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ORIGINAL RESEARCH article

Front. Vet. Sci., 25 September 2020
Sec. Parasitology
Volume 7 - 2020 | https://doi.org/10.3389/fvets.2020.578220

The Spatial Distribution of Dermacentor Ticks (Ixodidae) in Germany—Evidence of a Continuing Spread of Dermacentor reticulatus

Marco Drehmann1 Andrea Springer2 Alexander Lindau1 Katrin Fachet1 Sabrina Mai1 Dorothea Thoma1 Carina R. Schneider1 Lidia Chitimia-Dobler1,3 Michael Bröker4 Gerhard Dobler1,3 Ute Mackenstedt1 Christina Strube2*
  • 1Department of Parasitology, Institute of Biology, University of Hohenheim, Stuttgart, Germany
  • 2Institute for Parasitology, Centre for Infection Medicine, University of Veterinary Medicine Hannover, Hanover, Germany
  • 3Bundeswehr Institute of Microbiology, Munich, Germany
  • 4Global Health Press, Marburg, Germany

In Europe, two tick species of the genus Dermacentor occur, Dermacentor marginatus and Dermacentor reticulatus. When the spatial distribution of both species in Germany was studied comprehensively for the first time in 1976, D. marginatus populations were recorded along the Rhine and Main river valleys in southwestern Germany, while D. reticulatus was very rare. In the last 50 years, however, a considerable range expansion of D. reticulatus has been noted in several European countries. To assess the current distribution of Dermacentor spp. in Germany, citizens were asked to send in ticks suspected to belong to the genus Dermacentor or that were of “unusual” appearance. From February 2019 until February 2020, 3,902 Dermacentor ticks were received in total. Of those, 15.48% (604/3,902) were identified as D. marginatus and 84.24% (3,287/3,902) as D. reticulatus, while 11 specimens could not be identified to species level. The majority of D. reticulatus specimens was collected from dogs (1,212/2,535; 47.12%), while D. marginatus was mostly collected from horses (184/526; 34.98%). Our results confirm that the adults of both Dermacentor species are active all year round. D. reticulatus specimens were sent in from all federal states except the Free and Hanseatic City of Hamburg, while D. marginatus specimens were only received from locations in southwestern Germany. Overall, data obtained from this citizen-science study show that D. reticulatus has significantly expanded its range, especially in northern Germany. Regarding D. marginatus, new locations northwest of the previous range were detected, although the distribution has remained rather stable as compared to D. reticulatus. The spread of D. reticulatus, the vector of Babesia canis, is of major importance for veterinarians and dog owners in terms of canine babesiosis outbreaks or endemization in hitherto B. canis-free areas. Thus, veterinarians and veterinary students need to be informed about the new situation to be able to give adequate advice to dog owners on the extended D. reticulatus range and appropriate control measures.

Introduction

In Europe, the hard tick genus Dermacentor is represented by two species, Dermacentor marginatus (Sulzer, 1776) and Dermacentor reticulatus (Fabricius, 1794). The range of the ornate sheep tick, D. marginatus, extends from Portugal in the west throughout southern Europe and northern Africa into Central Asia. The species' southern and northern distribution limits are currently considered to be in Morocco and at the northern extension of the Rhine basin in Germany (1). Within this range, the species typically inhabits steppes, meadows, open forests, and semi-desert areas (2). The ornate dog tick, D. reticulatus, has a more northern distribution, occurring from northern Portugal to southern Latvia (1). It is found in a wide range of habitats, including meadows, open forests, heath-, and marshland, clearings, and suburban wasteland (3).

Immature stages of both D. marginatus and D. reticulatus are almost exclusively endophilic parasites of rodents. As adults, both sexes commonly infest larger mammals such as sheep, dogs, horses, goats, cattle (2), and occasionally humans (4). They play a role as vectors of various pathogens of considerable veterinary and medical importance. For example, both D. marginatus and D. reticulatus are competent vectors of protozoa of the order Piroplasmida, which may cause potentially fatal disease in animals. The most important causative agent of canine babesiosis in Europe, Babesia canis, is transmitted by D. reticulatus (5), while both Dermacentor species may transmit causative agents of equine piroplasmosis (6). Additionally, the vector function of D. reticulatus for tick-borne encephalitis virus (TBEV) has recently been proven (7). Although Ixodes ricinus (Linnaeus, 1758) is the main vector for TBEV in Europe, the virus has repeatedly been isolated from D. reticulatus in a TBEV-endemic area in Germany (8). Furthermore, Dermacentor spp. are the most relevant vectors for two causative agents of tick-borne lymphadenopathy in central Europe, Rickettsia slovaca transmitted by D. marginatus and R. raoultii transmitted by D. reticulatus (2, 3). In addition, both species are relevant in central Europe as vectors of Francisella tularensis (9), and D. marginatus may contribute to the transmission of Coxiella burnetii, the causative agent of zoonotic Q fever (10).

