Abstract
Maladaptive behaviors reflecting a “bad” choice of habitat or resource have been widely documented; however, their persistence is often difficult to interpret. The potter wasp Delta dimidiatipenne constructs mud cells, in each of which it lays a single egg and places several caterpillars to feed its offspring. Preliminary observations indicated that a portion of these caterpillars were already parasitized and contained the offspring of the gregarious parasitoid Copidosoma primulum. As a result, the offspring of the potter wasp often failed to develop. To characterize the distribution, frequency and consequences of this intriguing phenomenon, we surveyed potter wasp nests throughout the Negev Desert. Evidence for parasitized caterpillars (mummies) was found in ~85% of the sampled sites, in ~20% of previous years’ nest cells and in ~70–80% of the same year’s cells. The survival and pupal mass of the potter wasp offspring were negatively associated with the presence and number of parasitized caterpillars inside the cells. We concluded that the collection of parasitized caterpillars by D. dimidiantipenne is frequent and costly. The persistence of this behavior may result from limited discrimination ability against parasitized prey by female potter wasps, or by their limited ability to exhibit choosiness under field conditions.
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Introduction
Under the assumptions of natural selection, animals are expected to evolve traits that increase their reproductive success in the environment. Nevertheless, maladaptive traits, i.e., traits that do not contribute and could even negatively affect the fitness of an organism, are often observed in nature1. In particular, maladaptive behaviors reflecting a “bad” choice of habitat, resource, mate, or oviposition sites have been widely documented. The persistence of such behaviors is often difficult to interpret; yet, it may have severe consequences for the survival of individuals, populations, and even species2,3.
Some maladaptive behaviors may represent a response to manipulations imposed by a different species. For example, many parasites induce their host to behave in a maladaptive way to enhance their own transmission4,5. Other maladaptive responses may be expressed as the result of rapid environmental changes that cause a mismatch between environmental cues and their adaptive value6,7,8. Such situations are often termed “ecological” or “evolutionary traps” as the organism is attracted to a novel habitat or resource with unexpected negative outcomes. For example, Albatrosses and other seabirds were shown to ingest and to feed their chicks with plastic objects that resemble their prey9,10. In addition, several parasitoid wasps were shown to lay eggs in an invasive host, unsuitable for their development11,12. However, maladaptive behaviors may persist even in the absence of a recent environmental change13. Moreover, some behaviors may entail deleterious outcomes to all interacting players. Such responses have received little attention, and the mechanisms maintaining their persistence are poorly understood. Here, we investigated the occurrence of such an extreme interaction, where all species involved seem to suffer a high cost.
The potter wasp Delta dimidiatipenne, Saussure (Hymenoptera, Vespidae, Eumeninae) collects caterpillars to feed its offspring. Females construct mud cells, in each of which they lay a single egg and place several paralyzed caterpillars. When the egg hatches, the juvenile completes its development while feeding on the “preserved meal” and eventually breaks out of the mud cell as an adult14. Preliminary observations (D. Gerling 1967, confirmed by M. Segoli 2017, unpublished data) revealed that a large proportion of potter wasp nest cells in a certain location (Havarim Wadi, Negev Desert, Israel) failed to develop and remained sealed. Closer examination indicated that some of the caterpillars placed by the potter wasps in these cells were already parasitized and contained the offspring of the gregarious parasitoid Copidosoma primulum, Mercet (Hymenoptera, Encyrtidae) inside their bodies. As a result, all players in the interaction perished—the caterpillars were consumed internally by C. primulum larvae (as evidenced by their distinct remains); the potter wasp offspring could not fully exploit the parasitized caterpillars and presumably starved to death (as evidenced by the absence of an emergence hole); and the C. primulum parasitoids completed their development, but could not break out of the mud and remained trapped in the sealed cell (as evidenced by their dead bodies).
