- Research
- Open access
- Published:
Pupal Exuviae of Culex Pipiens L. (Diptera: Culicidae) Can be Utilised as a Non-Invasive Method of Biotype Differentiation
Biological Procedures Online volume 26, Article number: 17 (2024)
Abstract
Background
Culex pipiens L. is a principal vector of zoonotic arboviruses in Europe, acting in both an amplification role in enzootic transmission between avian hosts and as a bridge vector between avian hosts and mammals. The species consists of two forms which are indistinguishable using morphological methods but possess varying ecological and physiological traits that influence their vector capacity. In this study we validate methods that can be used to extract trace DNA from single pupal exuviae of Cx. pipiens for use in molecular speciation of samples. These DNA extraction methods are compared using measurement of the total yield and successful identification using a real-time polymerase chain reaction (PCR) assay.
Results
Genomic DNA was initially extracted from colony-derived individuals using an ethanol precipitation method, two commercially available DNA extraction kits: DNeasy® Blood & Tissue Kit (Qiagen, UK) and Wizard® SV Genomic DNA Purification System (Promega, UK) and a direct real-time PCR method. Time elapsed between eclosion and processing of pupae significantly influenced Cx. pipiens form identification as nucleic acid concentration and PCR amplification success decreased with increased time elapsed. Real-time PCR amplification success, however, was not shown to vary significantly between the three extraction methods, with all methods successfully identifying all samples, but the direct real-time PCR method achieved a lesser amplification success rate of 70% (n = 20 for each treatment). More variable results were produced when field-derived exuviae were used, with no significant difference in real-time PCR amplification success found across the four methods and a lower overall rate of successful identification of 55–80%.
Conclusions
This study shows that both colony and field derived Cx. pipiens pupal exuviae can be a useful non-invasive source of trace DNA permitting accurate biotype differentiation for at least twenty-four hours post-eclosion. The significance and utility of this technique in ecological and behavioural studies of Cx. pipiens is discussed and recommendations made for use according to experimental scenario.
Background
Vector-borne diseases have a major global impact on the health of human and animal populations. More than 17% of all infectious diseases in humans are transmitted by insects and ticks [1], whilst in livestock, one-quarter of pathogens causing a notifiable disease, as defined by the World Organisation for Animal Health (WOAH, founded as OIE), are vector-borne [2]. Culex pipiens Linnaeus 1758 is a vector of pathogens of global importance, including arborviruses (e.g. West Nile and Usutu viruses), protozoa (e.g. avian malaria) and dirofilarial worms [3,4,5]. The Cx. pipiens species comprises two biotypes that cannot be separated by morphology: Cx. pipiens f. pipiens (L.) and Cx. pipiens f. molestus Forskål 1775. Traditionally, physiological and behavioural traits including stenogamy, autogeny and host preference have been used to differentiate the biotypes [6]. This variation was hypothesised to result from adaptation to different habitats, with the Cx. pipiens f. molestus biotype being primarily found in underground environments and Cx. pipiens f. pipiens occurring above-ground [7, 8]. More recent analysis of Cx. pipiens populations in Europe, however, indicates a far more complex scenario, with inter-breeding of above- and below-ground sympatric populations and the occurrence of hybrids that exhibit variation in physiological and behavioural phenotype [9,10,11,12,13,14,15].
Species identification methods utilising target organism DNA or RNA are now a fundamental tool for study of vector populations and the pathogens they transmit [16]. The lack of clarity in classification of Cx. pipiens biotypes has led to application of molecular methods being applied more frequently in differentiating these forms, predominantly through amplification of the CQ11 microsatellite locus [9, 17]. Molecular methods of taxonomic identification are typically lethal for the individual sampled, or at a minimum involve the removal of body parts with subsequent impact on behaviour and survival [18]. In recent years, however, non-lethal sampling methods for DNA extraction have gained popularity across a wide range of subject areas including conservation, behaviour and population genetics [19]. Previously, a single tibia has been shown to be a sufficient non-lethal source of DNA in several insect species including bumble bees [20] and mosquitoes of the Anopheles genus [21]. Haemolymph, wing edges and tips have also been shown to provide a sufficient source of DNA for identification in other insect species [18, 22]. These methods are fundamentally inappropriate, however, for behavioural studies that rely on minimal disturbance such as studies of leg tapping within the Cx. pipiens group, where females are observed to perform rejection kicks to prevent mating with incompatible males [23, 24].
Collection and identification of insect pupal exuviae has been an important tool in many ecological studies of insects aiming to estimate population densities [25], species distribution [26, 27] and adult emergence periods [28]. Successful extraction of DNA has been demonstrated for a variety of invertebrates including from the exuviae of butterflies [29], honey bees [30], mosquitoes [31], dragonflies [32], scarabs [33] and from the moults of tarantulas [34]. The exoskeleton of the pupal exuviae is comprised of extracellular chitin and does not itself contain any nucleic acids [35], but trace quantities of epithelial cells, hairs and muscle tissues from the adult remain attached to the inner surface of the cuticle [35]. Trace DNA from chironomid pupal exuviae has been shown to be sufficient for PCR amplification and sequencing of the COI barcoding gene in 46% of samples tested [36]. A further study isolated genomic DNA from an average of 61.2% of chironomid samples tested across five different extraction methods, with varying success depending on the method used [37]. Pupal exuviae from Aedes and Culex mosquitoes were used successfully to obtain DNA for molecular speciation targeting the ITS2 and ITS1 regions, respectively, although success was limited to within the first 24Â h post-eclosion and no success was seen when tested in field collected samples [31]. A subsequent study was unable to obtain enough DNA from pupal exuviae of Aedes aegypti (L. 1762) for downstream molecular testing [38].
