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Systematic Review

Global Distribution of Babesia Species in Questing Ticks: A Systematic Review and Meta-Analysis Based on Published Literature

by
ThankGod E. Onyiche
1,2,
Cristian Răileanu
2,
Susanne Fischer
2 and
Cornelia Silaghi
2,3,*
1
Department of Veterinary Parasitology and Entomology, University of Maiduguri, P. M. B. 1069, Maiduguri 600230, Nigeria
2
Institute of Infectology, Friedrich-Loeffler-Institut, Federal Research Institute for Animal Health, Südufer 10, 17493 Greifswald-Insel Riems, Germany
3
Department of Biology, University of Greifswald, Domstrasse 11, 17489 Greifswald, Germany
*
Author to whom correspondence should be addressed.
Pathogens 2021, 10(2), 230; https://doi.org/10.3390/pathogens10020230
Submission received: 20 January 2021 / Revised: 17 February 2021 / Accepted: 17 February 2021 / Published: 19 February 2021

Abstract

:
Babesiosis caused by the Babesia species is a parasitic tick-borne disease. It threatens many mammalian species and is transmitted through infected ixodid ticks. To date, the global occurrence and distribution are poorly understood in questing ticks. Therefore, we performed a meta-analysis to estimate the distribution of the pathogen. A deep search for four electronic databases of the published literature investigating the prevalence of Babesia spp. in questing ticks was undertaken and obtained data analyzed. Our results indicate that in 104 eligible studies dating from 1985 to 2020, altogether 137,364 ticks were screened with 3069 positives with an estimated global pooled prevalence estimates (PPE) of 2.10%. In total, 19 different Babesia species of both human and veterinary importance were detected in 23 tick species, with Babesia microti and Ixodes ricinus being the most widely reported Babesia and tick species, respectively. Regardless of species, adult ticks with 2.60% had the highest infection rates, while larvae had the least with 0.60%. Similarly, female ticks with 4.90% were infected compared to males with 3.80%. Nested-polymerase chain reaction (PCR) 2.80% had the highest prevalence among the molecular techniques employed. In conclusion, results obtained indicate that Babesia species are present in diverse questing tick species at a low prevalence, of which some are competent vectors.

1. Introduction

Both Theileria and Babesia species belong to the order Piroplasmida, are widely distributed and are among the economically important tick-borne hemoparasites of mammals [1]. Babesiosis has been well-known since the 19th century and is distributed worldwide as a disease of veterinary importance in cattle, sheep, pigs, dogs, and horses and in recent times has attracted attention as a zoonotic infection in humans [2,3].
Babesia is second only after Trypanosomes globally as the commonly found hemoparasites in the blood of mammals [4]. In 1888, Victor Babes, a Romanian biologist, was the first to discover the presence of intra-erythrocytic microorganisms in the blood of cattle, and he later observed similar intra-erythrocytic organisms in the blood of sheep [5]. A few years later, these microorganisms, which were later named “Babesia”, were noted in the blood of cattle in the United States [6]. These microorganisms in cattle were named Babesia bovis and B. bigemina, and in sheep, B. ovis [7]. Ever since, different species of Babesia have been observed parasitizing the blood of domestic animals. Over 100 species have been described thanks to the advances in microscopy, cell culture, and molecular techniques [1,3]. The clinical manifestations of babesiosis vary considerably across different animal species, but abortions, decreased milk and meat production, and mortality have been observed [8].
Furthermore, human babesiosis was first documented in the former Yugoslavia republic in 1957 [9]. Babesiosis in humans is becoming a public health concern as several species, including B. microti, B. divergens and B. venatorum, can infect humans accidentally, causing disease [8]. Babesia microti infections are less acute compared with B. divergens, while those due to B. venatorum are milder [10]. Affected persons are often asymptomatic except in immunocompromised individuals where the outcome can be fatal [8,11]. Clinical complications, such as hemolysis, acute respiratory distress and multiorgan malfunctioning leading to death have been observed [12].
Ixodid ticks are obligate hematophagous acarines, which feed on a wide variety of hosts, and over 700 species have been described [13]. To complete their life cycle, ticks must look for suitable hosts. Therefore, newly hatched larvae, nymphs and adults that are unfed need to seek a host for a blood meal for their further development into the next stage [14]. Detection and attachment to potential hosts in Ixodidae can be achieved through three major behavioral patterns: hunting, tick-host cohabitation, and questing [15].
Species of questing ticks within the genera Ixodes, Dermacentor and Haemaphysalis have been described and collected for the detection of tick-borne pathogens. Other species within the genus Rhipicephalus and Hyalomma have also been collected from the environment [16]. Questing ticks can be collected principally by flagging or dragging, among other methods, including trapping using baits (e.g., carbon dioxide) [14]. Ixodid ticks are the primary vectors of Babesia, but the parasites are sustained in a complex system of animal reservoirs and tick vectors [17,18]. In Ixodid ticks, the sexual phase of the life cycle of Babesia typically takes place acquiring and transmitting the parasites during blood meals from their host [19,20]. Transovarial transmission is exclusive within the Babesia sensu stricto evolutionary lineage, thereby allowing the pathogens to perpetuate their long-term persistence in ticks and serving as parasite reservoirs when vertebrate hosts are absent [18,20].
Ixodes ricinus is the most common tick, widely distributed in Europe (Western Palearctic), while the focal distribution of Dermacentor reticulatus has been observed [17,21,22,23,24,25]. Other species like I. scapularis are common in the United States of America [26,27], I. ovatus and Hemaphysalis longicornis in East Asia [28,29,30] and I. persulcatus in Europe (Russia) and parts of Central and Northern Asia [31,32]. Other species of Rhipicephalid ticks have also been reported globally [8,33,34].
Major interest in the role of questing ticks as vectors of pathogens of zoonotic importance began to emerge in the early 2000s. In questing ticks, aside from B. microti, which has been well reported in Europe, Asia, and America with varying infection rates [35,36,37,38], B. divergens and B. venatorum have been exclusively reported in Europe in the last two decades [17,39,40]. Other species of Babesia that infect domestic animals and that have been detected in questing ticks include B. canis [24,41], B. odocoilei [26,42], B. ovata [29,43], B. bigemina [8,43], B. bovis [43,44], B. caballi [41,45], B. capreoli [17,46,47] and many more.
In the last two decades, several individual studies around the world attempted to screen for the presence of Babesia species in questing ticks using molecular techniques, but no attempt has been made to synchronize the results from all these studies. Assessing the global state of the pathogen prevalence in unfed host-seeking ticks is essential to develop effective control measures. Therefore, in this study, we undertook a comprehensive assessment to determine the occurrence of Babesia species in unfed host-seeking ticks collected from vegetation while using globally published epidemiological data. To achieve the above aim, we evaluated prevalence rates according to tick species, region of sampling, life stages of ticks, sex of adult ticks, sampling years and molecular detection techniques.

