The natural distribution of the honeybee (Apis mellifera L.) has been changed by humans in recent decades to such an extent that the formerly widest-spread European subspecies, Apis mellifera mellifera, is threatened by extinction through introgression from highly divergent commercial strains in large tracts of its range. Conservation efforts for A. m. mellifera are underway in multiple European countries requiring reliable and cost-efficient molecular tools to identify purebred colonies. Here, we developed four ancestry-informative SNP assays for high sample throughput genotyping using the iPLEX Mass Array system. Our customized assays were tested on DNA from individual and pooled, haploid and diploid honeybee samples extracted from different tissues using a diverse range of protocols. The assays had a high genotyping success rate and yielded accurate genotypes. Performance assessed against whole-genome data showed that individual assays behaved well, although the most accurate introgression estimates were obtained for the four assays combined (117 SNPs). The best compromise between accuracy and genotyping costs was achieved when combining two assays (62 SNPs). We provide a ready-to-use cost-effective tool for accurate molecular identification and estimation of introgression levels to more effectively monitor and manage A. m. mellifera conservatories.
Pollination by the honeybee (Apis mellifera L.) is a blended ecosystem service of managed and unmanaged (feral or wild) colonies that is under threat from human-mediated environmental changes including climate change, habitat loss, habitat fragmentation, pesticides, and introduced parasites and pathogens1,2. There is growing evidence that management of locally adapted genetic diversity in honeybee subspecies and ecotypes is key to the long-term sustainability of this service3,4,5. Accordingly, actions towards preserving the large stores of genetic diversity held by the 31 honeybee subspecies6,7,8,9 are expected to counteract the trend of global colony losses.
Of the 31 subspecies that have been identified in the natural distributional range of A. mellifera in Africa, Middle East, Western Asia, and Europe6,9,10 there are 10 European subspecies grouped into two evolutionary lineages10: the Western and Northern European (lineage M) and the South-eastern European (lineage C). Lineage M includes only two subspecies: the Dark honeybee Apis mellifera mellifera and the Iberian honeybee Apis mellifera iberiensis. Yet, these two subspecies cover the largest territory in Europe with A. m. iberiensis occupying the Iberian Peninsula and A. m. mellifera ranging from France in the south to Scandinavia in the north, and from Ireland and the UK in the west to the Ural Mountains in the east10. Lineage C occurs in a smaller geographical area composed of the Apennine and Balkan peninsulas and includes the most widely kept honeybee subspecies: the Italian Apis mellifera ligustica and the Carniolan Apis mellifera carnica. In spite of its wide distribution, A. m. mellifera is the subspecies most under threat as it is considered extinct in many parts of Europe not only because of the human-mediated environmental changes but more insidiously through replacement by and introgression from non-indigenous subspecies, particularly A. m. ligustica and A. m. carnica11,12,13.
It has been argued that, unlike with other domesticated stock organisms, management and selective breeding in honeybees increase genetic diversity through introgression14. However, this form of admixture reduces the frequency of locally adapted gene complexes, leading to an increased likelihood of reduced survival rates of colonies15. How to protect locally adapted gene complexes that are more suited to local environments is a growing problem, as the increased breeding and movement of C-lineage honeybees promotes sympatry and gene flow between A. m. mellifera and imported commercial breeds. Efforts to assist conservation of A. m. mellifera are gathering momentum in multiple European countries (www.sicamm.org) and with the knowledge that reduced adapted genetic diversity threatens both managed and unmanaged populations, the interests of commercial beekeeping and honeybee conservationists should be aligning, particularly in A. m. mellifera indigenous areas.
An important first step in protecting A. m. mellifera populations in official or unofficial conservatories is to give the stakeholders an accurate and cost-efficient tool to test for C-lineage introgression. Microsatellites have been extensively used to examine C-lineage introgression in A. m. mellifera11,12,16. Yet, the numerous advantages of SNPs over microsatellites promise to make them the tool of choice for population monitoring and conservation purposes. In addition to being more abundant and widespread in the genome17, SNPs display lower genotyping error, have higher quality data, are more amenable to automated analysis and data interpretation, and can be easily transferred between laboratories18. Moreover, SNPs proved to be more powerful than microsatellites at estimating C-lineage introgression in A. m. mellifera19. These properties make SNPs a powerful tool for testing the breeding stock in A. m. mellifera conservatories and SNP data can be readily incorporated in shared genetic databases, facilitating implementation of a conservation strategy at the European scale.
Whilst SNP analysis on whole genome (WG) sequence data may be required in studies concerned with fine-scale relatedness, such deep sequencing is disproportionate when determining introgression levels for the discrimination of A. m. mellifera breeding stocks. Also, while costs have dropped dramatically, WG sequencing is still unaffordable for most stakeholders committed to the long-term sustainability and conservation of honeybees. Costs are accrued as WG analysis requires considerable computing storage and processing power and trained bioinformatics personnel. However, encouragingly, Muñoz, et al.20 showed that reduced panels of highly informative SNPs can accurately identify honeybee stocks20,21,22,23. Genotyping using reduced SNP panels considerably decreases laboratory processing costs. Furthermore, analysis of the generated genotypes requires low computational power and conventional bioinformatics skills.
Muñoz, et al.20 developed reduced SNP panels for genetic identification and introgression analysis in A. m. mellifera. The authors used a combination of metrics to rank by information content over 1183 SNPs that had been genotyped in A. m. mellifera, A. m. ligustica and A. m. carnica using the 1536-plex GoldenGate® Assay of Illumina13. The top-ranked SNPs were combined into five nested panels whose sizes (48, 96, 144, 192, 384 SNPs each20) fitted the plexes of the now discontinued GoldenGate® Assays formerly genotyped with the VeraCode® technology. Here, we built from the 144-SNP panel to propose four customized assays tailored for high sample throughput genotyping using the iPLEX MassARRAY system. By providing a ready-to-use molecular tool for accurately, rapidly, and cost-effectively genotyping large sample sizes of A. m. mellifera, we hope to bring affordable C-lineage introgression detection to stakeholders in the fight to safeguard remaining reservoirs of unique combinations of genes and adaptations in A. m. mellifera and to expand its reduced current distribution.