The present study aims to assess the utility of Cx. pipiens pupal exuviae as a non-lethal source of DNA for distinguishing the two Cx. pipiens biotypes from mixed populations under both laboratory and field conditions. The effect of processing method on DNA yield and PCR amplification success from exuviae samples was investigated, including an assessment of handling time and cost. Processing time post-eclosion on DNA yield and PCR amplification success was also quantified using a mixed biotype colony line. The validated protocol was subsequently applied to field collected exuviae samples and DNA yield and PCR amplification success of samples processed individually and in pools of five exuviae compared. The effect of body size as well as environmental factors, such as light intensity and water temperature, on DNA yield were also investigated. DNA extraction from pupal exuviae was then used to establish single biotype colonies from a mixed population and to estimate how long these colonies remain pure in culture, as a tool to facilitate behavioural studies between the two biotypes.
Methods
Mosquito Rearing
Experiments utilised a mixed colony of Cx. pipiens biotypes originating from an allotment area in Brookwood, Surrey, UK established in 2011 and identified as the ‘Brookwood’ line [11]. Five to seven days old adults from this colony line were offered defibrinated horse blood (TCS Biosciences, UK) overnight using a Hemotek™ membrane feeding system (Hemotek™ Ltd., UK). Five days after blood feeding, egg rafts were collected from oviposition cups and left to hatch in approximately 500 ml of fresh tap water. Larvae were reared at a density of 200 larvae/L water and maintained on a diet of 1 mg of guinea pig pellets/larva (Pets at Home, UK) on alternate days. Larvae were reared in an environmentally controlled incubator maintained at a temperature of 25oC ± 1oC and relative humidity of 50% ± 1% and were exposed to a lighting regime of 16:8 h light: dark. Conditions in the incubator were monitored using a HOBO™ U12-012 temperature/relative humidity/light data logger (Measurement Systems Limited, UK). Daylight period light intensity was approximately 3500 lx whilst light intensity during the night-time period was 3.5 lx. Dusk and dawn were simulated by either an increase or decrease in light intensity, respectively, each over a one-hour period.
Pupal Exuviae Sample Collection and Preparation
Following the onset of pupation, pupae were collected daily and placed into separate 2 ml tubes containing 1 ml of water and monitored for eclosion. Pupal exuviae and eclosing adults were collected and used for two different experiments. Firstly, to compare the efficacy between DNA extraction methods, pupal exuviae and emerged adult mosquitoes were placed in 70% ethanol immediately following eclosion and stored individually at room temperature prior to DNA extraction. Secondly, to assess the effect of time elapsed between eclosion and preservation on DNA extraction efficiency, adult mosquitoes and their corresponding pupal exuviae were placed individually into 70% ethanol at defined time points post-eclosion (0, 1, 6, 12, 18 and 24 h). Pupal exuviae and adult mosquitoes were then removed from ethanol and left to air dry for approximately 10 min prior to DNA extraction. Comparisons of DNA quantity between different processing times post-eclosion were assessed using Kruskal-Wallis with Bonferroni correction for multiple comparisons. For all statistical tests, the statistical significance level was set at P < 0.05 and analyses were computed in R studio version 1.2 [39].
Use of Pupal Exuviae as a Non-Invasive Method of Sampling Field Populations
Two periods of pupal exuviae collection were undertaken in the field, each spanning two weeks. The first collections were performed in August 2020 and used for comparison between individual and pooled processing approaches. The second collection period was between June to July 2021 and used to validate processing methods in field collected samples. The oviposition site in the field was created using a 20 L polypropylene black bucket of 28.3 cm x 47.8 cm x 33.0 cm (HxWxD), filled with 10 L of tap water and seeded with 5 g crushed guinea pig pellets (Pets at Home, UK) to attract gravid female Cx. pipiens. The bucket was placed in a residential garden in Guildford, Surrey (51°240’N; -0°578’W). Pupal exuviae floating on the surface were collected and placed into 70% ethanol each morning over a period of two weeks and transferred to the laboratory for processing. Samples were either processed individually or in pools containing five exuviae using the ethanol precipitation method described below. Water temperature and light intensity in the bucket were measured using a HOBO™ temperature/light weatherproof pendant data logger (Measurement Systems Limited, UK). Mann-Whitney U tests were used to assess the effect of pooling or year of collection on nucleic acid concentrations from field collected pupal exuviae.
DNA Extraction Method Comparison
Three extraction methods and a direct real-time PCR processing method were chosen to compare DNA yield and subsequent PCR amplification success: an ethanol precipitation method and two commercially available kits, DNeasy® Blood & Tissue Kit (Qiagen, UK) and Wizard® SV Genomic DNA Purification System (Promega, UK), hereafter referred to as DNeasy® and Wizard® respectively. For each of the extraction methods, total genomic DNA was isolated from 20 individual pupal exuviae alongside a distilled water negative control, with ten males and ten females processed for each method. DNA extracted using the same method from the corresponding adult heads were additionally included as positive controls.
Ethanol Precipitation
DNA was extracted as follows: samples were placed into 200 µl of digestion solution comprised of 100 mM UltraPure™ 1 M Tris-HCL (pH 8.0) (Invitrogen™ by Thermo Fisher Scientific, UK), 200 mM NaCl (Invitrogen™, UK), 0.2% (w/v) SDS (Merck Life Science UK Limited, UK), 5 mM UltraPure™ 0.5 M EDTA (pH8.0) (Invitrogen™, UK), 200 µg/ml proteinase K (Qiagen, UK) made up to a total volume of 200 µl per sample using UltraPure™ water (Invitrogen™, UK). Samples were incubated overnight at 37oC before proceeding with DNA extraction. Immediately following incubation, 500 µl of ice-cold 100% ethanol, 20 µl 3 M NaOAc pH 5.5 (Invitrogen™, UK) and 2 µl of GlycoBlue™ coprecipitant (15 mg/ml) (Invitrogen™, UK) were added to each sample and incubated at -20oC for 1 h. DNA was pelleted by centrifugation at 14,000 rpm at 4oC for 30 min and supernatant was removed. Pellets were then washed in 400 µl 70% ethanol, re-pelleted by centrifugation under the same conditions for 15 min and supernatant was removed. Pellets were air-dried for 20 min to allow for the evaporation of excess ethanol and resuspended in either 15–200 µl nuclease free water for pupal exuviae and adult samples respectively.