2. Results

2.1. Literature Search and Eligible Studies

A total of 4359 relevant articles were identified following a search for all four databases using the procedure enumerated in Figure 1. After the removal of duplicates, we were left with 2826 studies for further review. A careful review of the titles and abstracts was done, and a total of 122 full-text articles were downloaded for detailed review. In total, 18 studies were excluded for various reasons. These included (i) the exact number of positive Babesia isolates were not clearly stated (n = 5), (ii) non-separation of the number of positive isolates of Babesia from questing ticks and other vertebrate hosts/feeding ticks (n = 4), (iii) incomplete information on tick collections (n = 3), (iv) lack of delineation of the results of positive Babesia species from other piroplasms (n = 2), and (v) no information on the number of tick DNA used for polymerase chain reaction (PCR) screening (n = 2), (vi) study with samples size below 40 (n = 2). One hundred and four (104) studies were further subjected to the quantitative synthesis. The quality assessment score (QAS) from the Joanna Briggs Institute (JBI) critical appraisal ranges from 6 to 8 out of a possible score of 9, equivalent to 66.7–88.89% in 100 out of the 104 included studies. Only 4 studies had a score of 5 (55.67%) (Table 1; Supplementary Table S2).

2.2. Characteristics of Eligible Studies

The characteristics of all eligible studies comprising of 137,364 ticks from 104 studies across different regions of the world are presented in Table 1. Included studies were from Europe (n = 78), North America (n = 13), Asia (n = 12), and Africa (n = 1). All eligible studies were carried out using molecular techniques to screen for tick-borne pathogens with particular reference to Babesia species. The prevalence for all the individual studies was computed and presented in Table 1. Individually, apart from a few studies, which recorded a 0% prevalence, the majority of the studies ranges from 0.25% to 12.96%, with a median of 1.78%. There were two studies with a prevalence of 20.65% and 21.67% and another two studies with a prevalence of 51.04% and 58.33% (Table 1). The majority of the studies were carried out from the year 2000 onward, with only one study undertaken in 1985.

2.3. Pooling, Heterogeneity and Subgroup Analysis

2.3.1. Prevalence Based on Tick Species, Life Stages, Sex, and Diagnostic Technique

The overall and subgroup prevalence estimates of Babesia spp. based on tick species, life stages, sex and diagnostic technique, including confidence intervals and statistical parameters, are presented in Table 2. Globally, the overall pooled prevalence estimated (PPE) for Babesia species in questing ticks was 2.10% for all studies with 3069 positive cases from a total of 137,364 ticks screened and substantial study heterogeneity was observed (Table 2; Figure 2). Babesia species were detected in 23 different tick species within 4 genera Ixodes (5 species), Dermacentor (4 species), Rhipicephalus (4 species), Haemaphysalis (9 species) and Hyalomma (1 species) (Table 2). Ixodes ricinus was the most collected tick species with over 74,802 ticks in number and 1756 positive cases with PPE at 2.40% (Table 2; Figure 3). Other tick species included: I. persulcatus with PPE at 1.50%, I. scapularis at 4.10%, D. reticulatus at 2.10%, and H. longicornis at 4.30% (Table 2).
Other tick species that were reported, but no Babesia species were detected: H. sp. 1 & 2 [8]; H. bispinosa [28]; Hy. spp. [109]; H. hystricis and H. kitaokai [110]; Amblyomma testudinarium [110]; I. nipponensis [110]; I. turdus [37,110]; I. tanuki [37]; H. douglasi [29,37]; H. megaspinosa [29]; H. wellingtoni [112].
With regard to tick life stages, we observed an increasing infection rate from larvae with 0.60% to nymphs with 1.70% and the highest in adults with 2.60% (Table 2). Statistically significant differences (p < 0.0001) were observed across the different life stages. Additionally, the infection rate between the adult and larva was significantly different (p = 0.0033). The PPE was significantly (p = 0.0211) higher in the females with 4.90% compared to the males with 3.60% (Table 2).
Six different molecular diagnostic techniques were employed in all the included studies, with conventional PCR being the most widely utilized in 66 studies with a PPE of 1.90%. Others include nested-PCR with 2.80% and qPCR with 1.70% (Table 2, Figure 4).

2.3.2. Prevalence Based on Babesia Species, Region, and Sampling Periods

Globally, 19 different Babesia species were identified in ticks, with B. microti being the most observed species in 46 studies with a PPE of 1.90% (Table 3; Figure 5). This was followed by B. venatorum with 0.90% and B. divergens with 0.40%, which were exclusively found in ticks from Europe except for one study from Mongolia where B. venatorum DNA was amplified (Table 3). The prevalence of B. ovata was 0.60%, and B. spp. Xinjiang with 6.70% was observed only in ticks collected from Asia (Table 3).
According to region, Europe accounted for the majority of the studies (n = 78) with a PPE of 1.90% compared with Asia (n = 12) with a PPE of 2.00% (Table 3). North America had the highest PPE of 4.30% (Table 3). A single study was eligible from Africa, but none of the ticks was positive for Babesia spp.
We observed a statistically significant (p < 0.001) downward trend with respect to the PPE, with the highest being in period 1 (1992–1997) and the lowest in period 5 (2015–2020) (Table 3).

2.3.3. Species Diversity of Babesia within Different Tick Species

The results of the distribution of different Babesia species according to the different tick species are presented in Figure 6. Ixodes ricinus was associated with 9 different Babesia spp. with B. microti and B. venatorum having the highest number of isolates: 523 and 359, respectively (Figure 6). Furthermore, I. persulcatus and I. scapularis ticks were associated with 5 and 3 different Babesia species, respectively, with a total of 911 Babesia isolates shared between both ticks. Additionally, B. microti accounted for 746 Babesia isolates in I. scapularis. Finally, D. reticulatus was associated with 6 different Babesia species, with B. canis being the highest with 126 isolates (Figure 6).

2.4. Spatial Distribution of Eligible Studies

In total, the results for 36 individual countries across four continents are presented in Table 4. In Europe, Poland and Germany had the highest number of eligible studies with 13 and 12 entries, each with PPE of 3.40% and 2.20%, respectively (Table 4). In addition, United States had 12 eligible studies with a PPE of 4.30%. Some other countries, including France, Russia, and Switzerland, have a PPE of 3.30%, 1.20% and 1.50%, respectively. A map with the spatial distribution of Babesia spp. across the different countries in Europe in different tick species is shown in Figure 7.

2.5. Publication Bias

The funnel plots and their corresponding bias coefficient (Begg and Mazumdar rank) for the estimation of the overall pooled MIR for published studies (Z = −48.00, p = 0.446) provides no evidence for the presence of publication bias among the eligible studies globally. For a few subgroup analyses, significant publication bias was observed for studies used for the computation of B. canis (Z = −35.00, p = 0.05), B. divergens (Z = −72.00, p = 0.01) and B. microti (Z = −203.00, p = 0.02). Additionally, mild bias was observed in studies from Asia (Z = −32.00, p = 0.014).

