Rickettsiaceae and Anaplasmataceae infections in Ixodes ricinus ticks from urban and natural forested areas of Poland

Abstract

Background

Ixodes ricinus is a major vector for a range of microbial pathogens and the most prevalent and widely distributed tick species on the European continent, occurring in both natural and urban habitats. Nevertheless, little is known about the relative density of ticks in these two ecologically distinct habitats and the diversity of tick-borne pathogens that they carry.

Methods

We compared densities of questing I. ricinus nymphs and adults in urban and natural habitats in Central and Northeastern Poland, assessed the prevalence and rate of co-infection with A. phagocytophilum, Rickettsia, Ehrlichia and ‘Ca. Neoehrlichia spp.’ in ticks, and compared the diversity of tick-borne pathogens using molecular assays (PCR).

Results

Of the 1325 adults and nymphs, 6.2% were infected with at least one pathogen, with 4.4%, 1.7% and less than 0.5% being positive for the DNA of Rickettsia spp., A. phagocytophilum, Ehrlichia spp. and Ca. N. mikurensis, respectively. Although tick abundance was higher in natural habitats, the prevalence of the majority of pathogens was higher in urban forested areas.

Conclusion

We conclude that: (i) zoonotic genetic variants of A. phagocytophilum are widely distributed in the Polish tick population, (ii) although the diversity of tick borne pathogens was higher in natural habitats, zoonotic species/strains were detected only in urban forests, (iii) and we provide the first description of Ca. N. mikurensis infections in ticks in Poland.

Background

Pathogens that cause tick-borne diseases (TBDs), such as borreliosis or anaplasmosis, constitute a significant problem for the health of humans, companion animals and livestock worldwide. The majority of TBDs are classified as emerging infectious diseases because of the growing awareness of their importance, the availability of better diagnostic reagents and the consequent rising statistics for incidence in the human population [1,2]. In Europe, Ixodes ricinus is the most prevalent and widely distributed tick species and serves as the most important vector for several microbial pathogens [3-5]. However, tick abundance and the prevalence of transmissible pathogens in ticks varies locally depending on many factors, i. e. temperature, accessibility of suitable vertebrate hosts etc. [6-9]. The range of available hosts differs depending on the habitat characteristics (i.e. urban versus natural) and is likely to also influence the species/strain variability of pathogens vectored by ticks [10]. In urban habitats, humans, pets (mainly dogs), synantropic rodents (Apodemus sylvaticus) and birds probably play a significant role as tick hosts and the sources of TBPs. In natural forest habitats in Europe mainly deer (Cervidae), wild rodents (Myodes glareolus, Apodemus flavicollis) and birds are considered to be the most important hosts for I. ricinus and the major source of many TBDs [11-14].

In Poland, studies on the occurrence and diversity of Rickettsia, Anaplasma, Ehrlichia and ‘Candidatus Neoehrlichia’ in I. ricinus have been few and the subject has been relatively neglected when compared with other TBPs [15,16]. The best recognized is the occurrence of A. phagocytophilum in I. ricinus ticks, but little is known about the existence of co-infections and the species/strain diversity of other Rickettsiaceae and Anaplasmataceae species.

Tick-borne rickettsiosis is caused by intracellular bacteria belonging to the spotted fever group (SFG) of the Rickettsiaceae family. Since the early 1990s and the introduction and increasingly popular use of molecular methods (PCR, PCR-RFLP and sequencing), 17 new Rickettsia species have been added to the list of rickettsiae that are known to cause human diseases in different parts of the world [17]. Ticks are believed to act as vectors and reservoirs of the SFG group Rickettsia and interestingly, Rickettsia spp. are among the most common pathogens found in Dermacentor reticulatus and I. ricinus ticks in Europe [18]. However, reservoir hosts of Rickettsia are still not well defined and further investigations are required to elucidate the full range of potential host species.

The family Anaplasmataceae are gram-negative, intracellular bacteria, and include the genera Anaplasma and Ehrlichia as well as bacteria of the new candidate species ‘Candidatus Neoehrlichia mikurensis’ and ‘Candidatus Neoehrlichia lotoris’. It is already well established that I. ricinus ticks constitute competent vectors for A. phagocytophilum, an agent of human granulocytic anaplasmosis [19]. These bacteria are widespread over the territories of the USA, Europe and Asia and, apart from humans, can infect many mammalian species, i.e. dogs, cats, horses, sheep, rodents, birds and roe deer [14,20-22]. Molecular analyses have indicated that some strains/ genetic variants of A. phagocytophilum that are pathogenic for humans and domestic animals, circulate widely in nature in different hosts and display different vector tropisms and degrees of host pathogenicity [23-26].

Bacteria of a new candidate species ‘Candidatus Neoehrlichia mikurensis’ were discovered for the first time recently in small rodents and I. ovatus ticks in Japan [27]. It is believed that small rodents serve as reservoir hosts for Ca. N. mikurensis [28,29]. Moreover, human infections with these bacteria have been described recently in North and Central Europe as well as in China [30-33]. The occurrence of Ca. N. mikurensis DNA in I. ricinus ticks has been confirmed already in western and northern parts of Europe [34-36] and in I. persulcatus ticks in eastern Russia [20].