Assay design, quality control and genotyping accuracy
Of the 144 highly-informative SNPs selected by Muñoz, et al.20, the Assay Design software was able to multiplex 127 into four assays (identified by letter M), each containing a variable number of SNPs ranging from 38 in M1 to 24 in M4 (Supplementary Table S1). A total of 573 samples (Fig. 1) were genotyped for the four customized assays using the iPLEX MassARRAY system. Of the 573 samples, only seven displayed a SNP call failure rate >30% and these were excluded from further analysis (Supplementary Table S2). Of the 566 remaining samples, 551 displayed a low percentage (<10%) of missing data indicating a high genotyping success rate (96%).
The quality control and assessment of the genotyping accuracy of the 127 SNPs (Supplementary Table S3) led to identification of 10 problematic SNPs, of which seven were typed in <80% of the individuals, three were called heterozygous for >10% of the haploid individuals (Supplementary Tables S1 and S3), and three exhibited inconsistent calls among the three genotyping technologies in >5% of the individuals (Fig. 2). The latter SNPs were also identified as having high rates of missing data or heterozygosity (Supplementary Table S3). Once the 10 SNPs were removed from the datasets, the rates of missing data of the remaining 117 SNPs were low with 113 having <10% and four varying between 10.4% and 15.5% (Supplementary Table S1). The genotypes generated for the 117 high-quality SNPs in the MassARRAY platform were highly concordant with those of the Illumina’s platforms (99.9% for the BeadArray and 99.6% for the HiSeq. 2500). Following the quality control step, 339 of the 573 genotyped samples had no missing data and the highest rate of missing data was 29% but only in two samples (Supplementary Table S2).
The final multiplexes contained M1 = 34, M2 = 32, M3 = 28, and M4 = 23 SNPs distributed across the 16 honeybee linkage groups, LGs (Fig. 3 and Supplementary Tables S1 and S4). LG 2 harboured the highest number of SNPs (13) while LG 3 had the lowest (2). The number of LGs covered by the assays varied between 12 (M4) and 14 (M1). Most SNPs (90 of 117) are located in non-coding regions, including intergenic (50 SNPs), intronic (30 SNPs), and UTRs (10 SNPs). Of the 27 coding SNPs, only two (1384-est6107 and 661-AMB-00398036) are non-synonymous (Supplementary Table S1).
Assessing performance of the SNP assays
The performance of the four assays was assessed by comparing their Q-values (inferred from single or combined assays) with those inferred from the genome-wide SNPs, which provides the best estimate of the admixture proportions (Supplementary Table S5). The four assays exhibited a good individual performance with a mean accuracy >94% and Q-values highly correlated (0.980 ≤ r ≤ 0.983) with those inferred from the WG dataset (Table 1). The largest plex assay M1 (34 SNPs) and the smallest M4 (23 SNPs) showed the best and the worst behaviour, respectively, as indicated by most statistics (Table 1). The best performance was achieved when the four assays (117 SNPs) were used together (r = 0.996; mean accuracy = 97.84%; absolute precision error = 0.033), although the combination of M1 + M3 (62 SNPs) and M1 + M2 + M3 (94 SNPs) with the highest individual correlations produced equally interesting statistics with mean accuracies >96.9%, absolute precision error <0.04, and with over 28 individuals (out of 32) with absolute accuracy error <0.05. Performance was also assessed by counting purebred A. m. mellifera individuals misclassified as admixed (Q-values > 0.05) and vice versa (Table 1). Except for M4, single assays and their combinations repeatedly misclassified two or three (always identified amongst individuals M23, M24, M25, and M26; Supplementary Table S5) purebred as admixed from 11 A. m. mellifera individuals identified by genome-wide SNPs. The degree of A. m. mellifera misclassification was lower for the class “admixed identified as purebred” with M3, and its combination with one (M1), two (M1 + M2) or three assays (M1 + M2 + M4) correctly identifying all 16 admixed individuals (0.05 < Q-value < 0.95).
Validating the SNP assays
The assays were validated using an independent set of 62 individuals, including 30 A. m. mellifera, 16 A. m. carnica, and 16 F1 hybrids. On average, Q-values inferred from the genotypes called using the four individual (M1, M2, M3, M4) and three combined assays (M1 + M3, M1 + M2 + M3, M1 + M2 + M3 + M4) fit the thresholds defined for the two subspecies and hybrids (P-value ≥ 0.18, Mann-Whitney test; Supplementary Table S6). Despite good overall performance of the individual assays, a few purebred A. m. mellifera and A. m. carnica were misclassified as admixed (estimated Q-values deviated from thresholds of <0.05 for A. m. mellifera and >0.95 for A. m. carnica) when the Q-values were inferred from called genotypes. However, when mixed combinations of the four assays were employed, the estimated Q-values matched the expectations with all A. m. mellifera and A. m. carnica correctly classified as purebred (Fig. 4a,b) and the F1 hybrids varying between 0.52 ± 0.04 (mean ± SD), for M1 + M3, and 0.56 ± 0.03, for the four assays combined, with the slight bias toward the A. m. carnica in the F1 (Fig. 4c) reflecting the known low level of C-derived introgression in the Læsø source population13.
Assessing sensitivity of the MassARRAY system in pooled DNA
The sensitivity of the MassARRAY system in detecting A. m. ligustica was assessed in pools combining the DNA of two haploid individuals (one A. m. mellifera and one A. m. ligustica) at five dilution ratios. Of the 117 SNPs, only 103 were informative in this experiment (five were monomorphic, and nine were bi-allelic, but only one allele was called across dilutions). As expected, the sensitivity decreased as the dilution ratios increased, with only 29 unlinked SNPs being able to detect the A. m. ligustica alleles in every dilution and replicate (Supplementary Fig. S1, Supplementary Information). Yet, it was still possible to detect introgression with either the four assays (117 SNPs) or the two assays M1 + M3 (62 SNPs), even when the A. m. ligustica DNA was as diluted as 1:20 (Fig. 5 and Supplementary Table S7).