The first comprehensive study on the spatial distribution of the genus Dermacentor in Germany was published by Liebisch and Rahman (11). The authors reported a mosaic-like pattern of D. marginatus occurrence along the Rhine and Main river valleys in southwestern Germany. In contrast, an established D. reticulatus population was found at only one location in Germany at that time, in a forest near Tübingen. In the 1960s, D. reticulatus was also reported from the area of Potsdam in the former German Democratic Republic (12). In the recent past, comprehensive data on the distribution of both species in Germany have been gathered from either citizen-science approaches (13) or literature reviews (1, 14). These data, including reports on Dermacentor occurrence up to the year 2014, showed a considerable range expansion of D. reticulatus, which is in accordance with reports from other European countries, e.g., Slovakia and Poland (15, 16).

In 2019, we received indications of a further significant spread of D. reticulatus in Germany and thus aimed to assess the current distribution of D. reticulatus and D. marginatus in Germany by involving the general public. Citizens were asked to send in ticks belonging to the genus Dermacentor or of unusual appearance to allow mapping the distribution of both Dermacentor species in detail and identifying new areas of occurrence.

Materials and Methods

Citizen-Science Call

In February 2019, a single male specimen of D. reticulatus collected from a dog in the city of Hanover, northern Germany, was received by the Institute for Parasitology, University of Veterinary Medicine Hannover. This was an unusual finding, as hitherto the region of Hanover has not been considered within the range of this tick species. Upon request, the owner stated that the tick was found crawling on the dog after a walk and that the dog had not traveled recently. Additionally, in March 2019, a member of the institute noticed one female and three male Dermacentor ticks on her dog after a walk in Clausthal-Zellerfeld, located about 75 km southeast of Hanover, also hitherto not recognized as within the German Dermacentor range. To investigate whether these were accidental findings or if a further range expansion of D. reticulatus has occurred in Germany, a call to send in Dermacentor ticks was published in the May issue of the gazette of the Federal Chamber of Veterinarians, which is sent to every veterinarian in Germany. Furthermore, a press release was issued at the beginning of May 2019, asking citizens to send in Dermacentor ticks, which was shared through several print and social media.

Additionally, as of the end of February 2019, the Department of Parasitology at the University of Hohenheim near Stuttgart, southern Germany, released a call to send in Hyalomma ticks as well as ticks of unusual appearance. Again, respective press releases were circulated in various regional and national media, and, additionally, a website was designed for further information, where citizens were also specifically asked to send in ticks of the genus Dermacentor.

All media releases included pictures to help citizens distinguish between different tick genera. Along with the ticks, citizens were asked to provide information on the date and location of collection [Global Positioning System (GPS) data or postal code], the involvement of potential hosts, and details about the circumstances under which the tick was discovered. To increase motivation to participate, citizens were informed about the tick species of their specimen(s).

Tick Identification and Geographical Classification

Ticks were identified to species level using detailed morpho-metrical keys provided by Arthur (17), Siuda (18), and Estrada-Peña et al. (19).

The accuracy of the reported locations where ticks were found was categorized based on the details provided by the senders as follows: (i) the accuracy was estimated to be high if there was a high probability that a natural habitat of the collected tick was in close proximity to the location where it was found. For example, a high accuracy was assumed for ticks collected from cattle and horses, which did not leave their pasture in the days before an infestation was detected, as well as for ticks found on vegetation, but only when the sender provided a GPS reference or precise address. (ii) A medium accuracy was assumed for unengorged ticks found on dogs or humans during or immediately after a walk, as well as for ticks from cats or wild terrestrial animals, or if the location met the criteria for a high accuracy ranking but was reported only in the form of a postal code. (iii) The reported location was considered to be of low accuracy in cases of engorged ticks found on dogs or ticks found in an unsuitable habitat (e.g. inside a house), as the origin of these ticks was often unclear. (iv) If no information on the location or the circumstances of tick detection was provided or the ticks were detected on dogs or humans travelling large distances, the accuracy was categorized as unknown.

Only locations with a high or medium accuracy were used for distribution maps. These distribution maps were compared with the results reported by Rubel et al. (1) and Naucke (13). Maps were generated in R v. 3.5.1 (20) with spatial data retrieved via the rworldmap package (21), via the eurostat package (22), and from the Global Administrative Areas Database (23).

Results

Tick Collection and Identification

From mid-February 2019 until the end of February 2020, 3,902 ticks of the genus Dermacentor were received. With a total of 3,287 (84.24%) specimens, D. reticulatus was sent in much more frequently than D. marginatus (604 specimens; 15.48%). The remaining 11 specimens (0.28%) could not be identified to species level, as essential morphological features had been destroyed. The sex ratio of D. reticulatus was almost 1:1 [48.65% females (1,599/3,287) vs. 51.32% males (1,687/3,287)]. In addition, one D. reticulatus nymph was received (0.03%). In contrast, slightly more female than male D. marginatus were sent in [56.79% females (343/604) vs. 43.21% males (261/604)].

