Introduction

Arthropod-borne and especially tick-borne diseases have become a growing public health concern over the past decades (World Health Organization 2004, 2014) and cause severe health problems in humans and animals (Estrada-Peña 2009). In order to maintain tick-borne diseases in a population, it is essential that the pathogen, a susceptible vertebrate host, and ticks with competence for the pathogen are available. Many different biotic and abiotic factors can influence these three components and all components must be available in sufficient numbers at the same time and the same place as described e.g., by Pfeffer and Dobler (2010). In nature, for new and emerging diseases, the chance for such a scenario is most likely very low. Nevertheless, outbreaks of vector-borne animal diseases like bluetongue disease or Schmallenberg virus infection in Europe (Wilson and Mellor 2009; Hoffmann et al. 2012) as well as Usutu virus infection in Germany (Becker et al. 2012) have shown that this scenario is reality, and in some cases cannot only cause severe medical problems but also financial losses in agriculture.

The spread of ticks and tick-borne pathogens can be promoted by global trade, animal migration (Pfeffer and Dobler 2010), and climate change (Estrada-Peña 2009). In this context, migratory birds play a more important role than less mobile wingless hosts (Hasle 2013).

In Germany, only a small number of studies have been carried out to investigate ticks from birds for tick-borne pathogens, and so far no data are available about tick infestation of birds. Franke et al. (2010a, b) checked 221 and 191 ticks, respectively, from birds for bacterial pathogens and detected Borrelia spp., Anaplasma phagocytophilum, Rickettsia spp., Babesia spp. and Francisella tularensis.

Initially, our aim was to determine the number of tick-carrying birds in Germany. It was hypothesized that tick infestation depends on species and age and the biology of the individual bird species, migratory bird species were compared to sedentary bird species and ground feeder species were compared to non-ground feeder species.

Except for TBEV, knowledge about tick-borne viral pathogens in birds in Germany is limited. It is expected that viral infection is more likely in adult ticks or nymphs than in larvae. In addition to tick infestation of birds, adult ticks and nymphs were checked for viral pathogens. Ticks were investigated by various real-time PCR systems for detection of whole virus genera or phylogenetic groups as a screening test that is less time-consuming and costly than species specific PCR systems, and with some specific real-time PCR tests for viral pathogens that are common in Germany, such as TBEV and Sindbisvirus.

Finally, adult ticks and nymphs were tested for Borrelia spp., the most common tick-borne pathogen in Germany.

Materials and methods

From July 2008 to December 2010, data on captured birds and collected ticks were provided by 25 persons or groups of persons in six federal states in Germany. Nine of them did not send in a complete dataset (ticks and total number of birds caught); hence, we had to exclude them from the risk factor analysis for tick infestation. Nevertheless, these ticks were included in the following parts of our study about the screening for tick species and tick-borne pathogens. The remaining persons caught birds in five different federal states (Table 1). Birds were caught in mist nets or in Helgoland traps and were identified by species and ring number. If possible, sex and age were determined. Bird species were allocated to migratory birds and differentiated as long-distance migratory birds which overwinter in Sub-Saharan Africa, and short-distance migratory birds which overwinter in Western Europe and Northern Africa, and sedentary birds that stay in the same region year-round. Ticks were removed by special tweezers, collected in plastic vials, frozen at −20 °C, transported to the lab, and differentiated according to Estrada-Peña et al. (2004), Pfister (2006) or Eckert et al. (2008), and finally stored at −80 °C for further investigations.

Table 1 Places of tick collection from birds
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Data of birds and ticks from birds were statistically analysed with the R statistical software 3.1.1., using Fisher exact test (fisher.test {stats}) and MS Excel 2010.