Commercially Available Kits
DNA was extracted according to the manufacturer’s instructions with the following modifications to enhance DNA yield [40, 41]. Mosquito exuviae were subjected to a homogenisation stage within the digestion solution detailed in each of the kit’s instructions using 3 mm stainless steel homogenisation beads (Qiagen, UK) for 1 min at 30 Hz using a Qiagen tissue lyser (Qiagen, UK). Samples were then incubated overnight at 56oC prior to DNA extraction. To maximise DNA yield from exuviae samples, 30 µl of elution buffer was incubated on the spin column membrane at room temperature for 5 min prior to elution. For DNA extraction from mosquito heads, elution was performed twice in 30 µl for a total elution volume of 60 µl.
Direct Real-Time PCR
Samples were prepared according to Thongjued et al. [42] with minor adjustments to sample preparation. Briefly, pupal exuviae were removed from ethanol and left to air-dry for approximately 10 min before being placed in 20 µl PBS (pH 7.4) (Gibco™ by Thermo Fisher Scientific, UK). Samples were vortexed before incubating at 98oC for 4 min and 2 µl of supernatant was added directly to the PCR mix.
In all samples, prior to PCR processing, nucleic acid concentrations were measured for all extraction methods using the Qubit® dsDNA HS assay kit (Invitrogen™, UK) and read by a Qubit® 3.0 fluorometer (Invitrogen™, UK). For all samples, 2 µl of DNA template were used in 198 µl of the dsDNA HS assay. Variation in DNA yield between processing methods for both colony and field collected exuviae were assessed using a Kruskal-Wallis with Bonferroni correction for multiple comparisons.
Differentiation of Cx. Pipiens Biotypes
Mosquitoes were simultaneously assigned to species and biotype level using a real-time PCR assay originally designed by Rudolf et al. [9] with minor adaptations to primer concentrations. Reactions were performed in 10 µl reaction volume consisting of 5 µl TaqMan™ multiplex master mix (2x) (Applied Biosystems™ by Thermo Fisher Scientific, UK), 0.3 µM CxPipF, 0.4 µM CxPipR, 0.2 µM CxPipP, 0.2 µM CxPipPipP, 0.2 µM CxPipMolP, 0.15 µM CxTorrF, 0.15 µM CxTorrR R, 0.1 µM CxTorrP, 0.16 µl BSA (20 mg/ml) (Merck Life Science UK Limited, UK), 1.14 µl UltraPure™ water (Invitrogen™, UK) and 2 µl DNA extract. Sequences for the primers and probes are shown in Table 1. The thermal profile started with an initial activation step of 95oC for 20 s, followed by 40 cycles of 95oC for 3 s and 60oC for 1 min using a QuantStudio™ 7 Flex Real-Time PCR machine (Applied Biosystems™, UK). All samples were run alongside positive controls consisting of pure f. pipiens, f. molestus, hybrid and Cx. torrentium DNA as well as negative controls including extraction and PCR negative controls. Real-time PCR amplification success was defined by the number of samples for which the quantification cycle (Cq) value was below the assay cutoff of 39. Any samples not producing a Cq value were assigned a value of 40 for analysis. Cq values obtained from each of the probes for each sample were averaged for use in analysis. Variation in PCR amplification success between processing time post-eclosion or processing method was assessed with pairwise chi-squared tests for independence with Bonferroni adjustment for multiple comparisons.
DNA Extraction Cost and Handling Time
The cost of the extraction method for each sample was estimated based on the retail price of the chemicals or kits used in the UK. The handling time for each sample was calculated as the time required to complete all processing, starting from dehydration of the pupal exuviae, to obtaining a DNA extract ready for PCR. This was replicated three times with each round containing 10 individuals and averaged.
Wing Length Measurements
Wing length was measured as a proxy for body size to control for specimen size variation for the method comparison and time trial experiments [43]. Wings from sampled individuals were transferred to a piece of paper towel dampened with 70% ethanol, flattened, and left to air dry for approximately 5 min. Wings were then transferred to a strip of Scotch Magic Tape™ with both wings from one adult placed together and placed on a glass microscope slide for imaging. Wing images were visualised using a Leica EZ4HD microscope (Leica Microsystems, Germany) alongside a stage micrometer for scale where one division is equal to 0.01 mm. Images were subsequently processed for size measurement using ImageJ [44]. Wing length was measured from the axillary incision to the apical margin, excluding the fringe (Fig. 1) [45]. Measurements were taken from both wings of the same adult and averaged for use in analysis. Correlations between concentration, wing measurement and Cq values were assessed using Spearman’s correlation.
Creation of Single Biotype Colony Lines
Approximately five days after blood-feeding, egg rafts were collected from the Brookwood colony line (F97) and each egg raft separated into individual 25 ml pots in approximately 15 ml of dechlorinated tap water for hatching. Larvae from each egg raft were reared separately under the same conditions described above. Following the onset of pupation, pupae were collected daily into individual 2.0 ml tubes and monitored for eclosion. Pupal exuviae were collected into 70% ethanol every twelve hours and stored prior to processing. Exuviae from emerging adults were processed for DNA extraction by ethanol precipitation and biotype identified daily by real-time PCR as described above. PCR results were used to allocate adult mosquitoes to separate colony cages (Bugdorm, Watkins and Doncaster, UK) according to the biotype of their corresponding exuviae with approximately 80–100 individuals per biotype used to create single biotype colonies. The colony lines were subsequently maintained according to Manley et al. [11]. After 10 generations, DNA was extracted from 40 adults from each line using the Wizard® kit and biotype identified by real-time PCR as described to confirm the lines remained homologous or heterozygous as determined by the CQ11 microsatellite marker. Heads of adult mosquitoes were used to obtain genomic DNA using the Wizard® SV Genomic DNA Purification System (Promega, UK) and biotype characterised, as described above.