3. Discussion

3.1. Babesia Species in Ticks with Medical Importance

With the dawn of DNA-based techniques, molecular characterization has fostered the description and classification of new Babesia species. Therefore, the list of new species of Babesia continues to increase. In an attempt to synchronize the results from diverse epidemiological surveys for Babesia piroplasms in unfed host-seeking ticks comprising all live stages collected from vegetation across the globe, we undertook a systematic review and meta-analysis to estimate the pooled prevalence using random effect models.
Undoubtedly, Babesia microti was the most prevalent and widespread species of Babesia found in questing ticks in this study. DNA of B. microti has been detected in Europe, North America, and Asia with a PPE of 1.90%. This finding is comparable to the individual prevalence rates reported in previous studies [27,38,107,117]. Higher prevalence rates above 5.00% have also been reported in several other countries like United States [114,121], Poland [79,82] and Mongolia [32].
Babesia microti, B. duncani, B. divergens and B. venatorum are all regarded as zoonotic Babesia species. Clinically, most infected individuals are asymptomatic but could register lethal evolution depending on the species of Babesia and immunocompetence of the patient [18]. It is important to note that B. microti is responsible for most cases of human babesiosis and with great impact in North America but rare in Europe and Asia [18]. In Europe, both B. divergens and B. venatorum (formerly Babesia spp. EU1) are the predominant species causing human babesiosis. Interestingly, no study reported the detection of B. duncani in questing ticks. However, a recent report suggests the possible role of larval forms of D. albipictus as a possible vector of B. duncani transmission [122].
With the exception of one study from Mongolia [111], studies reporting the detection of B. divergens and B. venatorum were exclusively found in Europe with a PPE below 1.00%. This finding is comparable to the reports from over 70% of studies reporting the detection of this Babesia species in Europe [17,47,48,65,106]. The widespread presence of these species of Babesia of zoonotic importance in questing ticks has public health implications, especially in recreational parks during the period of tick activity. Therefore, humans could be exposed to pathogens with tick bites. Alternatively, blood transfusion-associated transmission has been reported in endemic areas, and it is regarded as the most common way of transmission in North America [123]. Therefore, Giemsa stained blood, serological testing or the use of PCR may significantly reduce the likelihood for transmission to occur by blood transfusion in endemic areas. Naturally, B. microti and B. divergens parasitize microtine rodents and cattle, respectively, these hosts being regarded as their reservoir [12]. On the other hand, B. venatorum is maintained naturally in wild cervids (deer), while the mule deer (Odocoileu hemionus) and possibly other species of wild ungulates in western North America may be the primary reservoir for B. duncani [122].

3.2. Babesia Species in Ticks with Veterinary Importance

Several species of Babesia are causing babesiosis in animals, including B. bovis, B. bigemina, B. occultans, B. divergens, B. ovata, B. odocoilei and B. capreoli (large ruminants and deer); B. caballi (equines); B. crassa, B. ovis, B. motasi-like and B. spp. Xinjiang (small ruminants), and B. vogeli, B. canis, B. rossi and B. gibsoni (canines). These species were observed in questing ticks across several regions. Of these species, some were observed to be geographically restricted (like B. ovata and B. spp. Xinjiang in Japan and China, respectively), in addition to uncharacterized Babesia species. The PPE for animal babesiosis in questing ticks ranges between 0.30% and 1.50%, with the exception of B. spp. Xinjiang with a PPE of 6.70%. These low prevalences are comparable to the infection rates reported for individual studies [24,29,41,43,47,68,108].
The PPE for B. canis was low, comparable to the prevalence reported in ticks from Slovakia [97], Russia [22] and Germany [24]. Furthermore, we observed that with the exception of B. canis, the agent of canine babesiosis, all other species of Babesia causing babesiosis in dogs were only reported separately, in one study each. Nonetheless, B. canis was reported in 14 studies from Europe. Therefore, B. canis appears to be the principal agent of canine babesiosis in Europe. In autochthonous cases where clinical canine babesiosis was reported, flagged ticks (Dermacentor reticulatus) in surrounding areas were positive to B. canis [23,41]. Additionally, in the majority of the studies (about 78%), B. canis DNA was reported in D. reticulatus tick, which is a competent vector for the protozoan parasite and is frequently found in urban biotypes in Europe [21].
Babesia caballi, one of the etiological agents of equine piroplasmosis, was observed at a low infection rate. The DNA of B. caballi was observed in R. bursa [44], D. nutalli [45] and D. reticulatus [41,44]. In the latter studies, both B. caballi and B. canis were detected in D. reticulatus ticks. Interestingly, both B. canis and B. caballi can be maintained for several generations in D. reticulatus ticks [41].
The PPE for agents of small ruminant’s babesiosis in questing ticks is consistent with reports from other individual studies where they occur at a very low prevalence [43,108]. Unlike B. motasi in Europe, B. spp. Xinjiang is known to principally infect sheep in China. From all available evidence, their presence in questing ticks is very low. Nonetheless, this Babesia spp. (B. spp. Xinjiang) has been amplified from blood samples from sheep and goats in China [28]. Earlier studies reported that Hy anatolicum anatolicum is the principal and competent vector [124]. The detection of B. spp. Xinjiang in H. longicornis and H. qinghaiensis, which are widespread in China, has raised several questions of their potential as vectors, but this remains speculative, and further studies will be required to verify this claim [28]. Additionally, B. crassa was detected in questing H. parva ticks in Turkey [108].
We observed seven species of bovine/cervid Babesia in host-seeking ticks. Unlike the virulent B. bovis and B. bigemina, B. ovata is of lower pathogenicity in cattle [29] and is one of the geographically restricted species of Babesia, similar to B. spp. Xinjiang in China. Babesia ovata is endemic in Japan and principally infects cattle [29]. H. longicornis is a known competent tick vector that can transmit the protozoan parasite transovarially [29,125], and further studies are needed to ascertain the probable role of I. ovatus that was observed to harbor this Babesia species. Additionally, B. occultans DNA was reported in Hy. marginatum, which is a known competent vector with empirical evidence from natural transovarial transmission [108], and transstadial survival [126]. Therefore, transstadial persistence of B. occultans in Hy. marginatum has been attributed to transovarial transmission of the pathogen [108], as only the adult ticks feed on the blood from cattle [127].