Geographic Distribution

For 3,877/3,902 ticks, the federal state of origin was unambiguous, whereas for 24 D. reticulatus and one D. marginatus, the federal state of origin was unclear due to travel activity of the senders. With the exception of the Free and Hanseatic City of Hamburg, D. reticulatus was collected in all federal states of Germany (Figure 1A). The number of D. reticulatus exceeded the number of D. marginatus received from each federal state, except for Rhineland-Palatinate, where D. marginatus was collected more frequently (Table 1, Figure 1B). In contrast to D. reticulatus, D. marginatus specimens were received from only six federal states located in southern and western Germany (Baden-Wuerttemberg, Bavaria, Hesse, North Rhine-Westphalia, Rhineland-Palatinate, and Saarland) (Table 1, Figure 1). Compared with the distribution maps provided by Rubel et al. (1) and Naucke (13), several additional sites of D. reticulatus occurrence are evident, especially in the north of Germany (Figure 2A). The spatial distribution of D. marginatus is largely comparable to the data provided by Rubel et al. (1) and Liebisch and Rahman (11). However, additional areas of occurrence were identified, for example, in the vicinity of Cologne (Figure 2B).

FIGURE 1
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Figure 1. Distribution of Dermacentor reticulatus (A) and Dermacentor marginatus (B) in Germany based on ticks submitted by German citizens from February 2019 to February 2020. Only locations with medium to high accuracy are shown (D. reticulatus: N = 1,744/3,287, D. marginatus: N = 450/604). More intense colors indicate multiple findings in close proximity. Red shaded areas in (A) represent areas of D. reticulatus distribution as reported by the European Centre for Disease Prevention and Control (ECDC) in July 2019 (https://www.ecdc.europa.eu/en/publications-data/dermacentor-reticulatus-current-known-distribution-july-2019) for comparison. In the map insert, federal states are abbreviated with italic letters (B, Berlin; BR, Bremen; BW, Baden-Wuerttemberg; BV, Bavaria; BB, Brandenburg; HH, Free and Hanseatic City of Hamburg; H, Hesse; LS, Lower Saxony; MWP, Mecklenburg-Western Pomerania; NRW, North Rhine-Westphalia; RP, Rhineland-Palatinate; S, Saxony; SA, Saxony-Anhalt; SH, Schleswig-Holstein; SL, Saarland; T, Thuringia). Cities are abbreviated with bold letters (BS, Brunswick; C, Cologne; F, Freiburg; G, Gießen; H, Hanover; K, Karlsruhe; L, Leipzig; M, Mannheim; S, Stuttgart).

TABLE 1
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Table 1. Distribution of the 3,263 Dermacentor reticulatus, 603 Dermacentor marginatus, and 11 unidentified Dermacentor specimens of unambiguous origin among the federal states of Germany.

FIGURE 2
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Figure 2. Distribution of (A) Dermacentor reticulatus (blue dots) and (B) Dermacentor marginatus (red dots) in Germany based on ticks submitted by German citizens from February 2019 to February 2020 in comparison to data from previous studies. In (A), D. reticulatus locations as reported by Rubel et al. (1) are shown in orange and those reported by Naucke (13) in green. In (B) D. marginatus locations as reported by Rubel et al. (1) are shown in yellow. More intense colors indicate multiple findings in close proximity. In the map insert, federal states are abbreviated with italic letters (B, Berlin; BR, Bremen; BW, Baden-Wuerttemberg; BV, Bavaria; BB, Brandenburg; HH, Free and Hanseatic City of Hamburg; H, Hesse; LS, Lower Saxony; MWP, Mecklenburg-Western Pomerania; NRW, North Rhine-Westphalia; RP, Rhineland-Palatinate; S, Saxony; SA, Saxony-Anhalt; SH, Schleswig-Holstein; SL, Saarland; T, Thuringia). Cities are abbreviated with bold letters (BS, Brunswick; C, Cologne; F, Freiburg; G, Gießen; H, Hanover; K, Karlsruhe; L, Leipzig; M, Mannheim; S, Stuttgart).

Temporal Course of Citizens' Dermacentor Collections

For 2,785/3,287 D. reticulatus and 596/604 D. marginatus specimens, information on the month of collection was provided. Both Dermacentor species occurred throughout the whole year. Most D. reticulatus specimens were found in September (940/2,785; 33.75%) and October 2019 (666/2,785; 23.91%), while smaller peaks occurred in March 2019 (187/2,785, 6.71%; following the press release by the University of Hohenheim), May 2019 (156/2,785, 5.60%; following the press release by the University of Veterinary Medicine, Hanover), and February 2020 (234/2,785, 8.40%). In comparison, D. marginatus numbers showed a peak in March 2019 (157/596; 26.34%) and February 2020 (199/596; 33.39%) (Figure 3).

FIGURE 3
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Figure 3. Dermacentor reticulatus (N = 2,785) and Dermacentor marginatus (N = 596) specimens by month of collection, sent in by German citizens from February 2019 to February 2020.