This raises the following questions: why do potter wasps collect caterpillars parasitized by C. primulum in their nests, and how is this behavior maintained? This is clearly not the result of a manipulation by another species, as the outcome is costly to all players. It is also not likely to represent a novel interaction (and hence an ecological trap), as it was observed over 50 years ago (D. Gerling, personal communication), and presumably all interacting species are native to the area (see Methods section). Models predict that maladaptive behaviors could persist depending on the portion of individuals in the population exposed to the low quality habitat or resource, the severity of the outcome of exposure, and the ability of the organism to evolve a corrective behavior15,16,17. On this basis, it can be hypothesized that the interaction between potter wasps and caterpillars parasitized by C. primulum is either not frequent enough or not costly enough (e.g., not always fatal) to induce a strong selection pressure. Alternatively, constraints may prevent the potter wasps from evolving or exhibiting discrimination against parasitized prey.
Here, we took a first step in addressing these hypotheses by characterizing the geographical distribution and frequency of the interaction between potter wasps and caterpillars parasitized by C. primulum, and by quantifying some of its costs and consequences. For this, we surveyed potter wasp nests in multiple locations throughout the Negev Desert in Israel, quantified the proportion of cells containing caterpillars parasitized by C. primulum, and related their occurrence to cell fate (i.e., developmental failure and body size of the potter wasp offspring). In addition, we collected caterpillars from nearby vegetation to determine the natural parasitism rate by C. primulum, and we observed potter females during nest construction. We hypothesized that if the time invested in caterpillar collection is substantial, and if the parasitism rate is high, females may be limited in their ability to evolve or exhibit choosiness under natural conditions.
Methods
Study species
Delta dimidiatipenne
The caterpillar hunting wasp D. dimidiatipenne is named for its habit of collecting caterpillars to feed its offspring. Females construct nests of ~20 cells during the spring (March–May). Adult wasps are around 25 mm long and feed on floral nectar. The species’ geographical distribution is wide-ranging, spanning from northwest Africa, Egypt and Somalia, throughout the Middle East, and east to India and Nepal. In Israel, its distribution ranges from the center to the south of the country14. Preliminary observations suggested that potter wasp females in the Negev Desert often collect caterpillars of the family Noctuidae. In particular, caterpillars of the native species Heliothis nubigera18 are the most common prey item found both in potter wasp nests and on nearby Zygophyllum dumosum shrubs, where potter wasps were observed to forage (M. Segoli and T. Rozenberg, personal observations).
Copidosoma primulum
Parasitoids of the genus Copidosoma are polyembryonic, i.e., each wasp egg proliferates to produce a clone of genetically identical embryos. Females parasitize the egg stage of their host (mostly lepidopteran). The host larva hatches and develops to its final instar. During this period, the Copidosoma egg proliferates clonally to produce numerous genetically identical embryos inside the host19,20,21,22. Embryos develop into larvae that consume the host internally and eventually pupate within the remnant host cuticle to form a “mummy”. Adult wasps (typically 1–2 mm in size) emerge from the mummy around two weeks later. Importantly for this study, the mummies have a distinct appearance that is easily identifiable even following wasp emergence. Parasitoids found in potter wasp nests in the Negev are of the species C. primulum. Although to date, there has been no formal description of this species from Israel, it is known from similar environments in Europe, Africa, and Central Asia23, and hence is likely to be native to this area. In the Negev Desert, C. primulum were found to develop in moth caterpillars of the family Noctuidae (Lepidoptera) and specifically on the common native species Heliothis nubigera.
Survey of previous-years nests
To obtain general information on the geographical distribution and frequency of the collection of parasitized caterpillars, we surveyed potter wasp nests of previous years (age unknown) during January 2018, in 13 sites throughout the Negev Desert (Fig. 1). Potter wasp nests (i.e., cell clusters) were found mostly in water passages under vehicle roads or under bridges. D. dimidiatipenne nests were identified based on their size and shape, although occasionally we might have sampled the nests of other potter wasp species that occur in the area (e.g., Katamenes dimidiativentris). In each site, we collected the content of up to 10 cells, from each of up to 10 nests (depending on availability) for a total of 505 cells. Evidence for C. primulum presence (i.e., dead adult wasps or remains of parasitized caterpillar mummies) was documented. While this wide survey allowed us to obtain some basic information on the distribution and frequency of this interaction in the Negev Desert, the poor condition of the nests (some of which were partially disintegrated or contained secondary residences such as spiders or beetles) might have caused biases in our estimations (e.g., some evidence of C. primulum might have been lost, or only preserved in certain cells). Hence, to achieve more accurate estimations and to relate cell fate to the presence of caterpillars parasitized by C. primulum, we conducted a second survey of newly constructed D. dimidiatipenne nests (see below).