Classification into ground feeders and non-ground feeders is not always clear because most bird species have main places where they search for food and visit both, ground and non-ground places. Additionally, the places where birds mainly find food depend on the season. In this study, classification was done regarding the tick season for sedentary birds and the breeding season for migratory birds. In addition to the statistical analysis of the registered data sets from ticks and birds, in adult ticks and nymphs arthropod- and bird-associated viral pathogens as well as Borrelia spp. as the most common tick-borne bacterial pathogen in Germany were investigated. DNA and RNA were extracted as follows: Ticks were ground up in a mixer mill with three stainless steel beads (Retsch GmbH, Haan, Germany) and 400 μl medium (MEM Earle, Biochrom AG, Berlin, Germany). For DNA and RNA extraction, pools of five tick suspensions were generated with 100 μl of each tick suspension. The remaining sample was stored for further investigation of single ticks in case of pathogen detection in some of the pools. The pools were used for DNA and RNA extraction according to the manufacturer’s instructions using the NucleoSpin® 96 Virus kit (Macherey-Nagel, Düren, Germany). Detection of viral pathogens was performed by using the TBEV-real-time RT-PCR according to Schwaiger and Cassinotti (2003, modified by Klaus et al. 2010), a Flavivirus-RT-PCR (Johnson et al. 2010), a Simbuvirus-RT-qPCR (Fischer et al. 2013), a Lyssavirus-RT-qPCR (Fischer et al. 2014), and a Sindbisvirus-RT-qPCR (Jöst et al. 2010). Genome detection of Borrelia spp. was performed by Pan-Borrelia real-time PCR according to Strube et al. (2010).

Results

Birds

In total, 892 birds infested with ticks were found. After removing all datasets with missing data, especially without the total number of captured birds, 725 tick-infested birds, captured during ringing of 23,949 birds, could be further analysed for infestation rates, and a mean rate of 3.01 % (CI 2.80–3.24) was found. Most of the ticks were collected at the head around beak, eye and ear. The infestation rates were 5.59 % (CI 5.13–6.08) in ground feeders and 1.40 % (CI 1.22–1.61) in non-ground feeders. There is a significant difference between both groups (OR 4.16, p < 0.01, Fig. 1; Table 2). Referring to migration behaviour, the infestation rates were 4.29 % (CI 3.84–4.78 %) in sedentary birds and 2.45 % (CI 2.22–2.70) in migratory birds (OR 1.78, p < 0.01). Short-distance migratory birds were affected with higher rates (3.03 %, CI 2.71–3.38) than long-distance migratory birds (1.55 %, CI 1.27–1.88) as illustrated in Fig. 1 (OR 1.98, p < 0.01) in the groups of ground feeders and non-ground feeders, and Table 2.

Fig. 1
figure 1

Proportion of birds with ticks related to migration and feeding type. b birds, mb migratory birds, gf ground feeders, ngf non-ground feeders

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Table 2 Result of the pairwise comparison for feeding and migration type
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In the next steps, all 892 birds which were infested by ticks were included. In order to analyse tick infestation referring to data from birds, complete data sets were available from 838 tick-infested birds and were analysed with the following results: The mean tick infestation per bird was 4.2 ticks in the ground feeder group and 3.0 in the non-ground feeder group (Table 3). Referring to migration behaviour, remarkable differences were seen: Sedentary birds had an average of 4.7 ticks per bird, short-distance migratory birds 3.2 ticks and long-distance migratory birds only 2.0 ticks per bird (Table 4). Figure 2 highlights that in every group of birds referring to migration or feeding behaviour, some single individuals were infested by 10 up to 55 ticks per bird.

Table 3 Ticks collected from birds—non-ground feeders compared to ground feeders
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Table 4 Ticks collected from birds—compared to migration type
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Fig. 2
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Ticks per bird related to migration and feeding type. mb migratory birds, gf ground feeders, ngf non-ground feeders

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In the next analysis, all 892 birds were included. Table 5 shows the bird species with 10 or more individuals infested by ticks. Two hundred forty-five birds were blackbirds (Turdus merula), followed by 99 song thrushes (Turdus philomelos), 91 robins (Erithacus rubecula) and 71 blackcaps (Sylvia atricapilla). Altogether the 732 birds represent 14 species with 10 or more tick-infested individuals, and the remaining 160 tick-infested birds represent the other 34 species with tick-infested individuals only in single cases.

Table 5 Most infested bird species (10 or more individuals infested by ticks)
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The highest proportions of tick-infested birds were again found in blackbirds (Turdus merula), and song thrushes (Turdus philomelos), followed by bullfinches (Pyrrhula pyrrhula). The lowest proportions were found in siskin (Carduelus spinus), tree sparrows (Passer montanus) and reed buntings (Emberiza schoeniclus).

In the years 2009 and 2010, ticks were collected year-round, in 2008 only from July to December. Therefore, only the years 2009 and 2010 could be compared in this study. A remarkable difference in the number of ticks per bird was only seen in the group of short-distance migratory birds, which were non-ground feeders: in 2009, 3.8 ticks were collected, whereas in 2010 only 1.9 ticks per bird could be collected (data not shown in detail). All other data did not differ remarkably between the years. For this reason, the data were interpreted in the discussion-section over the whole period of tick collection and not separated into 2009 and 2010.