Results
Comparison of Processing Methods for DNA Extraction and Biotype Identification in Colony Populations
Genomic DNA was successfully extracted from a total of 80 samples (n = 20 for each method). The quantity of DNA extracted was shown to vary significantly between the four processing methods (KW χ2 = 57.144, df = 3, P < 0.001; Fig. 2A). The greatest quantity of total DNA yield was achieved using the ethanol precipitation method (x̅ = 17.780 ng; sd = 6.874 ng) which was significantly greater (P < 0.001) than yields from both the DNeasy® (x̅ = 2.193 ng; sd = 1.149 ng) and the Wizard® (x̅ = 3.015 ng; sd = 0.999 ng). The two commercial kits did not differ significantly in their yield (P = 0.145). The direct PCR method generated the lowest DNA yield (x̅ = 1.35 ng; sd = 0.864 ng) which was significantly less than quantities obtained from the Wizard® (P = 0.005) and highly significantly less than ethanol precipitation (P < 0.001) methods but did not differ from the DNeasy® kit (P = 0.178).
Despite the differences in total DNA yields obtained through the four methods, PCR amplification success was not shown to vary significantly between the three extraction methods used (Fisher’s exact P = 1.00) with all showing 100% amplification success. PCR amplification success for the direct PCR method was significantly reduced, however, when compared with the other extraction methods tested (P = 0.007) with an amplification success rate of 70% (Fig. 2B). A general trend was observed in decreasing Cq values with increasing DNA yields (Fig. 2C). This correlation was significant for the ethanol precipitation (R= -0.47, P = 0.037), Wizard® (R=-0.51, P = 0.021) and DNeasy® (R= -0.75, P = 0.018) methods. The correlation between total DNA yield and Cq value was not significant for the direct PCR method (R= -0.25, P = 0.29).
Comparison of three DNA extraction methods and a direct PCR assay from individual Cx. pipiens pupal exuviae. A) Comparison of total DNA quantity (ng) obtained from individual Cx. pipiens pupal exuviae. Horizontal black lines indicate median, 25th and 75th percentiles, whiskers extend to the largest and smallest values within 1.5 times the interquartile range from the 25th and 75th percentiles, closed dots indicate outliers. B) Comparison of PCR amplification success (%) for DNA extracts. Error bars indicate mean ± SD. The letters above the bars and boxplots indicate which groups differ significantly (P < 0.05) from one another. Specifically, groups which share a common letter are not significantly (P < 0.05) different from one another. C) Comparison of total yield (ng) compared with average Cq values following PCR amplification of DNA extracts. Grey shaded area indicates the 95% confidence interval
DNA Extraction Cost and Handling Time
The direct PCR method was the most inexpensive method with almost no associated extraction costs, followed by the ethanol precipitation which involved purchase of individual reagents (Table 2). The DNeasy® and Wizard® kits had a higher handling cost per sample with the Wizard® kit having an almost five-fold increase in price per sample compared with the ethanol precipitation. Moreover, the cost of the DNeasy® kit was substantially higher; almost double the Wizard® kit per sample (Table 2). Increased processing costs were associated with decreased Cq values (R = -0.76, P < 0.01) and therefore higher PCR amplification success. Despite this, when considering methods which involved extraction of samples prior to PCR, these higher processing costs did not enhance DNA yield, rather, a significant negative correlation between increased processing costs and DNA yield was detected (R = -0.8, P < 0.01). When considering the methods that required prior extraction of samples before PCR, decreased cost was correlated significantly with increased processing time (R = -0.95, P < 0.01).
The direct PCR was the quickest processing method, with no requirement for prior extraction of samples therefore eliminating the overnight incubation step. Of the three extraction methods tested, the ethanol precipitation possessed the longest processing time with the DNeasy® and Wizard® kits taking considerably less time, approximately 2 h less each (Table 2). A significant positive correlation was detected between handling time and DNA yield, with the longer the time spent preparing the samples, the higher the DNA yield prior to PCR amplification (R = 0.8, P < 0.01). Processing time was also negatively correlated with Cq values (R = -0.12, P = 0.293), therefore increasing PCR amplification success, however, this interaction was not shown to be significant.
Investigating the Influence of Processing Time Post-Eclosion on DNA Yield and PCR Amplification Success from Cx. Pipiens Pupal Exuviae from Colony Populations
Genomic DNA yield was found to vary significantly between the different time points post-eclosion (KW χ2 = 92.125, df = 5, P < 0.01; Fig. 3A). The greatest DNA yield resulted from samples processed immediately after eclosion (x̅ = 1.190 ng/µl; sd = 0.458 ng/µl) which were found to be significantly higher than all other groups (P < 0.05) with the exception of the 1-hour time point (P = 1.00). Generally, there was a negative correlation between time of processing post-eclosion and DNA yield with mean nucleic acid concentrations decreasing as time passed.
The time that elapsed between eclosion and preservation was shown to significantly influence PCR amplification success (Fisher’s exact = P < 0.001). No significant difference was observed between amplification success in samples preserved up to and including 12 h post-eclosion (P = 1.00) with all samples showing amplification. In contrast, samples preserved at 18–24 h post-eclosion demonstrated significantly lower PCR amplification success (55% and 40%) compared with samples preserved within 12 h of eclosion (P = 0.0184 and P < 0.001 for 18 and 24 h respectively). Similarly, a decrease in Cq value as nucleic acid concentration increased (Fig. 3C) was only significant for the first two time points (R = -0.57, P = 0.0086 and R= -0.64, P = 0.0029 for 0 h and 1 h respectively).
Comparison of DNA yield and amplification success of individual Cx. pipiens pupal exuviae at varying time points post-eclosion. A) Comparison of DNA quantity (ng/µl) from all DNA extractions using the ethanol precipitation method. Horizontal black lines indicate median, 25th and 75th percentiles, whiskers extend to the largest and smallest values within 1.5 times the interquartile range from the 25th and 75th percentiles, closed dots indicate outliers. B) Comparison of PCR amplification success (%) of DNA extracts. Error bars indicate mean ± SD. C) Comparison of nucleic acid concentrations (ng/µl) with mean Cq values for DNA extracts. Grey shaded area indicates the 95% confidence interval. Different letters above the boxplots and bars indicate which groups differ significantly (P < 0.05) from one another
Effect of Body Size on Nucleic Acid Concentration
Wing length as a proxy of body size, was shown to be positively correlated with nucleic acid concentrations recovered from exuviae (t = 2.62, df = 111, P = 0.01) and this interaction was shown to be significant in each time group except for the 18 and 24-hour time points (Figure S1B). There was no significant variation in wing length between groups of mosquitoes included in each treatment (F = 0.172, df = 5, P = 0.972), in different Cx. pipiens forms (F = 1.458, df = 2, P = 0.237; Figure S1A) or in the left and right wing length recorded for each individual (t = 13.737, df = 224, P = 0.956).
