrisia meridionalis, Ferrisia terani, Phenacoccus baccharidis
34Marialva23°31.164' S, 51°49.372' W Vitis vinifera 22/07/2009 Planococcus citri, Ferrisia cristinae
35Petrolina09°15.793' S, 40°36.648' W Vitis vinifera 07/10/2009 Planococcus citri
36Sarandi23°21.520′ S, 51°48.561' W Vitis vinifera 22/07/2009 Planococcus citri
37Caxias do Sul29°14.787′ S, 51°16.474′ W Vitis vinifera 21/05/2009 Phenacoccus baccharidis
38Pinto Bandeira29°07.236' S, 51°27.002' W Rumex sp.23/04/2009 Dysmicoccus brevipes
39Caxias do Sul29°08.014′ S, 51°13.969′ W Vitis vinifera 20/05/2009 Pseudococcus viburni
40Petrolina09°14.404' S, 40°27.881' W Vitis vinifera 08/10/2009 Planococcus citri
41Marialva23°30.246' S, 51°49.323' W Vitis vinifera 22/07/2009 Planococcus citri
42Petrolina09°20.733' S, 40°36.767' W Malva sp.07/10/2009 Phenacoccus solenopsis
43Sarandi23°21.401' S, 51°48.476' W Sonchus oleraceus 22/07/2009 Pseudococcus nr. meridionalis
44Petrolina09°14.313' S, 40°27.475' W Vitis vinifera 04/06/2008 Dysmicoccus brevipes
45Petrolina09°23.136' S, 40°38.130' WSpecies not identified21/01/2009 Phenacoccus solenopsis
46Marialva23°30.015' S, 51°49.628' WSpecies not identified22/07/2009 Phenacoccus parvus
47Caxias do Sul29°16.045′ S, 51°02.166′ W Vitis vinifera 29/04/2009 Pseudococcus viburni
48Marialva23°30.496' S, 51°49.048' W Vitis vinifera 22/07/2009 Planococcus citri
All samplings were conducted in private areas, except the sampling done in the Bento Gonçalves city (Table 1, population codes 14 and 15) which were carried out at the research center of Embrapa Grape and Wine (Brazilian Agricultural Research Corporation; responsible person for the permit: Dr. Marcos Botton, marcos.botton@embrapa.br). No specific permission was required for the sampling in other areas. Most collected species are well-known agricultural pests that cause damage to crops and are widely distributed. None of them is an endangered species.

DNA extraction, amplification and sequencing

When possible, we analyzed five mealybug individuals from each of the samples collected. In total, we extracted DNA from 215 mealybugs, with the DNeasy Blood and Tissue Kit (QIAGEN, Valencia, CA). We ensured that voucher specimens were available for morphological identification, by not crushing the specimens before extraction. Instead, we used the non-destructive method described by Malausa et al. [23]. We aimed to amplify and sequence five DNA loci known to be informative for species identification and providing sufficient data for the subsequent design of species-specific PCR primers for the identification kit (see next section): two slightly overlapping parts of the cytochrome oxidase subunit I (COI) gene, 28S-D2, internal transcribed spacer 2 (ITS2), and the leuA-16S region of the DNA of the symbiont Tremblaya princeps. Except for the first region of the COI gene (the LCO-HCO region used in most international DNA barcoding projects), for which we used an updated version of the primers [17], we followed the protocol described by Malausa et al. [23]. The primers used (Forward, Reverse) were 5′AGAGAGAGTTCAAGAGTACGTG3′ and 5′TTGGTCCGTGTTTCAAGACGGG3′ for 28S-D2, 5′CTCGTGACCAAAGAGTCCTG3′ and 5′TGCTTAAGTTCAGCGGGTAG3′ for ITS2; 5′YAATATAATRATTACWWTWCATGC3′ and 5′TTTWCCATTTAAWGTTATTATTC3′ for the first region of COI hereafter referred to as “LCO”; 5′CAACATTTATTTTGATTTTTTGG3′ and 5′GCWACWACRTAATAKGTATCATG3′ for the second region of COI hereafter referred to as “C1”; and 5′GTATCTAGAGGNATHCAYCARGAYGGNG3′ and 5′GCCGTMCGACTWGCATGTG3′ for leuA-16S. The annealing temperature for these primer pairs was 58°C for 28S-D2 and ITS2, 48°C for LCO, 56°C for C1 and leuA-16S. The PCR conditions were provided in a previous study [23], and are kept updated at http://bpi.sophia.inra.fr/dnabarcoding/. PCR was performed with a 23 µl reaction mixture and 2 µl of diluted DNA (1–20 ng of DNA matrix). The reagent concentrations were 1×Phusion HF buffer (Phusion High-Fidelity DNA polymerase 530 [Thermo Fisher Scientific, Vantaa, Finland]), 0.01 U/µl Phusion enzyme, 200 µM dNTPs and 0.5 µM of each primer. For bidirectional sequencing, all PCR products were sent to Genoscreen (Lille, France) or to the French National Genoscope (Paris, France) for capillary electrophoresis on ABI automatic sequencers (Applied Biosystems, Foster City, CA, USA). Consensus sequences were generated and checked with Seqscape v2.7 (ABI). Alignments were edited manually with Bioedit version 7.01 [30]. Sequences were compared by direct alignment, and any specimen sequence with a different nucleotide present at one or more positions was considered to constitute a different haplotype. We also used Haplotype Detector software (http://www2.sophia.inra.fr/urih/sophia_mart_fr/genotyping_tools.php) to distinguish between and sort the various haplotypes automatically. The sequences analyzed were deposited in GenBank for future access and use (Table 2).
Table 2

GenBank accession number, Blast Hits, corresponding taxon, % similarity and coverage between the Brazilian mealybug sequences and sequences from the NCBI GenBank database.