The age of the birds was only recorded for tick-infested birds. These birds were divided into two groups: juvenile birds (up to one year) and adult birds. Four hundred forty-three juvenile birds and 422 adult birds with ticks were caught. No statistical differences between the two groups were noticed. For 27 birds, it was not possible to determine the age (data not shown in detail).

Ticks

From 2008 to 2010, 3195 ticks were collected, identified and connected to the bird data (Tables 3 and 4). The most frequently detected tick species was Ixodes (I.) ricinus (78.02 %). 21.03 % of the ticks (especially engorged larvae) could only be identified as Ixodes spp. Among the 2520 ticks identified as different Ixodes spp., only 1.07 % belonged to the species I. hexagonus, I. canisuga or I. lividus. Only three nymphs from three different birds were identified as Haemaphysalis spp., other species like Hyalomma spp. or Dermacentor spp. were not found.

Birds were mostly infested by nymphs (65.10 %), followed by larvae (32.96 %). Only 1.94 % of the bird-infesting ticks were female or male adult ticks.

Only 12 of 838 tick-infested birds were infested with other than I. ricinus or not further differentiated Ixodes spp. (mostly engorged larvae). Among these 12 birds, only three were infested with Haemaphysalis spp. (three birds, three ticks), the others with I. canisuga (four birds, 10 ticks), I. hexagonus (two birds, two ticks) and I. lividus (three birds, 15 ticks).

Detection of pathogens

For pathogen screening, a total of 425 pools created from five homogenized tick samples (nymphs, female and male adult ticks, larvae were not included) were investigated. In case of positive results, single ticks of the positive pool were investigated.

In a first PCR-screening, all pools were investigated for TBEV-RNA as the most likely viral pathogen in ticks in Germany. The PCR was combined with an Ixodes-specific extraction control in a duplex assay. Successful nucleic acid extraction could be confirmed in all 425 pools. However, no TBEV-RNA could be co-amplified from those samples. Identical negative results were obtained using the broad-range PCR-assays for Flaviviruses, Simbuviruses and Lyssaviruses as well as the Sindbisvirus RT-qPCR. However, the positive control reactions confirmed that the assay and test conditions were suitable.

In contrast to the viral pathogens, the Pan-Borrelia real-time PCR determined 57 pools as Borrelia spp.-positive. Forty of the 57 Borrelia spp.-positive tick pools consisted of tick samples collected from two or more birds. From these 40 pools, all single ticks were analysed together with 45 larvae that had not been tested in pools before. Ninety-seven Borrelia spp.-positive nymphs and 27 Borrelia spp.-positive larvae were detected.

Seventeen Borrelia spp.-positive pools were not checked as single ticks because each of these pools consisted of ticks collected from one bird. The result of Borrelia spp.-positive ticks in these pools can theoretically match between 17 (only one tick in the pool was Borrelia spp.-positive) and a maximum of 85 (all five ticks in the pool were Borrelia spp. positive) and was not further differentiated. Together with the 97 Borrelia spp.-positive nymphs and 27 Borrelia spp.-positive larvae, investigated as single ticks, in total between 141 and 209 Borrelia spp.-positive ticks were found. In relation to the whole number of Borrelia-examined ticks (2125 nymphs and adults plus 45 larvae) 6.50–9.63 % of the ticks were found to be Borrelia spp.-positive.

Borrelia spp.-positive ticks were collected from 76 birds, representing 8.52 % of all tick-infested birds. Among the 76 birds, a majority of 54 individuals were blackbirds (Turdus merula), followed by 12 song thrushes (Turdus philomelos), and 10 individuals belonging to six species: pied flycatcher (Ficedula hypoleuca), bullfinch (Pyrrhula pyrrhula), dunnock (Prunella modularis), great tit (Parus major), long-tailed tit (Aegithalos caudatus) and marsh warbler (Acrocephalus palustris).

Figure 3 shows the bird collecting places. All places where birds with Borrelia spp.-positive ticks were caught were marked with a red dot, places with Borrelia spp.-negative ticks were marked with a blue dot. Most birds with Borrelia spp.-positive ticks were caught in Mülverstedt, Thuringia (18 birds, 11.8 % of all tick-wearing birds caught at this place), Dresden, Saxony (14 birds, 13.5 % of all tick-bearing birds caught at this place), Frankfurt, Hesse (11 birds, 12.8 % of all tick-wearing birds caught at this place), and Annaberg-Buchholz, Saxony (10 birds, 13.7 % of all tick-bearing birds caught at this place).