Survey of same-year nests during development and subsequent emergence
This survey was conducted in four sites nearby water holes (Fig. 1), during the spring (Apr–May) of 2018. Newly constructed nests (of the same year) were identified via direct observations of active D. dimidiatipenne females during nest building, or according to nest appearance (made of smooth fresh mud). We documented the contents of 69 cells of 10 nests from these sites during potter wasp development. Since potter wasp females add a few cells to their nest every day, potter wasp offspring in these nests were at various developmental stages (mostly larval or pupal). Evidence for the presence of C. primulum in the cells was documented; however, the initial number of healthy caterpillars placed in each cell was often difficult to determine since some could have already been eaten by the potter wasp larvae. Cell content was further characterized as having either a live potter wasp larva, a dead or absent (assumed dead) potter wasp larva, or a potter wasp pupa (see Fig. 2 for examples of typical cell contents). While we could not predict what would have been the fate of still living larvae if not collected, the occurrence of dead or no larvae indicated that the potter wasp offspring did not survive, while the occurrence of pupae indicated that the potter wasp offspring were able to complete their development. These data allowed us to quantify the proportion of D. dimidiatipenne cells with evidence for caterpillars parasitized by C. primulum more accurately than in the first survey, and to relate the occurrence of parasitized caterpillars with potter wasp offspring survival, developmental stage, and pupal mass.
In addition, five newly constructed nests (N = 82 cells in total) were kept untouched until the end of the season. These nests were sampled following potter wasp emergence, allowing us again to quantify the proportion of cells that contained caterpillars parasitized by C. primulum, and also to relate their presence to cell failure (as indicated by the lack of emergence hole).
Behavioral observations
To characterize the investment of potter wasps in nest building, we directly observed nine potter wasp females during nest building in the sites surveyed for the same-year nests (overall 10 observations from the beginning till the end of cell construction). We quantified the number and duration of each component of the cell building process. In particular, we were interested in the relative investment in caterpillar collection vs. other components of the nest building.
Proportion of parasitized caterpillars on natural vegetation
To determine the parasitism rate by Copidosoma on caterpillars in the field, we collected Heliothis caterpillars from Zygophyllum dumosum shrubs near a potter wasp activity zone in the Havarim Wadi in March 2018 (N = 15) and dissected them under the microscope to search for parasitoid larvae. An additional sample was taken in Yacham in March 2019 (N = 39) and caterpillars were either dissected (N = 21) or reared till moth or Copidosoma pupation (N = 18).
Statistical analyses
We calculated the proportion of sites, nests, and cells with evidence for C. primulum in the survey of previous-years nests. The effects of the presence and number of caterpillars parasitized by C. primulum in a cell (1, 2, 3, 4, or more than 4), on potter wasp offspring survival and pupation success in same-year nests were tested via a nominal logistic regression. The effect of C. primulum presence on potter wasp offspring pupal mass was tested using a one-tailed t-test. The choice of this test was based on our assumption that parasitized caterpillars cannot be readily consumed by the potter wasp larvae, and hence their presence in the cell should lead to lower pupal mass. Due to the small number of cells with parasites other than C. primulum and their unknown role (see below), we did not examine their effect on cell fate. Statistical analyses were performed using JMP version 13.0.0 (SAS Institute Inc., Cary, North Carolina, USA).
Results
Survey of previous-years nests
Altogether we sampled 505 cells from 113 clusters in 13 sites. Evidence of C. primulum presence was found in 11 out of the 13 sampled sites, in 28% ± 7% of the nest clusters per site, and in 19% ± 5% (mean ± SE) of the cells per site (see Table 1). The overall distribution of this interaction ranged throughout the Negev Desert (Fig. 1).
Other than C. primulum, some cells in our survey contained parasites and parasitoids of either the potter wasp or caterpillars or both. Nest parasitoids included Melittobia acasta (Hymenoptera, Eulophidae), a new finding for Israel, and cuckoo wasps (Hymenoptera, Chrysididae). One unidentified species of ichneumonid (Hymenoptera, Ichneumonidae) and braconid wasps (Hymenoptera, Braconidae) are probably lepidopteran caterpillar parasitoids, but this was not verified. A species of the genus Monodontomerus (Hymenoptera, Torymidae), bombyliid flies (Diptera, Bombyliidae), and tachinid flies (Diptera, Tachinidae) were also found in the nests, but their host species could not be determined. Finally, some cells contained spiders, beetles, and bees that were probably secondary residents in the nests.