Comparison of Processing Methods for DNA Extraction and Biotype Identification from Field Collected Pupal Exuviae
Genomic DNA yield varied significantly between individually processed and pooled field exuviae samples (W = 16.6, P < 0.001; Figure S2A) when tested using the ethanol precipitation method. The greatest DNA quantities resulted from the pooled samples (x̅ = 1.000 ng/µl; sd = 0.181 ng/µl), yet results showed that DNA yield from individually processed samples was still sufficient for detectable results, despite yielding lower concentrations (x̅ = 0.243 ng/µl; sd = 0.141 ng/µl). Amplification success was also affected significantly by pooling as 100% of pooled samples successfully amplified target sequence, significantly higher than the 55% recorded in individually processed samples (Fisher’s exact P = 0.0292; Figure S2B). Nucleic acid concentration was shown to be correlated with Cq value for both individually processed and pooled samples with Cq values shown to decrease as nucleic acid concentrations increased (Figure S2C).
Comparison of Three DNA Extraction Methods and a Direct Real-Time PCR Assay for Field Collected Pupal Exuviae
Quantity of DNA obtained from field samples was shown to vary significantly between the four extraction methods (KW χ2 = 45.82, df = 3, P < 0.001; Fig. 4A). The greatest total DNA quantity was achieved using the ethanol precipitation method (x̅ = 5.17 ng; sd = 1.75 ng) which was statistically greater than both the DNeasy® kit and the direct PCR (P < 0.001). The Wizard® kit yielded the second largest DNA quantities which again were significantly greater than both the DNeasy® (P = 0.00869) and direct PCR (P = 0.0276) methods. There were no statistically significant differences in PCR amplification success between the four processing methods (Fisher’s exact P = 0.367) although the Wizard® kit yielded the highest rate of amplification success (80%) (Fig. 4B). A correlation of decreasing Cq with increasing DNA yields (Fig. 4C) was detected although this was not statistically significant for any of the processing methods.
Comparison of the efficiency of three extraction methods for obtaining DNA from individual field collected Cx. pipiens pupal exuviae and a direct PCR method that did not include an extraction step. A) Comparison of total DNA quantity (ng) from DNA extractions. Horizontal black lines indicate median, 25th and 75th percentiles, whiskers extend to the largest and smallest values within 1.5 times the interquartile range from the 25th and 75th percentiles, closed dots indicate outliers. B) Comparison of PCR amplification success (%). Error bars indicate mean ± SD. C) Comparison of total DNA yields (ng) with mean Cq values for different processing. Grey shaded area indicates the 95% confidence interval. Different letters above the boxplots and bars indicate which groups differ significantly (P < 0.05) from one another
Nucleic acid concentrations obtained using the ethanol precipitation method differed significantly between sampling years (W = 52, P = 0.0366), with samples collected in 2021 yielding higher average concentrations compared with those collected in 2020 (x̅ = 0.243 ng/µl; sd = 0.141 ng/µl and x̅ = 0.345 ng/µl; sd = 0.117 ng/µl for 2020 and 2021 sampling period respectively; Fig. 5A). Although amplification success was higher for samples collected in 2021, this difference was not statistically significant (P = 0.5402; Fig. 5B).
During 2020, average water temperatures of 21.3 ± 2.71oC were significantly higher than those recorded during 2021 (17.7 ± 1.20oC; W = 354, P < 0.001). Similarly, 2020 recorded significantly higher lux levels (34,444 lx; W = 813, P < 0.001) compared with those recorded during collections conducted in 2021 (10,066 lx). All field collected specimens were characterised as Cx. pipiens f. pipiens according to the CQ11 microsatellite marker.
Comparison of nucleic acid concentration and PCR amplification success of individual field collected Cx. pipiens pupal exuviae between different sampling years. (A) Comparison of nucleic acid concentration (ng/µl) from DNA extracts between different sampling periods using the ethanol precipitation extraction method. Horizontal black lines indicate median, 25th and 75th percentiles, whiskers extend to the largest and smallest values within 1.5 times the interquartile range from the 25th and 75th percentiles, closed dots indicate outliers. (B) Comparison of PCR amplification success (%) for two different sampling periods. Error bars indicate mean ± SD. Different letters above the bars indicate which groups differ significantly (P < 0.05) from one another
Creation of Pure Colony Lines Using DNA Extraction from Pupal Exuviae to Select Live Individuals
Extraction of DNA from pupal exuviae was successfully used to select live individuals to create single biotype colonies from a mixed population, which were reared for more than 10 generations. Mosquitoes tested from the 10th generation demonstrated that the colonies remained stable until this point (Table 3) with the hybrid line consisting of the expected mixture of forms (22.5% f. pipiens, 20% f. molestus and 57.5% hybrid specimens).
Discussion
In this study, successful DNA extraction and PCR amplification from individual pupal exuviae was demonstrated from colony- and field-reared Cx. pipiens populations using three different extraction methods. Extracted DNA was successfully used to accurately identify biotypes within the Cx. pipiens species and the method was employed to create single-biotype colony lines from a mixed population which retained their homologous genetic signature according the CQ11 for over 10 generations. The method has wide applicability for future studies of the genetic underpinning of behaviour in Cx. pipiens both in the field and laboratory through the provision of non-invasive identification.
Successful DNA extraction and PCR amplification from individual pupal exuviae was demonstrated for up to twenty-four hours post-eclosion, although amplification success was shown to decrease as time elapsed since post-eclosion increased. Time points up to and including twelve hours post-eclosion showed 100% amplification success, but this decreased for the eighteen (55%) and twenty-four-hour (40%) time points highlighting the requirement for relatively rapid processing. This limitation is likely to be due to nucleic acid degeneration and imposes greater limitations in the field where the age of the exuviae processed may be unknown.