Among the five described Ehrlichia species, three cause infections in dogs and humans (E. canis, E ewingii and E. chaffeensis), E. muris is a rodent pathogen and E. ruminantium is an agent of heartwater disease in domestic ruminants [20]. The first case of E. muris infection was described originally in a wild-caught specimen of the mouse Eothenomys kageus in Japan [37] and since then single cases of E. muris infection have been detected in rodents [38] and I. ricinus ticks [39] in Europe. In Poland only one report has been published thus far and that was for the occurrence of Ehrlichia sp. in common voles, Microtus arvalis[40].

The key hypothesis driving our research was that tick abundance and hence the prevalence and the diversity of the TBPs that they carry should differ markedly between natural and urban forests where ticks abound, because of the contrasting ecology with either little or considerable human intervention, respectively, and the availability of different hosts for the ticks and hence reservoirs of varying competence for the pathogens. Our aims were therefore (1) to compare the densities of questing I. ricinus ticks (nymphs and adults) in forested urban and natural habitats; (2) to estimate the prevalence of A. phagocytophilum, Rickettsia, Ehrlichia and ‘Ca. Neoehrlichia spp.’ in I. ricinus ticks in these two different habitat types (urban and natural), and (3) to compare the species/strain diversity of tick-borne pathogens in two representative habitats in Central and Northeastern Poland.

Methods

Study sites

Five study sites in Central and North Eastern Poland were investigated in 2011. The two sites selected as examples of urban areas are located within the administrative borders of Warsaw city, near the city center (<8 km). Natural areas are situated in protected areas of national or landscape parks in rural settings at some distance from major conurbations.

Urban areas

The Bielański [52°17’32”N, 20°57’36”E] and Kabacki Forests [52°6’58”N, 21°3’26”E] act as large city parks (130 ha and 903 ha, respectively), surrounded by dense urban and sub-urban settlements and are fragmented by paved roads and pedestrian/ cycle paths (Figure 1). The Kardynał Wyszyński University is situated in Bielański Forest. Access to urban forests is facilitated by main roads, the metro line and is within easy walking distance from nearby housing estates. These forests are affected by high anthropopression, being used daily as recreational areas by children, and intensively throughout the year by amateur cyclists, runners and country ski runners. The forests are also frequented by free-ranging feral dog populations and cats from the local housing estates. In Kabacki Forest, visitors are permitted to leave the paths to access facilities such as playgrounds for children, sports grounds, banks, approved camp fire/barbeque sites. In these urban parks, tick collection sites were selected near to the main park entrance (<1 km) and main roads. The fauna of Kabacki and Bielański forests is mainly limited to synantropic mammals such as rodents, urban foxes, hedgehogs, martens, badgers and a variety of species of birds. Roe deer, hare and wild boar may also occasionally venture into these locations. Elk migrating from the Kampinoski National Park may be occasionally encountered in Bielański Forest.

Figure 1.

Map of the natural and urban areas in Central, North-eastern and East Poland where ticks were collected.

Natural areas

Three of the five study sites (Kampinoski National Park, KNP [52°18’21”N, 20°36’32”E], Białowieża National Park, BNP [52°46’20”N, 23°50’60”E], Mazury Landscape Park, MLP [53°48’25”N, 21°38’36”E]) are situated in protected areas of national or landscape parks and were considered as ‘natural’ areas, in Central (KNP) and Northeastern Poland (BNP, MLP) (Figure 1). Białowieża National Park (62 500 ha) has a global reputation as a model natural habitat, representative of the ancestral European primeval deciduous forests (World Heritage List of UNESCO since 1972). It is known also for its populations of game species, including roe and red deer and wild boar, and in particular for its free-living population of European bison (Bison bonasus). Among other mammalian species regularly encountered in the forest are wolves, elks, lynx and beavers.

Both Kampinoski National Park and Mazury Landscape Park comprise a mixture of natural and managed forests, some of the latter having been managed for over 120 years in the case of MLP. Managed forests consist of pine trees (Pinus sylvestris) with the addition of deciduous tree species (birch, alder, elm and oak). MLP is well known for its combination of impressive forests and numerous (>1000) natural lakes. These forests are not fragmented, but are surrounded by agricultural areas, with minimal numbers of human settlements and are inhabited by a range of wild game and protected species indigenous to the region. As with BNP these include: roe and red deer, wild boar, elk, lynx, wolf, beaver and many other species of small and medium size mammals (i.e fox, badger, hare, marten) and birds. Human activity in the forests is very limited and seasonal; hunters, local people collecting berries or mushrooms, tourists (mainly cyclers), forestry workers. It is mandatory to keep dogs on the leash in the national parks in Poland, otherwise entry is prohibited by law and contravention is enforced by fines.

As far as we are aware there are no quantitative census data through which anthropopression can be reliably compared between our urban and natural study sites, but from our personal experience of having visited our study sites regularly we estimate the number and density of visitors to be 1000-10000 higher in the urban parks compared to the natural forests. Similarly, the predator pressure from domestic and feral dogs and cats is undoubtedly much higher in the two urban forests, as opposed to the natural predator-prey relationships that exist in natural forests.