Haplotype (GenBank accession #)Identification (DNA + morphology)Best GenBank BLAST hitCorresponding taxon% similarityCoverage (bp)
28S-01 (KJ530578) Dysmicoccus brevipes GU134658.1 Dysmicoccus brevipes 100%321
28S-02 (KJ530579) Planococcus citri JF714181.1 Planococcus citri 100%310
28S-03 (KJ530580) Ferrisia meridionalis AY179461.1 Ferrisia gilli 99%314
28S-04 (KJ530581) Ferrisia terani AY179469.1 Ferrisia terani 99%309
28S-05 (KJ530582) Ferrisia cristinae AY179464.1 Ferrisia cristinae 100%308
28S-06 (KJ530583) Pseudococcus viburni GU134653.1 Pseudococcus viburni 100%319
28S-07 (KJ530584) Pseudococcus nr. viburni GU134653.1 Pseudococcus viburni 99%319
28S-08 (KJ530585) Pseudococcus viburni GU134652.1 Pseudococcus viburni 100%319
28S-09 (KJ530586) Pseudococcus cryptus GU134654.1 Pseudococcus comstocki 96%321
28S-10 (KJ530587) Pseudococcus nr. sociabilis AY427312.1 Pseudococcus maritimus 98%315
28S-11 (KJ530588) Pseudococcus nr. sociabilis GU134653.1 Pseudococcus viburni 94%323
28S-12 (KJ530589) Phenacoccus solenopsis JQ085532.1 Phenacoccus solenopsis 100%317
28S-13 (KJ530590) Phenacoccus parvus GU134663.1 Phenacoccus parvus 100%317
28S-14 (KJ530591) Phenacoccus baccharidis AY427337.1 Phenacoccus madeirensis 89%321
28S-15 (KJ530592) Dysmicoccus texensis AY427323.1 Dysmicoccus neobrevipes 99%318
28S-16 (KF804137) Pseudococcus nr. maritimus GU134653.1 Pseudococcus viburni 96%320
28S-17 (KJ530593) Dysmicoccus sylvarum AY427359 1 Dysmicoccus sp.94%323
28S-18 (KJ530594) Pseudococcus sp.GU134655.1 Pseudococcus nr. maritimus 97%317
28S-19(KJ530595) Pseudococcus nr. meridionalis GU134655.1 Pseudococcus nr. maritimus 100%315
16S-01 (KJ530566) Pseudococcus viburni JF714174.1 Pseudococcus viburni 100%1003
16S-02 (KJ530567) Pseudococcus nr. maritimus GU134644.1 Pseudococcus nr. maritimus 97%1017
16S-03 (KJ530568) Dysmicoccus texensis GU134650.1 Dysmicoccus brevipes 97%1007
16S-04 (KJ530569) Pseudococcus nr. viburni JF714174.1 Pseudococcus viburni 99%1003
16S-05 (KJ530570) Dysmicoccus brevipes GU134650.1 Dysmicoccus brevipes 100%994
16S-06 (KJ530571) Dysmicoccus sylvarum GU134644.1 Pseudococcus nr. maritimus 96%1016
16S-07 (KJ530572) Planococcus citri JF714171.1 Planococcus citri 100%1003
16S-08 (KJ530573) Pseudococcus nr. sociabilis GU134644.1 Pseudococcus nr. maritimus 98%1014
16S-09 (KJ530574) Ferrisia terani JF714173.1 Dysmicoccus boninsis 93%1023
16S-10 (KJ530575) Pseudococcus cryptus GU134648.1 Pseudococcus comstocki 97%1017
16S-11 (KJ530576) Ferrisia meridionalis JF714173.1 Dysmicoccus boninsis 92%1023
16S-12 (KJ530577) Ferrisia cristinae JF714173.1 Dysmicoccus boninsis 93%1022
LCO-20 + C1-05 (KJ530600) Dysmicoccus brevipes JQ085558.1 Dysmicoccus brevipes 99%760
LCO-23 + C1-06 (KJ530601) Dysmicoccus brevipes JQ085558.1 Dysmicoccus brevipes 99%760
LCO-26 + C1-19 (KJ530602) Dysmicoccus sylvarum JQ085558.1 Dysmicoccus brevipes 89%760
LCO-27 + C1-10 (KJ530603) Dysmicoccus sylvarum JQ085558.1 Dysmicoccus brevipes 89%760
C1-21 (KJ530604) Ferrisia meridionalis AY179445.1 Ferrisia pitcairnia 94%384
LCO-22 + C1-22 (KJ530605) Ferrisia terani JQ085554.1 Ferrisia virgata 92%760
LCO-21 + C1-22 (KJ530606) Ferrisia terani JQ085554.1 Ferrisia virgata 92%760
LCO-14 + C1-13 (KJ530607) Ferrisia cristinae JQ085554.1 Ferrisia virgata 92%760
C1-12 (KJ530608) Ferrisia cristinae AY179448.1 Ferrisia cristinae 99%385
LCO-24 + C1-24 (KJ530609) Phenacoccus parvus GU134711.1 Phenacoccus parvus 97%740
C1-23 (KJ530610) Phenacoccus solenopsis AB858432.1 Phenacoccus solenopsis 100%362