3.3. Ticks as Vectors of Babesia Species

Ixodes ricinus was the most abundant tick species in this study. This is not surprising considering that majority of the studies were from Europe, where this tick is predominant and a vector of several pathogens of protozoan, viral and bacterial agents of veterinary and medical importance [128,129]. Reports from various studies indicate that this tick is mostly found in urban and peri-urban areas in city parks, gardens, forest patches and litter layers [129]. Forested areas and particularly mixed and deciduous forests provide a sheltered canopy, and this tick species thrives due to the microclimates provided [128,130]. Due to climate change, current evidence points to the increasing distribution of I. ricinus steadily towards higher latitudes and altitudes. This was obvious in this study as several works were found investigating the presence of Babesia pathogen in questing tick in Sweden [92,93] and Finland [50]. Furthermore, I. ricinus harbors diverse Babesia species, which have been reported in Western Europe [46,52,73], Eastern Europe [98,99], Central Europe [39,104], Scandinavia [70,71,92], Southern Europe [44,64] and Balkan Peninsula [100], with varying prevalence and spread across the continent.
Other species within the genus Ixodes, such as I. persulcatus, I. ovatus and I. pavlovskyi, were reported in the Northern Hemisphere precisely in Russia and parts of southern Eurasia to harbor Babesia spp. at a prevalence ranging from 0.30 to 1.60%. According to [131], I. persulcatus ticks are closely related to I. pavlovskyi. For now, the vector competence of I. pavlovskyi is largely unknown. Nonetheless, I. persulcatus has been implicated as a possible competent vector for B. divergens [132].
Ixodes scapularis is widely distributed in the northeast, upper Midwest, mid-Atlantic and southeast states of the United States as well as in Canada [26,133] and was observed to be the major tick vector reported from North America. The PPE of Babesia spp. in this tick was low at 3.60%, comparable to the prevalence reported from other individual studies [118,120]. Higher prevalence has been reported in other parts of America [113,117]. Both B. microti and B. odocoilei are Babesia spp. found to be associated with this tick species causing human and cervid (white-tailed deer) babesiosis, respectively. The vector competence for B. odocoilei is unknown, but I. scapularis has been involved [42].
Haemaphysalis longicornis was reported in five studies, all from eastern Asia, where this tick species is native and originated from. The PPE was low to moderate at 4.3%. This tick species was observed to harbor B. ovata in Japan [29] and B. spp. Xinjiang in China [28]. Therefore, babesiosis in cattle and sheep, respectively, in that region is believed to be caused by B. ovata and B. spp. Xinjiang is probably transmitted by H. longicornis.

3.4. Association between Ticks and Babesia Including Other Factors

Ixodid tick species play a crucial role in the epidemiology of babesiosis. Reports of the detection of Babesia DNA may not necessarily denote evidence of vector competence, whether in unfed or engorged ticks [134]. In transovarial transmission, most Babesia species invade the tick ovaries and persist in the larvae. Consequently, infection is transmitted vertically. The acquisition of the parasites (Babesia species) from their respective host by either the larvae or nymphs is referred to as transstadial transmission.
Furthermore, of all tick species in this study, I. ricinus had the highest association with several Babesia species with three and six species of human and veterinary importance, respectively. This tick is a known competent vector for 3 Babesia parasites (B. divergens, B. venatorum and B. microti), causing human babesiosis [129]. Since all stages (larvae, nymph, and adult) of I. ricinus can transmit B. divergens and B. venatorum, the risk of infection is high after tick bites in humans during periods of peak tick activity. Detailed review on the association of I. ricinus with Babesia and other tick-borne pathogens can be obtained elsewhere [129,134].
The fact that the adult ticks and, by extension, female ticks were the most predominant with the highest infection rates compared with the nymphs and larvae may have some implications in transmission. In transovarial transmission involving most Babesia species, it has been asserted that only the female ticks can acquire the infection. Immature stages are less likely to become infected due to the smaller blood volumes they ingest. Furthermore, the fewer number and size of the midgut epithelial basophilic cells of immature stages, which play a role in parasite development, are believed to be an important factor as well [134]. Furthermore, evidence of transstadial transmission has been observed for some Babesia spp., but also, not all tick stages are capable of transmitting the parasite as observed for B. bovis, where only the larvae of R. annulatus can transmit. On the other hand, only the nymphal and adult stages of R. annulatus can transmit B. bigemina [134]. Additionally, many Babesia spp., including B. major, B. motasi, B. rossi, B. venatorum, B. vogeli and B. divergens, can persist from larval to their adult stages (transstadial transmission) in their competent vectors without reinfection for a minimum of one generation [134].
Female ticks had higher infection rates compared with their male counterparts. It is well known that female ticks require blood meals to develop their ovaries and lay thousands of eggs to perpetuate their existence. In addition, as earlier mentioned, the transovarial transmission is one of the utmost successful evolutionary strategies among the Apicomplexa and specifically in Babesia sensu stricto [20]. Therefore, female ticks take larger blood meals (high volume of blood) due to prolonged feeding, which may result in higher chances of infection. Furthermore, females require a higher number of blood meals for molting before reaching the adult stage.
The use of molecular-based techniques for the diagnosis and classification of Babesia species has been widely adopted due to greater sensitivity and specificity [18]. All studies used molecular-based techniques. In the various epidemiological investigation of Babesia species in questing ticks as observed in this study, several molecular approaches, including qPCR [49,120], nested-PCR [8,28,74], conventional PCR [47,57,88], reverse line blot hybridization [39,43] and more recently, next-generation sequencing [33] among other methods have been adopted. Despite the observation of differences in the prevalence rates between techniques, no statistical significance was noted. Similar findings were observed in a Euro-wide meta-analysis of Borrelia burgdorferi sensu lato prevalence in questing I. ricinus ticks [135]. The highest in the prevalence rate was nested-PCR, but it is difficult to conclude considering the fact that the number of studies that utilized this technique is comparatively fewer compared with the conventional PCR. The geospatial distribution indicates that extensive studies have been conducted in Germany, Poland, and United States. This observation could be connected with a research interest in those countries with a bias towards tick-borne diseases.
This systematic review has spawned data on the prevalence of Babesia species in questing ticks. However, some limitations were observed in our study. First, we excluded articles published in languages other than English, and hence some vital information may have been set aside. Second, our study focused only on questing ticks; therefore, areas without reported Babesia pathogen may still have the pathogen. Third, due to the use of different DNA-based techniques with varying sensitivity, some Babesia species with low detection sensitivity might have been missed. Fourth, the global prevalence was obtained from studies from four continents. Therefore, the global pooled prevalence of Babesia spp. may vary from the actual estimate, but we believe that the apparent prevalence in this study is close to normal. Fifth, the heterogeneity observed could be due to sampling error, sample size, or variation of endemicity and study design. Despite the limitations highlighted above, this study used a large number of eligible studies (n = 104) and ticks screened (137,364) from a global perspective to clearly provide a comprehensive insight and meta-analysis on the distribution of Babesia species in different questing ticks across four continents from published literature. Our results clearly indicate that these ticks harbor potentially disease-causing Babesia parasites of human and veterinary importance.

