The Asian gypsy moth (AGM) is considered a very serious invasive threat in North America. For this reason, it is subjected to a bio-surveillance program that includes an extensive network of pheromone traps. For regulatory purposes, the term “AGM” designates a group of Asian Lymantria species and subspecies, comprising two L. dispar subspecies (L. d. asiatica and L. d. japonica), and three closely related species (L. umbrosa, L. albescens and L. postalba). These moths are attracted to the same pheromone as the European gypsy moth (EGM), L. dispar dispar, which is already established in North America and typically makes up the bulk of moths caught in gypsy moth pheromone traps. These different Lymantria taxa are difficult to distinguish from one another using morphological characters alone. Here, we designed a TaqMan triplex assay capable of detecting AGM in bulk pheromone trap samples. The assay targets SNPs found in three different mitochondrial genes. Using a DNA dilution series, we show that the assay can detect AGM taxa at AGM:EGM dilution ratios ≥ 1:1000. The assay was validated using batch DNA extractions of moth legs tested at a 1:100 AGM:EGM leg ratio, a proportion that is around the operational limit for a single pheromone trap. The assay provided correct identification for all AGM taxa tested. An experiment examining the integrity of DNA extracted from gypsy moths left in pheromone traps under field conditions for up to 4 months indicated that DNA quality remains sufficient, during that period, for the present assay to remain accurate.
The gypsy moth, Lymantria dispar (Linnaeus) (Lepidoptera: Erebidae: Lymantriinae), is considered a major threat to North America’s forest resources and economy. This species comprises three recognized subspecies, including the European gypsy moth (EGM), L. dispar dispar (Linnaeus), which is found over most of continental Europe and north-western Africa (Pogue and Schaefer 2007). EGM was accidentally introduced in Massachusetts in 1869 (Liebhold et al. 1989) and has since become established in north-eastern North America, where it is responsible for recurrent and substantial defoliation resulting in important economic losses (Bradshaw et al. 2016). The other two subspecies, L. dispar asiatica Vnukovskij and L. dispar japonica (Motschulsky), are found throughout mainland eastern Asia and Japan, respectively (Pogue and Schaefer 2007). Along with three closely related Lymantria species (L. umbrosa Butler, L. albescens Hori and Umeno, and L. postalba Inoue), they form a complex informally known as Asian gypsy moth (AGM). As a group, these insects are considered a much more serious threat than the European subspecies, in large part because AGM females, unlike those of L. dispar dispar, are flight-capable, increasing the probability of a rapid invasion following an unchecked accidental introduction. Such introductions have indeed occurred in the past, but eradication operations appear to have been successful (APHIS 2016; Nealis 2002, 2009).
Molecular markers and diagnostic tools targeting the gypsy moth have become important to help prevent invasions via early intervention (Arimoto and Iwaizumi 2014; Armstrong and Ball 2005; Armstrong et al. 2003; Ball and Armstrong 2006; Bogdanowicz et al. 1993, 1997, 2000; Boykin et al. 2012; Chen et al. 2013, 2015; deWaard et al. 2010; Garner and Slavicek 1996; Harrison and ODell 1989; Islam et al. 2015; Kang et al. 2015, 2017; Keena et al. 2008; Lacković et al. 2015; Pfeifer et al. 1995; Qian et al. 2014; Stewart et al. 2016; Wu et al. 2015). Given that egg masses and larvae of gypsy moth subspecies are impossible to distinguish from one another and from those of other closely related species, we recently developed a suite of TaqMan assays that enables the rapid and accurate identification of 10 Lymantria species and subspecies from intercepted egg masses and older life stages (Stewart et al. 2016). These assays were designed for the processing of individual samples, regardless of their life stage, during inspection or surveys. However, they are not optimal for processing bulk pheromone trap samples, inasmuch as the capture of an AGM is a rare event in North America, where specimens are typically all L. dispar dispar. Detection of a single AGM specimen in such samples would be laborious if all moths were to be assayed individually. For this reason, only a fraction of the moths caught in a given trap are processed for identification in current survey procedures, which could result in a failure to detect the presence of AGM (i.e., false negatives).
