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. 2018 Dec 26;13(12):e0208615. doi: 10.1371/journal.pone.0208615

A survey of argasid ticks and tick-associated pathogens in the Peripheral Oases around Tarim Basin and the first record of Argas japonicus in Xinjiang, China

Li Zhao 1, Xiang-Mei Lin 2, Fei Li 1,3, Kai-Rui Li 1, Bo He 1, Lu-Yao Zhang 1, Jiao-Jiao Pan 1, Qiang-Rong Wang 1, Jia-Min Gao 1, Nicholas Johnson 4, Xiang-Fen Yuan 2, Ji-Zhou Lv 2,*, Shao-Qiang Wu 2,*, Yong-Hong Liu 1,*
Editor: Ben J Mans5
PMCID: PMC6306169  PMID: 30586406

Abstract

Argasid ticks (Acari: Argasidae) carry and transmit a variety of pathogens of animals and humans, including viruses, bacteria and parasites. There are several studies reporting ixodid ticks (Acari: Ixodidae) and associated tick-borne pathogens in Xinjiang, China. However, little is known about the argasid ticks and argasid tick-associated pathogens in this area. In this study, a total of 3829 adult argasid ticks infesting livestock were collected at 12 sampling sites of 10 counties in the Peripheral Oases, which carry 90% of the livestock and humans population, around the Tarim Basin (southern Xinjiang) from 2013 to 2016. Tick specimens were identified to two species from different genera by morphology and sequences of mitochondrial 16S rRNA and 12S rRNA were derived to confirm the species designation. The results showed that the dominant argasid ticks infesting livestock in southern Xinjiang were Ornithodoros lahorensis (87.86%, 3364/3829). Ornithodoros lahorensis was distributed widely and were collected from 10 counties of southern Xinjiang. Argas japonicus was collected from Xinjiang for the first time. In addition, we screened these ticks for tick-associated pathogens and showed the presence of DNA sequences of Rickettsia spp. of Spotted fever group and Anaplasma spp. in the argasid ticks. This finding suggests the potential role for Argas japonicus as a vector of pathogens to livestock and humans.

Introduction

Ticks could carry and transmit a variety of pathogens, including viruses, bacteria, rickettsiae, spirochetes, protozoans, chlamydia, mycoplasma and nematodes [14]. Two families of ticks are of medical significance: Ixodidae (hard ticks) and Argasidae (soft ticks). Argasid ticks comprise about 185 species from four genera. Approximately 19 species of Argasidae have been identified in China [5].

As the largest province of China, Xinjiang Uygur Autonomous Region covers over one-sixth of the country’s territory, including the majority of the arid areas in the country [6]. Forty two species of ticks in 9 genera have been identified in Xinjiang, which represent more than 1/3 of total tick species found in China [7]. Six species of argasid ticks from two genera have been reported in Xinjiang, including Argas vespertilionis, Ar. persicus, Ar. reflexus, Ornithodoros lahorensis, Or. papillipes, and Or. tartakovskyi.

The Tarim Basin is an endorheic basin, occupying an area of about 1,020,000 km2 [8]. It is sometimes used synonymously to refer to the southern half of the province, or southern Xinjiang. The vast territory, with complex geography, and diverse ecological environments within the Tarim Basin provides various habitats for argasid ticks [9]. Ninety percentage of humans and animals of Tarim Basin inhabit the Peripheral Oases, which are the most important ecosystems in the arid area [10]. Argasid ticks-livestock-humans interfaces in the Oases could promote the spread of tick-borne diseases.

More importantly, previous studies have shown that a high prevalence of tick-borne pathogens exists in Xinjiang province, such as piroplasms, Anaplasma spp., Rickettsia spp. and Borrelia spp. [6, 1113]. However, these studies focused on ixodid ticks and there have been few research regarding argasid ticks and assciated tick-borne pathogens.

In the present study, the populations of argasid species associated with livestock at the sites around the Tarim Basin of Southern Xinjiang had been investigated. In addition, the presence of argasid tick-associated pathogens was assessed using molecular techniques.