4. Material and Methods

4.1. Search Strategy

We followed the protocol as outlined by the preferred reporting items for systematic reviews and meta-analyses (PRISMA) in carrying out this systematic review and meta-analysis [136]. We searched for citations with no time restrictions through to 10 July 2020 solely in English databases of Science Direct, Springer Link, PubMed, and Google Scholar. Key operators used in the systematic search were “Babesia”, “questing ticks”, and “tick-borne pathogens”. Key terms used in the search were used individually or in combination with “AND” and/or “OR” operators. Duplicates were removed, and relevant titles and abstracts were scanned, and those articles in line with the aim of the study were downloaded.

4.2. Inclusion and Exclusion Criteria

Selected relevant articles, after the review of titles and abstract, were downloaded for further screening of the full text for eligibility. Included articles for the study must fulfill the following seven criteria, namely (i) the collected ticks must be questing ticks from vegetation, (ii) the total number of ticks screened was stated, (iii) the country of the study was known, (iv) the study screened for the presence of Babesia in questing ticks, and the number of positives/negatives was stated (v) the molecular diagnostic method employed in the study was stated (vi) for a tick species to be included in the result, at least one Babesia spp. DNA must have been amplified for that species (vii) no limit to the minimum sample size of screened ticks, but for statistical reasons, it was set at less than 40 samples. Where the exact number of the respective live stages were not clearly stated, the total number of screened ticks collected for that study was used only in the computation of the overall prevalence. Studies were excluded if (i) the exact number of positive Babesia isolates were not clearly stated, (ii) separation of the number of positive isolates of Babesia from questing ticks and other vertebrate host/feeding ticks was missing, (iii) incomplete information on tick collections (iv) lack of delineation of the results of positive Babesia species from other piroplasms (v) no information on the number of tick DNA samples used for PCR screening (vi) study with sample size below 40.

4.3. Data Cleaning

In most of the studies, the developmental stages (larva and nymphs) were pooled before pathogen detection. Therefore, we calculated the minimum infection rates (MIR) (based on the assumption of a single positive tick per pool) for all included studies to avoid overestimation of a prevalence. Consequently, the prevalence throughout reflects the MIR in ticks. With regard to the years of sampling, where sampling was undertaken over two or more years, and the results were presented separately for each year, we divided the entries accordingly. Similarly, where entries involved different tick species and countries but published on the same articles, the data were separated meticulously. For the calculation of the overall prevalence, we used data from all eligible studies incorporating the total number of ticks screened irrespective of the live stages. Overall, only tick species that showed at least one positivity to Babesia spp. were presented in Table 2. Therefore, tick species reported without any single cumulative positivity to Babesia spp. were not included in the results. Furthermore, the number of positive Babesia spp. isolates that were confirmed by good quality sequences as reported in the articles were used for the subgroup analysis (Babesia species).

4.4. Data Extraction

All studies meeting the inclusion criteria were cataloged, and data were extracted using a charting form developed by the research team. Data extracted from all the eligible studies included all the variables as contained in the inclusion criteria, such as the name of the authors, year of sampling, geographical location, the total number of ticks screened, the molecular diagnostic technique used, the life stages of the ticks, tick species, sex of the ticks, species of Babesia detected as well as the number of positive/negative Babesia isolates. The MIR was calculated according to the various subgroups.

4.5. Quality Assessment of Included Studies

The quality assessment of each article included in the study was undertaken using the Joanna Briggs Institute (JBI) critical appraisal instrument for studies with prevalence data [137]. This JBI instrument consists of nine questions, of which details are available (Supplementary Table S1). Each answer to the individual question was assigned a score of 0 or 1 for no or yes answers. When the question was not applicable to the study, not applicable (NA) was used. Results of Babesia species distribution were summarized on a country level and exported as a CSV file into ArcGis Desktop (Esri, version 10.5.1, Redlands, CA, USA). Data were visualized in pie charts per country.

4.6. Statistical Analysis

All statistical analyses were carried out using Comprehensive Meta-analysis (CMA) Version 3.0 by Biostat (Englewood, NJ, USA) unless otherwise stated. The weighted pooled minimum infection rate (MIR) and 95% confidence interval (CI) were computed. For each individual study, we recalculated the MIR (prevalence) by summing the total number of samples and positive cases irrespective of the number of tick species reported for that study. When the pooled analysis was performed, each logit event estimate undergoes a transformation within the CMA software into proportions with its corresponding 95% CI. We calculated the overall MIR as a percentage. Forest plots were used to visualize the data generated. Cochran’s heterogeneity (Q) among the included studies, as well as the percentage inverse variation (I2), was calculated using the Cochrane Q test. If I2 was ≤25%, 50% or ≥75%, then heterogeneity was described as low, moderate, or high (substantial), respectively [138]. If there was only a single study for a particular category, the positive rate was computed without heterogeneity (Q). All pooled estimates were arrived at using a random-effects model except for sex, where we used the fixed-effect model due to the homogeneity of the data. The chi-squared test was used to test for significance for all the subgroups using GraphPad Prism, version 5.04 (GraphPad Software, Inc, La Jolla, CA, USA, www.graphpad.com). p values of <0.05 were considered statistically significant unless otherwise stated. Funnel plots using visual inspection and the Beg and Mazumdar rank correlation test [139] were used for assessing the publication bias.

5. Conclusions

In this meta-analysis of pooled data on Babesia species in questing ticks from a global perspective, our findings indicate both human and animal Babesia species DNA in a variety of species of questing hard ticks with low to moderate prevalence. We reported the detection of 19 Babesia species in 23 different tick species across four continents. Adult male and female ticks had the highest infection rates compared with immature and male ticks, respectively. Ixodes ricinus was the main tick species of interest, and it is a tick species of economic importance, with B. microti being the most widely detected species of Babesia across the different regions. The information generated from this study will be helpful to the relevant stakeholders in the design and future implementation of programs aimed at controlling competent vectors against Babesia parasites.

Supplementary Materials

The following are available online at https://www.mdpi.com/2076-0817/10/2/230/s1, Table S1: JBI Critical appraisal checklist for studies reporting prevalence data; Table S2: Quality assessment scores for eligible studies.

Author Contributions

Conceptualization, T.E.O. and C.S.; methodology, T.E.O., C.R.; validation, T.E.O., C.R., S.F. and C.S.; data curation, T.E.O., C.R., S.F. and C.S.; writing—original draft preparation, T.E.O.; writing—review and editing, C.R., S.F. and C.S.; visualization T.E.O., S.F.; supervision C.S.; All authors have read and agreed to the published version of the manuscript.

Funding

This research received no external funding.

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

The data presented in this study are available in the current article and the supplementary material.

Acknowledgments

We thank Franz J. Conraths and Christoph Staubach (Friedrich-Loeffler-Institut, Greifswald-Insel Riems, Germany) for providing the ArcGIS software licenses and their useful comments on the manuscript.

Conflicts of Interest

The authors declare no conflict of interest.