Ixodes ricinus ticks

Questing ticks, only nymphs and adults, were collected from vegetation by blanket dragging (white blanket 1.5×0.75 m) in central and north-eastern regions of Poland in May, July and September 2011. Ticks were collected twice daily (about 9 a.m. and 4-5 p.m.), for a minimum of four consecutive days in each month. In each collection site, tick abundance was measured by conventional flagging in 300-500 m² plots and then extrapolated to a standard 100 m². The species, developmental stage of individual ticks, as well as the sex of adults were recorded, and the nymphs from a single drag during flagging were pooled in groups of 10 prior to DNA extraction. In the case of positive PCR results for nymphs, it was assumed that at least one nymph was infected (minimal infection rate; MIR). Genomic DNA was extracted from homogenized tick specimens using the DNAeasy Blood and Tissue Kit (Qiagen, Crawley, UK ) and stored at –20°C.

PCR analysis

Detection and genotyping of Rickettsia, A. phagocytophilum, Ehrlichia spp. and Ca. Neoehrlichia spp. were performed by amplification and sequencing of different loci: the groESL heat shock operon and 16S rRNA gene for the Anaplasmataceae family and gltA for the Rickettsiaceae family. The primers and thermal profiles used in this study have been described previously [19,41,42]. Reactions were performed in a final volume of 20 μl and contained 0.33 mM dNTPs (Eurobio, Lille, France), 2 mM MgCl₂, 1× PCR buffer, 1 U Taq polymerase (Fermentas), 1 μM of each primer and 5 μl of the extracted DNA sample. Negative controls were performed in the absence of template DNA. To check whether amplifiable DNA had been extracted, we used PCR reactions employing tick-specific primers [43]. Only positive samples were chosen for further analysis. Amplicons were visualized with Midori Green stain (Nippon Genetics Europe GmbH) following electrophoresis in 2% agarose gels. Amplicons were purified using the Axygen Clean-up purification kit (Axygen, USA) and sequenced by a private company (Genomed S.A., Poland) in both directions.

Phylogenetic analysis

DNA sequence alignments and phylogenetic analysis were conducted using MEGA version 5.0 [44]. After testing the data for the best substitution model, phylogenetic trees were obtained using Maximum Likelihood as the tree construction method and Hasegawa-Kishino-Yano parameter algorithm as a distance method. For comparison, sequences of Rickettsia, A. phagocytophilum, Ehrlichia and Ca. Neoehrlichia species/strains obtained from GenBank (http://www.ncbi.nlm.nih.gov) were implemented in the sequence alignment. The stability of inferred phylogenies was assessed by bootstrap analysis of 1000 randomly generated sample trees.

Statistical analysis

Data are expressed as arithmetic means ± 95% confidence limits per 100 m² of blanket dragging. Tick abundance was analyzed using multifactorial general linear models (GLM) with normal error structures in SPSS v.20 for Windows. We fitted quality of habitat (HABITAT, 2 levels- urban [Bielański + Kabacki Forests] and natural [KNP + BNP + MLP]), SITE (5 levels: KNP, BNP, MLP, Bielański Forest, Kabacki Forest) and tick STAGE of development (3 levels: nymphs, females and males) as factors. Differences in Rickettsia, A. phagocytophilum, Ehrlichia and Ca. Neoehrlichia prevalence in ticks between study sites were analyzed using the χ² test in Instat or Fisher Exact Test when applicable.

New nucleotide sequences

New nucleotide sequences have been deposited in GenBank with the accession numbers KF312351-KF321354 for 16S rRNA of A. phagocytophilum, KF312355-KF321361 for groESL of A. phagocytophilum, KF312362 for groESL of E. muris and KF312363 for groESL of Ca. N. mikurensis.

Results

Abundance of I. ricinus ticks

Overall a total of 1589 ticks were collected and of these 72% (1147) were nymphs and 28% were adults (241 males and 201 females) (Table 1). The abundance of questing I. ricinus (nymphs and adults) varied significantly between study sites (GLM, main effect of SITE; F₄,₁₄₀ = 4.80, P = 0.001). The highest tick density per 100 m² was recorded in Białowieża National Park (Table 1). Average tick densities were similar in Bielański Forest and MLP. The overall abundance of I. ricinus was lowest in KNP and Kabacki Forest (Table 1). The abundance of nymphs was highest in Bielański Forest and BNP (GLM, main effect of SITE; F_4,140 = 3.90, P = 0.002, Table 1). Female and male abundances were relatively low (0.6-2.8 ticks per 100 m²) and no significant differences were observed between sampling areas. The abundance of I. ricinus ticks was almost twice as high in natural as in urban areas (GLM, main effect of HABITAT; F_1,140 = 5.80, P = 0.017) (Table 1). Because the difference in the average tick densities per 100 m² between the two types of forest was significant, the sampling areas were divided into two groups with: (1) low tick abundance (5.7 [2.7-8.7]; Kabacki Forest and KNP), and (2) high tick abundance (14.5 [12.2-16.7]; Bielański Forest, BNP, MLP) (GLM, main effect of HABITAT; F_1,140 = 21.2, P < 0.001) (Table 1). No statistical differences in tick abundance between study months were observed.

Table 1.