Survey of same-year nests during development
We found evidence of C. primulum presence in all four sites sampled, in 9 out of the 10 nest clusters, and in 71% of the cells (N = 69 pooled across sites). Cells with evidence for C. primulum were more likely to contain dead or no potter wasp larvae, and were less likely to contain potter wasp offspring that reached the pupal stage (Fig. 3A; nominal logistic regression, df = 2, χ2 = 11.36, P = 0.003). Moreover, potter wasp larva survival was further reduced as the number of parasitized caterpillar mummies found in a cell increased (Fig. 3A; nominal logistic regression, df = 8, χ2 = 24.38, P = 0.002). Finally, potter wasp pupae from cells with C. primulum had a lower body mass than those from cells without C. primulum (Fig. 3B; one-tailed t-test, t1 = 1.95 P = 0.04, N = 12). Hence, the presence of C. primulum seemed to have had a negative effect on potter wasp survival rate and body mass, but was not necessarily fatal. In accordance, we found evidence for parasitized mummies that were partially consumed—indicating that the potter wasp larvae could potentially feed on parasitized caterpillars prior to C. primulum pupation.
Other than C. primulum, several cells contained other potential parasites including a cuckoo wasp (Chrysididae) in one cell, torymid wasps in three cells, fly pupae in five cells, and a braconid wasp in one cell. None of these cells contained live potter wasp offspring.
Survey of same-year nests following wasp emergence
We found evidence of C. primulum presence in 79% of the same-year cells that were sampled at the end of the season (N = 82 cells). The presence of C. primulum was positively related with cell failure (Fig. 4; nominal logistic regression, df = 1, χ2 = 21.87, P < 0.001). Moreover, the probability of cell failure further increased with the number of parasitized caterpillar mummies per cell (nominal logistic regression, df = 5, χ2 = 12.07, P = 0.034). This again suggests that the presence of caterpillars parasitized by C. primulum reduces potter wasp developmental success, but does not entirely eliminate it.
Other than C. primulum, we found evidence for fly parasites in 13 cells, for braconid wasps in four cells, for torymid wasps in one cell, and for a cuckoo wasp in one cell.
Behavioral observations
Direct observations of females during cell construction (N = 10) revealed that the construction of a single cell included 4 ± 0.5, 2–6 (Mean ± SE, Range) excursions for collecting water, taking 4.3 ± 0.8, 1.4–8 min each, and 12.3 ± 1.5, 9–24 excursions to collect soil, taking 1.6 ± 0.2, 1–2.5 min each, which was then deposited on the nest. At the completion of the pot structure, the female laid a single egg inside the cell. The female then disappeared to forage for caterpillars that were then placed in each cell for a total of 5.2 ± 0.3, 3–7 caterpillars; each excursion for a single caterpillar took 19.5 ± 3.6, 9–39 min. The female then sealed the cell and deposited additional soil on the cell and on adjacent cells, presumably to protect it from parasites24. Altogether, cell construction took 34.4 ± 4.5, 21–57 min till oviposition, and an additional 120.2 ± 18.4, 59–218 min till cell provisioning was completed, and the cell was sealed. Hence, caterpillar collection constituted a major portion of the time dedicated to nest building. An ethogram of the nest building behavior is depicted in Fig. 5.
Proportion of parasitized caterpillars on natural vegetation
Six out of 15 (40%) of the caterpillars collected in Havarim, contained Copidosoma embryos or larvae, which were easily identifiable19. In addition, one caterpillar contained a single larva of an unknown solitary parasitoid. 12 out of 39 (31%) of the caterpillars collected in Yacham, contained Copidosoma larvae while dissected or produced Copidosoma following rearing. In addition, three caterpillars produced other unidentified parasitoids.