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Figure 1. Preferred reporting items for systematic reviews and meta-analyses (PRISMA) flowchart used in the selection of eligible studies.
Figure 1. Preferred reporting items for systematic reviews and meta-analyses (PRISMA) flowchart used in the selection of eligible studies.
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Figure 2. Forest plot showing the pooled prevalence of Babesia species globally. N.B. The squares show the individual point estimate. The diamond at the base indicate the pooled estimates from the total studies. Event rate: the frequency of occurrence of an event in a population, and it takes into account the possibility of an event occurring several times in an individual.
Figure 2. Forest plot showing the pooled prevalence of Babesia species globally. N.B. The squares show the individual point estimate. The diamond at the base indicate the pooled estimates from the total studies. Event rate: the frequency of occurrence of an event in a population, and it takes into account the possibility of an event occurring several times in an individual.
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Figure 3. Forest plot showing the prevalence of Babesia species in questing Ixodes ricinus in Europe. N.B. The squares show the individual point estimate. The diamond at the base indicate the pooled estimates from the total studies. Event rate: is the frequency of occurrence of an event in a population, and it takes into account the possibility of an event occurring several times in an individual.
Figure 3. Forest plot showing the prevalence of Babesia species in questing Ixodes ricinus in Europe. N.B. The squares show the individual point estimate. The diamond at the base indicate the pooled estimates from the total studies. Event rate: is the frequency of occurrence of an event in a population, and it takes into account the possibility of an event occurring several times in an individual.
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Figure 4. Mean prevalences of Babesia species globally using different diagnostic techniques. Error bars, standard errors of the means.
Figure 4. Mean prevalences of Babesia species globally using different diagnostic techniques. Error bars, standard errors of the means.
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Figure 5. Forest plot showing the prevalence of Babesia microti globally. N.B. The squares show the individual point estimate. The diamond at the base indicate the pooled estimates from the total studies.
Figure 5. Forest plot showing the prevalence of Babesia microti globally. N.B. The squares show the individual point estimate. The diamond at the base indicate the pooled estimates from the total studies.
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Figure 6. Heat map of the association of different Babesia species in different tick species globally.
Figure 6. Heat map of the association of different Babesia species in different tick species globally.
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Figure 7. Distribution of Babesia species in different tick species across Europe.
Figure 7. Distribution of Babesia species in different tick species across Europe.
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Table 1. Characteristics of all 104 studies used in the meta-analysis of molecular Babesia detection in questing ticks.
Table 1. Characteristics of all 104 studies used in the meta-analysis of molecular Babesia detection in questing ticks.
Study YearCountryContinentMolecular
Technique
Sample SizeCasesMIRJBI QASStudy Ref.
2005AustriaEuropePCR86444151.045[2]
2009BelarusEuropePCR45351.107[48]
2016–2017DenmarkEuropeqPCR101350.497[49]
2015FinlandEuropeqPCR/PCR51561.177[50]
2012–2017FinlandEuropeqPCR7070410.588[51]
2009FranceEuropePCR/RLB49540.817[52]
2006–2007FranceEuropePCR572356.128[53]
2002FranceEuropePCR921920.658[54]
2012–2013FranceEuropePCR2620150.578[55]
2017FranceEuropeqPCR60813.338[56]
2008FranceEuropePCR55861.088[40]
2009GermanyEuropePCR22683.548[57]
2007GermanyEuropePCR1962110.718[36]
2008GermanyEuropePCR293268.878[58]
1999–2001GermanyEuropePCR3113310.998[59]
2006–2007GermanyEuropePCR1000505.008[60]
2006GermanyEuropePCR1962110.718[61]
2011–2012GermanyEuropePCR4381451.038[46]
2011GermanyEuropePCR19963.028[38]
2009–2010GermanyEuropePCR6593280.428[47]
2008–2010GermanyEuropePCR1721362.098[17]
2010–2013GermanyEuropePCR33910.298[24]
2011–2012GermanyEuropePCR2000008[62]
* 2010–2018Germany, Netherland, Belgium, and Great BritainEuropeMicrofluidic qPCR1486161.086[25]
2006–2008HungaryEuropePCR1800150.835[63]
2014–2015HungaryEuropePCR413348.238[21]
2006–2008ItalyEuropePCR19110.528[64]
2006ItalyEuropePCR35630.846[65]
2006–2007ItalyEuropeNested PCR1861191.027[66]
2000–2001ItalyEuropeMultiplex PCR1931311.615[67]
2005–2007LatviaEuropePCR1125191.698[68]
2006Latvia and
Lithuania
EuropeNested PCR2810401.428[69]
2006–2008NorwayEuropeqPCR, nested PCR1908170.898[70]
2006Norway and
Lithuania
EuropeqPCR36451.378[71]
2005LithuaniaEuropePCR62007[72]
2003–2007NetherlandsEuropeRLB/PCR1488161.087[73]
NAPolandEuropeNested PCR603558.336[74]
2008PolandEuropeNested PCR1392221.588[75]
2009–2012PolandEuropeNested PCR20562.935[76]
2001PolandEuropePCR1328282.117[77]
2000–2004PolandEuropePCR151350.338[78]
1999PolandEuropePCR20951306.218[79]
2009–2010PolandEuropeqPCR1875472.518[80]
2009–2010PolandEuropePCR3165501.586[81]
2008–2009PolandEuropePCR, nested PCR468214.498[82]
2011–2012PolandEuropePCR, nested PCR1435553.838[83]
2011PolandEuropePCR634264.107[84]