Abundance of I. ricinus ticks in forested urban and natural regions of Poland

Collection site	Quality of habitat	Abundance of Ixodes ricinus ticks (per 100 m 2 [95% CL])												Total, all months
		May				July				September
		Nymphs	Females	Males	Total	Nymphs	Females	Males	Total	Nymphs	Females	Males	Total	Nymphs	Females	Males	Total
Bielański Forest	urban	8.3	0.9	1.2	10.5	17.5	4.0	0.5	22.0	9.5	2.0	1.5	13.0	11.8	2.3	1.1	15.2*	8.8
		[5,3-11,3]	[0,1-1,8]	[0,2-2,3]	[6,8-14,1]	[5,4-29,6]	[0,4-7,6]	[0,0-4,9]	[7,2-36,8]	[0,0-21,6]	[0,0-5,6]	[0,0-5,9]	[0,0-27,8]	[6.0-17.6]	[0.6-4.0]	[0.0-3.2]	[8.1-22.2]	[5.9-11.6]
Kabacki Forest		3.7	0.2	0.3	4.2	6.0	1.5	1.0	8.5	9.5	0.0	1.5	11.0	6.4	0.6	0.9	7.9
		[0,0-7,5]	[0,0-1,3]	[0,0-1,6]	[0,0-8,8]	[0,0-18,1]	[0,0-5,1]	[0,0-5,4]	[0,0-23,3]	[0,0-21,6]	[0,0-3,6]	[0,0-5,9]	[0,0-25,8]	[0.6-12.2]	[0.0-2.3]	[0.0-3.0]	[0.8-15.1]
BNP	natural	11.5	3.4	3.9	18.8	21.3	2.3	2.7	26.3	8.2	2.2	1.7	12.1	13.7	2.6	2.8	19.1*	13.4
		[7,6-15,5]	[2,2-4,5]	[2,5-5,4]	[14,0-23,6]	[14,3-28,3]	[0,3-4,4]	[0,2-5,2]	[17,8-34,9]	[2,5-13,9]	[0,5-3,9]	[0,0-3,7]	[5,1-19,1]	[10.4-17.0]	[1.7-3.6]	[1.6-3.9]	[15.1-23.1]	[10.9-16.0]
KNP		1.7	2.1	2.9	6,8	2.3	0.8	1.3	4.5	6.0	0.3	1.0	7.3	3.4	1.1	1.8	6.2
		[0,0-6,2]	[0,8-3,4]	[1,3-4,5]	[1,4-12,2]	[0,0-9,3]	[0,0-2,9]	[0,0-3,8]	[0,0-13,0]	[0,0-14,6]	[0,0-2,8]	[0,0-4,1]	[0,0-17,7]	[0.0-7.3]	[0.0-2.2]	[0.3-3.2]	[1.3-11.0]
MLP		13.3	0.3	0.5	14,1	3.0	0.0	5.0	8.0	10.0	2.0	2.4	14.4	8.8	0.8	2.6	12.2*
		[8,6-18,1]	[0,0-1,7]	[0,0-2,2]	[8,3-19,9]	[0,0-20,1]	[0,0-5,0]	[0,0-11,2]	[0,0-28,9]	[2,3-17,7]	[0,0-4,3]	[0,0-5,2]	[5,0-23,8]	[2.3-15.2]	[0.0-2.7]	[0.3-4,9]	[4.2-20.0]
Total, all sites		7.7	1.4	1.7	10.9	10.0	1.7	2.1	13.9	8.6	1.3	1.6	11.6	8.8	1,5	1.8	12.1 [9.3-14.9]
		[5.9-9.5]	[0.9-1.9]	[1.1-2.4]	[8.7-13.1]	[4.8-15.2]	[0.2-3.3]	[0.2-4.0]	[7.5-20.3]	[4,4-12.9]	[0.0-2.6]	[0.1-3.2]	[6.3-16.8]	[6.5-11.1]	[0.8-2.2]	[1.0-2.7]

CL- 95% confidence limits.

^*classified as high-tick-density forests.

N- nymphs, F- females, M-males.

Prevalence of pathogens in ticks

Of the 1325 adults and nymphs, a total of 6.2% (n = 82) were infected with at least one pathogen. As expected, the prevalence of pathogens in ticks was significantly higher in adults (10.0%; 42/421) than the MIR in nymphs (4.4%; 40/904) (χ² = 14.31, df = 1, P < 0.0001). Prevalence of pathogens in ticks differed between urban and natural habitats (Table 2). Overall prevalence of TBPs was almost three times higher in urban compared with natural forests (χ² = 22.97, df = 1, P < 0.0001).

Table 2.

The prevalence of tick-borne pathogens in I. ricinus collected in forested urban and natural areas of Poland

Site	Quality of habitat	Overall TBD prevalence%	Prevalence% (no. infected/no. tested)
			Rickettsia sp.		A. phagocytophilum		Ca. Neoehrlichia sp.		Ehrlichia sp.
Bielański Forest*	urban	11.6 (42/405)	4.5 (9/201)	7.7 (31/405)	6.0 (12/201)	3.0 (12/405)	0.0 (0/201)	0.2 (1/405)	0.0 (0/201)	0.7 (3/405)
Kabacki Forest			10.8 (22/204)		0.0 (0/204)		0.5 (1/204)		1.5 (3/204)
Białowieża National Park*	natural	4.4 (40/920)	1.6 (10/625)	2.9 (27/920)	1.3 (8/625)	1.1(10/920)	0.0 (0/625)	0.2 (2/920)	0.0 (0/625)	0.1 (1/920)
Kampinos National Park			3.8 (6/156)		1.3 (2/156)		0.0 (0/156)		0.0 (0/156)
Mazury Lake District*			7.9 (11/139)		0.0 (0/139)		1.4 (2/139)		0.7 (1/139)

^*classified as high-tick-density forests.