Assessing sensitivity of the MassARRAY system in pooled tissue
The sensitivity of the MassARRAY was further assessed in 22 tissue pools. Of the 2,574 called genotypes (117 SNP loci × 22 pools), 1,977 (77%) were accurate, as determined by comparing the calls for single workers with those of the pools. The most common sources of mismatch were “the most frequent allele” and “higher DNA concentration” (Table 2). The average rate of accurately called SNPs per pool was high (77%, 90 SNPs) and varied between 83% (97 SNPs), for the pools of two workers, and 50% (58 SNPs), for the pools of eight workers (Table 3).
The Q-values estimated for the 22 pools from the called genotypes were similar to those estimated from the expected genotypes using either the four assays, M1 + M3, or the 29 SNPs (P-value ≥ 0.35, Mann-Whitney test). Furthermore, the MassARRAY platform was able to detect low frequency alleles, either of M-lineage (pools containing A. m. mellifera) or C-lineage ancestry (pools containing A. m. carnica or Buckfast), even when the tissue dilution was as low as 1:7 (Supplementary Table S8).
Applying the SNP assays
The four assays were applied to 478 colonies of various ancestries, represented by single (431 colonies) or pooled individuals (47 colonies), collected in 13 European countries (Fig. 1). The Q-values estimated for each A. m. mellifera colony (Fig. 6a), indicated that introgression varies throughout Europe, ranging on average from 0.0 in Norway to 0.447 ± 0.265 in Wales (Supplementary Table S9). The least introgressed A. m. mellifera colonies were from conservatories of Norway (0 ± 0.000), Scotland (0.006 ± 0.011) and Netherlands (0.046 ± 0.141) with over 80% of the individuals showing a Q-value < 0.05, although most individuals (91%) of the unprotected populations of Ireland were also very pure (0.021 ± 0.022). Populations of Denmark, France and Switzerland exhibited greater Q-values (0.148 ≤ Q-value ≤ 0.280) in both protected and unprotected populations with ≤11% of pure individuals. Admixture proportions estimated for A. m. ligustica and A. m. carnica sampled from native and introduced ranges showed that they are very pure (0.972 ≤ Q-value ≤ 1.000), excepting for some Swiss colonies (0.750 ± 0.296). The commercial breed Buckfast was mostly of C-derived ancestry (0.806 ± 0.055).
The genotype data were further examined by network analysis. The correlation network graph shown in Fig. 6b consisted of 5,522 edges and 418 nodes (samples). Samples with similar allele profiles clustered together. In total, three clusters were identified with cluster 1 containing 342 nodes (highest similarity to M-lineage), cluster 2 containing 58 nodes (highest similarity to C-lineage) and cluster 3 containing 18 nodes (highest rates of introgression). All samples from Norway, Ireland, Netherlands and Belgium were in cluster 1 whilst all samples from Italy, Croatia and Serbia were in cluster 2. Of 70 samples from Scotland, 61 samples were in cluster 1, 6 in cluster 2 and only 2 in cluster 3; a similar distribution was seen for samples from France and Switzerland. Samples from England, Denmark and Wales were also predominantly found in cluster 1.
The admixture patterns were also examined in pooled individuals representing an independent set of 47 colony samples from Switzerland and the UK (Supplementary Table S10). The average Q-values estimated for the Swiss samples of A. m. mellifera varied between 0.145 ± 0.074 (protected) and 0.118 ± 0.042 (unprotected), which were lower than those inferred from a single individual (Supplementary Table S9). However, these estimates are not directly comparable as the pooled- and single-individual samples were from different apiaries. More comparable results were obtained for four colonies of variable ancestry from the UK that were simultaneously represented by a single worker and a pool of 16 workers. The Q-values inferred for each colony from the single worker and the pools were similar but always lower for the latter (Supplementary Table S10), a pattern that was also observed in the Swiss samples. This is an interesting finding that deserves to be fully investigated in a larger sample size.
The success of the numerous initiatives that are developing across Europe to protect and bring back the endangered dark honeybee rely on molecular tools capable of accurately detecting varying levels of C-derived introgression in a time- and cost-effective manner. In many conservation programs, the breeding stock has been routinely identified through wing morphometry and, more recently, through microsatellites24. However, inferring from data on Africanized honeybees25, wing morphometry is likely unable to detect low levels of C-lineage introgression into A. m. mellifera, a limitation that is overcome by microsatellites11,12. While adoption of microsatellites represented a major step in conservation management of A. m. mellifera12, it has been shown that a reduced number of high-graded SNPs20, outperform the multiallelic marker in estimating introgression19,26.
Here, from the 144 top-ranked SNPs, selected by their power in discriminating C- from M-lineage honeybees20, we designed, tested and validated four assays for genotyping with the iPLEX MassARRAY system. We provide the genomic information along with the PCR and iPLEX primers for 117 high-quality SNPs multiplexed in the four assays for immediate application in genetic surveys and conservation management of A. m. mellifera. In addition, we provide the dataset with the genotypes for haploid and diploid individuals of A. m. mellifera, A. m. carnica and A. m. ligustica, which can be used by others in introgression analysis as baseline reference populations with no need for inter-laboratory calibration18. As opposed to microsatellites, merging of SNP databases is straightforward as there are only two alleles per locus and different platforms will provide the same allele calls. If needed, curation will only involve SNP conversion from different platforms to be on the same DNA strand, which is much simpler than trying to harmonize different microsatellite allele sizes genotyped in different laboratories.
We show that C-lineage introgression can be accurately estimated from haploid, diploid, and combined haploid and diploid datasets (see Supplementary Information for details). These findings indicate that honeybee conservation managers can choose the software of their preference and, more importantly, can simultaneously analyse workers and drones without biasing estimates of C-lineage introgression in A. m. mellifera colonies.
The Assay Design software was able to combine only 127 of the 144 high-graded SNPs20 into four multiplexes. While the iPLEX protocol allows multiplexing up to 40 SNPs, only assay M1 (38 SNPs) approached the maximum plexing capacity. This is in part due to the relatively small size of the baseline SNP set from which the Assay Design had to work. However, the plex level of each assay can be expanded any time. By using the Replex option of the software, additional high-graded nuclear SNPs or even mitochondrial SNPs can be added to the customized four assays for detecting C-derived genes at both genetic compartments.