2004–2006PolandEuropeNested PCR1620573.527[85]
2001PolandEuropeNested PCR701162.287[86]
2006–2008EstoniaEuropeRLB, nested PCR2603361.386[87]
2012PortugalEuropePCR26300.08[88]
2012–2013PortugalEuropePCR17500.08[89]
2007LuxembourgEuropePCR1394362.587[90]
2010RomaniaEuropePCR40008[91]
2013–2014SwedenEuropePCR519234.437[92]
2015–2016SwedenEuropePCR277008[93]
2000RussiaEuropePCR73870.956[94]
2009RussiaEuropePCR48151.046[95]
2003–2004RussiaEuropeNested PCR20931.446[22]
2008–2009RussiaEuropeNested PCR922242.606[96]
2010–2015RussiaEuropeNested PCR91140.446[31]
2002SlovakiaEuropePCR10011.08[97]
2011SlovakiaEuropePCR5148781.638[98]
2011–2012SlovakiaEuropePCR886121.357[99]
1997SloveniaEuropePCR135139.637[100]
2003Czech RepublicEuropePCR35051.438[101]
2011–2014Czech RepublicEuropePCR2473321.298[102]
1997BelgiumEuropePCR230006[103]
2011–2013Netherlands and BelgiumEuropeRLB/PCR855171.997[41]
2003–2005SpainEuropeRLB/PCR562173.038[44]
2002–2003SwitzerlandEuropePCR86540.467[104]
2006SwitzerlandEuropeRLB/PCR2568441.718[105]
2009–2010SwitzerlandEuropeRLB/PCR1476281.897[39]
2015–2016SwitzerlandEuropeqPCR107960.568[106]
2012SwitzerlandEuropePCR261166.138[23]
2013–2014UkraineEuropePCR767131.697[107]
2011–2013TurkeyEurope-AsiaNGS20510.497[33]
2014–2018TurkeyEurope-AsiaPCR1019272.658[108]
2013–2014ChinaAsiaRLB/PCR450378.228[43]
2013–2014ChinaAsiaNested PCR55820.368[8]
2013–2014ChinaAsiaNested PCR797516.397[28]
2013–2014IsraelAsiaPCR119630.256[109]
2013–2015JapanAsiaNested PCR62450.808[110]
2000–2003JapanAsiaNested PCR1656402.428[37]
2008JapanAsiaPCR1459181.238[29]
2000–2003JapanAsiaPCR294175.788[30]
NAMongoliaAsiaNested PCR10876.486[45]
2009MongoliaAsiaPCR40092.258[111]
2012–2013MongoliaAsiaNested PCR219198.687[32]
2015ThailandAsiaPCR12,18410.018[112]
2009NigeriaAfricaPCR700008[34]
2001United States of AmericaNorth AmericaPCR10798.416[113]
2013–2014United States of AmericaNorth AmericaPCR42330.716[114]
1985United States of AmericaNorth AmericaPCR3954812.158[115]
1996United States of AmericaNorth AmericaPCR10055.06[116]
2003–2006United States of AmericaNorth AmericaPCR3944110.417[117]
2003United States of AmericaNorth AmericaPCR68710.296[42]
2015–2017United States of AmericaNorth AmericaHRM1721623.608[118]
2010United States of AmericaNorth AmericaPCR191008[119]
2012–2014United States of AmericaNorth AmericaqPCR1855542.918[120]
2003–2004United States of AmericaNorth AmericaMultiplex PCR11,1842832.538[27]
2011United States of AmericaNorth AmericaPCR1245352.817[35]
2011United States of AmericaNorth AmericaqPCR43682555.848[121]
2016–2017CanadaNorth AmericaPCR24941.618[26]
PCR: polymerase chain reaction; qPCR: real-time polymerase chain reaction; RLB: reverse line blotting; HRM: high-resolution melting; NGS: next-generation sequencing; NA: not available; MIR: minimum infection rate; JBI: Joanna Briggs Institute; QAS: quality assessment score. * Sprong et al. (2019): The sample number and results from Germany were excluded from our computation.
Table 2. Pooled minimum infection rate (MIR) estimates of Babesia spp. in questing ticks based on tick species, life stages, sex, and diagnostic technique.
Table 2. Pooled minimum infection rate (MIR) estimates of Babesia spp. in questing ticks based on tick species, life stages, sex, and diagnostic technique.
SubgroupNumber of
Studies
Pooled Prevalence EstimatesMeasure of Heterogeneity
Sample SizeNo of PositivesWeighted MIR95% CI (%)Q ValueI2Qp
All studies104137,36430692.10 (1.60–2.70)4438.9797.65p < 0.0001
Tick species
Ixodes ricinus5774,80217562.40 (1.50–3.60)3737.8698.50p < 0.0001
I. persulcatus1458231021.50 (0.70–3.20)154.4491.58p < 0.0001
I. ovatus31420390.60 (0.00–9.20)17.2388.39p < 0.0001
I. scapularis1422,6947864.10 (2.70–6.20)296.3695.95p < 0.0001
I. pavlovskyi157720.30 (0.01–1.40)
Dermacentor
reticulatus
2011,8021972.10 (1.30–3.50)174.8989.14p < 0.0001
D. marginatus239010.80 (0.10–9.4)2.2655.65p < 0.0001
D. nuttalli338971.30 (0.10–12.10)7.6073.76p = 0.022
D. silvarum222341.80 (0.20–18.50)3.0667.23p = 0.080
R. bursa412022.90 (0.90–8.50)0.990.00p = 0.802
R. sanguineus s.l.5166830.60 (0.10–2.60)8.7754.39p < 0.001
R. (Boophilus) microplus3149820.30 (0.10–1.90)1.630.00p = 0.443
R. turanicus19111.1 (1.50–50.00)0.000.00p = 1.000
Hemaphysalis
longicornis
5626284.30 (1.60–10.90)13.1769.62p = 0.010
H. concinna413066.10 (3.00–11.90)0.7600.00p = 0.825
H. qinghaiensis24307317.20 (10.90–26.0)4.3276.86p = 0.038
H. punctata111143.60 (1.40–9.20)0.000.00p = 1.000
H. parva1793131.60 (1.00–2.80)0.000.00p = 1.000
H. inermis18711.10 (0.20–7.70)0.000.00p = 1.000
H. flava228231.30 (0.50–3.80)0.49-p = 0.484
H. formosensis115921.30 (0.30–4.90)0.000.00p = 1.000
H. lagrangei111,30910.00 (0.00–0.01)0.000.00p = 1.000
Hyalomma marginatum11051312.38 (7.30–20.20)0.000.00p = 1.000
Life stages
Adult7955,41114842.60 (2.00–3.40)1693.3495.34p < 0.0001
Nymphs5344,74610661.70 (1.10–2.50)1578.8296.77p < 0.0001
Larvae1320,8661740.60 (0.10–3.60)699.7798.29p < 0.0001
Sex
Male2675341993.60 (3.10–4.20)145.5382.82p < 0.0001
Female2683952754.90 (4.40–5.60)256.9890.27p < 0.0001
Diagnostic technique
Conventional PCR6676,02116631.90 (1.30–2.90)3339.9998.05p < 0.0001
qPCR1223,3145221.70 (1.00–3.00)332.8696.69p < 0.0001
Nested PCR1614,6533762.80 (1.70–4.70)339.9795.59p < 0.0001
RLB710,0021952.20 (1.30–3.80)85.8892.99p < 0.0001
Multiplex PCR213,1152461.90 (1.70–2.10)0.890.00p = 0.344
NGS120521.00 (0.20–3.80)0.000.00p = 1.000
PCR: polymerase chain reaction; qPCR: real-time polymerase chain reaction; RLB: reverse line blotting; NGS: next-generation sequencing; I2: inverse variance; Q-p: Cochran’s; CI: confidence interval; MIR: minimum infection rate. Measure of heterogeneity: the weighted sum of squared differences between individual study effects and the pooled effect across studies.