Rickettsia spp. infections

This was the predominant pathogen in our study, 4.4% (58/1325) of the tested ticks being recorded as positive for Rickettsia spp. The prevalence of infected ticks was about 2.5 times higher in urban (7.7%) than in natural sites (2.9%) (χ² = 7.77, df = 1, P = 0.0053). The DNA of Rickettsia spp. was detected in 3.7% nymphs (MIR) (33/904) and in 5.9% adults (25/421) (NS). Prevalence of Rickettsia was significantly higher in low-tick-density forests (7.8% in KNP + Kabacki Forest) than in high-tick-density forests (3.1% in BNP + MLP + Bielański Forest) (χ² = 12.60, df = 1, P < 0.001).

Sequence analysis of the 770 bp fragment of the gltA gene of 40 isolates (20 of each habitat type, urban and natural) showed the presence of two different Rickettsia species. The most prevalent was R. helvetica (38/40, 95%), closely related (99.9% homology) to the R. helvetica isolates [GenBank: EU359285] originally obtained from Ixodes ticks in Switzerland and differed from them by only one nucleotide (G → T) at position 713. Rickettsia helvetica isolates were found in all study sites. Two of 40 isolates (5%) were identified as R. monacensis. These isolates showed 99.7% similarity (nucleotide substitutions at positions 476 [T → C] and 713 [G → C]) to R. monacensis IrR/Munich strain [GenBank: DQ100163] derived from I. ricinus in Germany and were identical with R. monacensis isolated from human patients in Spain [GenBank: DQ517498] and Korea [GenBank: FJ009429]. The two R. monacensis isolates both originated from an urban forest (Kabacki Forest).

Anaplasma phagocytophilum infections

The overall prevalence of A. phagocytophilum in I. ricinus was 1.7% (22/1325). Prevalence was significantly higher in urban than in natural sites (3% versus 1.1%) (Table 2, χ² = 4.98, df = 1, P = 0.026). No positive ticks were found in Kabacki Forest and Mazury Landscape Park forest. The MIR in nymphs was significantly lower (0.6%; 5/904) than the prevalence in adults (4.0%; 17/421) (χ² = 18.26, df = 1, P < 0.0001), and prevalence did not differ statistically between ticks from low- and high-tick-density forests (Table 2).

The 540 bp fragment of the 16S rRNA gene and the 1200 bp fragment of the groESL heat shock operon were further analyzed in 18 isolates. The nucleotide identity/similarity of the sequenced 16S rDNA fragments was very high (99.6-100%). Eight of 18 sequences from natural areas (Table 3; KNP + BNP) were identical, representing genetic variant I, which is considered to be zoonotic (Figure 2). A further eight isolates could be distinguished on the basis of substitution at position 376 (G → A) in the variable region near the 5’ end of the 16S rRNA gene, representing genetic variant II (Table 3). Variant III was represented by one isolate and differed by two nucleotides at positions 199 (G → T) and 376 (G → A). Variant IV included one isolate that differed by two nucleotides at position 376 (G → A) and 539 (G → T). Isolates belonging to variant I were found in ticks collected from natural areas. Isolates of variants II, III and IV were found only in ticks from one urban forest- Bielański Forest (Table 3).

Table 3.

Polymorphism in the fragment of 16S rRNA gene in A. phagocytophilum isolates from ticks and human pathogenic strains (sequences published in GenBank)

Strain/genetic variant		Nucleotide positions 5’ → 3’ a				Quality of habitat/country	No. of isolates (reference no. of samples)/site of study	GenBank acc. number	Host/vector found in other studies (only 100% homology; nucleotide sequences deposited in GenBank)
		199	328	376	539
This study	I	G	A	G	G	natural/ Poland	2 (6,153)/KNP	KF312352	bank vole (Myodes glareolus, KC740432); dog (KF985242); elk (Alces alces, KC800983); roe deer (Capreolus capreolus, JQ965530); cotton rat (Sigmodon hispidus, JQ063025); rat (Rattus norvegicus, KC470064); reindeer (Rangifer tarandus, JX841254); hedgehog (Erinaceus europaeus, JN571163); I. ricinus (KF481930), I. trianguliceps (KF481934)
							6 (39, 54, 73, 85, 90, 283)/BNP
	II	G	A	A	G	urban/Poland	8 (29, 37, 38, 47, 62, 67, 71, 73)/Bielański Forest	KF312353	dog (EF668225); cat (HM138366); I. ricinus (JX909354); D. reticulatus (KF381413)
	III	T	A	A	G		1 (57)/Bielański Forest	KF312351	n. m.b
	IV	G	A	A	T		1 (64)/Bielański Forest	KF312354	n. m.b
A. phagocytophilum strains pathogenic for human		G	A	G	G	Poland		KF111754
		G	A	G	G	Slovenia		GU236658
		G	A	G	-	Italy		DQ029028
		G	A	G	G	USA		GU236664
		G	A	G	G	USA		NR_074113

^aThe number corresponds to the positions of nucleotide substitutions relative to the sequence of the complete 16S rRNA gene of A. phagocytophilum strain HZ (NR_074113). Base substitutions are shown in bold.

^bNo match has been found in GenBank.

Figure 2.

Phylogenetic tree of the A. phagocytophilum, Ehrlichia i Ca. Neoehrlichia isolates studied in the current work and chosen isolates from GenBank based on the fragment of the groESL heat shock operon. Numbers at the nodes of the tree indicate bootstrap values (1000 replicates).