The iPLEX MassARRAY system revealed highly accurate and delivered high-quality calls for 117 of the 127 SNPs. Quality assessment was greatly facilitated by the honeybee haplodiploid system. Using the SNP calls of the drone subset, problematic SNPs were easily detected by locating genotypes erroneously typed heterozygous. Three such SNPs were consistently identified in numerous drones. While the mechanism responsible for the false allele is unclear, it is possible that gene homology is the source of miscalling at least in locus 1379-est5929. Using the 120-bp flanking region of this SNP locus, a NCBI query found a second hit with 98% similarity in the honeybee genome. The 117 SNPs were successfully genotyped in over 96% of the samples, indicating that the customized four assays and the iPLEX MassARRAY system work well in DNAs obtained from a variety of tissues with the virtually full spectrum of extraction methods routinely employed in honeybee research27.
The four combined SNP assays were able to estimate introgression with a high degree of accuracy. However, performance decreased to some extent when SNP assays were used singly and the 23-plex M4 showed the worst behaviour for most statistics. This finding is consistent with studies on other organisms which have also detected drops in accuracy when the number of SNPs is <2528,29. Further assessment of the four assays (used singly or combined) at the individual level indicates that there is a greater chance of misclassifying purebred individuals as admixed than the reverse, viz. misclassifying admixed individuals as purebred. This result has practical implications in conservation management suggesting that it is more likely that A. m. mellifera genetic diversity is erroneously discarded from the breeding population than C-derived genes are maintained. At this point, simulation and empirical studies are needed to determine the best threshold criterion to separate purebreds from admixed individuals30. While the stringent Q-value threshold of <0.05 arbitrarily established here for defining purebred A. m. mellifera may assure a more efficient purging of C-derived alleles, it may also lead to erosion of A. m. mellifera diversity and loss of unique gene complexes. The problem is that low diversity is particularly detrimental for honeybees because it may decrease colony resistance to brood diseases31 and increase genetic load at the sex locus32. Therefore, managers of A. m. mellifera conservatories need to make a trade-off between purging foreign alleles from the breeding population while minimizing the effects of reduced diversity.
Validation of the four SNP assays in an independent set of individuals, including F1 hybrids (obtained from controlled crosses purposely established for this study, as opposed to the simulated hybrids more commonly found in the literature), further confirms the resolution power of our customized SNP assays. Interestingly, the Q-values obtained for the F1 hybrids were in close proximity to the expected 0.50, although there was a bias towards C-derived genes as most Q-values were >0.50. When used singly, the SNP assays failed to correctly identify all purebred individuals and the Q-values were more dispersed around 0.50. However, when the assays were combined, the performance increased with all purebred individuals correctly classified and the Q-values showing a lower dispersion around 0.50. Interestingly, despite the lower number of SNPs contained in M1 + M3 (62 vs 117), this assay combination shows an overall performance similar to that of M1 + M2 + M3 + M4.
Sustainable conservation management requires tools capable of reliably identifying breeding colonies in a time- and cost-efficient manner. The SNP assays tested herein have a high resolution power for accurately estimating introgression, and the iPLEX MassARRAY system offers an interesting option for rapid and cost-effective genotyping. This system is very flexible and scalable allowing a variety of options for sample and assay throughput at a variable cost, depending on the chip format (24, 96, or 384) chosen. The 384 format, for example, allows genotyping 384 samples with a single assay at an approximate outsourced cost of 4.5€ per sample. Alternatively, this format could be used to genotype 192, 128, or 96 samples with two, three, or four assays, respectively. This option would incur in an increment of 4.5€ for any additional assay. Based on overall results, the best compromise between genotyping costs and assay accuracy is achieved when using M1 + M3.
Genotyping a single microsatellite multiplex in a 96-plate format costs approximately 2.5€ per sample. Introgression proportions using microsatellites has typically been estimated from over 11 loci, which requires genotyping a minimum of two multiplexes11,24,26,33 thereby doubling the per-sample cost. However, this charge does not include PCR and microsatellite fragment analysis. Contrary to microsatellites, outsourced SNP genotyping with the iPLEX MassArray system only requires DNA (instead of PCR products) to generate a table of genotypes ready to analyse, avoiding the hurdle of fragment analysis.
Honeybee queens mate in flight with up to 20 drones34. This means that in areas where A. m. mellifera and commercial colonies are sympatric, matings may occur with drones of C-lineage ancestry originating colonies made up of subfamilies with diverse genetic backgrounds. Although population-level studies typically require genotyping a single worker per colony16, colony-level introgression estimates may require genotyping several individuals to more effectively capture the colony structure. The problem is that genotyping several workers per colony is time consuming and costly. An economical way to circumvent this issue is to genotype pools instead of individuals35, provided that the genotyping system of choice is sensitive enough to detect low-frequency alleles.
Here, we assessed whether our customized SNPs assays and the iPLEX MassARRAY system offer a reliable alternative for pool genotyping. Both DNA and tissue pooling experiments show that the genotyping system is very sensitive as it was able to detect low frequency alleles. Despite the small number of SNPs showing consistent amplification across experiments, introgression analysis indicates that as few as 62 SNPs (M1 + M3) were able to detect highly diluted C-derived alleles. These results suggest that this system has the potential to detect C-lineage introgression in colonies with hybrid sub-families at low frequency, a scenario that might occur if drones of commercial colonies are able to accidentally enter congregation areas of conservatories.
Analysis of pool genotypes showed that miscalling was mainly due to the unequal contribution of each individual (different concentrations) and to the unbiased representation of allelic products that are present in a DNA pool, both common problems reported for DNA pools35,36. While pools constructed from equi-molar DNA concentrations would be the most correct approach to genotype a colony, pooling tissues is often the only option in conservation programs requiring screening of numerous colonies with a limited budget. Pooling tissue instead of DNA requires less time, effort and money during preparation in the laboratory and still enables detection of C-derived alleles even when most of the individuals in the pool are A. m. mellifera.