Discussion
The collection of parasitized caterpillars by females of the potter wasp D. dimidiatipenne seems maladaptive as females invest time and energy in building and provisioning cells with resources that ultimately will not (or will hardly) serve their offspring. The results of our field survey suggest that this interaction is not rare or anecdotal, and that it entails a high cost in terms of reduced survival and potential fitness of the potter wasp offspring. Hence, it is likely to impose a strong selection on the potter wasps.
Estimations of the proportion of cells with parasitized caterpillars varied widely among the sampled locations and was generally lower when surveying previous-years nests (~20%), than when surveying same-year nests (~70–80%). However, even if we consider the lower estimation range, the proportion of the population that is likely to be affected and the loss of reproductive success to the potter wasps, seems substantial. Moreover, this phenomenon was found to be widely distributed throughout the Negev Desert and, hence, cannot be considered as a local sink. Given the presumed large overlap in the distribution of the studied species, it is likely to be even more widely distributed than documented here. Finally, similar interactions may potentially occur involving other potter wasp species that collect similar prey or whose prey also suffer high parasitism rates. Indeed, in several anecdotal reports, the authors documented the occasional occurrence of parasitized prey or prey-parasites25,26,27,28,29 in potter wasp nests. However, the distribution and consequences of such interactions were not examined further. We suggest that while the phenomenon by itself is not unique, the high frequencies and consequences reported here are probably exceptional.
Despite the implied reduced survival of D. dimidiatipenne potter wasp offspring, the presence of parasitized caterpillars was not always fatal. This could be explained by the simultaneous occurrence of non-parasitized caterpillars inside the cells, sufficient for the potter offspring’s nourishment. In addition, although potter wasp offspring are not likely to feed on sclerotized pupae or adult C. primulum parasitoids, they may still be able to feed to some extent on parasitized caterpillars at earlier developmental stages, as implied by the presence of partially consumed mummies. Hence, parasitized caterpillars could still occasionally provide a limited amount of food to the potter wasp offspring, depending on the timing of potter wasp development relative to C. primulum pupation. Our observations suggest that this window of opportunity is short—as we have often observed potter wasp larvae cohabiting with already mummified caterpillars.
Under the abovementioned scenarios, the cost may sometimes be manifested in the development of smaller potter wasp offspring, rather than in their mortality. Indeed, we found that potter wasp offspring that reached pupation in cells with parasitized caterpillars had a lower body mass, suggesting that they will develop into smaller adults. The consequences of smaller body size for D. dimidiatipenne adult reproductive success have not yet been explored; however, body size is known to be related to adult fitness in many insects30. Specifically in potter and other solitary nest-provisioning wasps, larger females were shown to live longer, provision more offspring, and collect more and heavier food items in their nests than smaller females31,32,33. Hence, even in cases in which the potter wasp offspring survive to complete their development, the occurrence of parasitized caterpillars in the cell is likely to compromise their fitness.
Given the high frequency and high implied costs, the question as to why D. dimidiatipenne potter wasps collect parasitized caterpillars becomes even more intriguing. One possibility is that certain constraints prevent potter wasps from evolving or exhibiting discrimination against parasitized caterpillars. Many parasitoid wasps are able to discriminate against already parasitized hosts, on which the survival and development of their offspring are compromised34,35. Although selection in relation to prey species is probably common in potter wasps36,37,38,39, discrimination in relation to prey parasitism status has rarely been reported. In one case, females of the species Euodynerus foraminatus were observed to inspect and evacuate caterpillars from their nests31. This was speculated to be a mechanism to eliminate parasites of the wasps or parasitized caterpillars; however, this interpretation has not been confirmed. Hence, the ability of potter wasps, in general, and of D. dimidiatipenne, specifically, to identify already parasitized prey is yet unknown.
Another option is that the high costs of examining prey items and discriminating while foraging in the field may overcome their potential advantages40. This may be especially true in light of potential environmental risks such as predation and parasitism. Indeed, potter wasps are known to be attacked by birds while foraging and to suffer from parasitism in their nest25,28,37,41,42. Our observations of D. dimidiatipenne females during nest building revealed that the largest portion of their time was devoted to searching for caterpillars to provision their nest. In addition, we observed potential parasites (flies and wasps) visiting cells while the potter wasp was absent (M. Segoli and T. Rozenberg, personal observation), as well as developing inside the nest cells. Such environmental risks may hinder females from evolving or exhibiting choosiness under natural conditions.