To tackle this issue, we developed a triplex TaqMan assay that can be used on bulk samples, with the objective of achieving sensitivity levels sufficient to detect one AGM in a background of 1000 EGMs. We modified our previously published suite of assays (Stewart et al. 2016) to ensure that AGM species and subspecies could be discriminated against EGM in a single reaction. This required that we identify markers enabling the design of not only discriminatory probes, but also discriminatory primers for each of the three subassays targeting different AGM taxa. The tool we developed will prove very useful to perform large-scale screening for AGM adults in traps and provide early warning of ingress.
Materials and methods
A scan of the SNP data presented in Djoumad et al. (2017) enabled the identification of markers in cytochrome b (cytb) and NADH-ubiquinone oxidoreductase chain 1 (ND1) potentially suitable for distinguishing the two Asian L. dispar subspecies (treated here together) and L. umbrosa, respectively, from the other AGM taxa. However, selection of these SNPs was based on a very small sample of mitochondrial genome sequences. To increase confidence in the suitability of these markers for species discrimination, sequences gleaned from Djoumad et al. (2017) were aligned with corresponding cytb and ND1 sequences from L. dispar [69 cytb sequences (Wu et al. 2015); Popset 756785935) and 19 ND1 sequences (Lin and Zhu, Genbank submissions, accession numbers JX133717 – JX133736)]. We also amplified and sequenced the appropriate region of the ND1 gene from additional L. umbrosa specimens provided by RZ, using primers and PCR conditions described in Djoumad et al. (2017). The cytochrome c oxidase I (COI) marker used for discrimination of L. albescens and L. postalba (treated here together) from other AGM taxa were the same as those employed by Stewart et al. (2016).
Sources of specimens used
For the purpose of developing the assay and conducting initial dilution tests, we used DNA extracts from Lymantria specimens generated in the context of an earlier study (Stewart et al. 2016); see Table 1 for details on sample origins and providers. For assay validation, fresh L. dispar dispar male moths were collected in Canada using pheromone traps (milk-carton type; Distribution Solida, Saint-Ferréol-les-neiges, Canada) containing a Vaportape II insecticidal strip (Dichlorvos 10%, Hercon Environmental, Emigsville, USA) and a gypsy moth pheromone dispenser ((+) Disparlure, Trécé Inc., Adair, USA). The traps were suspended from trees at a height of ~ 1.5 m, from 15 June to 15 September 2017. Moths were collected and stored in glassine envelopes at − 20 °C until used.
One hundred L. dispar dispar moths were sampled from each of four collection sites, three in the province of Quebec and one in the province of Ontario, for a total of 400 moths. Two parallel assays were conducted for each of the four sets of 100 moths. In the first assay, we used one leg from each L. dispar dispar specimen, while for the second assay we used another leg from the same 100 specimens, plus a single AGM leg (from either L. dispar japonica, L. dispar asiatica, L. albescens or L. umbrosa; see Table 2 for sources). The legs were collected in 2 mL round-bottom Eppendorf safe-lock tubes and placed at − 20 °C until used.
DNA batch extraction
DNA was extracted from each batch of legs (30–50 mg of tissue) using the DNeasy Blood and Tissue Mini Kit (Qiagen, Valencia, CA). A 5 mm stainless steel bead was added to the moth legs in each 2 mL tube. The tubes were then flash-frozen in liquid nitrogen and placed at − 80 °C in a prechilled Tissuelyser block. Liquid nitrogen disruption was used to maximize the likelihood that all legs would be sufficiently disrupted to produce similar yields of DNA, as we were not confident that we would achieve this goal with the micro pestle method. The samples were disrupted using a Qiagen Tissuelyser (Qiagen, Valencia, CA) at a speed of 26 Hz for 60 s to produce a fine powder. Buffer ATL (1080 µL) and proteinase K (120 µL) were then added to each tube, followed by vortexing. The samples were incubated overnight at 56 °C with constant gentle mixing, using a Robbins Scientific Model 400 Hybridization oven set at 4 rpm. After incubation, samples were vortexed and transferred to individual 15 mL Falcon tubes. Buffer AL (1200 µL) was added to the tubes and vortexed, followed by addition of 1200 µL of 100% ethanol and vortexing. For each sample, the lysate was split and transferred to two 2 mL Eppendorf safe-lock tubes and centrifuged at 5000 rpm for 1 min to pellet the debris. The cleared lysates were then added to two spin columns (DNeasy Mini spin columns; Qiagen, Valencia, CA) in three steps of 600 µL, and centrifuged at 8000 rpm for 1 min after each addition of lysate. The wash steps with buffers AW1 and AW2 were performed according to the manufacturer’s instructions. For each sample, DNA was eluted from the two spin columns using 150 µL of buffer AE each. The eluted DNA was recovered and then passed through the column a second time; eluates from the two columns were subsequently combined for a final volume of 300 µL DNA per sample. The DNA was quantified on a Nanodrop ND-100 spectrophotometer (ThermoFisher Scientific).