The introgression analysis on the samples collected throughout Europe and genotyped using the four SNP assays and the iPLEX MassARRAY system provides a rough picture of the genetic integrity of A. m. mellifera. This SNP survey adds to Pinto, et al.13 by expanding the sampling in France, Switzerland, UK and by including de novo Wales and Ireland. Concordant with earlier microsatellite11,12 and SNP13,21 surveys, C-lineage introgression in A. m. mellifera is heterogeneous across Europe. Samples originating from conservatories were generally less introgressed than those from unprotected areas. Our previous and this SNP survey revealed that Scotland, Norway, Netherlands and now Ireland possess important pockets of pure A. m. mellifera. Ireland represents a particularly interesting case of A. m. mellifera diversity because, contrary to the other countries, the survey was performed in unprotected populations from a wide geographical area.
As this and previous studies11,12,13,21 represent only partial, and in some cases biased, assessments on the status of the genetic integrity of A. m. mellifera across its distributional range, this novel tool now makes it possible to perform a comprehensive genetic survey in a time- and cost-efficient manner. We suggest that if the efficacy of this SNP tool is generally agreed among stakeholders the next step is for them to seek input from government agencies and/or research facilities and begin to describe the purity of their honeybee populations on as wide a geographic area as possible in order that conservation efforts correctly and efficiently target regions of greatest concern and greatest possible reward.
Muñoz, et al.20 identified 144 highly informative SNPs for estimating C-lineage introgression in A. m. mellifera. The flanking regions (60 bp of either side) of these SNPs were used to design multiplexed assays with the software Assay Design 4.0 (Agena BioScienceTM) for genotyping using the Agena BioScience iPLEX chemistry and the MassARRAY® MALDI-TOF platform (hereafter abbreviated to iPLEX MassARRAY). The software searched for optimal areas within the 120-bp flanking regions to design forward and reverse PCR primers while constructing the different multiplexes. The maximum multiplexing capacity (40 SNPs) allowed by the iPLEX chemistry was attempted whilst preventing hairpin and dimer formation. In addition to the PCR primers, the software designed the iPLEX extension primer placed immediately adjacent to each SNP. Of the 144 SNPs, the Assay Design was able to combine 127 SNPs distributed along four multiplexed assays (see Supplementary Table S1 for sequences of the flanking regions, sequences of PCR and iPLEX reaction primers, and composition of the four multiplexes). The putative functional role of the genes marked by each SNP was identified using SNPeff 4.3 tool build37 and the NCBI Apis mellifera annotation genome version 10238.
A wide array of analyses were carried out to validate the SNP assays and to assess (i) their accuracy when genotyped with the MassARRAY system, (ii) their performance when employed individually or combined, (iii) and their sensitivity when employed in pools of DNA and tissue. To that end, different combinations of samples, representing single and pooled, haploid and diploid individuals were used, as depicted in Fig. 2 and detailed in each section below.
Samples and DNA extraction
A total of 464 colonies (represented by a single haploid drone, a single diploid worker, multiple workers, or pools of drones or workers; Supplementary Table S2) were sampled across Europe (Fig. 1). The samples originated from colonies in the (i) A. m. mellifera (N = 462) native range in Western and Northern Europe (protected and unprotected areas), (ii) A. m. ligustica (N = 10), and A. m. carnica native ranges (N = 10) in South-eastern Europe, (iii) introduced range of A. m. carnica in Switzerland (N = 8), Germany (Kirchhain; N = 16) and Scotland (N = 3), (iv) commercial strain Buckfast from Switzerland, Scotland, and Denmark (N = 11), and (v) F1 hybrid crosses performed in isolated mating stations in Denmark (N = 19). Nine samples of A. m. carnica and seven A. m. ligustica, previously genotyped using the GoldenGate® Assay in the BeadArray platform of Illumina13, were added to the dataset to have a better representation of C-lineage.
Genomic DNA was extracted from the head, antennae, thorax (entire or ~half), legs, or abdomen of adults or immatures (larvae or pupae) of a single individual, multiple individuals (extracted, then pooled), or a pool of individuals (mixed tissue, then extracted) per colony in 561 samples (Supplementary Table S2). The extraction methods included phenol-chloroform, CTAB, commercial kits (Qiagen EZ1 DNA tissue kit, Omega bio-tek EZNA kit), and magnetic beads using the KingFisher™ Flex Purification System. These represent the wide array of tissues and extraction methods commonly used in honeybee research27. The DNA samples were set at a concentration of 10–15 ng/µl and sent to Instituto Gulbenkian de Ciência (Portugal) for SNP genotyping.
SNP genotyping and quality control
A total of 573 samples (561 plus 12 DNA pools, Supplementary Table S2) were genotyped for the 127 SNP loci multiplexed in the four assays using the iPLEX chemistry and the MassARRAY® MALDI-TOF genotyping platform39. The genotypes generated for the 573 samples (Supplementary Table S11) were subjected to quality control filters to discard SNP loci and samples with poor or inconsistent amplification. SNPs and samples with missing data >20% (Supplementary Table S1) and >30% (Supplementary Table S2), respectively, were excluded from the dataset (Supplementary Table S3).
Assessing genotyping accuracy
The genotyping accuracy was assessed on the subset of single haploid drones of A. m. mellifera (N = 103), A. m. ligustica (N = 10) and A. m. carnica (N = 15), by (i) identifying the heterozygous SNP loci (N = 128; Fig. 2 and Supplementary Table S2) and (ii) comparing the SNP calls generated for a variable number of individuals by the iPLEX MassARRAY system with those obtained with the GoldenGate® Assay genotyped in the BeadArray platform of Illumina (N = 96 individuals13) and with the HiSeq. 2500 platform of Illumina (N = 32 individuals; see whole-genome sequencing details in Parejo, et al.21 and Henriques, et al.40). The SNP loci that were called heterozygous by the MassARRAY system in >10% of the drones and showed inconsistent genotypes between at least two genotyping technologies in >5% of the drones were excluded from further analysis (Supplementary Tables S1 and S3).
Introgression proportions (Q-values) were estimated by ADMIXTURE41 using datasets of varying ploidies (haploids, diploid, and their combination), which produced similar Q-values (see Supplementary Information for details). Q-values were estimated for K = 2 using 10,000 iterations in 20 independent runs. The convergence between iterations was monitored by comparing log-likelihood scores (LLS) using the default termination criterion set to stop when LLS increases by <0.0001 between iterations. CLUMPAK42 was used to summarize and visualize the Q-plots.