Host Association

Information on host association was available for 3,061/3,902 ticks (2,535/3,287 D. reticulatus and 526/604 D. marginatus). The majority of ticks were attached to or crawling on (potential) hosts, especially dogs (1,233/3,061; 40.28%) and horses (608/3,061; 19.86%). While D. reticulatus was collected more often from dogs (1,212/2,535; 47.81%) than from horses (423/2,535; 16.69%), D. marginatus was more common on horses (184/526; 34.98%) than on dogs (16/526; 3.04%). Both species were also detected on humans [D. reticulatus: 110/2,535 (4.34%); D. marginatus: 66/526 (12.55%)]. In 18 cases, citizens reported having been bitten by the ticks [nine times by D. marginatus (1.71%), nine times by D. reticulatus (0.36%)]. These ticks were often attached to the scalp. Detailed results on host association or collection location, respectively, are shown in Table 2.

TABLE 2
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Table 2. Host association or location of collection for the subset of Dermacentor ticks for which this information was available.

Discussion

The present study aimed to assess the current distribution of Dermacentor spp. in Germany. A continuing range expansion of D. reticulatus has been observed in several European countries (2426). This range expansion has been attributed to climatic changes as well as changes in land use, travel activities of humans and pets, and an increase in available wildlife hosts, e.g., red foxes and wild boar (3). The spread of D. reticulatus is of considerable veterinary importance, since it is the vector of Babesia canis, a life-threatening protozoan blood parasite of dogs. Currently, B. canis transmission only occurs in restricted areas in Germany (27, 28), while autochthonous infections with other piroplasms transmitted by Dermacentor spp., such as B. caballi and T. equi causing equine piroplasmosis, are rare in Germany (29). Nevertheless, introduction of these pathogens with infected animals or ticks from endemic areas may lead to the emergence of new transmission foci in areas where Dermacentor populations are present, especially since Babesia spp. are transmitted transovarially in ticks (30). Furthermore, D. reticulatus may pose a risk for humans due to its vector role for R. raoultii, F. tularensis, and TBEV, among other tick-borne pathogens (2, 3).

Although D. reticulatus is considered to have been part of the German tick fauna for at least 100 years (31), it was limited to only few reported locations during most of the 20th century (12, 32, 33). After 1976, D. reticulatus apparently started spreading probably from at least two different populations, one in southwestern (11) and one in northeastern Germany (12). In the 1990s, several previously unknown D. reticulatus populations were described following autochthonous cases of canine babesiosis (28, 34), although comprehensive studies on the species' distribution during the last quarter of the 20th century are lacking. Since the turn of the millennium, the distribution of D. reticulatus in Germany has been the subject of several studies, especially with regard to its increased spread (1, 13, 32, 35, 36). As compared to field studies or literature surveys, studies involving citizens can cover a wider spatial extent and result in a larger number of records (37, 38), although the quality of the obtained data can be variable.

In the current study, only records presumably reflecting the true occurrence of the tick species, i.e., those assigned to a high or medium geographic accuracy, were taken into account for distribution maps. Our results confirm earlier studies (1, 13, 32), indicating that D. reticulatus is continuing its spread throughout Germany.

When compared with the most recent data provided by the European Centre for Disease Prevention and Control (39) (ECDC, cf. Figure 1A), our results show that multiple new foci of D. reticulatus occurrence have appeared in northern, western, and southern Germany. However, the comparability of the ECDC's map with the data generated in the present study is limited, as the resolution of the map provided by the ECDC is based on government districts and is therefore comparatively low (39).

The obtained data show notable clusters of D. reticulatus occurrence around the cities of Hanover and Brunswick (eastern part of the northern German federal state of Lower Saxony), Stuttgart, Mannheim, Freiburg, and Karlsruhe (western part of the southern German federal state of Baden-Wuerttemberg). In this context, however, it has to be kept in mind that citizens were asked to participate in the study via press releases, which were covered by various regional and national media. Regional media coverage was probably enhanced in the vicinity of the involved research institutions (located in Hanover and Stuttgart); thus, the clusters near Hanover and Stuttgart may reflect this bias in media attention. Nevertheless, D. reticulatus was detected for the first time in the greater Hanover area, where occurrence was also verified by flagging of questing ticks in 2019 (data not shown). In addition, the data indicate several other potentially new locations outside the hitherto known range, especially in northwestern Germany. D. reticulatus was even found in the northernmost part of Germany, on the island of Sylt in the North Sea (~8.34° E/54.91° N). Two independent submissions of unfed male ticks from Sylt indicate that a D. reticulatus population may be present on the island. However, Sylt is also a popular tourist destination, and it cannot be entirely excluded that the unfed male ticks did not originate on the island, but reached it together with traveling dog hosts.

A further cluster of D. reticulatus occurrence was noted in the eastern part of Germany, around the federal state of Berlin. Interestingly, the citizen-science data do not confirm the presence of D. reticulatus in the area between the cities of Leipzig and Berlin, where the species was previously reported (1, 32). However, this may be due to the low population density in this area, limiting the number of participants in the study. Alternatively, D. reticulatus may be so widespread in this region that the local population did not consider respective findings worth reporting.