Primer and probe design
Primers and probes were designed using the Oligo Explorer program (http://www.genelink.com/tools/gl-downloads.asp), except for “locked nucleic acid” (LNA) probes, which were designed using the IDT Biophysics design tool (http://biophysics.idtdna.com/). The latter were employed to increase sensitivity and specificity of annealing in cases where probe-based discrimination was provided by a single SNP; a triplet of LNA nucleotides surrounding a single base mismatch site tends to maximize probe specificity (Owczarzy et al. 2011). Similarly, we used “Amplification Refractory Mutation System” (ARMS) primers whenever only one discriminatory SNP was available for primer design. With this approach, an artificial ARMS SNP can be added adjacent to an existing 3′-end SNP, at either position 2 or 3 of the primer, to significantly increase the discriminatory ability of that primer (Newton et al. 1989). ARMS primer combinations were tested against non-ARMS primer pairs to determine the combination that gave the best discrimination against non-target species while having a minimal effect on the specificity of the target species amplification. Primer and probe sequences are provided in Table 3.
qPCR conditions for copy number determination
Optimal performance of the TaqMan assay described here requires that DNA concentrations be normalized. To this end, we quantified COI copy number using a quantitative real-time PCR (qPCR) approach and primers targeting COI (Table 3). qPCR was performed using an Applied Biosystems 7500 Fast Real Time PCR machine. 96-well MicroAmp Fast Optical real-time PCR plates were used (Applied Biosystems, Foster City, CA) with MicroAmp Optical Adhesive Film (Applied Biosystems, Foster City, CA). The 10 µL amplification reactions contained 1 µL of DNA and 500 nM of primers. PCR conditions were as follows: a 15-min initial denaturation step at 95 °C for enzyme activation, followed by 50 cycles of 95 °C, 15 s; 58 °C, 30 s; 65 °C, 90 s. PCR was performed using the Qiagen Quantitect SYBR Green PCR Kit (Qiagen, Valencia, CA). Two technical replicates were run for each sample. DNA copy number was calculated using the linear regression of efficiency (LRE) approach (Rutledge 2011).
TaqMan conditions for AGM detection in bulk samples
The TaqMan assays were performed using the same equipment as described above. The assays were tested in simplex and triplex formats using the Quantitect Multiplex PCR No Rox 2X Mastermix (Qiagen, Valencia, CA). Final primer and probe concentrations were set at 500 nM and 100 nM, respectively, in a 10 µL reaction volume. The L. dispar asiatica/L. dispar japonica cytb probe was an LNA probe, with a fluorescein (6-FAM) label at the 5′ end and an Iowa Black FQ quencher at the 3′ end. The L. umbrosa ND1 probe was an LNA probe with a HEX label at the 5′ end and an Iowa Black FQ quencher at the 3′ end. The L. albescens/L. postalba COI probe was labelled at the 5′ end with Cy5 and was a double quenched Tao probe with an Iowa Black RQ quencher at the 3′ end (Integrated DNA Technologies, Coralville, IA). Two µL of L. dispar dispar DNA (equivalent to 500,000 COI copies) was used for each reaction. PCR conditions for the TaqMan reactions were as follows: a 15-min initial denaturation step at 95 °C for enzyme activation, followed by 45 cycles of 95 °C, 15 s; 60 °C, 90 s. Three technical replicates were run for each sample.