Assessing performance of the SNP assays
The performance of the SNP assays in estimating C-lineage introgression in A. m. mellifera was assessed by comparing the Q-values inferred by them with those inferred from 2.399 million SNPs identified in WGs (see Parejo, et al.21 and Henriques, et al.40 for further details). A total of 38 drones (4 A. m. ligustica, 7 A. m. carnica, 11 purebred A. m. mellifera, and 16 admixed A. m. mellifera), for which there were WG sequence data available, was used in this comparison (Fig. 2). The 4 A. m. ligustica and 2 of the 7 A. m. carnica previously genotyped using the GoldenGate® Assay13 were added to this step for a better representation of lineage C. The performance of the four assays (individually or combined) was assessed by (i) Pearson’s correlation coefficient (r), (ii) similarity score obtained by CLUMPAK, (iii) absolute accuracy error calculated as the absolute difference between Q-values inferred from the SNP assays and the 2.399 million SNPs, (iv) mean accuracy calculated via percentage of absolute error, (v) absolute precision error calculated via standard deviation of the absolute differences, (vi) number of purebred individuals classified as admixed, and (vii) number of admixed individuals classified as purebred. Admixed individuals were defined by a threshold Q-value > 0.05. Any individual with Q-value between 0 and <0.05 or >0.95 and 1 was classified as purebred A. m. mellifera and C-lineage (A. m.carnica or A. m. ligustica), respectively.
Validating the SNP assays
The four assays were validated and tested using an independent subset of 62 workers, including 30 A. m. mellifera (Endelave, Denmark), 16 A. m. carnica (Kirchhain, Germany), and 16 F1 hybrids obtained from crosses between A. m. mellifera queens, from the conservatory in Læsø, and A. m. carnica drones from Mandø, Denmark (Fig. 2 and Supplementary Table S12). The crosses were performed in the isolated mating station of Mandø in 2016. Q-values were inferred from the four assays (individually or combined) by ADMIXTURE and then compared with the defined thresholds of >0.95 for A. m. carnica, <0.05 for A. m. mellifera, and ~0.5 for the F1 hybrids.
Assessing sensitivity of the MassARRAY system in pooled DNA
Pools of tissue or DNA are a cost-efficient option for estimating introgression in organisms with a polyandrous mating system like the honeybee. However, pooling can only be adopted if the genotyping system is able to consistently detect low-frequency alleles. The sensitivity of the MassARRAY system was assessed in a dilution experiment of varying ratios of DNAs of two haploid drones: one A. m. ligustica and one A. m. mellifera (Fig. 2). The two drones displayed the highest number of alternate alleles for the 127 highly-informative SNPs identified in a large dataset previously genotyped with the GoldenGate® Assay13.
The experiment was performed by pooling the DNA of the two drones using volume ratios of 10:20, 5:20, 2:20, 1:20, and 0.5:20 A. m. ligustica to A. m. mellifera (Fig. 2). The number of replicates was three for 1:20 and 0.5:20 and two for the remaining ratios, as they were nested in the higher dilution factors. The pools were genotyped for the four assays using the iPLEX MassARRAY. The genotypes generated from the pooled DNAs were compared with those expected and the number of mismatches was recorded. The expected genotypes of the pools were inferred from the SNP calls for the single drones.
The sensitivity of the genotyping system in detecting C-lineage ancestry in the pooled samples was also assessed via introgression analysis. The Q-values were estimated by ADMIXTURE for each DNA pool using the expected and called genotypes for a variable number of SNPs (four assays and best assay combination, as defined by r).
Assessing sensitivity of the MassARRAY system in pooled tissue
The sensitivity of the MassARRAY system was further assessed in tissue pools (Supplementary Table S12). A total of 22 pools were constructed using varying ratios of workers (1:1, 1:2, 1:3, 1:7) of two different ancestries chosen among A. m. mellifera (N = 30), A. m. carnica (N = 16), Buckfast (N = 3), and F1 hybrids (A. m. mellifera queens x A. m. carnica drones; N = 19), as detailed in Fig. 2 and Supplementary Table S13. The DNA was extracted twice (individually and pooled) from the thorax, which had been cut in two identical portions. The DNA concentrations of individual and pooled extractions were measured using NanoDropTM (Supplementary Table S12).
The sensitivity of the genotyping system was first assessed by comparing the SNP calls obtained for the single workers with those obtained for the pools of workers. Mismatches were counted and the error identified among the following sources: (i) pools displayed alleles uncalled in single workers and vice versa, (ii) SNP calls of the pools matched those of the worker with higher DNA concentration, (iii) SNP calls of the pools matched the most frequent allele, and (iv) the least frequent allele. The sensitivity of the genotyping system in detecting C-lineage ancestry in the different pools was also assessed via introgression analysis. The Q-values were estimated for the 22 pools from the expected and called genotypes, for a variable number of SNPs (four assays and best assay combination), using ADMIXTURE. The expected genotypes were inferred from the calls obtained for the single workers.
Applying the SNP assays
The four assays were used to genotype in the MassARRAY platform 462 samples representing A. m. mellifera (N = 425), A. m. ligustica (N = 10), A. m. carnica (N = 21), and Buckfast (N = 6) from 8 13 European countries (Figs 1 and 2). Samples of A. m. mellifera originated from protected (N = 125) and unprotected (N = 300) areas. Of the 462 samples, 415 were represented by a single individual and 47 by pooled individuals (16 pooled workers from colonies of A. m. mellifera, A. m. carnica and Buckfast; 30 pooled drones from colonies of A. m. mellifera; Supplementary Table S2). Additionally, a subset of four colonies (two A. m. mellifera, one A. m. carnica, and one Buckfast) from Scotland and England was represented by both a pool of 16 workers and one individual worker. For a better C-lineage representation, nine samples of A. m. carnica and 7 of A. m. ligustica (each representing a single individual and colony), previously genotyped using the GoldenGate® Assay13, were added to the dataset. Q-values were inferred from the genotypes of single and pooled samples using ADMIXTURE.