The acceptance of a low-quality resource may also depend on the availability of alternatives. Both theoretical models and empirical evidence suggest that individuals are more likely to accept poor quality food items or hosts if the availability of high quality resources in the environment is limited43. For example, parasitoid females are more likely to accept an already parasitized host, if they had previously experienced encounters with such low quality hosts35,44,45. Our data suggest that the parasitism rate by Copidosoma on caterpillars in the field was not negligible. Hence, even if potter wasp females have the potential ability to discriminate against parasitized caterpillars, they may not exhibit such choosiness if they frequently encounter already parasitized caterpillars in the field.
Another intriguing possibility is that innate biases make the parasitized caterpillars even more attractive to the foraging potter wasp females. For example, it was previously shown that caterpillars parasitized by Copidosoma spp. feed for longer durations and reach a higher mass than non-parasitized ones19,20,46. In addition, preference for larger prey items was demonstrated in several species of predatory wasps, at least within the limitation of wasp size47,48,49,50. Hence, D. dimidiatipenne potter wasp females may exhibit a preference for parasitized caterpillars due to their higher mass, despite their eventual poor suitability for feeding their offspring. Finally, parasitism by C. primulum may induce the caterpillars to behave in a way that makes them more exposed or vulnerable to potter wasp females, e.g., due to their different feeding habits or compromised immune system. These possibilities should be further explored.
Responses at the population level should also be considered. Despite the high costs from the collection of parasitized prey, D. dimidiatipenne populations in the Negev Desert seem to remain viable. This may suggest that females are able to partially compensate for these costs. Compensation via collecting other prey types is not likely as H. nubigera is the most common prey species in the nests. This may reflect its high density in the environment, possibly enhanced by the wasp conditioning on this prey type, as demonstrated in other wasp species51. Instead, potter wasps probably compensate by their ability to construct many cells during their lifetime. In fact, many solitary and parasitoid wasps suffer high rates of developmental failure due to varied causes, including host unsuitability and interference with other parasitoids52,53,54. Such cases of developmental failure often still cause the death of the host/prey and hence may have subsequent negative effect on their populations53. Although in the case described here, already parasitized caterpillars have minimal survival prospects whether or not they are collected to the nests, some cells that fail to develop may also contain healthy caterpillars. Hence, studying the population dynamics and feedback mechanisms between these three interacting species could shed further light on the occurrence and persistence of this phenomenon.
In conclusion, we have demonstrated high frequency and substantial costs for the collection of parasitized caterpillars by D. dimidiatipenne females. Additional observations and experimentations are required in order to further determine the spatial and temporal variations in the parasitism rate and population densities in the field; as well as to test whether parasitism by C. primulum induces a change in caterpillar attractiveness or susceptibility to potter wasp females. Such data will shed light on the mechanisms for the maintenance of this specific interaction, as well as on the persistence of maladaptive behaviors in nature, in general.
Data availability
The datasets generated during and/or analyzed during the current study are available from the corresponding author on reasonable request.
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Acknowledgements
This manuscript is dedicated to the memory of Prof. Dan Gerling who has shared his fascinating observations with us. We thank Ofir Altestein and Enosh Zin for technical support; Eviatar Feingold, Ariel-Leib-Leonid Friedman, John Noyes, Oz Ritner and Zoya Yefremova, for aid in specimen identification; Tamar Keasar for comments on this manuscript and Samara Bel for English editing. We thank the Koshland Family Career Development Fund for Desert Studies. This is publication number 1067 of the Mitrani Department of Desert Ecology.
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M.S., S.L. and T.R. conceived the ideas; M.S., S.L., T.R. and I.H. designed the methods; M.S., S.L., T.R., I.H., M.K. and F.M. performed the field experiments; M.S., T.R. and I.H. sorted the collected samples; M.K. identified the specimens; M.S. analyzed the data and led the writing of the manuscript; S.L., T.R., F.M., M.K. and I.H. provided comments on the manuscript.
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Segoli, M., Leduc, S., Meng, F. et al. Frequency and consequences of the collection of already parasitized caterpillars by a potter wasp. Sci Rep 10, 8655 (2020). https://doi.org/10.1038/s41598-020-65096-9
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DOI: https://doi.org/10.1038/s41598-020-65096-9
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