Assessing DNA integrity in pheromone trap samples
Since the assay we developed is meant to be used on samples containing moths that have resided in pheromone traps for various periods of time under field conditions, we wanted to determine whether the quality of DNA extracted from such moths was sufficient to ensure reliable molecular identification. Because we did not have access to fresh AGM specimens, we ran this experiment using L. dispar dispar moths only, with the assumption that DNA stability in dead moths will be comparable for all gypsy moth subspecies.
Freshly killed L. dispar dispar male moths were obtained from Insect Production Services (Natural Resources Canada, Sault Ste. Marie, Ontario) and placed in six delta bi-directional insect sticky traps (Better World Manufacturing, Fresno, California) on May 20, 2016, at a density of 5–6 moths/trap. The traps were suspended on spruce trees ~ 3 m above ground, in a semi-wooded area on the Laurentian Forestry Centre property in Quebec City, Canada. Moths were then collected on a monthly basis, between May and September, and frozen at − 20 °C until used; time-zero samples were placed directly in the freezer. DNA was extracted from two legs (or head plus thorax, if legs were absent), using the Qiagen DNeasy Blood and Tissue Mini Kit protocol, according to the manufacturer’s instructions. The tissue disruption step was performed in 180 µL buffer ATL using a micro-pestle.
The PCR primers used are those designed by Stewart et al. (2016) for EGM detection (i.e., subassays 3A, 4A and 4B). One pair is specific to the L. dispar dispar mitochondrial COI gene while the other is specific to the nuclear FS1 marker (Table 4). DNA was quantified and diluted to 2.5 ng/µL, and qPCR reactions were run using 5 ng of genomic DNA. Ct values for both mitochondrial (COI) and nuclear (FS1) DNAs were monitored over time, and the Ct ratio calculated to determine if mitochondrial DNA was more stable than nuclear DNA, as expected. The qPCR conditions were similar to those described above for copy number determination (initial 15 min denaturation step at 95 °C, followed by 50 cycles of 95 °C, 15 s; 50 °C, 30 s; 65 °C, 90 s).
To achieve our goal of designing a multiplex assay that could be conducted in a single tube, we treated as a single taxon each of two taxon pairs, namely L. dispar asiatica and L. dispar japonica, and L. albescens and L. postalba, given the high within-pair similarity observed in their mitogenomes (Djoumad et al. 2017; Djoumad et al. unpublished data).
Bulk triplex A subassay
Among the primers and probes developed by Stewart et al. (2016), the set developed for L. albescens/L. postalba, targeting COI, was directly transferable to this assay as it met our requirements for species-specificity and dual primer/probe-based discriminatory capabilities. Species discrimination was here provided by two ARMS primers and a probe (for details, see Fig. 2 under the “Bulk Triplex A” tab of Online Resource 1). However, for the other two subassays (see below), new primers and probes had to be designed from alternative marker genes, as sufficient discriminatory SNPs for primer development could not be found in the COI gene.
Bulk triplex B subassay
For the L. dispar asiatica/L. dispar japonica taxon pair, analysis of the mitochondrial genome sequences reported by Djoumad et al. (2017) led to the identification of discriminatory SNPs in the cytb gene. Comparison of this target sequence with equivalent sequences gleaned from public databases indicated that inter-individual sequence homogeneity of the cytb gene in L. dispar asiatica and L. dispar japonica was sufficient to yield discriminatory amplification; discrimination was here provided by a forward ARMS primer and an LNA probe (Fig. 1, alignment provided as an example; see also Fig. 3 under the “Bulk Triplex B” tab of Online Resource 1).
Bulk triplex C subassay
With respect to L. umbrosa, an analytical approach similar to the one described above for the selection of cytb pointed to ND1 as the most likely source of SNPs that would enable discrimination of this species from other taxa. As no L. umbrosa ND1 sequences other than the one we had reported (Djoumad et al. 2017) were available in public databases, inter-individual sequence stability was confirmed through the sequencing of this region from additional specimens. For this subassay, discrimination was provided by two ARMS primers and an LNA probe (see Fig. 2 under “Bulk Triplex C” tab of Online Resource 1).