The genotype data were further examined by network analysis using the software Graphia Professional (Kajeka Ltd, Edinburgh, UK). For each sample, SNPs were scored 0 when same as reference (A. m. carnica), 1 for heterozygous and 2 for homozygous different to reference, i.e. representing the A. m. mellifera allele. Where data was missing, the SNP was scored 1.01. For ease of interpretation, the total combined score for each SNP in each sample was calculated and the SNPs reordered from the smallest score to the largest. The SNP data and associated sample metadata was loaded into Graphia and a Pearson correlation matrix was calculated comparing the profile of SNP scores for each sample. A network graph was then constructed by connecting the nodes (samples) with edges (where the correlation exceeded the threshold value r > 0.27). Utilising the overlay of metadata the graph was then explored and clustered using the Markov Cluster (MCL) algorithm43 at an inflation value (which determines cluster granularity) of 1.2.
A. m. carnica and A. m. mellifera whole-genome sequence data is deposited at the ENA (www.ebi.ac.uk/ena) under study accession number PRJEB16533.
Potts, S. G. et al. Global pollinator declines: trends, impacts and drivers. Trends in Ecology & Evolution 25, 345–353, https://doi.org/10.1016/j.tree.2010.01.007 (2010).
van Engelsdorp, D. & Meixner, M. D. A historical review of managed honeybee populations in Europe and the United States and the factors that may affect them. Journal of Invertebrate Pathology 103(Supplement), S80–S95, https://doi.org/10.1016/j.jip.2009.06.011 (2010).
Büchler, R. et al. The influence of genetic origin and its interaction with environmental effects on the survival of Apis mellifera L. colonies in Europe. Journal of Apicultural Research 53, 205–214 (2014).
Meixner, M. D. et al. Occurrence of parasites and pathogens in honeybee colonies used in a European genotype-environment interactions experiment. Journal of Apicultural Research 53, 215–229 (2014).
Meixner, M. D., Kryger, P. & Costa, C. Effects of genotype, environment, and their interactions on honeybee health in Europe. Current Opinion in Insect Science 10, 177–184, https://doi.org/10.1016/j.cois.2015.05.010 (2015).
Chen, C. et al. Genomic analyses reveal demographic history and temperate adaptation of the newly discovered honeybee subspecies Apis mellifera sinisxinyuan n. ssp. Molecular biology and evolution 33, 1337–1348 (2016).
Engel, M. S. The taxonomy of recent and fossil honeybees (Hymenoptera: Apidae; Apis). Journal of Hymenoptera Research 8 (1999).
Meixner, M. D., Leta, M. A., Koeniger, N. & Fuchs, S. The honeybees of Ethiopia represent a new subspecies of Apis mellifera- Apis mellifera simensis n. ssp. Apidologie 42, 425–437, https://doi.org/10.1007/s13592-011-0007-y (2011).
Sheppard, W. S. & Meixner, M. D. Apis mellifera pomonella, a new honeybee subspecies from Central Asia. Apidologie 34, 367–375, https://doi.org/10.1051/apido:2003037 (2003).
Ruttner, F. Biogeography and Taxonomy of Honeybees 165–257 (Springer-Verlag, 1988).
Jensen, A. B., Palmer, K. A., Boomsma, J. J. & Pedersen, B. V. Varying degrees of Apis mellifera ligustica introgression in protected populations of the black honeybee, Apis mellifera mellifera, in northwest Europe. Molecular Ecology 14, 93–106 (2005).
Soland-Reckeweg, G., Heckel, G., Neumann, P., Fluri, P. & Excoffier, L. Gene flow in admixed populations and implications for the conservation of the Western honeybee. Apis mellifera. Journal of Insect Conservation 13, 317, https://doi.org/10.1007/s10841-008-9175-0 (2008).
Pinto, M. A. et al. Genetic integrity of the Dark European honeybee (Apis mellifera mellifera) from protected populations: a genome-wide assessment using SNPs and mtDNA sequence data. Journal of Apicultural Research 53, 269–278, https://doi.org/10.3896/ibra.1.53.2.08 (2014).
Harpur, B. A., Minaei, S., Kent, C. F. & Zayed, A. Management increases genetic diversity of honeybees via admixture. Molecular Ecology 21(4414–4421), 1365–4294X (2012).
De la Rúa, P. et al. Conserving genetic diversity in the honeybee: Comments on Harpur et al. (2012). Molecular Ecology 22, 3208–3210, https://doi.org/10.1111/mec.12333 (2013).
Meixner, M. D. et al. Standard methods for characterising subspecies and ecotypes of Apis mellifera. Journal of Apicultural Research 52, 1–28 (2013).
Weinstock, G. M. et al. Insights into social insects from the genome of the honeybee Apis mellifera. Nature 443, 931–949, https://doi.org/10.1038/nature05260 (2006).
Vignal, A., Milan, D., SanCristobal, M. & Eggen, A. A review on SNP and other types of molecular markers and their use in animal genetics. Genetics Selection Evolution 34, 275 (2002).
Muñoz, I. et al. SNPs selected by information content outperform randomly selected microsatellite loci for delineating genetic identification and introgression in the endangered dark European honeybee (Apis mellifera mellifera). Molecular Ecology Resources 17, 783–795 (2017).
Muñoz, I. et al. Reduced SNP panels for genetic identification and introgression analysis in the dark honeybee (Apis mellifera mellifera). Plos One 10, e0124365, https://doi.org/10.1371/journal.pone.0124365 (2015).
Parejo, M. et al. Using Whole-Genome Sequence information to foster conservation efforts for the european dark honeybee, Apis mellifera mellifera. Frontiers in Ecology and Evolution 4, https://doi.org/10.3389/fevo.2016.00140 (2016).
Chapman, N. C. et al. A SNP test to identify Africanized honeybees via proportion of ‘African’ ancestry. Molecular Ecology Resources 15, 1346–1355, https://doi.org/10.1111/1755-0998.12411 (2015).
Chapman, N. C. et al. An abbreviated SNP panel for ancestry assignment of honeybees (Apis mellifera). Apidologie 48, 776–783 (2017).
Bouga, M. et al. A review of methods for discrimination of honeybee populations as applied to European beekeeping. Journal of Apicultural Research 50, 51–84, https://doi.org/10.3896/ibra.1.50.1.06 (2011).