Successful DNA extraction and PCR amplification from pupal exuviae of laboratory reared Culex and Aedes species within the first twenty-four hours post-eclosion has previously been reported [31]. However, no successful amplification was observed after twenty-four hours (and up to nine days) post-eclosion when testing pupal exuviae from colony reared individuals. Contrastingly, a subsequent study attempting to replicate this with Ae. aegypti pupal exuviae collected one-hour post-eclosion entirely failed to amplify PCR targets [38]. Neither study quantified the resulting DNA extraction concentrations, therefore it is unknown whether the quantity of DNA used in the PCR was sufficient to meet the lower threshold of the reaction to allow detection. In contrast, the current study utilised a real-time PCR method with a high dynamic range, capable of amplifying small quantities of DNA as low as 2 × 10− 4 ng (unpublished data). Real-time PCR methods are likely to have a lower detection threshold compared with the traditional PCR methods used in previous studies, which could in part explain the increased amplification success seen [46]. Further work should determine if DNA yield obtained from methods developed during this study are sufficient for successful amplification in endpoint PCR assays and sequencing enabling use of this method for a broader array of species and scenarios.
Processing methods involving extraction of DNA from samples provided superior concentration of isolated trace DNA from single Cx. pipiens pupal exuviae than the direct protocol. Although isolation of DNA by ethanol precipitation had the longest processing time, the DNA quantity was significantly higher than the other processing methods whilst also having the lowest processing cost compared with the other extraction methods. In contrast, DNA extraction success from chironomid pupal exuviae found that commercial kits yielded the best results [37], although a DTAB/CTAB lysis protocol was used rather than ethanol precipitation to compare against commercially available kits. The lower material cost of the ethanol precipitation method may in some scenarios facilitate processing of greater sample sizes. More broadly, selection of the optimal method is dependent on the monetary and time resources available, as well as ease of use and application to a variety of sample types, that may favour the use of commercial kits for some projects.
Despite a reduced amplification success (70% compared with 100%), direct PCR was significantly cheaper and quicker to perform than the other processing methods tested. Although this would not be suitable for highly valuable specimens, direct PCR would be of particular benefit when utilising starting material with higher PCR amplification success rates such as whole larvae [42] as it would facilitate rapid screening of populations at a reduced cost. Significantly higher PCR amplification success (70%) was obtained during the present study compared with similar studies in chironomids [37], attributed to the use of an optimised direct PCR methodology. Incubation of the exuviae in PBS may dilute PCR inhibitors whilst also maintaining the pH of the reaction [47]. Moreover, the heating step within the direct PCR approach aids cell lysis, releasing DNA and denaturing proteins that could degrade DNA or inhibit the PCR [48, 49]. Amplification success rates of 90.5% have been achieved from Diptera specimens when using a high-fidelity DNA polymerase specifically designed for use in direct PCR application with increased tolerance to PCR inhibitors [42]. Thus, further optimisation of this protocol using a high fidelity Taq has the potential to be beneficial in increasing PCR amplification success rate.
The present study also demonstrated successful DNA extraction and PCR amplification of field collected pupal exuviae when processed both individually and in pools of five exuviae, with individual processing applicable when comparing multiple processing methods. As expected, processing of exuviae in pools yielded higher nucleic acid concentrations as well as consistent PCR amplification success compared with individually processed exuviae (100% compared with 55%). Successful extraction and amplification from field collected insect exuviae has been demonstrated previously [36, 37, 50], but attempts to extract PCR amenable DNA from field collected mosquito exuviae were not previously successful [31]. Factors including ultraviolet B radiation (UVB), pH, salinity and presence of microorganisms can all influence degradation rate of environmental DNA (eDNA) [51, 52]. Here, average temperature and light intensity varied between the two sampling years, which could have influenced the differences in nucleic acid concentrations obtained, as well as other unknown and unquantified factors such as microbial content of the water.
Conclusions
The present study has demonstrated for the first time that Cx. pipiens pupal exuviae can be utilised as a non-invasive source of trace DNA for accurate biotype differentiation for at least twenty-four hours post-eclosion. Successful PCR amplification was demonstrated from both colony and field collected exuviae through various methods of processing and is therefore accessible to a wide range of projects with different levels of available resources. This method could be of particular benefit to further studies examining behavioural differences between the forms from sympatric populations and could be utilised to establish pure colonies from field derived individuals. In addition, identification using pupal exuviae may provide a useful tool for work with other cryptic insect species.
Data Availability
All data generated or analysed during this study are included in this published article and its additional Fles.
References
World Health Organization. Vector-borne diseases 2020. https://www.who.int/news-room/fact-sheets/detail/vector-borne-diseases.
World Organisation for Animal Health. OIE-listed diseases, infections and infestations in force 2014. http://www.oie.int/animal-health-in-the-world/oie-listed-diseases-2014.
Brugman VA, Hernandez-Triana LM, Medlock JM, Fooks AR, Carpenter S, Johnson N. The role of Culex pipiens L. (Diptera: Culicidae) in Virus Transmission in Europe. Int J Env Res Pub He. 2018;15(2).
Zele F, Vezilier J, L’Ambert G, Nicot A, Gandon S, Rivero A, et al. Dynamics of prevalence and diversity of avian malaria infections in wild Culex pipiens mosquitoes: the effects of Wolbachia, filarial nematodes and insecticide resistance. Parasit Vectors. 2014;7:437.
Cancrini G, Magi M, Gabrielli S, Arispici M, Tolari F, Dell’Omodarme M, Prati MC. Natural vectors of Dirofilariasis in Rural and Urban areas of the Tuscan Region, Central Italy. J Med Entomol. 2006;43(3):574–9.
Byrne K, Nichols RA. Culex pipiens in London Underground tunnels: differentiation between surface and subterranean populations. Heredity. 1999;82(1):7–15.
Becker N, Jost H, Weitzel T, Rettich K, editors. Exploiting the biology of urban mosquitoes for their control. Proceedings of the 3rd International Conference on Urban Pests; 1999; Czech University of Agriculture, Prague, Czech Republic.