Fig. 3
figure 3

Bird and tick collecting places. red: Borrelia spp.-positive ticks were found, blue: no Borrelia spp.-positive ticks were found

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Three places with Borrelia spp.-positive ticks (Mülverstedt, Thuringia, Annaberg-Buchholz and Dresden, both Saxony) were chosen because ticks from birds were collected over 2 years at these places. Here, a species differentiation of Borrelia spp. was performed. Forty-eight single ticks were tested, and, in spite of the very limited amount of original material, Borrelia strains from 18 ticks were successfully determined (Table 6). In total, the most common species at these three places was B. garinii (10 samples, 5 different strains), followed by B. valaisiana (6 samples, 2 different strains) and one strain each of B. burgdorferi s.s. and B. afzelii.

Table 6 Borrelia-species differentiation, detected in ticks collected at three selected places
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Discussion

For many years, it has been well known that birds can serve as hosts for ticks, and depending on their specific biology they can cover smaller or greater distances, for example a long-distance migratory bird up to 1600 km non-stop across the Sahara (Hoogstraal and Kaiser 1961; Hoogstraal et al. 1961, 1963). Ticks and tick-borne pathogens can thus be transported to new non-endemic areas. In Sweden, 13 tick species have been listed, at least some of them occasionally, and the potential introduction of exotic pathogens is considered to be evident. It is mainly caused by the large number of people, animals and materials transported across the world, but also by migratory birds (Jaenson et al. 1994).

In most of the existing studies, only a small number of migratory birds was found to be infested with ticks. In Sweden 8 % (Elfving et al. 2010), in Great Britain 8 % (Jameson et al. 2012), in Greece (Antikythira) and Italy (Capri) 5 % (Lindeborg et al. 2012), in Finland 2.1 % of the birds were infested, on average with two ticks per bird (Nuorteva and Hoogstraal 1963). Our results with 3 % tick-infested birds (2.45 % of the migratory birds, 4.29 % of the sedentary birds) were in the same range. For Finland, extrapolated on the whole number of 600 million migratory birds, this means that every year nearly 25 millions of ticks are imported by birds (Nuorteva and Hoogstraal 1963). In the USA, more than 3000 birds were checked for ticks around the Gulf of Mexico. 3.56 % were infested with ticks (seven Amblyomma spp., one Ixodes spp.), and extrapolation of these findings suggests that four to 39 million exotic neotropical ticks could be transported to the USA annually by migratory songbirds with uncertain consequences for humans and animals (Cohen et al. 2015). For Europe such hypothesis should be handled with care: Most of the ticks found on birds were Ixodes spp.. Larvae need 2–5 days and nymphs 2–7 days for the blood meal, which limits the transportation distance. Birds need five and more days from Southern France to Iceland; however, the time span is strongly influenced by the weather conditions (Mehl et al. 1984). The average daily distance of small migratory bird species included in this study is about 60 to 75 km with a maximum of 150 km (Alerstam and Lindström 1990; Ellegren 1993; Berthold 2012). Depending on the bird species at least 6 to 14 days are needed to migrate from Northern African countries to Germany. In addition, the birds often stay at resting grounds for several days which further increases the migration time.

In contrast to Ixodes spp. Hyalomma marginatum needs up to 12–27 days for the blood meal (Balashov 1972), and in this time span it is possible that ticks can be transported from Africa to Europe. This was e.g., confirmed by the detection of Hyalomma marginatum in Norway (Mehl et al. 1984), Finland (Nuorteva and Hoogstraal 1963) and Sweden (Brinck et al. 1965) as well as in Great Britain (Jameson et al. 2012), Italy and Greece (Molin et al. 2011; Lindeborg et al. 2012; Wallmenius et al. 2014). In our investigations, no Hyalomma marginatum ticks were found. Thus, it can be concluded that Ixodes spp. collected from long-distance migratory birds were most likely acquired at a stopover place or near the place birds were caught for tick collection. Thus, a pathogen transfer by these ticks for example from Africa is not very likely.