Materials and methods

Sampling area, tick sampling and identification

During the period from 2013 to 2016, we collected argasid tick specimens associated with livestock at twenty-seven sampling sites in Oases around the Tarim Basin of southern Xinjiang. This included farms at Aral, Artux, Awat, Hejing, Hetan, kargilik, Kuqa, Luntai, Makit, Minfeng, Pishan, Poskam, Qiemo, Qira, ShanShan, Shufu, Tumxuk, Tuokexun, Uqturpan, Wensu, Xayar, Xinhe, Yanqi, Yarkand, and Yopurga (Fig 1a). For the majority of counties, there was only one sampling site except Wensu county, which had three sampling sites.

Fig 1. A map of Xinjiang Province and phylogenetic analyses of tick species based on 12S rRNA and 16S rRNA.

Fig 1

A. argasid ticks were surveyed in 25 counties in southern Xinjiang. Argasid ticks were collected from 10 counties which are marked with red dots, while other 15 counties are marked with black dots, B. Neighbour joining phylogenetic analysis based on partial 16S rRNA sequences of ticks, C. Neighbour joining phylogenetic analysis based on partial 12S rRNA sequences of ticks. Bootstrap values are indicated at the nodes. Scale bar indicates the degree of divergence represented by a given length of branch. The red and blue dots indicate the DNA sequences of tick specimens acquired in this study. Abbreviations: AL, Aral; AX, Artux; AW, Awat; HJ, Hejing; HT, Hetan; KG, kargilik; KQ, Kuqa; LT, Luntai; MK, Makit; MF, Minfeng; PS, Pishan; PK, Poskam; QM, Qiemo; QR, Qira; SS, ShanShan; SF, Shufu; TX, Tumxuk; TK, Tuokexun; UP, Uqturpan; WS, Wensu; XY, Xayar; YP, Yopurga; XH, Xinhe; YQ, Yanqi; YA, Yarkand.

Each sampling site was examined for argasid ticks associated with livestock from January to December during a one-year period at approximately 14 or 15-day intervals. Twenty-four samples were performed during the one-year period for each sampling site. The sampling sites of Uqturpan, Tumxuk, Pishan, Qiemo, and Tuokexun counties were examined in 2013. The sampling sites of Xinhe, Artux, Awat, Hejing, Hetan, and kargilik counties were examined in 2014. The sampling sites of Luntai, Kuqa, Qira, Yopurga, Minfeng, and Xayar counties were examined in 2015. The sampling sites of Yanqi, Aral, Makit, Poskam, Shufu, Shanshan, Wensu and Yarkand counties were examined in 2016.

Above counties are primarily livestock husbandry regions. The livestock reared in these regions are mainly autochthonous. The vast majorities (approximately 95%) of the sheep are Kazakh, Chinese Merino, Hu, and Altay breeds; the majority of the cattle are Xinjiang Brown, Holstein and Kazakh breeds.

Adult argasid ticks infesting animals were collected from body surface of livestock. Summary information regarding all of the collected specimens, including their location, host, number of ticks collected and the date of collection, was recorded (Table 1). Tick sampling was performed on the entire body (head, neck, feet, chest, shoulders, axilla, crotch, udder, abdomen, thorax, rib area, tail, perianal region and vulva) of each animal, including sheep and cattle on 12 farms of 10 counties. The collected ticks were kept alive until they were transferred to the laboratory. These ticks were counted, and identified to species by morphology according to standard morphological keys, including dorsal view and dorsal integument, and corroborated by deriving sequences for mitochondrial 16S ribosomal Ribonucleic Acid (rRNA) and 12S rRNA [1417]. Ticks were grouped according to location/host of collection, date of collection, gender and species. All specimens are preserved in 70% ethanol. All of the livestock checked for ticks were grazed in the traditional manner, and there was no evidence that chemical acaricides were used prior to the tick sampling.

Table 1. The counts of each argasid species collected at the sampling sites around Tarim Basin between 2013 and 2016.