The distribution of D. marginatus as indicated by this study is still very similar to the data presented by Liebisch and Rahman (11), also included in the distribution map by Rubel et al. (1). Nevertheless, additional locations were found in the federal state Rhineland-Palatine and in North Rhine-Westphalia, near the city of Cologne (6.96° E/50.94° N). To date, the current northern distribution limit of D. marginatus was believed to be near Giessen, federal state of Hesse, Germany, at coordinates 8.32° E/50.65° N (40). Thus, a slight northward spread, probably along the Rhine, did occur. Interestingly, the ecological niche model by Walter et al. (40) identified most of Rhineland-Palatinate as suitable habitat for D. marginatus, as well as a large area to the northeast of the distribution limit, including the entire federal state of Hesse and even the southern part of Lower Saxony. In contrast, North Rhine-Westphalia, which is located to the northwest of Giessen, was not identified as a suitable habitat by Walter et al. (40). Further studies should continue to examine whether stable populations of D. marginatus are permanently established in North Rhine-Westphalia.

The seasonal activity of both Dermacentor species in Central Europe was studied multiple times in the past (2, 3). The data presented here accord with former reports (41), as D. reticulatus numbers in Germany peaked in September and October and, to a lesser extent, from March to May, whereas D. marginatus numbers peaked in February and March. Similar patterns were observed in field studies on questing Dermacentor ticks in other parts of Europe [e.g. (42, 43)]. Likewise, the current study confirms winter activity of both tick species (3, 43). However, it must be kept in mind that media coverage and human behavior, among other factors, can bias data gathered by a citizen-science approach, which limits the comparability to data from field collections. Sendings in March and May 2019 were probably influenced by the preceding press releases issued by the involved research institutions.

D. reticulatus was found predominantly on dogs, whereas D. marginatus was found mostly on equids. Among domestic animals, adult D. reticulatus seems to prefer dogs and may even outnumber I. ricinus on these hosts in areas where both species occur (44). In contrast, the main hosts of adult D. marginatus are ungulates, especially sheep (11). The fact that no D. marginatus was collected from sheep in the present study may be attributed to the study design, as horse or dog owners are far more likely to notice Dermacentor ticks on their animals as something unusual and worth reporting than shepherds, who probably do not consider D. marginatus ticks as unusual. In addition, sheep are probably less often checked for tick infestation than dogs or horses, and their thick wool makes ticks hard to spot if the infestation is not severe.

In light of the zoonotic pathogens that may be transmitted by Dermacentor spp., it is worth noting that human tick bites were only rarely reported. Although 4.34% of D. reticulatus and 12.55% of D. marginatus for which information on host association was provided were found crawling on humans, the proportions of ticks that had actually bitten humans were only 0.36 and 1.71%, respectively. In Spain, where both D. reticulatus and D. marginatus occur, these species accounted for 2.22 and 12.52% of 4,049 ticks found on humans, respectively (4). These numbers are comparable to our data; however, no information on the proportion of ticks that had actually bitten humans appears in the Spanish study. In the areas of Liguria and Tuscany, Italy, D. marginatus was identified as the second most important anthropophagic tick, after I. ricinus, accounting for 9.1% of 565 human tick bites (45). In contrast, among 2,547 ticks removed from humans in Germany between 2013 and 2017, only 0.16% were identified as Dermacentor spp. (46). Overall, the available data indicate that D. marginatus is more likely to attach to or even bite humans than D. reticulatus.

Conclusions

The present study shows that D. reticulatus is continuing to spread in Germany, especially in the northwestern part of the country. Overall, this tick was found in all federal states except the Free and Hanseatic City of Hamburg. In contrast, the distribution of D. marginatus is still restricted to southwestern Germany; however, newly identified locations in North Rhine-Westphalia show that this species has also undergone a geographical spread. A range expansion of both species is particularly worrying in light of their role as vectors. Both species may transmit human pathogens; however, they rarely seem to bite humans in Germany. Thus, the implications for public health may be considered of minor importance. By contrast, the spread of D. reticulatus is of major importance for veterinarians and dog owners in terms of canine babesiosis outbreaks or endemization in hitherto B. canis-free areas. Thus, veterinarians and veterinary students need to be informed about this situation, with updates during continuing education. Similarly, dog owners need to be advised on the expanding D. reticulatus range and the need for careful tick control measures by veterinarians and, where appropriate, by veterinary associations such as the German chapter of the European Scientific Counsel Companion Animal Parasites (ESCCAP).

Data Availability Statement

The original contributions presented in the study are included in the article/supplementary material, further inquiries can be directed to the corresponding author/s.

Author Contributions

CS, GD, UM, MD, AS, and AL designed the study. UM and CS coordinated the study and communicated with media representatives. MD designed the website. LC-D, MB, and GD contributed collected ticks. AS, MD, AL, KF, and LC-D identified tick species. AS, MD, AL, KF, SM, DT, and CRS participated in communication with the public and individual citizens as well as data handling. MD and AS drafted the manuscript. All authors participated in data interpretation, reviewed the manuscript draft, read, and approved the final manuscript.

Funding

AS and CS were supported by a grant of the European Union through the European Regional Development Fund and the Interreg North Sea Region Programme 2014–2020 as part of the NorthTick project (reference number J-No. 38-2-7-19).