Ground-feeder birds, migratory as well as sedentary birds, spend a predominant part of their live span in potential tick habitats and have a higher chance to be infested by ticks than birds that do not feed on the ground (Brinck et al. 1965; Cohen et al. 2015). This is in accordance with our results that demonstrated significant differences of tick infestation between ground feeders and non-ground feeders (5.59 % versus 1.40 % infested birds). Especially passerine birds, and in Europe the blackbird (Turdus merula) appear to be very important for harbouring ticks (Špitalská et al. 2006; Hasle 2013; Sándor et al. 2014). For Germany, our study confirmed that the blackbird (Turdus merula) plays a very important role. However, of the 14 most strongly infested bird species, nine species were migratory birds and able to transport ticks and pathogens to new potential foci, for example from the Mediterranean Sea to Germany. The importance of migratory birds for tick transportation could also be shown in the Danube delta by Sándor et al. (2014) where 92.25 % of the collected ticks were I. ricinus. This was also the predominant species in our investigations. Among the 3195 ticks, only three Haemaphysalis spp. ticks were detected, all the others belonged to the Ixodes spp., mostly I. ricinus. In our study in most cases, birds were infested with a low number of ticks per bird, i.e., between one and five. A mean infestation rate of two ticks per bird was found in winter in the Czech Republic (Literak et al. 2007), and six ticks per bird from spring to autumn in the Czech Republic and Slovakia (Taragel’ová et al. 2005). An influence on bird condition can thus be excluded. Norte et al. (2013) observed a significantly reduced general condition and weight loss in blackbirds (Turdus merula) infested with up to 10 or more larvae. In our study, the highest infestation in one bird was 55 ticks; however, such a high infestation rate is very seldom (Brinck et al. 1965).

Ticks on birds can be infected with a varying number of tick-borne pathogens, like Borrelia spp. (Anderson et al. 1986; Olsén et al. 1995; Gylfe et al. 2000; Comstedt et al. 2006; Poupon et al. 2006; Franke et al. 2010a, b), Babesia spp. (Hildebrandt et al. 2011), Rickettsia spp. (Elfving et al. 2010), Anaplasma and Ehrlichia spp. (Bjöersdorff et al. 2001; Hildebrandt et al. 2011). Only little is known about viral pathogens found in ticks from birds. Waldenström et al. (2007) checked 13,260 migratory birds in Sweden, 447 (3.4 %) birds were infested with ticks but only four birds were infested with six TBEV-infected ticks. It was concluded that TBEV can be distributed by tick-infested migratory birds in spite of the very low number of TBEV positive ticks detected. These findings were confirmed in Estonia (Geller et al. 2013), Switzerland (Lommano et al. 2014) and Latvia (Kazarina et al. 2015). Ernek et al. (1968) detected TBEV antibodies in sera from blackbirds (Turdus merula) and sparrows (Passer domesticus) as well as TBEV in ticks from blackbirds (Turdus merula). Other bird species might have a high natural resistance against TBEV. Experimental infections of buzzards (Buteo buteo), kestrels (Falco tinnunculus) (Rehaček et al. 1963), great tits (Parus major) (Grešíková et al. 1962) or pheasants (Phasianus colchicus) (Nosek et al. 1962) induced only in some cases TBEV-specific antibodies; neither viraemia nor clinical signs were observed. In our investigations, no TBEV-RNA could be detected. However, the most infested species blackbird (Turdus merula) could serve as transportation host for TBEV-infected ticks according to Ernek et al. (1968).

Hubálek (2004) emphasized that some species of migratory birds play an important role for circulation and ecology of some arboviruses like Sindbis virus or some Flaviviridae. Tick-borne Bunyaviridae in wild birds were not amplified, no clinical signs occurred, but the virus was detected in the blood for several days, which might be sufficient for an effective transportation to a new area (Hubálek et al. 1982). It was predicted that natural foci of tick-borne Bunyaviridae in Europe might spread from the south up to Switzerland, Austria and Germany, provided that winters in the next years are mild and summers are dry (Hubálek 2009). Crimean-Congo haemorrhagic fever virus (CCHFV), mostly found in Hyalomma spp., could adapt to other vectors (Bente et al. 2013). It might be spread to the north via animal trade and migratory birds, viraemia in the birds is not a precondition (Bente et al. 2013). Lindeborg et al. (2012) collected ticks from migratory birds on Capri (Italy) and Antikythira (Greece), 5 % of the birds were infested with ticks, mostly Hyalomma marginatum, only one bird was infested with three CCHFV virus positive Hyalomma marginatum.