Initial tests of the bulk assay using DNA dilution series
As a first assessment of the performance of the bulk assay, tests were conducted in both simplex and triplex formats, using DNA dilution series. For example, 1000, 100, 10 and 0 COI copies of L. albescens DNA were assayed alone or in combination with 1 million COI copies of L. dispar dispar DNA, generating dilution ratios of 1:103, 1:104, 1:105 and 0:106. Amplification curves observed in the presence of L. dispar dispar DNA were similar to those generated by L. albescens DNA alone, at all three non-zero dilutions tested (Fig. 2a; simplex format), indicating that this subassay could detect 1 L. albescens specimen against a background of 100,000 L. dispar dispar moths. No amplification was observed when 106COI copies of L. dispar dispar DNA were assayed alone, indicating that the primers and probe designed for this subassay are highly specific to L. albescens. Similar results were obtained in triplex mode (see Table 1 under “Bulk Triplex A” tab of Online Resource 1). The Bulk Triplex B subassay, targeting L. dispar asiatica and L. dispar japonica, provided complete discrimination against L. dispar dispar at a 1:1000 dilution (i.e., 103:106), but its performance gradually declined at higher dilutions (Fig. 2b; simplex format). Comparable results were obtained in triplex format as well as in tests involving alternative dilution series run in simplex format (see “Bulk Triplex B” tab of Online Resource 1). Finally, the Bulk Triplex C subassay, which targets L. umbrosa, showed a degree of sensitivity similar to that obtained with the Bulk Triplex A subassay (Fig. 2c; simplex format). Again, assay performance was equally good when run in triplex format (see Table 1 under the Bulk Triplex C tab of Online Resource 1).
To validate the present assay using DNA extracts from different moths (as opposed to varying proportions of DNA used, as in the above dilution series), we used DNA extracted from 100 L. dispar dispar legs (1 leg/moth), either alone or in combination with a leg from an AGM specimen (L. dispar asiatica, L. dispar japonica, L. albescens or L. umbrosa), resulting in a 1:100 AGM:EGM leg ratio. No amplification was observed for any of the four negative controls (L. dispar dispar alone, obtained from four different collection sites; 106COI copies), whereas each of the four test assays generated a positive amplification (Fig. 3; see also Online Resource 2). To determine whether a mixture of AGM taxa present in a given sample could be detected and identified in a single assay, three of the above DNA extracts were combined in equal aliquots, effectively diluting copy number for L. umbrosa, L. albescens and L. dispar asiatica by a factor of three. All three samples generated a species-specific, positive amplification (Online Resource 2).
DNA integrity in pheromone trap samples
DNA extracted from L. dispar dispar moths that were left in pheromone traps under field conditions for different periods of time, was assessed for its reliability in an assay such as the one reported here, using qPCR primers developed for EGM detection (Stewart et al. 2016). All of the samples at all of the time points, for both markers tested, yielded positive results for the presence of EGM (Table 5). Overall, the DNA appears to have remained in good condition over the 4 months the insects were left in the traps, as judged by the relative stability of the Ct values obtained for both COI and FS1 over time (Table 5). Nonetheless, a slight increase in variation in Ct values became apparent in months 3 and 4 (T3 and T4), with two samples showing significant shifts (T3-2, COI and FS1; T4-2, FS1; Table 5), suggesting the DNA in these moths had begun degrading at the time they were sampled, albeit not to a degree sufficient to jeopardize the assay. The greater COI:FS1 ratio recorded for these two samples (Table 5) also pointed to the higher stability of mitochondrial DNA, versus nuclear DNA, as predicted.
Detecting an extremely rare invasive species against a background of an abundant, already established close relative is akin to looking for a needle in a haystack. For example, networks of pheromone traps deployed for the detection of AGM can easily produce situations where an AGM individual, if caught, is greatly outnumbered by local EGMs. Unlike other molecular assays designed by others to detect a single species in a large background of another species (e.g., Zink et al. 2017, 2018), the assay reported here had to overcome the additional hurdle of distinguishing taxa within the AGM complex. To this end, we developed independent sets of qPCR primers and TaqMan probes for AGM species/subspecies, using SNPs identified earlier in three distinct mitochondrial genes (Djoumad et al. 2017). This approach enabled the development of a highly sensitive triplex TaqMan assay capable of detecting a single specimen of L. umbrosa or L. albescens (or L. postalba) in a background of up to 100,000 L. dispar dispar moths, and a single specimen of L. dispar asiatica or L. dispar japonica in a background of at least 1000 L. dispar dispar moths, based on DNA dilution series (Fig. 2). In the validation tests we conducted using DNA extracted from batches of moth legs, the above-mentioned AGM taxa were all easily detected when present in a 1:100 AGM:EGM leg ratio (Fig. 3), a proportion believed to be near the maximum to be ever processed operationally. Of course, given that DNA extraction efficiency for such samples may not be uniform among legs, the proportion of DNA from a single AGM leg could, by chance, be lower than that suggested by the 1:100 leg ratio. However, given the high sensitivity of this assay (≥ 1:1000 AGM:EGM, as indicated by the dilution series), the likelihood of a failed AGM detection is very low.