LCO-01 + C1-03 (KJ530611) Planococcus citri JQ085542.1 Planococcus citri 99%760
LCO-02 + C1-04 (KJ530612) Planococcus citri JQ085542.1 Planococcus citri 99%760
LCO-03 + C1-01 (KJ530613) Planococcus citri JQ085543.1 Planococcus citri 99%760
LCO-04 + C1-01 (KJ530614) Planococcus citri JQ085543.1 Planococcus citri 100%760
LCO-04 + C1-02 (KJ530615) Planococcus citri JQ085543.1 Planococcus citri 100%760
LCO-05 + C1-01 (KJ530616) Planococcus citri JQ085543.1 Planococcus citri 99%760
LCO-19 + C1-14 (KJ530617) Pseudococcus cryptus JQ085562.1 Pseudococcus comstocki 94%760
LCO-07 + C1-11 (KJ530618) Pseudococcus viburni JQ085549.1 Pseudococcus viburni 99%760
LCO-08 + C1-10 (KJ530619) Pseudococcus viburni JQ085549.1 Pseudococcus viburni 99%760
LCO-09 + C1-08 (KJ530620) Pseudococcus viburni JQ085549.1 Pseudococcus viburni 99%760
LCO-10 + C1-09 (KJ530621) Pseudococcus viburni JQ085549.1 Pseudococcus viburni 98%760
LCO-11 + C1-09 (KJ530622) Pseudococcus viburni JQ085549.1 Pseudococcus viburni 98%760
LCO-12 (KJ530623) Pseudococcus viburni JQ085549.1 Pseudococcus viburni 98%760
LCO-06 + C1-07 (KJ530624) Pseudococcus viburni JQ085549.1 Pseudococcus viburni 100%760
LCO-15 + C1-28 (KJ530625) Pseudococcus nr. viburni JQ085549.1 Pseudococcus viburni 93%760
C1-16 (KJ530626) Pseudococcus nr. sociabilis JF714166.1 Pseudococcus viburni 92%431
LCO-13 + C1-15 (KJ530627) Pseudococcus nr. sociabilis JQ085554.1 Ferrisia virgata 93%760
LCO-17 + C1-18 (KJ530628) Dysmicoccus texensis JQ085558.1 Dysmicoccus brevipes 93%760
C1-25 (KJ530629) Pseudococcus nr. meridionalis GU134683.1 Pseudococcus nr. maritimus 99%368
LCO-16 + C1-29 (KJ530630) Pseudococcus sp.JQ085549.1 Pseudococcus viburni 92%760
LCO-28 + C1-26 (KJ530631) Phenacoccus baccharidis HM474264.1 Phenacoccus solani 89%649
LCO-25 + C1-27 (KJ530632) Pheanacoccus baccharidis JQ085562.1 Pseudococcus comstocki 90%760
LCO-18 + C1-17 (KJ530633) Pseudococcus nr. maritimus JQ085562.1 Pseudococcus comstocki 91%760
ITS2-01 (KF804140) Dysmicoccus sylvarum JX228132.1 Dysmicoccus neobrevipes 71%716
ITS2-02 (KF804141) Dysmicoccus texensis JX228133.1 Dysmicoccus neobrevipes 90%704
ITS2-03 (KJ530596) Ferrisia cristinae JQ085571.1 Ferrisia virgata 73%957
ITS2-04 (KJ530597) Ferrisia cristinae JQ085571.1 Ferrisia virgata 72%959
ITS2-05 (KF804144) Dysmicoccus brevipes GU134673.1 Dysmicoccus brevipes 100%723
ITS2-06 (KF804154) Ferrisia meridionalis JQ085571.1 Ferrisia virgata 71%1032
ITS2-07 (KF804146) Ferrisia terani JQ085571.1 Ferrisia virgata 72%958
ITS2-08 (KF819646) Pseudococcus nr. meridionalis JF776370.1 Pseudococcus meridionalis 99%774
ITS2-09 (KF819647) Pseudococcus nr. sociabilis JF758861.1 Pseudococcus maritimus 85%741
ITS2-10 (KF819648) Pseudococcus nr. maritimus JN983134.1 Pseudococcus cribata 79%338
ITS2-11 (KJ530598) Phenacoccus parvus JQ085570.1 Phenacoccus parvus 99%582
ITS2-12 (KF819650) Phenacoccus solenopsis JQ085569.1 Phenacoccus solenopsis 98%551
ITS2-13 (KF819651) Phenacoccus solenopsis JQ085569.1 Phenacoccus solenopsis 99%652
ITS2-14 (KF819652) Planococcus citri HM628576.1 Planococcus citri 99%737
ITS2-15 (KF819653) Pseudococcus viburni AF006820.1 Pseudococcus affinis 100%754
ITS2-16 (KJ530599) Pseudococcus viburni AF006820.1 Pseudococcus affinis 99%756
ITS2-17 (KF819655) Pseudococcus nr. viburni AF006820.1 Pseudococcus affinis 89%730
ITS2-18 (KF819656) Phenacoccus baccharidis JF714191.1 Phenacoccus peruvianus 89%54
ITS2-19 (KF819657) Phenacoccus baccharidis JX228135.1 Phenacoccus solenopsis 93%95
ITS2-20 (KF819658) Pseudococcus sp.GU134667.1 Pseudococcus viburni 79%579