Estrada-Peña et al. (2012) discussed CCHFV distribution, the lack of knowledge about vector competence of other tick species than Hyalomma marginatum, and generally recommended more empirical studies on the importance of birds for distribution of infected ticks and survival chances of the pathogens in new and up to now non-endemic areas. It is possible that mosquito-borne pathogens can adapt to ticks as vectors. Hagman et al. (2014) checked 747 ticks from migratory birds for West Nile virus (WNV), but all ticks were negative. Hubálek and Rudolf (2012) listed 27 tick-borne viruses in Europe, some of them are associated with birds. TBEV was detected in some bird species, like the common redpoll (Acanthis flammea) and the sparrow (Passer domesticus); viraemia after experimental infection was observed in some bird species like the common quail (Coturnix coturnix) or the mallard (Anas plathyrhynchos). Birds were not susceptible for experimental infection with CCHFV. Experimental infection with Bunyavirus Bhanja was not lethal for passerine birds. Some bird species (European starling, Sturnus vulgaris; chaffinch, Fringilla coelebs) can serve as hosts for orbivirus Tribeć without clinical symptoms, the same applies to orthobunyavirus Bahig and passerine birds. In many cases, only little is known about virus and birds. For distribution of Thogotovirus migratory birds can also be important (Calisher et al. 1987; Hubálek and Rudolf 2012).

In our study, the screening results for viral pathogens (Flavivirus-RT-PCR, Simbuvirus-RT-qPCR, Lyssavirus-RT-qPCR, Sindbisvirus-RT-qPCR) in ticks from birds in Germany were all negative. It can be concluded that in our study, all checked birds could not be detected as competent hosts or transportation hosts for these viral pathogens. Nevertheless, screening of ticks and birds for viral pathogens should be continued, especially with broad-range PCR methods as an early warning system.

Four Borrelia spp. were detected in ticks from birds (Table 6), distributed at nine of the 25 tick collecting places (Fig. 3). Birds, especially blackbirds (Turdus merula) and song trushes (Turdus philomelos), play an important role in the distribution of Borrelia spp. (Humair et al. 1993; Olsén et al. 1995; Taragel’ová et al. 2008), serve as reservoir hosts (Lommano et al. 2014), and can establish new Borrelia foci. In our study also rodent-associated B. afzelii was found in ticks from birds and confirmed the findings of Olsén et al. (1995), Franke et al. (2010b) and Geller et al. (2013) that also rodent-associated B. afzelii strains can be harboured in ticks feeding on birds. Gylfe et al. (2000) found reactivation of Borrelia infections in migratory birds caused by stress factors, which could explain the distribution of Borrelia spp. over longer distances and the infection of a new so far non-infected tick population. Among the most strongly infested birds besides blackbirds (Turdus merula) as a sedentary bird species, nine species were registered as short- or long-distance migratory birds (Table 5) that have the potential to distribute Borrelia spp. as described in new previously non-infected areas under stress conditions (Gylfe et al. 2000). In conclusion, not only blackbirds (Turdus merula) and other passerine birds should be examined for epidemiological studies of Borrelia spp. but also migratory bird species with relevant tick infestation.

To our knowledge, this was the first study about ticks and birds including such a large number of birds and ticks at different places in six federal states in Germany. In our investigations of birds, all collected tick species were well known in Germany and no unexpected exotic species was detected. For the first time, ticks from birds in Germany were also investigated for a wide range of viral pathogens. This was possible due to the established broad-range PCR systems for different virus genera. Nevertheless, no positive results were seen in this study, but cannot be excluded for the future. In addition, a high relevance of birds for the epidemiology of Borrelia spp. could be confirmed. Blackbirds (Turdus merula) but also some species of migratory birds highly infested with ticks should be focused for further investigations of this topic.

It is further suggested that short-distance migratory birds should be checked frequently for ticks in the future. Their specific biology allows them to transport ticks with pathogens for example from around the Mediterranean Sea to Germany within a few days. In case of good weather conditions, progressing climate change and presence of susceptible hosts for ticks and pathogens new viral endemic foci can be generated within a short time.

Estrada-Peña et al. (2012) recommended more empirical studies on the importance of birds for distribution of infected ticks and survival chances of the pathogens in new and so far non-endemic areas. Hubálek and Rudolf (2012) suggested that an active search for new tick-borne viruses or for new pathogenic variants of the known tick-borne viruses in Europe should be continued because some of them may often pass unnoticed or be misdiagnosed. For the future, long-term studies in the field including pathogens, vectors, hosts, microclimate and habitat structure are needed and should be combined with laboratory investigations on the transmission competence of various hosts to improve the knowledge about viral tick-borne diseases (Estrada-Peña and de la Fuente 2014).