No. group of specimens Hosts(No.) Ornithodoros lahorensis (♂/♀) Argas japonicus (♂/♀) Collecting date Counties
1 Cattle (2) 42(11/31) / Apr. 2016 Aral (AL)
2 Sheep (5) 263(162/101) / Mar. 2016 Makit (MK)
3 Sheep (5) 300(179/121) / Feb- Mar. 2016 Poskam (PK)
4 Sheep (2) 239(230/9) / Feb- Mar. 2016 Shufu (SF)
5 Sheep (7) 660(409/251) / Feb- Mar. 2016 Shanshan (SS)
6 Cattle (3) 594(0/594) / Feb- Mar. 2016 Wensu-1 (WS)
7 Cattle (3) 214(118/96) / Mar-Apr. 2015 LunTai (LT)
8 Sheep (5) 747(510/237) / Feb-Apr. 2015 Yopurga (YP)
9 Sheep (2) 203(122/81) / Apr. 2013 Uqturpan (UP)
10 Sheep (2) 102(0/102) / Apr. 2013 Pishan (PS)
11 Cattle (2) / 109(0/109) Feb- Mar. 2016 Wensu-2 (WS-2)
12 Cattle (3) / 20(3/17) Feb- Mar. 2016 Wensu-3 (WS-3)
13 Cattle (3) / 336(271/65) Feb- Mar. 2016 Wensu-1 (WS-1)
Total Number of ticks of specific species 3364(1741/1623) 465(274/191)
Total Number of group of specimens of specific tick species 10 3
Total number of ticks 3829(2015/1814)
Total number of group of specimens 13

Nucleic acid extraction

Six representative tick specimens for each group of specimens were used for genomic DNA extraction. DNA templates were utilized for molecular identification of species and screening of pathogens.

Ethanol-preserved ticks were rinsed in distilled water and dried on filter paper. The total DNA was extracted using the DNeasy blood and tissue kit (Qiagen GmbH, Hilden, Germany) according to the manufacturer’s instructions. DNA was eluted in 80 μL elution buffer AE (provided with kit) and stored at -80°C until tested.

Molecular identification of tick species

Partial sequences of 16S rRNA and 12S rRNA were amplified by PCR using the primers listed in S1 Table. PCR amplifications were performed using GoTaq G2 Flexi DNA polymerase (Promega, WI, USA). The reaction master mix was prepared according to the manufacture’s protocol and the PCR conditions described were used as published. PCR reaction mixtures consisted of: 1 μL of upstream primer (100 pmol/μL), 1 μL of downstream primers (100 pmol/μL), 1 μL PCR Nucleotide Mix (10 mM of each deoxynucleoside triphosphate), 6 μL Mgcl2 Solution (25mM/μL), 10 μL 5×PCR buffer, 0.25 μL Taq DNA polymerase (1 U/μL), 1 μL sample DNA template (50–100 ng/μL) and 29.75 μL Nuclease-Free Water for each PCR in a 50 μL mixture reaction.

All PCR reactions were performed with positive controls and negative controls. Total DNA (mitochondrial DNA included) extracted from Hyalomma asiaticum asiaticum was used as a positive control. Sterile water was included in the DNA extraction procedure and was used as a negative control. PCR amplifications products were electrophoresed on 1% agarose gels, stained with SYBR Green Safe DNA Gel Stain (Invitrogen, CA, USA) and visualized under ultra-violet light. DNA bands of the correct size were purified and sequenced by BGI Tech Solutions Co., LTD (Liuhe, Beijing) (S1 Table).

Representative sequences were submitted to Genbank. The 12S rRNA sequences of argasid ticks acquired in this study have been deposited in GenBank under accession numbers MG651960 to MG651967 (Ornithodoros lahorensis) and MG668793 to MG668795 (Argas japonicus). The 16S rRNA sequences of argasid ticks acquired in this study have been deposited in GenBank under accession numbers MG651950 to MG651959 (Ornithodoros lahorensis), and MH782636 (Argas japonicus). The detailed information is provided in S2 Table.

Detection of DNA sequences of tick-associated pathogens

All primer sequences are provided in S1 Table and 78 argasid ticks of 13 groups of specimens were screened for tick-associated pathogens. Piroplasms were detected using the primer pair PIRO-A and PIRO-B, which targets 18S rRNA [18]. Borrelia spp. were detected using a primer pair that targeted the flagellin gene [19]. Anaplasma spp. were detected using two primer pairs that targeted major surface protein 4 gene (Msp4) and 16S rRNA [20, 21]. Rickettsia spp. was detected using a primer pairs targeting outer membrane protein B (ompB) protein [22, 23]. The summary of the pathogens found in the argasid ticks of southern Xinjiang is provided in Table 2.

Table 2. A summary of the pathogens found in the argasid ticks of southern Xinjiang.