The nucleotide sequences of isolates from groups I and II were identical to the sequences obtained from rodents, dogs, cats, roe deer, hedgehog and ticks (Table 3). Additionally, the 16S rRNA sequence of variant I was identical with the human pathogenic strains isolated in Slovenia, Italy and the USA (Table 3). The nucleotide sequences of isolates from groups III and IV did not show 100% identity to the known sequences of 16S rRNA of A. phagocytophilum deposited in GenBank.

The partial groESL fragments (1200 bp) were also sequenced for all positive samples (n = 18) since the 16S rRNA gene is too conserved for analysis of genetic heterogeneity. The level of homology between isolates was also high (98.0-100%). Sequence analysis allowed identification of seven different genetic variants (I-VII) that differed by 2 to 13 nucleotides (Table 4). Genetic variants I and II included 10 isolates from ticks collected only in Bielański Forest, an urban site (Table 4). Variants III-VII were composed of 1 or 2 sequences found only in ticks from natural forested areas (BNP, KNP). Analysis of these groESL fragments allowed the differentiation of 4 variants from BNP, all grouped in variant I based on the 16S rRNA gene fragment (Table 3).

Table 4.

Polymorphism in the fragment of the groESL heat shock operon in A. phagocytophilum isolates from ticks and human pathogenic strains (sequences published in GenBank)

Strain/genetic variant		Nucleotide positions 5’ → 3’ a																													Quality of habitat/country	No. of isolates (reference no. of samples)/site of study	GenBank acc. number	Host/vector found in other studies (only 100% homology; nucleotide sequences deposited in GenBank)
		167	398	401	431	476	486	497	511	561	776	821	836	837	840	845	857	872	890	923	956	965	980	992	1049	1085	1088	1112	1229	1244
This study	I	G	A	A	G	C	G	T	C	A	C	C	A	C	T	A	C	C	G	C	C	G	T	T	C	A	C	C	A	T	urban/Poland	9 (29, 37, 38, 47, 57, 62, 67, 71, 73)/ Bielański Forest	KF312357	dog (EU381151); I. ricinus (EU381152)
	II	G	A	A	G	C	G	C	C	A	C	C	A	C	T	A	C	C	T	C	T	G	T	T	T	A	C	C	G	C		1 (64)/ Bielański Forest	KF312360	red deer (Cervus elaphus, HM057225); I. ricinus (KF383239)
	III	G	A	A	A	C	G	T	C	A	C	C	A	C	T	A	C	C	T	C	T	G	T	T	T	A	C	C	G	C	natural/Poland	2(85, 90)/BNP	KF312358	I. ricinus (AY281831)
	IV	G	A	A	G	A	A	T	G	A	C	C	A	C	T	A	C	C	G	C	C	G	T	T	C	A	C	C	A	T		2(39, 54)/BNP	KF312355	n. m. b
	V	G	A	A	G	C	G	C	C	A	C	C	A	C	T	A	C	C	G	C	T	G	T	T	T	A	C	C	A	T		1(73)/BNP	KF312359	n. m b
	VI	A	A	A	G	C	G	C	C	A	C	C	A	C	T	A	C	C	G	C	T	G	T	T	C	A	C	C	G	C		1(283)/BNP	KF312361	n.m b
	VII	G	G	A	G	C	G	T	C	A	C	A	G	G	G	T	T	T	G	G	C	A	A	C	T	G	C	T	G	C		2(6, 153)/KNP	KF312356	roe deer (Capreolus capreolus, AF478560); I. ricinus (EU552914)
A. phagocytophilum strains pathogenic for human		G	A	G	G	C	G	T	C	G	C	C	A	A	T	A	C	C	G	C	C	A	T	T	C	G	A	T	G	C	USA		U96728
		G	A	A	G	C	G	T	C	G	C	C	A	A	T	A	C	C	G	C	C	A	T	T	C	G	A	T	G	C	USA		AF172159
		A	A	A	G	C	G	T	C	G	T	C	A	A	T	A	C	C	G	C	C	G	T	T	C	A	C	C	A	T	Slovenia		AF033101
		G	A	G	G	C	G	T	C	G	C	C	A	A	T	A	C	C	G	C	C	A	T	T	C	G	A	T	G	C	USA		JF494839

^aThe number corresponds to the positions of nucleotide substitutions relative to the sequence of the groESL heat shock operon of the human pathogenic A. phagocytophilum strain (U96728). Base substitutions are shown in bold.

^bNo match has been found in GenBank.

Scrutiny of the phylogenetic tree, based on the partial groESL operon sequences, showed that two isolates from variant VII were identical to other European isolates, mainly from I. ricinus ticks and roe deer (Figure 2, Table 4). Isolates belonging to variant I-III clustered with A. phagocytophilum pathogenic for human and domestic animals in Europe, as well as in North America, and differed from variant VII by 13 nucleotides (Table 4). Thus, these 6 variants (I-VI) are considered to represent zoonotic genotypes. The nucleotide sequences of isolates from groups IV-VI did not show 100% identity to the known sequences of groESL operon sequences of A. phagocytophilum deposited in GenBank.

Ehrlichia spp. and Candidatus Neoehrlichia spp. infections

The DNA of Ehrlichia spp. and that of Ca. Neoehrlichia spp. was found in 0.3% (4/1325; only in nymph pools) and 0.2% (3/1325; two males and 1 nymph pool) of the sampled ticks, respectively. Three ticks positive for Ehrlichia DNA were collected in an urban area (Kabacki Forest) and one in MLP (natural site) (Table 2). The presence of Ca. Neoehrlichia spp. was confirmed in nymphs from Kabacki Forest (urban area) and in 2 males from MLP (natural site) (Table 2).