For the sequences of LCO and C1, overlapping and covering around 750 bp of Cytochrome Oxidase Subunit I, the contig sequence was used for the Blast study (when both sequences were available).

For the sequences of LCO and C1, overlapping and covering around 750 bp of Cytochrome Oxidase Subunit I, the contig sequence was used for the Blast study (when both sequences were available). For rough species delimitation, we used the online version of ABGD - Automatic Barcode Gap Discovery (http://wwwabi.snv.jussieu.fr/public/abgd/), a tool that detects gaps in the sequence barcodes and limits the differences between groups, which are smaller between specimens from the same species and larger for specimens from different species [31]. We used a prior maximal distance P = 1.67 and a Jukes-Cantor MinSlope distance = 1.000000. We carried out BLAST searches of the GenBank database from NCBI (http://www.ncbi.nlm.gov/BLAST) to identify similarities between our sequence dataset and sequences already published in the GenBank online database. For 28S, COI and 16S, we used the MEGABLAST method (for highly similar sequences), whereas we used the BLASTn method for ITS2. We generated a neighbor-joining tree based on the number of nucleotide differences between the multilocus haplotypes, with Mega4 [32], to provide a visual representation of the data (this tree was not generated to provide phylogenetic information) (Figure 1).
Figure 1

Neighbor-joining tree calculated from the number of differences between 28S haplotypes.

Bootstrap values (1,000 replications) are displayed. The 28S alignment used to compute the tree (Figure S1 in File S1) differs from the alignment of raw sequences, because regions including numerous insertions/ deletions were removed to achieve a satisfactory alignment. The 16S, ITS2, C1 and LCO haplotypes of specimens displaying each of the 28S haplotypes are given after the 28S haplotype code.

Neighbor-joining tree calculated from the number of differences between 28S haplotypes.

Bootstrap values (1,000 replications) are displayed. The 28S alignment used to compute the tree (Figure S1 in File S1) differs from the alignment of raw sequences, because regions including numerous insertions/ deletions were removed to achieve a satisfactory alignment. The 16S, ITS2, C1 and LCO haplotypes of specimens displaying each of the 28S haplotypes are given after the 28S haplotype code.

Morphological examination

A few specimens displaying each combination of haplotypes (each multilocus haplotype) were slide-mounted for morphological examination and kept as voucher specimens. The slide-mounting process (using the cuticles after the DNA extraction) and morphological examination were carried out by JF Germain, using the protocol previously described by Malausa et al. [23]. Morphological identifications were based on four taxonomic keys [33]–[36]. The slide-mounted specimens were deposited in the national collection of ANSES, Laboratoire de la Santé des Végétaux (Montferrier-sur-Lez, France) under the code numbers presented in Table 3, and the other specimens were stored in 96% ethanol. DNA extracts were stored at INRA Sophia Antipolis, 400 route des Chappes, Sophia Antipolis, France.
Table 3

Summary of mealybug species identified, populations sampled (see Table 1) and different haplotypes obtained for each genetic marker. Different haplotypes obtained for the same species are shown in bold.