Serial number Pathogens Tick species No. group of specimens Counties
1 Candidatus Anaplasma boleense Ornithodoros lahorensis 7 LunTai (LT)
2 Anaplasma ovis Ornithodoros lahorensis 9 Uqturpan (UP)
3 Candidatus Anaplasma boleense Argas japonicus 11 Wensu-2 (WS-2)
4 Rickettsia spp. of spotted fever group Argas japonicus 13 Wensu-1 (WS-1)

The master mix reagents were prepared according to the manufacture’s protocol and the PCR conditions described in previous studies were used. All PCR reactions were performed with positive controls and negative controls. Genomic DNA sequences of Babesia divergens, Rickettsia spp. (Spotted fever group), Anaplasma phagocytophilum, Borrelia garinii and Coxiella burnetii were used as positive controls. Sterile water was used as negative control. DNA bands of the correct size were purified and sequenced by BGI Tech Solutions (Liuhe, Beijing) Co., LTD. Representative sequences were submitted to Genbank (S2 Table).

Sequences analysis

DNA sequences were assembled using Lasergene version 12.1 (DNASTAR) and edited in MEGA 5.0 [24, 25]. Sequence alignments were conducted using ClustalW within MEGA 5.0, using default parameters (open gap penalty = 10.0, extend gap penalty = 5.0) before subsequently being checked by visual inspection. Genetic distances were calculated based on the K2P model for all pair-wise comparisons in the matrix using MEGA5.0. Bootstrapping (1000 replicates) was utilized to estimate variance. Pairwise deletion was used for gaps/missing data. Based on K2P distances, phylogenetic trees were constructed with the combined data sets of major tick genera and tick-associated pathogens using the Neighbour-joining method as previous described [15, 26, 27].

Results

Tick collection and morphological identification

A total of 3829 adult argasid ticks, from two species of different genera, were collected at 12 sampling sites in 10 counties around the Tarim Basin of southern Xinjiang, including Wensu, Aral, Pishan, Makit, Shanshan, Poskam, Shufu, Luntai, Yopurga, Uqturpan counties (Fig 1a). Of these speimens, 2015 specimens were male while 1814 specimens were female.

The morphological characters of body dorsal and ventral views, dorsal integument, capitulum and legs of argasid ticks were used to species identification. Two argasid species, Ornithodoros lahorensis and Argas japonicus, were determined by the unique combination of morphological characters [28, 29].

Beside the morphological diagnosis, the phylogenetic analyses using sequences of 16S rRNA (Fig 1b) and 12S rRNA (Fig 1c) were performed. DNA sequences analyses showed that 16S rRNA sequence derived from group of specimens No.11 shares 99% sequence identity with 16S rRNA for Argas japonicus (AB819156.1 and AB819157.1) while 16S rRNA sequences derived from group of specimens No.1 to 10 share 99% sequence identity with 16S rRNA for Ornithodoros lahorensis (KX530874.1). Based on sampling sites, hosts, dates of collection, gender and species, we obtained 13 groups of specimens (Table 1). Ornithodoros lahorensis (87.86%, 3364/3829) was collected more frequently and was the widespread argasid species in the Tarim Basin while Argas japonicus (12.14%, 465/3829) was only collected from 3 farms of Wensu county. Furthermore, the seasonal population dynamics of Ornithodoros lahorensis and Argas japonicus were provided in S1 Fig.

Detection of Rickettsia spp.

DNA sequence of ompB of emerging Rickettsia spp. of spotted fever group (SFG) was detected in Ar. japonicus tick of group of specimens No.13, which was collected from Wensu county (Fig 2a). DNA sequence analysis showed that the sequence shares 99% sequence identity with the ompB of Candidatus Rickettsia barbariae (MF002508.1).

Fig 2. Detection and analysis of Rickettsia spp. in argasid ticks from southern Xinjiang.

Fig 2

A. The sampling site of Rickettsia spp-positive tick is marked with red dot. B. Neighbour joining phylogenetic analysis based on partial ompB sequences of Rickettsia spp. Bootstrap values are indicated at the nodes. Scale bar indicates the degree of divergence represented by a given length of branch. The red dots indicate the sequences acquired in this study. SFG indicates the spotted fever group. TG indicates the typhus group. TRG indicates the transitional group of Rickettisa spp. Abbreviations: WS, Wensu.

A phylogenetic analysis based on ompB of the representative Rickettsia spp. is shown in Fig 2b. The Rickettsia sequence derived from group of specimens No.13 clusters within the clade including Rickettsia species of SFG such as Candidatus Rickettsia barbariae (MF002508.1 and KY069250.1), Rickettsia conorii (AE006914.1) and Rickettsia massiliae (AF123714.1).