Conflict of Interest

The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.

Acknowledgments

The authors would like to thank all citizens participating in this study for their valuable support.

References

1. Rubel F, Brugger K, Pfeffer M, Chitimia-Dobler L, Didyk YM, Leverenz S, et al. Geographical distribution of Dermacentor marginatus and Dermacentor reticulatus in Europe. Ticks Tick Borne Dis. (2016) 7:224–33. doi: 10.1016/j.ttbdis.2015.10.015

CrossRef Full Text | Google Scholar

2. Nosek J. The ecology and public health importance of Dermacentor marginatus and D. reticulatus ticks in central Europe. Folia Parasitol. (1972) 19:93–102.

Google Scholar

3. Földvári G, Široký P, Szekeres S, Majoros G, Sprong H. Dermacentor reticulatus: a vector on the rise. Parasit Vectors. (2016) 9:314. doi: 10.1186/s13071-016-1599-x

PubMed Abstract | CrossRef Full Text | Google Scholar

4. Fernández-Soto P, Pérez-Sánchez R, Encinas-Grandes A, Álamo Sanz R. Rickettsia slovaca in Dermacentor ticks found on humans in Spain. Eur J Clin Microbiol. (2006) 25:129. doi: 10.1007/s10096-006-0087-1

PubMed Abstract | CrossRef Full Text | Google Scholar

5. Gray JS, Estrada-Peña A, Zintl A. Vectors of babesiosis. Annu Rev Entomol. (2019) 64:149–65. doi: 10.1146/annurev-ento-011118-111932

PubMed Abstract | CrossRef Full Text | Google Scholar

6. Rothschild CM. Equine piroplasmosis. J Equine Vet Sci. (2013) 33:497–508. doi: 10.1016/j.jevs.2013.03.189

CrossRef Full Text | Google Scholar

7. Ličková M, Fumačová Havlíková S, Sláviková M, Slovák M, Drexler JF, Klempa B. Dermacentor reticulatus is a vector of tick-borne encephalitis virus. Ticks Tick Borne Dis. (2020) 11:101414. doi: 10.1016/j.ttbdis.2020.101414

PubMed Abstract | CrossRef Full Text | Google Scholar

8. Chitimia-Dobler L, Lemhöfer G, Król N, Bestehorn M, Dobler G, Pfeffer M. Repeated isolation of tick-borne encephalitis virus from adult Dermacentor reticulatus ticks in an endemic area in Germany. Parasit Vectors. (2019) 12:90. doi: 10.1186/s13071-019-3346-6

PubMed Abstract | CrossRef Full Text | Google Scholar

9. Telford S., Goethert, H. Toward an understanding of the perpetuation of the agent of tularemia. Front Microbiol. (2011) 1:150. doi: 10.3389/fmicb.2010.00150

PubMed Abstract | CrossRef Full Text | Google Scholar

10. Körner S, Makert GR, Mertens-Scholz K, Henning K, Pfeffer M, Starke A, et al. Uptake and fecal excretion of Coxiella burnetii by Ixodes ricinus and Dermacentor marginatus ticks. Parasit Vectors. (2020) 13:1–11. doi: 10.1186/s13071-020-3956-z

PubMed Abstract | CrossRef Full Text | Google Scholar

11. Liebisch A, Rahman MS. Zum Vorkommen und zur vektoriellen Bedeutung der Zecken Dermacentor marginatus (Sulzer, 1776) und Dermacentor reticulatus (Fabricius, 1794) in Deutschland. Tropenmed Parasitol. (1976) 27:393–404.

PubMed Abstract | Google Scholar

12. Negrobov VP, Borodin VS. Einige seltene Zeckenfunde im mittleren Teil der DDR. Angew Parasitol. (1964) 5:107–11.

13. Naucke T. Dermacentor reticulatus in Germany and the spread of canine babesiosis. In: Canine Vector-Borne Disease (CVBD) Symposium. Sicily: Mazara del Vallo (2007)

14. Rubel F, Brugger K, Monazahian M, Habedank B, Dautel H, Leverenz S, et al. The first German map of georeferenced ixodid tick locations. Parasit Vectors. (2014) 7:1–5. doi: 10.1186/s13071-014-0477-7

PubMed Abstract | CrossRef Full Text | Google Scholar

15. Bullová E, Lukán M, Stanko M, Petko B. Spatial distribution of Dermacentor reticulatus tick in Slovakia in the beginning of the 21st century. Vet Parasitol. (2009) 165:357–60. doi: 10.1016/j.vetpar.2009.07.023

PubMed Abstract | CrossRef Full Text | Google Scholar

16. Karbowiak G, Kiewra D. New locations of Dermacentor reticulatus ticks in Western Poland: the first evidence of the merge in D. reticulatus occurrence areas? Wiad Parazytol. (2010) 56:333–6.