Multilocus haplotypePopulation sampledIdentificationSlide-mounted specimens28S16SLCOC1ITS2
MLH 0106, 07, 08, 09, 14, 23, 38 Dysmicoccus brevipes 902316, 902317, 902318, 902319, 902320, 902321, 902322, 902335, 1002170, 1200840, 1200905, 120090628S-0116S-05 LCO-20 C1-05 ITS2-05
MLH 0225, 44 Dysmicoccus brevipes 1200841, 1200842, 120084328S-0116S-05 LCO-23 C1-06 ITS2-05
MLH 0310 Dysmicoccus sylvarum 902323, 902324, 90232528S-1716S-06 LCO-26 C1-19 ITS2-01
MLH 0411 Dysmicoccus sylvarum 902326, 902327, 902328, 902329, 90233028S-1716S-06 LCO-27 C1-20 ITS2-01
MLH 0525, 33 Ferrisia meridionalis 1200858, 1200859, 1200860, 120086128S-0316S-11C1-21ITS2-06
MLH 0630 Ferrisia terani 120086328S-0416S-09 LCO-22 C1-22ITS2-07
MLH 0733 Ferrisia terani 120086428S-0416S-09 LCO-21 C1-22ITS2-07
MLH 0834 Ferrisia cristinae 120086728S-0516S-12LCO-14 C1-13 ITS2-04
MLH 0929 Ferrisia cristinae 1200865, 120086628S-05-- C1-12 ITS2-03
MLH 1022, 24, 46 Phenacoccus parvus 1200885, 1200886, 120088728S-13-LCO-24C1-24ITS2-11
MLH 1125, 42 Phenacoccus solenopsis 1200879, 1200880, 120088228S-12--C1-23 ITS2-12
MLH 1225, 42, 45 Phenacoccus solenopsis 1200881, 1200883, 120088428S-12--C1-23 ITS2-13
MLH 1319, 20, 21, 22, 25, 28, 35, 36, 40 Planococcus citri 1101834, 1101836, 110183728S-0216S-07 LCO-01 C1-03 ITS2-14
MLH 1429, 41, 48 Planococcus citri 1200848, 1200855, 1200856, 120085728S-0216S-07 LCO-02 C1-04 ITS2-14
MLH 1540 Planococcus citri 1200852, 1200853, 120085428S-0216S-07 LCO-03 C1-01 ITS2-14
MLH 1626, 27, 32, 34 Planococcus citri 1200844, 1200845, 1200846, 1200850, 120085128S-0216S-07 LCO-04 C1-01 ITS2-14
MLH 1729 Planococcus citri 120084928S-0216S-07 LCO-04 C1-02 ITS2-14
MLH 1827 Planococcus citri 1200847, 120089428S-0216S-07 LCO-05 C1-01 ITS2-14
MLH 1932 Pseudococcus cryptus 1200874, 1200875, 1200876, 120087728S-0916S-10LCO-19C1-14
MLH 2012 Pseudococcus viburni 902331, 1101681 28S-06 16S-01LCO-07 C1-11 ITS2-16
MLH 2113 Pseudococcus viburni 1101682 28S-06 16S-01LCO-08 C1-10 ITS2-16
MLH 2247 Pseudococcus viburni 1200871 28S-06 LCO-09 C1-08
MLH 2313 Pseudococcus viburni 902332 28S-06 16S-01LCO-10 C1-09 ITS2-16
MLH 2405, 47 Pseudococcus viburni 1200870, 902309, 1200908, 902310, 902311 28S-06 16S-01LCO-11 C1-09 ITS2-16
MLH 2518 Pseudococcus viburni 1101832 28S-06 -LCO-12 - ITS2-16
MLH 2601, 02, 06, 15, 17, 18, 31, 39 Pseudococcus viburni 902302, 902303, 902305, 902306, 902314, 1200862, 1200873 28S-08 16S-01LCO-06 C1-07 ITS2-15
MLH 276 Pseudococcus nr. viburni 902313, 90231528S-0716S-04LCO-15C1-28ITS2-17
MLH 2820, 29 Pseudococcus nr. sociabilis 1101839, 1200878 28S-10 16S-08- C1-16 ITS2-09
MLH 2920 Pseudococcus nr. sociabilis 1101838 28S-11 -LCO-13 C1-15 -
MLH 304 Dysmicoccus texensis 90230828S-1516S-03LCO-17C1-18ITS2-02
MLH 3143 Pseudococcus nr. meridionalis 1200890, 1200891, 1200892, 120089328S-19--C1-25ITS2-08
MLH 3216 Pseudococcus sp.110183028S-18-LCO-16C1-29ITS2-20
MLH 3333 Phenacoccus baccharidis 120088828S-14- LCO-28 C1-26 ITS2-19
MLH 3437 Phenacoccus baccharidis 120088928S-14- LCO-25 C1-27 ITS2-18
MLH 353 Pseudococcus nr. maritimus 90230728S-1616S-02LCO-18C1-17ITS2-10

Design of species-specific primers for the molecular identification kit

We used SP-Designer [37] software to design species-specific primers, using the list of haplotypes (for each locus studied, separately) as input data. Briefly, SP Designer designs PCR primers that (i) should hybridize to only a set of sequences targeted by the user (e.g. all the sequences displayed by the individuals of one target species), and (ii) allow the amplification of a DNA fragment of the desired size. We designed PCR primers hybridizing specifically to the sequences of five species. The first four species targeted were those found in this study to be the most common in Brazil (see results): D. brevipes, Ps. viburni, Pl. citri and Ph. solenopsis. The fifth species, Planococcus ficus (Signoret), constitutes a major threat to vineyards worldwide, and was therefore also selected so that the identification kit would rapidly detect its occurrence in cases of new invasions.

Species-specific amplification assay

We checked the specificity of the designed primer pairs for the targeted species, by testing each primer pair in PCRs with one or two samples from among the entire set of species surveyed in Brazil (see results). A multiplex PCR was then designed, with one primer pair per species. The primers were selected by testing various primer combinations in PCR with the various Brazilian species surveyed and checking the clarity of the results obtained by electrophoresis of the PCR products. All PCRs were performed with the Multiplex PCR Master Mix (QIAGEN), with a reaction mixture consisting of 1 x PCR Master Mix and primers (0.4 µM each), made up to a final volume of 10 µl with ultrapure water. The PCR conditions were as follows: initial denaturation for 15 min at 95°C; followed by 35 cycles of denaturation for 30 s at 94°C, annealing for 90 s at 62°C, extension for 90 s at 72°C; and a final extension for 30 min at 72°C. PCR products were separated on a QIAxcel advanced system (QIAGEN), and analyzed with QIAxcel ScreenGel Software (QIAGEN).