Guzmán-Novoa, E., Page, R. E. Jr. & Fondrk, M. K. Morphometric techniques do not detect intermediate and low levels of Africanization in honey bee (Hymenoptera: Apidae) colonies. Annals of the Entomological Society of America 87, 507–515 (1994).
Parejo, M., Henriques, D., Pinto, M. A., S.-R., G. & Neuditschkoa, M. Empirical comparison of microsatellite and SNP markers to estimate introgression in Apis mellifera mellifera. Journal of Apicultural Research accepted (2018).
Evans, J. D. et al. Standard methods for molecular research in Apis mellifera. Journal of Apicultural Research 52, 1–54 (2013).
Wilkinson, S. et al. Development of a genetic tool for product regulation in the diverse British pig breed market. BMC Genomics 13, 580 (2012).
Storer, C. G. et al. Rank and order: evaluating the performance of SNPs for individual assignment in a non-model organism. Plos One 7, e49018 (2012).
Vähä, J. P. & Primmer, C. R. Efficiency of model‐based Bayesian methods for detecting hybrid individuals under different hybridization scenarios and with different numbers of loci. Molecular Ecology 15, 63–72 (2006).
Seeley, T. D. & Tarpy, D. R. Queen promiscuity lowers disease within honeybee colonies. Proceedings of the Royal Society of London B: Biological Sciences 274, 67–72 (2007).
Page, R. E. The evolution of multiple mating behavior by honeybee queens (Apis mellifera L.). Genetics 96, 263–273 (1980).
Garnery, L. et al. Genetic diversity of the west European honey bee (Apis mellifera mellifera and A. m. iberica) II. Microsatellite loci. Genetics Selection Evolution 30(S49), 1297–9686 (1998).
Estoup, A., Solignac, M. & Cornuet, J.-M. Precise assessment of the number of patrilines and of genetic relatedness in honeybee colonies. Proceedings of the Royal Society of London B: Biological Sciences 258, 1–7 (1994).
Gautier, M. et al. Estimation of population allele frequencies from next‐generation sequencing data: pool‐versus individual‐based genotyping. Molecular Ecology 22, 3766–3779 (2013).
Sham, P., Bader, J. S., Craig, I., O’Donovan, M. & Owen, M. DNA Pooling: a tool for large-scale association studies. Nature Reviews Genetics 3, 862–871 (2002).
Cingolani, P. et al. A program for annotating and predicting the effects of single nucleotide polymorphisms, SnpEff: SNPs in the genome of Drosophila melanogaster strainw1118; iso-2; iso-3. Fly 6, 80–92, https://doi.org/10.4161/fly.19695 (2012).
Pruitt, K. D. et al. RefSeq: an update on mammalian reference sequences. Nucleic Acids Research 42, D756–D763, https://doi.org/10.1093/nar/gkt1114 (2013).
Gabriel, S., Ziaugra, L. & Tabbaa, D. SNP genotyping using the Sequenom MassARRAY iPLEX platform. Current protocols in human genetics 2.12. 11-12.12. 16 (2009).
Henriques, D. et al. Developing reduced SNP assays from whole‐genome sequence data to estimate introgression in an organism with complex genetic patterns, the Iberian honeybee (Apis mellifera iberiensis). Evolutionary Applications, https://doi.org/10.1111/eva.12623 (2018).
Alexander, D. H., Novembre, J. & Lange, K. Fast model-based estimation of ancestry in unrelated individuals. Genome Research 19(1655–1664), 1088–9051 (2009).
Kopelman, N. M., Mayzel, J., Jakobsson, M., Rosenberg, N. A. & Mayrose, I. Clumpak: a program for identifying clustering modes and packaging population structure inferences across K. Molecular Ecology Resources 15(1179–1191), 1755–0998 (2015).
Enright, A. J., Van Dongen, S. & Ouzounis, C. A. An efficient algorithm for large-scale detection of protein families. Nucleic Acids Research 30, 1575–1584 (2002).
We are deeply indebted to João Costa (Instituto Gulbenkian Ciência, Oeiras, Portugal), for designing the multiplexes and SNP genotyping. José Rufino provided computational resources at the Polytechnic Institute of Bragança, Portugal. DH was supported by a PhD scholarship (SFRH/BD/84195/2012) from the Portuguese Science Foundation (FCT). KAB receives a PhD fellowship from the Irish Research Council. MP was supported by the Swiss Federal Office for Agriculture FOAG and the Fondation Sur-la-Croix, Basel. IM was supported by Saavedra Fajardo fellowship from the Fundación Séneca (20036/SF/16). MAP is a member of and receives support from the COST Action FA1307 (SUPER-B). Funding for genotyping of Irish honeybees was gratefully received from the Eva Crane Trust, the Native Irish Honeybee Society and the Department of Agriculture, Food and the Marine (16/GR/09). MB and TCF are funded by an Institute Strategic Grant from the Biotechnology and Biological Sciences Research Council (BBSRC) (BB/JO1446X/1). Financial support for this research was provided to MAP and LG by 2013–2014 BiodivERsA/FACCE-JPI joint call for research proposals, with the national funders FCT (Portugal), “Agence Nationale de la Recherche” (France), and “Ministério de Economia y Competividade” (Spain).
The authors declare no competing interests.
Publisher's note: Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.
About this article
Cite this article
Henriques, D., Browne, K.A., Barnett, M.W. et al. High sample throughput genotyping for estimating C-lineage introgression in the dark honeybee: an accurate and cost-effective SNP-based tool. Sci Rep 8, 8552 (2018). https://doi.org/10.1038/s41598-018-26932-1
Journal of Apicultural Research (2020)
Tool for genomic selection and breeding to evolutionary adaptation: Development of a 100K single nucleotide polymorphism array for the honey bee
Ecology and Evolution (2020)
Conservation of the dark bee (Apis mellifera mellifera): Estimating C-lineage introgression in Nordic breeding stocks
Acta Agriculturae Scandinavica, Section A — Animal Science (2020)
Shotgun sequencing of honey DNA can describe honey bee derived environmental signatures and the honey bee hologenome complexity
Scientific Reports (2020)