PubMed Abstract | Google Scholar

17. Arthur DR. British Ticks. London: Butterworths (1963)

Google Scholar

18. Siuda K. Kleszcze (Acari: Ixodida) Polski: Cz. 1, Zagadnienia Ogólne. Warsaw. Naukowe PWN (1991)

19. Estrada-Peña A, Mihalca AD, Petney TN. Ticks of Europe and North Africa. Cham: Springer International Publishing. (2017). doi: 10.1007/978-3-319-63760-0

CrossRef Full Text | Google Scholar

20. R Core Team. R: A Language And Environment for Statistical Computing. Vienna: R Foundation for Statistical Computing (2018).

Google Scholar

21. South A. rworldmap: a new R package for mapping global data. R J. (2011) 3:35–43. doi: 10.32614/RJ-2011-006

CrossRef Full Text | Google Scholar

22. Lahti L, Huovari J, Kainu M, Biecek P. Retrieval and analysis of eurostat open data with the eurostat package. R J. (2017) 9:385–92. doi: 10.32614/RJ-2017-019

CrossRef Full Text | Google Scholar

23. Hijmans R, Garcia N, Wieczorek J. Global Administrative Areas Database (GADM) Version 3.6. Berkeley (2018) Available online at: http://www.gadm.org (accessed July 17, 2020).

24. Jongejan F, Ringenier M, Putting M, Berger L, Burgers S, Kortekaas R, et al. Novel foci of Dermacentor reticulatus ticks infected with Babesia canis and Babesia caballi in the Netherlands and in Belgium. Parasit Vectors. (2015) 8:232. doi: 10.1186/s13071-015-0841-2

PubMed Abstract | CrossRef Full Text | Google Scholar

25. Mierzejewska EJ, Estrada-Peña A, Alsarraf M, Kowalec M, Bajer A. Mapping of Dermacentor reticulatus expansion in Poland in 2012–2014. Ticks Tick Borne Dis. (2016) 7:94–106. doi: 10.1016/j.ttbdis.2015.09.003

PubMed Abstract | CrossRef Full Text | Google Scholar

26. Paulauskas A, Radzijevskaja J, Mardosaite-Busaitiene D, Aleksandravičiene A, Galdikas M, Krikštolaitis R. New localities of Dermacentor reticulatus ticks in the Baltic countries. Ticks Tick Borne Dis. (2015) 6:630–5. doi: 10.1016/j.ttbdis.2015.05.007

PubMed Abstract | CrossRef Full Text | Google Scholar

27. Beelitz P, Schumacher S, Marholdt F, Pfister K, Silaghi C. Untersuchungen zur Prävalenz von Babesia canis canis in Auwaldzecken (Dermacentor reticulatus) im Saarland. Berl Munch Tierarztl Wochenschr. (2012) 125:168–71. doi: 10.2371/0005-9311-125-116

PubMed Abstract | CrossRef Full Text | Google Scholar

28. Zahler M, Steffen T, Lutz S, Hähnel WC, Rinder H, Gothe R. Babesia canis and Dermacentor reticulatus in Munich: a new endemic focus in Germany. Tierarztl Prax K H. (2000) 28:116–20.

Google Scholar

29. Scheidemann W, Liebisch G, Liebisch A, Budde K. Equine Piroplasmose-Fallbericht einer akuten Infektion mit Theileria equi (syn. Babesia equi) in Deutschland. Pferdeheilkunde. (2003) 19:16–20. doi: 10.21836/PEM20030102

CrossRef Full Text

30. Chauvin A, Moreau E, Bonnet S, Plantard O, Malandrin L. Babesia and its hosts: adaptation to long-lasting interactions as a way to achieve efficient transmission. Vet Res. (2009) 40:37. doi: 10.1051/vetres/2009020

PubMed Abstract | CrossRef Full Text | Google Scholar

31. Vogel R. Dermacentor reticulatus F. in Württemberg. Württemberg Zbl Bakteriol I Abt Orig. (1924) 93:389.

32. Dautel H, Dippel C, Oehme R, Hartelt K, Schettler E. Evidence for an increased geographical distribution of Dermacentor reticulatus in Germany and detection of Rickettsia sp. RpA4. Int J Med Microbiol. (2006) 296:149–56. doi: 10.1016/j.ijmm.2006.01.013

PubMed Abstract | CrossRef Full Text | Google Scholar

33. Enigk K. Zum Vorkommen der Zecke Dermacentor pictus (Herm. 1804) in Deutschland. Z Parasitenkd. (1958) 18:419–22. doi: 10.1007/BF00260280

PubMed Abstract | CrossRef Full Text | Google Scholar

34. Gothe R, Wegerdt S. Babesiosis of dogs in Germany: epidemiologic case analysis. Tierarztl Prax K H. (1991) 19:170–3.

PubMed Abstract | Google Scholar

35. Petney T, Pfäffle M, Littwin N, Norra S, Böhnke D, Hogewind F, et al. Untersuchung der Ökologie von Zecken als Überträger von Krankheitserregern in Baden-Württemberg in Bezug auf Habitat, Landnutzung, Wirtstiere und Klima. BWPLUS project report. Karlsruhe: Karlsruhe Institute of Technology (2013).