Our operational goal in developing this assay was quite different from the one we pursued in designing our earlier suite of TaqMan assays (Stewart et al. 2016), which targeted individual samples of immature stages of gypsy moths. In an effort to streamline the bulk assay, we did not attempt to identify species other than those considered members of the AGM complex. However, we looked for markers that would enable AGM discrimination against both EGM and other Lymantria species that could accidentally find their way into gypsy moth pheromone traps, including those considered “OTLS” (“other threatening Lymantria species”) in our earlier work (Stewart et al. 2016); it should be noted that these OTLS moths are morphologically distinguishable from AGM and EGM, although this is not true of all Lymantria species. In addition, we had to make sure that species discrimination, for the present assay, was provided by both primers and probes (as opposed to probe-only-based discrimination) so as to avoid situations where all DNAs in a given bulk sample are amplified evenly, resulting in the drowning of the signal produced by a probe annealing to low-abundance AGM-related DNAs.
Examples of other assays designed for the detection of invasive species in bulk pheromone trap samples include the one developed for the detection of the invasive noctuid Helicoverpa armigera among large numbers of the native congener H. zea (Zink et al. 2017), and another one that targets the silver Y moth, Autographa gamma, in a background of several closely related species (Zink et al. 2018). For these two assays, the authors opted for the use of a different, more recent PCR technology known as droplet digital PCR (ddPCR), largely because of its high reported sensitivity (Milbury et al. 2014). Although ddPCR clearly provided excellent performance for these two assays, the level of sensitivity we achieved in the present TaqMan qPCR assay is at least as good as that reported by this group (1:1000, Zink et al. 2017; 1:200, Zink et al. 2018). The qPCR TaqMan assay also has the advantage of requiring a type of thermocycler that is less expensive and more ubiquitous than the ddPCR equipment employed by Zink et al. (2017, 2018). In addition, the work involved in data analysis and interpretation for the present assay is simpler and more easily automated than it is for the ddPCR technology.
The results reported here for the cytb subassay (L. dispar asiatica/L. dispar japonica), point to the somewhat lower discriminatory power of this assay against L. dispar dispar as compared to the other two subassays (Fig. 2), albeit at a level that remains more than adequate (1:1000 AGM:EGM) for operational bulk processing. Several factors are likely involved in the collapse of the AGM-positive curve that we observe at dilutions > 1:1000. First, mitochondrial sequences of L. dispar dispar show greater overall similarity to those of L. dispar asiatica and L. dispar japonica than to those of L. umbrosa and L. albescens, resulting in slightly lower primer-based discrimination. Compounding this effect is the significantly larger amplicon generated by this subassay (240 bp) as compared to those produced by the other two subassays (100 and 127 bp; see Table 3). Nonetheless, although the primers specific to the L. dispar asiatica/L. dispar japonica taxon pair likely generate an amplicon in the presence of very high excess L. dispar dispar DNA, the specific LNA probe is not expected to efficiently anneal to it.
The mitochondrial genomes of L. dispar asiatica and L. dispar japonica display a strikingly high degree of sequence similarity (Djoumad et al. 2017), making it very difficult to design a TaqMan assay that could distinguish one subspecies from the other in the context of a procedure meant to process bulk samples. In addition, to keep the present assay simple (i.e., single tube multiplex qPCR), an ability to distinguish the two Asian subspecies would have required that we increase the assay’s multiplexing capability to four. For these reasons, we opted for the simpler taxon combination used here, with an understanding that, should any given trap sample generate a positive L. dispar asiatica/L. dispar japonica signal, the exact subspecies involved could subsequently be identified through an analysis of DNA extracts from individual moths using our earlier assay (Stewart et al. 2016).