Fonseca DM, Keyghobadi N, Malcolm CA, Mehmet C, Schaffner F, Mogi M, et al. Emerging vectors in the Culex pipiens complex. Science. 2004;303(5663):1535–8.
Rudolf M, Czajka C, Borstler J, Melaun C, Jost H, von Thien H et al. First nationwide surveillance of Culex pipiens complex and Culex torrentium mosquitoes demonstrated the presence of Culex pipiens biotype pipiens/molestus hybrids in Germany. PloS one. 2013;8(9):e71832.
Osorio HC, Ze-Ze L, Amaro F, Nunes A, Alves MJ. Sympatric occurrence of Culex pipiens (Diptera, Culicidae) biotypes pipiens, molestus and their hybrids in Portugal, Western Europe: feeding patterns and habitat determinants. Med Vet Entomol. 2014;28(1):103–9.
Manley R, Harrup LE, Veronesi E, Stubbins F, Stoner J, Gubbins S et al. Testing of UK populations of Culex pipiens L. for Schmallenberg Virus Vector competence and their colonization. PLoS ONE. 2015;10(8).
Reusken CB, de Vries A, Buijs J, Braks MA, den Hartog W, Scholte EJ. First evidence for presence of Culex pipiens biotype molestus in the Netherlands, and of hybrid biotype pipiens and molestus in northern Europe. J Vector Ecol. 2010;35(1):210–2.
Vogels CB, van de Peppel LJ, van Vliet AJ, Westenberg M, Ibanez-Justicia A, Stroo A, et al. Winter Activity and Aboveground hybridization between the two biotypes of the West Nile Virus Vector Culex pipiens. Vector-Borne Zoonotic Dis. 2015;15(10):619–26.
Zittra C, Flechl E, Kothmayer M, Vitecek S, Rossiter H, Zechmeister T, et al. Ecological characterization and molecular differentiation of Culex pipiens complex taxa and Culex torrentium in eastern Austria. Parasites Vectors. 2016;9(1):197.
Di Luca M, Toma L, Boccolini D, Severini F, La Rosa G, Minelli G et al. Ecological distribution and CQ11 genetic structure of Culex pipiens Complex (Diptera: Culicidae) in Italy. PLoS ONE. 2016;11(1).
Meireles ACA, Rios FGF, Fietoza LHM, da Silva LR, Julião GR. Nondestructive methods of Pathogen Detection: importance of Mosquito Integrity in studies of Disease Transmission and Control. Pathogens. 2023;12(6):816.
Bahnck CM, Fonseca DM. Rapid assay to identify the two genetic forms of Culex (Culex) pipiens L. (Diptera: Culicidae) and hybrid populations. American Journal of Tropical Medicine and Hygiene. 2006;75(2):251-5.
Gerken T, Kurtz J, Sauer KP, Lubjuhn T. DNA preparation and efficient microsatellite analysis from insect hemolymph. Electrophoresis. 1998;19(18):3069–70.
Nguyen HQ, Kim YI, Borzee A, Jang Y. Efficient isolation method for high-quality genomic DNA from cicada exuviae. Ecol Evol. 2017;7(20):8161–9.
Holehouse KA, Hammond RL, Bourke AFG. Non-lethal sampling of DNA from bumble bees for conservation genetics. Insectes Sociaux. 2003;50(3):277–85.
Ruiz F, Quinones ML, Erazo HF, Calle DA, Alzate JF, Linton YM. Molecular differentiation of Anopheles (Nyssorhynchus) benarrochi and an. (N.) oswaldoi from southern Colombia. Memórias do Instituto Oswaldo Cruz. 2005;100(2):155–60.
Kurtz J, Sauer KP. The immunocompetence handicap hypothesis: testing the genetic predictions. Proc Royal Soc B: Biol Sci. 1999;266(1437):2515–22.
Kim S, Trocke S, Sim C. Comparative studies of stenogamous behaviour in the mosquito Culex pipiens complex. Med Vet Entomol. 2018;32(4):427–35.
Benelli G. Mating behavior of the West Nile virus vector Culex pipiens - role of behavioral asymmetries. Acta Trop. 2018;179:88–95.
Rodenhouse NL, Bohlen PJ, Barrett GW. Effects of Woodland shape on the spatial distribution and density of 17-year periodical cicadas (Homoptera: Cicadidae). Am Midl Nat. 1997;137(1):124–35.
Lee Y-F, Lin Y-H, Wu D-H. Spatiotemporal variation in circada diversity and distribution, and tree use by exuviating nymphs, in east Asian tropical reef-karst forests and forestry plantations. Ann Entomol Soc Am. 2010;103(2):216–26.
Ferrington LC Jr., Coffman WP. Differential efficiencies of dip-net sampling versus sampling surface-floating pupal exuviae in biodiversity survey of Chironomidae. Chironomus J Chironomidae Res. 2014;35(27):31–40.
Sato Y, Sato S. Spring temperature predicts the long-term molting phenology of two circadas, Cryptotympana facialis and Graptopsaltria Nigrofuscata (Hemiptera: Cicadidae). Ann Entomol Soc Am. 2015;108(4):494–500.
Feinstein J. DNA sequence from butterfly fras and exuviae. Conserv Genet. 2004;5(1):103–4.
Gregory PG, Rinderer TE. Non-destructive sources of DNA used to genotype honey bee (Apis mellifera) queens. Entomol Exp Appl. 2004;111(3):173–7.
Dhananjeyan KJ, Paramasivan R, Tewari SC, Rajendran R, Thenmozhi V, Leo SV, et al. Molecular identification of mosquito vectors using genomic DNA isolated from eggshells, larval and pupal exuvium. Trop Biomed. 2010;27(1):47–53.
Watts PC, Thompson DJ, Daguet C, Kemp SJ. Exuviae as a reliable source of DNA for populations genetic analysis of odonates. Odonatologica. 2005;34(2):183–7.