Table 3. Pooled MIR estimates of Babesia in questing ticks based on Babesia species, region, and sampling periods.
Table 3. Pooled MIR estimates of Babesia in questing ticks based on Babesia species, region, and sampling periods.
SubgroupNumber of StudiesPooled Prevalence EstimatesMeasure of Heterogeneity
Sample SizeNo of PositivesWeighted MIR95% CI (%)Q ValueI2Qp
All studies104137,36430692.10 (1.60–2.70)4438.4197.68p < 0.0001
Babesiaspecies
Babesia microti4668,53714251.90 (1.40–2.50)1071.9495.80p < 0.0001
B. venatorum3150,6113700.90 (0.70–1.10)163.4781.65p < 0.0001
B. divergens2033,5171410.40 (0.20–0.70)161.7588.47p < 0.0001
B. spp.1938,1251830.50 (0.20–1.10)363.1995.59p < 0.0001
B. capreoli615,927130.10 (0.10–0.20)7.3131.61p = 0.199
B. canis1514,9381321.10 (0.50–2.40)235.8394.06p < 0.0001
B. odocoilei68002520.90 (0.20–4.50)102.0695.10p < 0.0001
B. caballi31525171.40 (0.30–6.90)20.0290.01p < 0.0001
B. bovis2101230.30 (0.10–0.90)0.150.00p = 0.700
B. bigemina3157070.50 (0.20–1.40)2.7527.16p = 0.253
B. ovata21909180.60 (0.10–5.00)2.8564.87p = 0.092
B. spp. Xinjiang21247846.70 (5.50–8.30)0.390.00p = 0.528
B. gibsoni1659310.00 (0.00–0.10)0.000.00p = 1.000
B. ovis120510.50 (0.10–3.40)0.000.00p = 1.000
B. occultans11019121.20 (0.70–2.10)
B. rossi1101940.40 (0.10–1.00)0.000.00p = 1.000
B. vogeli1119631.50 (0.00–32.40)
B. crassa1101980.80 (0.40–1.60)0.000.00p = 1.000
B. motasi like145030.70 (0.20–2.00)0.000.00p = 1.000
Region
Europe7894,37620561.90 (1.30–2.70)3964.1298.06p < 0.0001
Asia1219,9452092.00 (1.10–3.50)174.67.6993.70p < 0.0001
North America1322,2998064.30 (3.00–6.20)237.7394.95p < 0.0001
Sampling period
1992–1997 (period 1)3465184.30 (1.30–13.90)8.2875.85p = 0.016
1998–2002 (period 2)910,2052692.90 (1.40–5.70)205.7996.11p < 0.0001
2003–2008 (period 3)2939,26613262.60 (1.40–4.80)2628.5098.94p < 0.0001
2009–2014 (period 4)3852,5719501.60 (1.20–2.20)627.3394.10p < 0.0001
2015–2020 (period 5)1020,7221030.90 (0.40–2.10)112.8492.91p < 0.0001
I2: inverse variance; Q-p: Cochran’s; CI: confidence interval; MIR: minimum infection rate. Measure of heterogeneity: the weighted sum of squared differences between individual study effects and the pooled effect across studies.
Table 4. Prevalence estimates of Babesia in questing ticks based on country.
Table 4. Prevalence estimates of Babesia in questing ticks based on country.
SubgroupNumber of StudiesPooled Prevalence EstimatesMeasure of Heterogeneity
Sample SizeNo of PositivesWeighted MIR95% CI (%)Q ValueI2Qp
Austria186444151.00 (47.70–54.40)
Belarus145351.10 (0.50–2.60)
Denmark1101350.50 (0.20–1.20)
Finland27585470.70 (0.40–1.40)2.5660.97p = 0.109
France64397873.30 (0.90–10.80)148.2296.62p < 0.0001
Germany1220,2572732.20 (1.10–4.40)326.8296.63p < 0.0001
Hungary22213492.70 (0.30–22.0)56.4898.23p < 0.0001
Italy44339541.20 (0.90–1.70)3.9323.64p = 0.269
Latvia21306241.90 (1.30–2.80)0.980.00p = 0.323
Norway22132190.90 (0.60–1.40)0.000.00p = 0.998
Lithuania32831642.30 (1.80–2.90)0.590.00p = 0.042
Netherland32893321.20 (0.40–3.50)13.3485.01p = 0.000
Poland1316,4914983.40 (2.10–5.50)330.4396.37p < 0.0001
Estonia12603361.40 (1.00–1.90)
Portugal243800.02 (0.00–1.60)0.0410.00p = 0.839
Luxembourg11394362.60 (1.90–3.60)0.000.00
Romania14001.20 (0.10–16.70)
Sweden2796231.20 (0.10–22.0)5.1480.53p = 0.023
Russia53261431.20 (0.60–2.30)15.4874.15p = 0.004
Slovakia36130971.60 (1.30–1.90)0.570.00p = 0.751
Slovenia1135137.40 (4.00–13.20)
Czech Republic22823371.30 (1.00–1.80)0.040.00p = 0.836
Belgium3105310.20 (0.10–0.90)0.540.00p = 0.761
Britain11131614.20 (8.90–21.90)
Turkey21224282.00 (0.80–4.80)1.9047.41p = 0.168
Spain1562173.00 (1.90–4.80)
Switzerland56259981.50 (0.80–3.00)40.0290.00p < 0.0001
Ukraine1767131.90 (1.10–3.20)
China31805904.10 (1.90–9.0)19.6389.81p < 0.0001
Israel1119630.30 (0.10–0.80)
Japan44033802.00 (1.00–4.20)27.6189.14p < 0.0001
Mongolia3727355.10 (2.20–11.50)11.8783.15p = 0.003
Thailand112,18410.00 (0.00–0.10)
Nigeria170000.00 (0.00–0.00)
United States1222,3008064.30 (3.00–6.20)237.3394.95p < 0.0001
Canada124841.60 (0.60–4.20)
I2: inverse variance; Q-p: Cochran’s; CI: confidence interval; MIR: minimum infection rate. Measure of heterogeneity: the weighted sum of squared differences between individual study effects and the pooled effect across studies.
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Onyiche, T.E.; Răileanu, C.; Fischer, S.; Silaghi, C. Global Distribution of Babesia Species in Questing Ticks: A Systematic Review and Meta-Analysis Based on Published Literature. Pathogens 2021, 10, 230. https://doi.org/10.3390/pathogens10020230

AMA Style

Onyiche TE, Răileanu C, Fischer S, Silaghi C. Global Distribution of Babesia Species in Questing Ticks: A Systematic Review and Meta-Analysis Based on Published Literature. Pathogens. 2021; 10(2):230. https://doi.org/10.3390/pathogens10020230

Chicago/Turabian Style

Onyiche, ThankGod E., Cristian Răileanu, Susanne Fischer, and Cornelia Silaghi. 2021. "Global Distribution of Babesia Species in Questing Ticks: A Systematic Review and Meta-Analysis Based on Published Literature" Pathogens 10, no. 2: 230. https://doi.org/10.3390/pathogens10020230

APA Style

Onyiche, T. E., Răileanu, C., Fischer, S., & Silaghi, C. (2021). Global Distribution of Babesia Species in Questing Ticks: A Systematic Review and Meta-Analysis Based on Published Literature. Pathogens, 10(2), 230. https://doi.org/10.3390/pathogens10020230

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