Molecular analysis of the 540 bp fragment of the 16S rRNA gene of Ehrlichia (n = 4) and Ca. Neoehrlichia (n = 3) isolates showed that all sequences were identical and differentiation between these genera was possible only on the basis of the partial groESL fragment (1200 bp). The four Ehrlichia isolates were identical [GenBank: KF312362] and showed 82.3% groESl sequence homology with Ca. Neoehrlichia and 100% sequence homology with E. muris originally obtained from rodents [GenBank: GU358690] and I. persulcatus [GenBank: GU358686] in Russia. All Ca. Neoehrlichia isolates were also identical [GenBank: KF312363] and showed 100% sequence homology with Ca. N. mikurensis from I. ricinus ticks [GenBank: EU810407] and humans [GenBank: EU810406] in Germany. Our isolates clustered also with other Ca. N. mikurensis pathogenic for humans [GenBank: HM045824] and dogs [GenBank: EU432375] in Europe (Figure 2).

Co-infections in I. ricinus ticks

4.8% (2/42) of adult ticks identified as carrying pathogens yielded positive results for two pathogens and none were infected with three or more. Rickettsia helvetica and A. phagocytophilum were involved in both co-infections. Both ticks co-infected with these pathogens were collected in an urban area (Bielański Forest). Analysis of co-infections in nymphs was not justified because DNA was extracted from pooled samples of ticks.

Discussion

The results of our study, focusing on a comparison of the abundance of I. ricinus ticks and prevalence of TBPs in ticks sampled in forested urban and natural habitats, revealed significant and interesting differences between these ecologically contrasting sites. Although tick abundance was higher in natural habitats, the prevalence of the majority of TBPs (A. phagocytophilum, Rickettsia spp., E. muris) was higher in urban areas. Interestingly, while the diversity of A. phagocytophilum was higher in natural habitats, only the zoonotic species/ strains (i.e. R. monacensis, A. phagocythophilum variants I-II [groESL operon sequences]) were detected in urban forests. This finding likely reflects the availability of different reservoir hosts and points to a higher risk of TBDs for humans venturing into urban forests compared with forests located in natural sites. We also report here for the first time the detection of Candidatus Neoehrlichia mikurensis in questing Ixodes ricinus ticks in Poland.

As in many previous studies on ticks [45,46], in our study also the abundance of questing I. ricinus varied significantly between study sites. The highest density was recorded in natural forested habitats, i.e. in the Białowieża National Park and the Mazury Landscape Park both of which correspond to the ‘medium tick abundance’ category of forests (11-40 ticks per 100 m²[47]). A similar high abundance was observed in Bielański Forest in Warsaw, which is a part of an ancient deciduous primeval forest and the soil humidity and plant coverage are very similar to those encountered in Białowieża Primeval Forest (BNP). Deciduous humid forests are known to constitute preferable habitats for I. ricinus ticks [48,49]. The overall abundance of I. ricinus was lowest in Kampinos National Park and Kabacki Forest, where pine Pinus silvestris are the main tree species because of the poorer sandy soil conditions that are less suitable for deciduous tree species (mainly low-humid sandy areas; ‘low tick abundance’, 3-10 ticks per 100 m²[47]).

Despite lower tick abundance, the prevalence of three of four pathogens detected in this study was at least twice as high in ticks from urban forests, a finding corresponding to the so-called ‘dilution effect’ of Estrada-Peña et al.[50]. The reasons underlying this difference and its consequences are of particular relevance for public health concerns. For an explanation of this phenomenon we looked at the genetic diversity of the most common pathogens. Although the diversity of A. phagocytophilum was higher in natural habitats, only zoonotic species/ strains (i.e. R. monacensis, A. phagocythophilum variants I-II [groESL operon sequences]) were detected in urban forests. This finding likely reflects the availability of different reservoir hosts for the pathogen and is consistent with the idea that in urban areas humans, companion animals (mainly dogs) as well as synanthropic rodents, foxes and hedgehogs constitute suitable hosts for ticks and act as reservoir hosts for the parasites. Rickettsia monacensis, which is pathogenic for humans, was found only in ticks from Kabacki Forest, supporting our hypothesis and pointing to a new health risk in this recreational area of Poland’s capital city, Warsaw. The greatest genetic variability of A. phagocytophilum (5 variants) was found in ticks from Białowieża and Kampinos National Parks (including also the non-zoonotic variant VII [groESL operon sequences]) probably reflecting the wide range of natural I. ricinus hosts that live in these forests and can act as reservoir hosts for A. phagocytophilum (i.e. Cervidae, Carnivores). In this context it is pertinent also that in our earlier studies on roe deer, the dominance of non-zoonotic over zoonotic A. phagocytophilum strains and other TBPs (i.e. Babesia, Bartonella) was noted [14]. Thus, although tick density and TBP diversity in ticks in urban areas appeared to be lower than in the natural habitats and to depend on a narrower tick host range, the risk for humans may be higher, as humans ‘share’ many TBPs with dogs, livestock and rodents, as a result of many years of co-existence.