Results

DNA and morphological characterization

We obtained 779 consensus DNA sequences from Brazilian mealybugs, making it possible to analyze 195 specimens. 178 sequences were obtained for 28S (19 different haplotypes), 123 sequences for 16S (12 different haplotypes), 135 sequences for LCO (28 different haplotypes), 183 sequences for C1 (29 different haplotypes) and 160 sequences for ITS2 (20 different haplotypes) (Table S1 in File S1). We observed 35 different multilocus haplotypes in total, corresponding to 19 different taxonomic groups, as defined by ABGD output (Figure 1). All specimens of ABGD group 1 were morphologically identified as the root mealybug Dysmicoccus brevipes (Cockerell). Two multilocus haplotypes (MLH 01 and MLH 02) were observed, with variation observed only for COI. We obtained BLAST hits with Genbank sequences corresponding to D. brevipes, with sequences similarities of between 99 and 100%. The second group (MLH 03 and MLH 04) was morphologically identified as Dysmicoccus sylvarum Williams and Granara de Willink. Genetic variation was observed only for COI. As this was the first time that DNA from D. sylvarum had been sequenced, no BLAST hits for this species were obtained with GenBank. Groups 3, 4 and 5 correspond to three different species from the genus Ferrisia Fullaway. Group 3 was identified morphologically as Ferrisia meridionalis Williams, and contained only one multilocus haplotype (MLH 05). A strong BLAST hit (99%) was obtained for the 28S-03 sequence and a sequence assigned to Ferrisia gilli Gullan by Gullan et al. [38]. For the other markers, no clear BLAST hit (with similarity >95%) was observed. Group 4 (MLH 06 and MLH 07) was morphologically identified as Ferrisia terani Williams and Granara de Willink. BLAST results with C1-22 and 28S-04 revealed hits with GenBank sequences assigned to F. terani, with sequence similarities of 97% and 99%, respectively. Group 5 (MLH 08 and MLH 09) was morphologically identified as Ferrisia sp. The BLAST hits with the highest degree of sequence similarity corresponded to GenBank sequences assigned to F. cristinae Kaydan and Gullan (Table 2) according to the last taxonomic revision of the genus [35]. Group 6 (MLH 10) were morphologically identified as Phenacoccus parvus Morrison. BLAST hits revealed similarities of between 97% and 100% with Ph. parvus sequences identified in previous studies (Table 2). Group 7 (MLH 11 and MLH 12) was identified morphologically as Phenacoccus solenopsis Tinsley. Again, BLAST hits were associated with high levels of sequence similarity (98% to 100%). Group 8 (MLH 13 to MLH 18) was morphologically identified as the citrus mealybug, Planococcus citri (Risso). In total, 65 specimens were identified as Pl. citri in this work, making this species the most frequently observed in Brazilian vineyards. Genetic variation was particularly common in this group, with six multilocus haplotypes observed and differences detected for four of the five markers used. BLAST results revealed hits with very similar sequences (99 to 100%) to a sample previously identified as Pl. citri. Group 9 (MLH 19) was morphologically identified as Pseudococcus cryptus Hempel. The BLAST study revealed one hit (99% similarity) with haplotype C1-14 and a Ps. cryptus sequence from Genbank. For LCO-19, 28S-09 and 16S-10, we observed hits with similarities of 94, 96 and 97%, respectively, with Pseudococcus comstocki Kuwana from Malausa et al. [23] and Abd-Rabou et al. [17]. Group 10 (MLH 20 to MLH 26) was morphologically identified as the obscure mealybug, Pseudococcus viburni (Signoret), intragroup variation was observed, with two 28S haplotypes (28S-6 and 28S-8) and different haplotypes at LCO, C1 and ITS2 associated with each 28S haplotype. All the haplotypes observed displayed similarity to Ps. viburni sequences previously published in GenBank (Table 2). Group 11 (MLH 27) was morphologically identified as Pseudococcus near viburni. BLAST hits revealed similarities of 99% for 28S-07 and 16S-04 with Ps. viburni sequences identified in previous studies (Table 2). Groups 12 and 13 (MLH 28 and MLH 29) were identified morphologically as Pseudococcus near sociabilis Hambleton. BLAST hits corresponding to 98% similarity were obtained between the 28S-10 and 16S-08 sequences and GenBank sequences assigned to Pseudococcus maritimus (Ehrhorn) by Gullan et al. [38] and Malausa et al. [23]. However, relatively high levels of divergence (e.g. 5% (14/278) between 28S-10 and 28S-11 and 10% (36/362) between C1-15 and C1-16) were observed between groups 12 and 13, which may thus correspond to two different species that could not be clearly identified as Ps. sociabilis. Group 14 was morphologically identified as Dysmicoccus texensis (Tinsley). Only one specimen was sampled (displaying the MLH 30 haplotype). This was the first time that DNA from D. texensis has been sequenced. The BLAST hits with the highest scores were obtained for the 16S-03 and 28S-15 loci, with the species D. brevipes (97%) and Dysmicoccus neobrevipes Beardsley (99%), respectively. Group 15 (MLH 35) was identified as closely related to the grape mealybug Ps. maritimus. For this group, no BLAST hit with a high percentage similarity was found. Group 16 (MLH 31) was morphologically identified as Pseudococcus near meridionalis Prado. BLAST hits showed 100% similarity between the 28S-19 sequence and that of Ps. near maritimus from the study by Malausa et al. [23] and 99% similarity between the ITS2-08 sequence and that of Pseudococcus meridionalis Prado described by Correa et al. [22]. However, not all the characters listed in the description of Ps. meridionalis [22] were visible in the specimens collected in this study. The specimens of group 17 (MLH 32) could not be identified to species level, but were found to belong to genus Pseudococcus Westwood. The highest degree of similarity (97%) was that between the 28S-18 sequence and a sequence from Ps. near maritimus described by Malausa et al. [23]. Groups 18 (MLH 33) and 19 (MLH 34) were both identified morphologically as Phenacoccus baccharidis Williams. As this species had not been sequenced before, no BLAST hit with a high percentage similarity was detected. The highest similarity observed was 91% between the C1-27 haplotype and Phenacoccus pergandei Cockerell, as described by Yokogawa and Yahara [39] (Table 2). The results summarizing the distribution of the various taxa identified in the three grapevine-producing regions of Brazil are provided in Figure 2.
Figure 2