Gypsy moth pheromone traps are typically emptied of their content only at the end of the trapping season. As a consequence, moths recovered at the end of the flight period may have spent up to 3–4 months in the field, exposed to environmental conditions that could be detrimental to DNA integrity. Given that compromised DNA quality could seriously jeopardize the reliability of the present bulk assay, we assessed moth DNA stability under field conditions, using L. dispar dispar moths as AGM surrogates. Our results point to a degree of DNA integrity that would be sufficient for the bulk assay to provide accurate species detection when run on moths that have spent up to 4 months in the field, at least under conditions similar to those tested here (Table 5; Online Resource 3). However, some of the samples collected in the second half of the experimental period displayed a somewhat delayed Ct relative to early samples, suggesting that their DNA may have begun to lose some of its initial quality. To avoid DNA degradation after field collection, we therefore recommend that samples be frozen until processed for species identification.
It is important to note that the present assay was designed to identify AGM specimens originating from their most likely sources when intercepted in North America, i.e., Japan, South Korea, eastern China and the Russian Far East. Indeed, given that our assay relies on mitochondrial markers, it will not detect specimens from central Asia if they possess an L. dispar dispar mitochondrial haplotype, even though their nuclear genomes and some of their biological traits (e.g., female flight capability) may display greater similarity to L. dispar asiatica than to L. dispar dispar, as earlier studies have suggested (Djoumad et al. 2017; Keena et al. 2008; Picq et al. 2018; Stewart et al. 2016; Wu et al. 2015). However, because countries/regions where populations showing this type of inter-subspecies introgression are relatively far from those mentioned above, the likelihood of such AGM-like hybrids finding their way to North America is currently low. Nonetheless, we are now conducting work aimed at identifying nuclear markers that could be added to our current panel and used to identify gypsy moths from central Asia.
Finally, it should be pointed out that, with the advent of three-channel portable qPCR devices, the assay described here could also be used for on-site screening of gypsy moth egg samples intercepted during ship inspections, whenever a rapid answer to the question “is this AGM?” may be required. Such samples could subsequently be re-processed using the Stewart et al. (2016) suite of assays for a more detailed analysis.
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We thank M. Keena (USDA Forest Service), S. Picq (Natural Resources Canada; NRCan), and D. Holden (Canadian Food Inspection Agency; CFIA) for providing specimens used in this study. We are also grateful to V. Nealis (NRCan), who brought to our attention the need for an AGM bulk assay. Finally, we thank J. Delisle, A. Labrecque and S. Picq (NRCan) for providing the weather data presented in the Online Resource 3. This work was funded by Genome Canada, Genome British Columbia, Genome Quebec, the Canadian Forest Service (Genomics Research and Development Initiative, GRDI) and the CFIA, through a Genomics Applications Partnership Program (GAPP 6102; Genome Canada) grant.
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Electronic supplementary material
Below is the link to the electronic supplementary material.
Details regarding primer and probe selection for each of the three subassays, and actual Ct values for each technical replicate of each qPCR analysis carried out for the dilution series experiment (XLSX 1347 kb)
Details regarding the validation tests, including actual Ct values for each technical replicate of each qPCR analysis conducted and data for an analysis involving the simultaneous detection of three AGM taxa (XLSX 909 kb)
Temperature (°C; in red) and relative humidity (%; in blue) for the period during which moths were left in pheromone traps under field conditions to assess integrity of their DNA over time. The thin lines represent temperature and relative humidity measured every 15 min. The bold lines represent cubic smoothing splines of temperature and relative humidity data to provide main trends. At the bottom of the graph, the grey bars indicate the lengths of time (T0 to T4) for which moths were held under field conditions; figures above each bar indicate the median temperature value and the median relative humidity value during the T length of time (PDF 517 kb)
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Stewart, D., Nisole, A., Djoumad, A. et al. A needle in a haystack: a multigene TaqMan assay for the detection of Asian gypsy moths in bulk pheromone trap samples. Biol Invasions 21, 1843–1856 (2019). https://doi.org/10.1007/s10530-019-01943-9