Previous molecular studies have shown relatively high prevalence of tick-borne pathogens in I. ricinus from different parts of Europe. The most common infection in the current study was Rickettsia spp. with a prevalence of 4.4%, and this is comparable to prevalence rates reported from other countries in Europe: 5% in Luxembourg [51], 14-17% in Germany [6], 1.4% in France [52], 11% in Slovakia [38] and 9% in Poland [53]. In contrast to the results obtained by Overzier et al.[10] and Venclikova et al. [54], a significantly higher prevalence of Rickettsia was found in urban than in natural areas (7.7 vs. 2.9%). On the basis of the gltA gene we have identified two different Rickettsia species. Isolation of R. helvetica in our study confirmed the high prevalence and widespread nature of this species in I. ricinus in Europe. Since 1999, several R. helvetica seropositive patients with relatively mild, self-limited illnesses associated with flu-like symptoms have been reported, so the pathogenicity of R. helvetica needs further investigation. The nucleotide sequences of the gltA fragment gene showed that our R. monacensis isolates were identical with the R. monacensis strain Rp-Sp1 that is known to be pathogenic for humans. R. monacensis is an etiological agent of human rickettsiosis in Spain [55] and the DNA of these bacteria has been detected in an asymptomatic patient in Croatia [56]. The presence of these bacteria in I. ricinus ticks has also been confirmed in other European countries including Germany and Romania [57,58]. In Poland, R. monacensis has been detected recently in Northwestern Poland (in Szczecin, near Poland’s western border with Germany), where this species has never been recorded previously in ticks [53].

A. phagocytophilum has been detected in I. ricinus ticks throughout Europe and the prevalence rate has been reported to vary from 1 to 5% in Poland, Switzerland, Russia and Belarus [59-61], however, locally it may exceed 24% (Italy [62]). As in our results with Rickettsia and the data of Venclikova et al. [54], we found a significantly higher prevalence of A. phagocytophilum in urban compared with natural areas (3.0 vs. 1.1%). In agreement with data published previously [26], sequence analysis of the 1200-bp fragment of groESL in the current work revealed two distinct genetic lineages of A. phagocytophilum: (1) genetic variants detected in humans, ticks, dogs, horses, sheep and red deer from Europe and USA which are believed to be pathogenic; and (2) genetic variants isolated from ticks and roe deer in Europe that are probably non-zoonotic strains [61,63]. In our study, molecular analysis of the 16S rRNA fragment gene showed that the nucleotide sequences of eight A. phagocytophilum isolates belonging to genetic variant I were identical with A. phagocytophilum strains known to be pathogenic for humans (Table 3). However, on the basis of molecular and phylogenetic analysis of the groESL fragment, two isolates from variant I (no. 6 and 153), were assigned to the non-zoonotic variant VII. Therefore, our results emphasize that analysis of the nucleotide sequences of several genes is necessary, indeed essential, for a detailed delineation of different A. phagocytophilum strains [20].

This study has reported for the first time the presence of ‘Ca. N. mikurensis’ in questing I. ricinus from Poland. The prevalence rates of ‘Ca. N. mikurensis’ and E. muris in our study were low and differed from those in reports from Slovakia (E. muris 3% [39]), Switzerland (Ca. N. mikurensis 6% [64]) and Germany (Ca. N. mikurensis 6% [35]). In our study, the 540-bp fragment of the 16S rRNA gene was highly conserved and differentiation of the two genera was possible only on the basis of the groESL operon fragment. Although E. muris is mainly a murine pathogen, ‘Ca. N. mikurensis’ is now considered to be an emerging tick-borne pathogen of veterinary and medical importance [65]. Isolates from this study were identical with ‘Ca. N. mikurensis’ detected in blood samples of patients with severe febrile illnesses and with the strain isolated from I. ricinus from Germany [32]. Our results confirm the presence of ‘Ca. N. mikurensis’ in questing I. ricinus from Poland and point to a new risk of infection with a recently discovered TBP for animals and humans.

Interestingly, both ticks in which two genera of TBPs were detected (R. helvetica/ A. phagocytophilum) were collected in Bielański Forests from the area of Warsaw. Thus, the risk of acquiring double infection from the infected ticks appears to be higher in urban areas. However, because the number of detected co-infections was so low, on the basis of the current results it is not possible to conclude whether these concurrently infected ticks can be considered as constituting an additional health risk for people visiting the city forests.

Conclusions

There were significant differences in tick abundance between natural and urban forested habitats. Although tick abundance was higher in natural habitats, the prevalence of the majority of TBPs was higher in urban areas. This finding, together with the detection of zoonotic species/strains of Rickettsiaceae and Anaplasmataceae indicates a high risk of TBDs in city forests. The new pathogen- Candidatus Neoehrlichia mikurensis- was detected for the first time in questing I. ricinus ticks in Poland, also in urban areas.

Competing interests

The authors declare that they have no competing interests.

Authors’ contributions

Designed the study, acquired the funding: ES, RWF; collected and identified ticks: MK, GK, ES; processed samples: MK, RWF; performed PCR: MK, RWF; analyzed sequences: RWF; analyzed the data: RWF, AB, MK, JMB; wrote the paper: RWF, AB, JMB, ES. All authors read and approved the final version of the manuscript.

Acknowledgements

This study was supported by the Ministry of Science and Higher Education, Grant NN404 795240 and funded by the Faculty of Biology Institute of Zoology intramural grant no. 501/86-102356.