Distribution of mealybug species in vineyards in the Paraná, Pernambuco and Rio Grande do Sul states (Brazil).

Identification kit

The seven multiplexed primer pairs (Table 4) yielded PCR products of a particular size for each species when used with the target DNA: 150 bp for Ps. viburni, 220 bp for Ph. solenopsis, 420 bp for Pl. citri, 590 bp for Pl. ficus, 890 bp for D. brevipes, and a positive control band for the presence of Pseudococcidae DNA at 90 bp (Figure 3). The reaction was found to be specific for the target species, whether that species was obtained from the Brazilian samples studied here or from other samples collected in France and Egypt (including the species surveyed by Abd-Rabou et al., [17]).
Table 4

Primers used for PCR amplification.

Mealybug speciesDNA regionFragment size (bp)Forward primer (5′ – 3′)Reverse primer (5′ – 3′)
Pseudococcus viburni COI159 CAGCAACTATAATTATTGCTATTCCAACTAG TAGAAAGAATAATTCCTGTRAAACCACC
Phenacoccus solenopsis 28S-D2216 TTTCTTCGTCGGACGTTTG AAAGCCGATCTACGCTTCAG
Planococcus citri and Planococcus minor ITS2422 GATGGTTGCGTTCTCGCG GACGGCGGTAACGTTAAGC
Planococcus ficus ITS2613 CATGCCAGAGTGATGCGA AGTACGCTTATAACGCGAATTGA
Planococcus minor COI686 CCGGTTGAACACTTTATCCC AGTTAATCCTCCTAATGTAAATATAATGATG
Dysmicoccus brevipes leuA-16S890 TAGGGAAGCTTTCCGGTACC TCCAGTTTACGACGTAGGCG
Control for the presence of DNA18S91 CAACTGTCGACGGTAGGTTCG CCGTTTCTCAGGCTCCCTCT
Figure 3

Electrophoresis profile obtained with the Qiaxcel Advanced System for each PCR product from the identification kit.

Each lane corresponds to one sample, and each band to a DNA fragment. The first and last lanes contain a molecular weight ladder extending from 50

Electrophoresis profile obtained with the Qiaxcel Advanced System for each PCR product from the identification kit.

Each lane corresponds to one sample, and each band to a DNA fragment. The first and last lanes contain a molecular weight ladder extending from 50

Discussion

DNA analyses

Overall, genetic differences between haplotypes clearly separated several taxa, consistent with the results obtained with the ABGD method [31]. We obtained satisfactory congruence between the groups defined by the ABGD method and the morphological identifications of the specimens. In most cases, the occurrence of several multilocus haplotypes assigned to a same ABGD group probably resulted from intraspecific variation, such as observed at the cytochrome oxidase I locus (LCO and C1 regions) for species collected from several sites, such as Pl. citri, D. brevipes or D. sylvarum. However, in at least three cases, we observed a discrepancy between the results of the different techniques. First, specimens from two ABGD groups were identified morphologically as Ph. baccharidis. In this case, the occurrence of a unique haplotype at the 28S locus, the low level of genetic divergence and the morphological homogeneity of the specimens were not consistent with the occurrence of two different species, as proposed by the ABGD method. Conversely, the two ABGD groups that were both identified as Ps. near sociabilis morphologically are more likely to correspond to two different unidentified species, both morphologically similar to Ps. sociabilis, given the sequence divergence observed for all the loci sequenced for both species (Figure 1). This work is currently inconclusive as concerns the delineation of the various Pseudococcus species (Ps. near viburni, Ps. near maritimus, Ps. near meridionalis, Ps. near sociabilis), but further progress will require a complete re-examination of this species because the morphological characteristics displayed by the collected samples differed from the descriptions of all species by at least a few characteristics. These differences may actually correspond to intraspecific variation, but the collection of samples from various sites and their comparison with the type specimens of each species would be required to improve identification. Unfortunately, only one or a few adults of these species were collected in this study. The third case is that of the ABGD group identified morphologically as Ps. viburni. This group is actually composed of two subgroups, with small fixed differences at all markers other than LeuA-16S, the most strongly conserved marker used in this study. The first subgroup (consisting of all multilocus haplotypes containing 28S-6) displayed remarkable genetic diversity at LCO and C1, whereas the second subgroup had a unique multilocus haplotype 28S-08, 16S-01, LCO-06, C1-07 and ITS2-15. The second subgroup actually includes haplotypes also found in France, Italy, Spain, and Chile [17], [23], [25], [26], whereas the haplotypes from the first subgroup had previously been observed only in southern Brazil (as in this study) by Malausa et al. [23]. Hence, the first subgroup may therefore correspond to a species closely related to Ps. viburni, endemic to Brazil. Regardless of the actual status of this taxon, the genetic diversity observed in Southern Brazil within populations morphologically identified as Ps. viburni supports the hypothesis of Charles [40] about the species being of Neotropical origin.