Detection of Anaplasma spp.

DNA sequences of Anaplasma spp. were detected in 3 groups of specimens collected from LunTai, Uqturpan and Wensu counties (Fig 3a), composed of Or. lahorensis (group of specimens No.7, 9) and Ar. Japonicus (group of specimens No.11).

Fig 3. Detection and analysis of Anaplasma spp. in argasid ticks from southern Xinjiang.

Fig 3

A. The sampling sites of A. Boleense-positive ticks are marked with red dots and the sampling site of A. Ovis-positive tick is marked with blue dot. B. Neighbour joining phylogenetic analysis based on partial 16S rRNA sequences of Anaplasma spp. C. Neighbour joining phylogenetic analysis based on partial msp4 sequences of Anaplasma spp. Bootstrap values are indicated at the nodes. Scale bar indicates the degree of divergence represented by a given length of branch. The red and blue dots indicate the sequences acquired in this study. Abbreviations: UP, Uqturpan; WS, Wensu; LT, Luntai.

DNA sequence analysis of two amplicons derived from groups of specimens No.7 and 11 showed that they were identical to each other and share 99% sequence identity with 16S rRNA sequence of Candidatus Anaplasma boleense (KX987335.1). A phylogenetic tree based on 16S rRNA of the representative Ehrlichia/anaplasma spp. is shown in Fig 3b and both sequences acquired in this study cluster within the clade including Candidatus A. boleense. The Candidatus A. boleense associated tick specimens were identified as Or. lahorensis and Ar. japonicus. Or. lahorensis ticks were collected from Luntai county while Ar. japonicus ticks were collected from Wensu county. Above argasid ticks were removed from cattle.

The amplicon derived from group of specimens No.9 shared 99% sequence identity with msp4 of A. ovis (KY283958.1). The phylogenetic tree based on msp4 of the representative Anaplasma spp. is shown in Fig 3c and the sequence derived from group of specimens No. 9 clusters within the clade corresponding to A. ovis. The A. ovis associated tick specimens collected from Uqturpan county were identified as Or. lahorensis. Above Or. lahorensis ticks were removed from sheep.

Detection of piroplasms, Borrelia spp. and Coxiella burnetii

The 78 argasid ticks were tested for the presence of DNA sequences of piroplasms, Borrelia spp. and Coxiella burnetii. All samples were negative for these pathogens.

Discussion

As globally important arthropod vectors, tick infestations cause substantial blood loss from livestock and can transmit an extensive range of viral, bacterial and protozoan pathogens to vertebrate hosts [30, 31]. It has been reported that ixodid ticks and argasid ticks are widely distributed in Xinjiang and previous studies have focused on the ixodid ticks and associated tick-borne pathogens in this area [6, 7, 32]. However, little is known about argasid ticks and argasid tick-borne pathogens associated with the livestock sector and public health in Xinjiang.

In this study, two argasid tick species, Or. lahorensis and Ar. japonicus, were collected from livestock in southern Xinjiang. Only adult feeding argasid ticks were sampled. According to the seasonal population dynamics of argasid ticks (S1 Fig), Ornithodoros lahorensis ticks infesting livestock occurred from late February to early April while Argas japonicus infesting livestock occurred from February to March. Based on our research, these argasid ticks only occurred in spring rather than other seasons. We deduce that the seasonal argasid tick infestation of animals is mainly influenced by climatic factors such as temperature and humidity just as ixodid ticks. For the anatomical distribution on the animals, the majority of argasid ticks were collected from the abdomen, thorax and rib areas and the rest of ticks were collected from neck, crotch and udder areas. Several factors influence argasid tick preference for certain body areas, including greater blood flow, lower hair density and the animal’s inability to groom.

Or. lahorensis, collected from 10 counties, was the dominant argasid ticks infesting livestock in this area. Or. lahorensis is an important ectoparasite of livestock and wildlife in lowlands and mountains of many countries and regions including Tibet, Kashmir, and Southern former USSR to Saudi Arabia, Turkey, Iran, Greece, Bulgaria, and former Yugoslavia [33]. In the present study, we found that the geographical distribution of Or. lahorensis is nearly identical to the investigation conducted in Xinjiang three decades ago [34]. Or. lahorensis ticks were collected at sites in the northern and western rather than the southern and eastern parts of Tarim Basin. Moreover, the peak activity time of adult Or. lahorensis is also consistent with reports three decades ago. There is a substantial warming trend across Xinjiang province due to increased human activity and greenhouse gas emissions associated with animal production over the past 50 years [35]. Previous reports reveal that the most important factor to influence ticks may be host seeking tick activity periods and it has great effect on tick development rates and seasonal activity patterns [36]. We speculate that the stable herds in southern Xinjiang provide steady hosts for Or. lahorensis and host seeking activity of Or. lahorensis ticks do not change with warming environment during recent three decades.