36. Pluta S, Hartelt K, Oehme R, Mackenstedt U, Kimmig P. Prevalence of Coxiella burnetii and Rickettsia spp. in ticks and rodents in southern Germany. Ticks Tick Borne Dis. (2010) 1:145–7. doi: 10.1016/j.ttbdis.2010.04.001

PubMed Abstract | CrossRef Full Text | Google Scholar

37. Lewis J, Boudreau CR, Patterson JW, Bradet-Legris J, Lloyd VK. Citizen science and community engagement in tick surveillance-A Canadian case study. Healthcare. (2018) 6:22. doi: 10.3390/healthcare6010022

PubMed Abstract | CrossRef Full Text | Google Scholar

38. Ott D, Ulrich K, Ginsbach P, Öhme R, Bock-Hensley O, Falk U, et al. Tick-borne encephalitis virus (TBEV) prevalence in field-collected ticks (Ixodes ricinus) and phylogenetic, structural and virulence analysis in a TBE high-risk endemic area in southwestern Germany. Parasit Vectors. (2020) 13:303. doi: 10.1186/s13071-020-04146-7

PubMed Abstract | CrossRef Full Text | Google Scholar

39. European Centre for Disease Prevention and Control and European Food Safety Authority. Dermacentor reticulatus - Current Known Distribution. Stockholm (2019). Available online at: https://ecdc.europa.eu/en/disease-vectors/surveillance-and-disease-data/tick-maps (accessed on May 05, 2020).

40. Walter M, Brugger K, Rubel F. The ecological niche of Dermacentor marginatus in Germany. Parasitol Res. (2016) 115:2165–74. doi: 10.1007/s00436-016-4958-9

PubMed Abstract | CrossRef Full Text | Google Scholar

41. Kohn M, Krücken J, McKay-Demeler J, Pachnicke S, Krieger K, von Samson-Himmelstjerna G. Dermacentor reticulatus in Berlin/Brandenburg (Germany): activity patterns and associated pathogens. Ticks Tick Borne Dis. (2019) 10:191–206. doi: 10.1016/j.ttbdis.2018.10.003

PubMed Abstract | CrossRef Full Text | Google Scholar

42. Bartosik K, Wisniowski L, Buczek A. Abundance and seasonal activity of adult Dermacentor reticulatus (Acari: Amblyommidae) in eastern Poland in relation to meteorological conditions and the photoperiod. Ann Agr Env Med. (2011) 18:340–4.

PubMed Abstract | Google Scholar

43. Hornok S. Allochronic seasonal peak activities of Dermacentor and Haemaphysalis spp. under continental climate in Hungary. Vet Parasitol. (2009) 163:366–9. doi: 10.1016/j.vetpar.2009.03.048

PubMed Abstract | CrossRef Full Text | Google Scholar

44. Mierzejewska EJ, Welc-Faleciak R, Karbowiak G, Kowalec M, Behnke JM, Bajer A. Dominance of Dermacentor reticulatus over Ixodes ricinus (Ixodidae) on livestock, companion animals and wild ruminants in eastern and central Poland. Exp Appl Acarol. (2015) 66:83–101. doi: 10.1007/s10493-015-9889-0

PubMed Abstract | CrossRef Full Text | Google Scholar

45. Selmi M, Tomassone L, Ceballos LA, Crisci A, Ragagli C, Pintore MD, et al. Analysis of the environmental and host-related factors affecting the distribution of the tick Dermacentor marginatus. Exp Appl Acarol. (2018) 75:209–25. doi: 10.1007/s10493-018-0257-8

PubMed Abstract | CrossRef Full Text | Google Scholar

46. Springer A, Raulf M-K, Fingerle V, Strube C. Borrelia prevalence and species distribution in ticks removed from humans in Germany, 2013-2017. Ticks Tick Borne Dis. (2020) 11:101363. doi: 10.1016/j.ttbdis.2019.101363

PubMed Abstract | CrossRef Full Text | Google Scholar

Keywords: Dermacentor reticulatus, Dermacentor marginatus, species distribution, Germany, range expansion, citizen-science

Citation: Drehmann M, Springer A, Lindau A, Fachet K, Mai S, Thoma D, Schneider CR, Chitimia-Dobler L, Bröker M, Dobler G, Mackenstedt U and Strube C (2020) The Spatial Distribution of Dermacentor Ticks (Ixodidae) in Germany—Evidence of a Continuing Spread of Dermacentor reticulatus. Front. Vet. Sci. 7:578220. doi: 10.3389/fvets.2020.578220

Received: 30 June 2020; Accepted: 13 August 2020;
Published: 25 September 2020.

Edited by:

Anja Joachim, University of Veterinary Medicine Vienna, Austria

Reviewed by:

Riccardo Paolo Lia, University of Bari Aldo Moro, Italy
Richard G. Robbins, Walter Reed Biosystematics Unit (WRBU), United States

Copyright © 2020 Drehmann, Springer, Lindau, Fachet, Mai, Thoma, Schneider, Chitimia-Dobler, Bröker, Dobler, Mackenstedt and Strube. This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.

*Correspondence: Christina Strube, christina.strube@tiho-hannover.de

These authors have contributed equally to this work

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