Geographic distribution

Pl. citri, D. brevipes and F. meridionalis were each found in more than one region. Pl. citri was sampled from 18 different populations in Paraná and Pernambuco. Interestingly, this species was not observed in Rio Grande do Sul. In Brazil, Pl. citri is also a major pest of Coffea sp. [41]–[44], occasionally occurs in Citrus sp. [45] and has been found in the wine grapes in Rio Grande do Sul [9], [46]. In the State of Paraná, a high level of intraspecific variation was observed, with five different multilocus haplotypes (MLH13, MLH14, MLH16, MLH17 and MLH18), whereas only two multilocus haplotypes were found in Pernambuco (MLH13 and MLH15). The root mealybug, D. brevipes, was observed in Rio Grande do Sul and Pernambuco with different multilocus haplotypes: MLH01 in Rio Grande do Sul, and MLH02 in Pernambuco. This species is an important pest of pineapple Ananas comosus (L.) Merrill, and, according to the scale insect database ScaleNet, it has previously been observed in several Brazilian states [9], [47]. F. meridionalis was observed in Pernambuco and Rio Grande do Sul, the same multilocus haplotype being identified in both regions. This is the first record of this species in Brazil, but it has previously been found in Argentina, Chile, Paraguay and Uruguay [35]. We identified 13 specimens from Pernambuco as Ph. solenopsis. This species was recently observed in Brazil on tomato Solanum lycopersicum Linnaeus, and then on plants from the Amaranthaceae and Caricaceae families in Espírito Santo State [48], [49]. Ps. viburni, D. sylvarum, D. texensis, F. terani, Ph. baccharidis and Ps. near maritimus were observed only in Rio Grande do Sul. Ps. viburni was very frequently found in this region, with 34 specimens identified at 12 sites. This species has also previously been reported to be present in Minas Gerais, Rio de Janeiro, Rio Grande do Sul, São Paulo and Espírito Santo State [47], [48]. D. sylvarum is a species first described in 1992 in Costa Rica [36], subsequently being described for the first time in Brazil in 2006, also sampled in weeds and found in the same region of Rio Grande do Sul State [50]. In this study, we found D. sylvarum on vineyard weeds of the genus Rumex L. D. texensis and Ph. baccharidis had already been observed in Brazil, in the states of Minas Gerais and Rio Grande do Sul [34], [36]. For F. terani, this is the first record of its presence in Brazil. In samples from Paraná, the species F. cristinae, Ps. cryptus and Ps. near sociabilis were sampled from grape plants. Nine specimens were identified as Ph. parvus, from three populations collected from grape plants and weeds. Ps. near meridionalis was sampled from vineyard weeds of the species Sonchus oleraceus Linnaeus. Ps. meridionalis is a recently described species first reported in Chilean vineyards (Correa et al., [22]). The species Pseudococcus longispinus (Targioni-Tozzetti), Ps. maritimus, and Pl. minor, which are major vineyard mealybugs worldwide [9], [51] were not observed in this study. The species-specific multiplex PCR successfully detected the four most abundant mealybug species in Brazilian vineyards and the principal threat, Pl. ficus, which is already present in Uruguay, close to southern regions of Brazil. The kit was extensively tested on specimens of 29 species found in Brazil, France and Egypt. This kit was found to be suitable for rapid and cost-efficient surveys in Brazilian vineyards. Moreover, the use of positive control PCR primers detecting Pseudococcidae DNA makes it possible to distinguish between an absence of signal due to poor DNA extraction and a lack of signal due to the specimen belonging to a non-target species. However, it is not possible to guarantee that this method is 100% reliable for use with DNA from taxa that have not yet been sampled but are very closely related to the target species.

Conclusions

The taxonomic identifications obtained in the DNA analyses were entirely consistent with the morphological characterization, allowing the clear identification of 17 species from Brazilian vineyards. Pl. citri, D. brevipes and Ps. viburni were the most frequently collected species. F. terani and F. meridionalis were reported for the first time in Brazil. The data and samples obtained from this survey were used to design an identification kit based on five multiplexed species-specific PCRs. This multiplex PCR proved useful for the rapid and cost-efficient identification of Ps. viburni, Pl. citri, D. brevipes, Ph. solenopsis and Pl. ficus. This file includes Figure S1 and Table S1. Figure S1. 28S sequence alignment used to calculate the Neighbor joining tree of Figure 1. Regions of the alignment with insertions / deletions are removed. Table S1. Summary of molecular and morphological identification of mealybug populations sampled in Brazilian vineyards. (DOCX) Click here for additional data file.
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