Argas japonicus ticks were collected for the first time in Xinjiang province. The cattle, infested with Ar. japonicus, were born in Xinjiang and had never travelled outside the province. Argas japonicus was first collected from swallows and swallow nests in Japan and Korea [29]. Clinical investigations due to the cases of dermatitis caused by argasid tick infestation demonstrated that Ar. japonicus occurs in provinces of Northeastern China, including Jilin, Liaoning and Beijing [37]. These provinces are geographically close to Korea and Japan. The tranditional geographic range of Ar. japonicus seems to be restricted to the Northeastern Asia bordering the Pacific Ocean. This research confirms the presence of Ar. japonicus in Wensu county, which locates in the China-Kazakhstan-Kyrgyzstan border. The environment of central Asia is completely different from that of Northeastern Asia. It shows that Ar. japonicus may cover large areas as this species could adapt to sorts of environments. Argas japonicus is considered as a species mainly infesting wild birds and domestic poultry such as swallows and chickens and is found to occasionally attack humans. Our data expands the list of known natural hosts of Ar. japonicus ticks, adding cattle and sheep. In some farms of southern Xinjiang, the livestock are mixed cultured with poultry such as chickens and pigeons. We deduce that the poultry should be the original hosts for Ar. japonicus while the sheep and cattle are only occasional hosts. The livestock could be contracted by close contact cultured with tick-infested poultry. Ar. japonicus is of high medical significance as the tick-borne pathogens could be transmitted among birds, livestock and humans.

Ticks are considered to be one of the most important vectors of pathogens of medical and veterinary interest [3, 5]. Previous studies have demonstrated that Or. lahorensis is an important tick species infesting livestock and could transmit pathogens such as Rickettsia spp., Anaplasma spp. and piroplasms [33, 34]. Six representative ticks from each group of specimens were screened for pathogens and finally 78 of the 3829 ticks were examined in this study. The argasid ticks of the same species collected from one farm (the same group of specimens) are likely to belong to the similar population and the differences within one tick population in tick-borne pathogens would be limited. Therefore, there would be great chance to detect pathogens when six ticks per group of specimens were screened though the possibility of missed detection could not be avoided completely.

We detected DNA sequences of Candidatus A. boleense and A. ovis in Or. lahorensis ticks and this suggested the potential role for Or. lahorensis as a vector of Anaplasma spp. A case of human dermatitis as a result of a bite by Ar. japonicus was recorded in 1986, but no pathogens associated with Ar. japonicus was revealed until now [37]. For the first time, we described the Ar. japonicus associated pathogens and the DNA sequences of Rickettsia spp. of SPF and Candidatus A. boleense were detected. Tick borne Rickettsia spp. within SPF are associated with several human diseases such as Mediterranean spotted fever and Israeli spotted fever [38, 39]. Ar. japonicus could attack humans and Ar. japonicus associated Rickettsia spp. within SPF have important medical and biological significance.

The screening of pathogens was performed with fed argasid ticks and there was a possibility of acquiring the infection by blood meal from host carrier. In this study, pathogens were detected in argasid ticks collected from 4 farms. The herd sizes of these four farms were small and varied from 2 to 3. It was guaranteed that two or three specimens from the same host were screened. It was noticed that only one of the specimens from each group of specimens was positive for specific pathogen while other specimens were negative. If the origin of pathogens was from the carrier host blood meal, all the specimens from the same host should be positive for this pathogen. Based on the above phenomenon, we deduced that the origin of pathogens should be ticks themselves rather than host blood meal. However, the possibility of artificial tick-pathogens association could not be completely dismissed. Further research utilizing unfed argasid ticks is needed to accurately determine the role for argasid ticks as vectors of Anaplasma spp. and Rickettsia spp.