Lefort MC, Boyer S, Worner SP, Armstrong K. Noninvasive molecular methods to identify live scarab larvae: an example of sympatric pest and nonpest species in New Zealand. Mol Ecol Resour. 2012;12(3):389–95.
Petersen SD, Masin TA, West R, White B, Wilson P. Species identification of tarantulas using exuviae for international wildlife law enforcement. Conserv Genet. 2007;8(2):497–502.
Nation JL. Insect physiology and biochemistry. 2nd ed. Boca Raton, Florida: CRC Press; 2008. ix, 544 p. p.
Krosch MN, Cranston P. Non-destructive DNA extraction form Chironomidae, including of fragile pupal exuviae, extends analysable collections and enhances vouchering. Chironomus J Chironomidae Res. 2012;25(25):22–7.
Kranzfelder P, Ekrem T, Stur E. Trace DNA from insect skins: a comparison of five extraction protocols and direct PCR on chironomid pupal exuviae. Mol Ecol Resour. 2016;16(1):353–63.
Wong J, Chu YY, Stoddard ST, Lee Y, Morrison AC, Scott TW. Microsatellite-based parentage analysis of Aedes aegypti (Diptera: Culicidae) using nonlethal DNA sampling. J Med Entomol. 2012;49(1):85–93.
RStudio Team. RStudio: Integrated Development for R. Boston, Massachusetts: RStudio, PBC; 2020. p. RStudio.
Qiagen. DNeasy® Blood & Tissue Handbook 2020 [updated July 2020. https://www.qiagen.com/us/resources/download.aspx?id=68f29296-5a9f-40fa-8b3d-1c148d0b3030=en.
Promega, Wizard®. SV Genomic DNA Purification System 2012. https://www.promega.co.uk/-/media/files/resources/protocols/technical-bulletins/101/wizard-sv-genomic-dna-purification-system-protocol.pdf?la=en.
Thongjued K, Chotigeat W, Bumrungsri S, Thanakiatkrai P, Kitpipit T. A new cost-effective and fast direct PCR protocol for insects based on PBS buffer. Mol Ecol Resour. 2019;19(3):691–701.
Siegel JP, Novak RJ, Lampman RL, Steinly BA. Statistical appraisal of the weight-wing length relationship of mosquitoes. J Med Entomol. 1992;29(4):711–4.
Schneider CA, Rasband WS, Eliceiri KW. NIH Image to ImageJ: 25 years of image analysis. Nat Methods. 2012;9(7):671–5.
Harbach R, Knight K. Taxonomists’ Glossary of Mosquito anatomy. Marlton, New Jersey: Plexus Publishing; 1980.
Smith CJ, Osborn AM. Advantages and limitations of quantitative PCR (Q-PCR)-based approaches in microbial ecology. FEMS Microbiol Ecol. 2009;67(1):6–20.
Kitpipit T, Chotigeat W, Linacre A, Thanakiatkrai P. Forensic animal DNA analysis using economical two-step direct PCR. Forensic Sci Med Pathol. 2014;10(1):29–38.
Grevelding CG, Kampkotter A, Hollmann M, Schafer U, Kunz W. Direct PCR on fruitflies and blood flukes without prior DNA isolation. Nucleic Acids Res. 1996;24(20):4100–1.
Loto F, Romero C, Baigori M, Pera L. Direct DNA amplification from fall armyworm (Lepidoptera: Noctuidae) samples. Fla Entomol. 2013;96(4):1618–20.
Kranzfelder P, Ekrem T, Stur E. DNA barcoding for Species Identification of Insect skins: a test on Chironomidae (Diptera) Pupal Exuviae. J Insect Sci. 2017;17(6).
Strickler KM, Fremier AK, Goldberg CS. Quantifying effects of UV-B, temperature, and pH on eDNA degradation in aquatic microcosms. Biol Conserv. 2015;183(1):85–92.
Tsuji S, Ushio M, Sakurai S, Minamoto T, Yamanaka H. Water temperature-dependent degradation of environmental DNA and its relation to bacterial abundance. PLoS ONE. 2017;12(4):e0176608.
Acknowledgements
The authors would like to thank Zoë Langlands for the maintenance and supply of the Brookwood Culex pipiens colony line.
Funding
This study was funded by the Biotechnology and Biological Sciences Research Council (BBSRC) BBS/E/I/00002118. Additional support was received from BBS/E/I/00007038 and BBS/E/I/00007039.
Author information
Authors and Affiliations
Contributions
LJ performed studies, conducted analysis, wrote, and approved the submission. SC, CS, ME and MC supervised the study, contributed to development of experimental design and edited and approved the submission.
Corresponding author
Ethics declarations
Ethics Approval and Consent to Participate
Not applicable.
Consent for Publication
Not applicable.
Competing Interests
The authors declare no competing interests.
Additional information
Publisher’s Note
Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.
Electronic Supplementary Material
Below is the link to the electronic supplementary material.
Rights and permissions
Open Access This article is licensed under a Creative Commons Attribution 4.0 International License, which permits use, sharing, adaptation, distribution and reproduction in any medium or format, as long as you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons licence, and indicate if changes were made. The images or other third party material in this article are included in the article’s Creative Commons licence, unless indicated otherwise in a credit line to the material. If material is not included in the article’s Creative Commons licence and your intended use is not permitted by statutory regulation or exceeds the permitted use, you will need to obtain permission directly from the copyright holder. To view a copy of this licence, visit http://creativecommons.org/licenses/by/4.0/. The Creative Commons Public Domain Dedication waiver (http://creativecommons.org/publicdomain/zero/1.0/) applies to the data made available in this article, unless otherwise stated in a credit line to the data.
About this article
Cite this article
Jones, L., Sanders, C., England, M. et al. Pupal Exuviae of Culex Pipiens L. (Diptera: Culicidae) Can be Utilised as a Non-Invasive Method of Biotype Differentiation. Biol Proced Online 26, 17 (2024). https://doiorg.publicaciones.saludcastillayleon.es/10.1186/s12575-024-00246-1
Received:
Accepted:
Published:
DOI: https://doiorg.publicaciones.saludcastillayleon.es/10.1186/s12575-024-00246-1