Conclusions

In this study, a total of 3829 adult argasid ticks, Or. lahorensis and Ar. japonicus, were collected at 12 sampling sites in 10 counties around Tarim basin. The results show that at present Or. lahorensis is the dominant argasid species infesting livestock in southern Xinjiang and Ar. japonicus was first recorded in Xinjiang of China. Besides, DNA sequences of some tick-associated pathogens such as Rickettsia spp. of SFG, Anaplasma spp. were detected in argasid ticks of southern Xinjiang. The potential role of Ar. Japonicus as the vector of pathogens was described for the first time.

Declarations

Permission was obtained from the farm owners before collection of the specimens.

Supporting information

S1 Fig. Seasonal population dynamics of argasid ticks associated with livestock during a one-year period (A, Ornithodoros lahorensis; B, Argas japonicus).

(TIF)

S1 Table. Primers used for identification of tick species and screening of pathogens.

(DOC)

S2 Table. Genbank Accession numbers for sequences of ticks and tick-borne pathogens.

(DOC)

Data Availability

The sequences of 12S rRNA of ticks obtained in this study were deposited in GenBank under accession numbers MG651960 to MG651967 and MG668793 to MG668795. The sequences of 16S rRNA of ticks obtained in this study were deposited in GenBank under accession numbers MG651950 to MG651959, and MH782636.

Funding Statement

This study was funded by National Natural Science Foundation of China (No. 31460655 to LZ and No. 31860698 to Y.H.L.), and the National key research and development program of China (No. 2016YFD0501100 to SOW), and the open project of Key Laboratory of Tarim Animal Husbandry Science and Technology, Xinjiang Production & Construction Corps (HS201501 to YHL, HS201801 to LJZ). The funders had no role in study design, data collection and analysis, decision to publish, or preparation of the manuscript.

References

  • 1.De lFJ, Estradapena A, Venzal JM, Kocan KM, Sonenshine DE. Overview: Ticks as vectors of pathogens that cause disease in humans and animals. Frontiers in Bioscience. 2008;13: 6938–6946. [DOI] [PubMed] [Google Scholar]
  • 2.Mediannikov O, Fenollar F. Looking in ticks for human bacterial pathogens. Microbial Pathogenesis. 2014;77: 142–148. 10.1016/j.micpath.2014.09.008 [DOI] [PubMed] [Google Scholar]
  • 3.Yu Z, Wang H, Wang T, Sun W, Yang X, Liu J. Tick-borne pathogens and the vector potential of ticks in China. Parasite Vector. 2015;8: 24. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 4.Dietrich M, Gomez-Diaz E, McCoy KD. Worldwide distribution and diversity of seabird ticks: implications for the ecology and epidemiology of tick-borne pathogens. Vector-Borne Zoonot. 2011;11: 453–470. [DOI] [PubMed] [Google Scholar]
  • 5.Wu X, Na R, Wei S, Zhu J, Peng H: Distribution of tick-borne diseases in China. Parasite Vector. 2013;6: 119. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 6.Wang Y, Mu L, Zhang K, Yang M, Zhang L, Du J, et al. : A broad-range survey of ticks from livestock in Northern Xinjiang: changes in tick distribution and the isolation of Borrelia burgdorferi sensu stricto. Parasite Vector. 2015;8: 449. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 7.Chen Z, Yang X, Bu F, Yang X, Yang X, Liu J. Ticks (acari: ixodoidea: argasidae, ixodidae) of China. Exp Appl Acarol. 2010;51: 393–404. 10.1007/s10493-010-9335-2 [DOI] [PubMed] [Google Scholar]
  • 8.Chen Y, Takeuchi K, Xu C, Chen Y, Xu Z. Regional climate change and its effects on river runoff in the Tarim Basin, China. Hydrol Process. 2006;20: 2207–2216. [Google Scholar]
  • 9.Feng Q, Jin H, Su Z. Desert evolution and climatic changes in the Tarim River basin since 12 ka BP. Science in China Series D. 1999;42: 101–112. [Google Scholar]
  • 10.Hao X, Li W, Deng H. The oasis effect and summer temperature rise in arid regions—case study in Tarim Basin. Sci Rep. 2016;6: 35418 10.1038/srep35418 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 11.Wei Q, Guo L, Wang A, Mu L, Zhang K, Chen C, et al. The first detection of Rickettsia aeschlimannii and Rickettsia massiliae in Rhipicephalus turanicus ticks, in northwest China. Parasite Vector. 2015;8: 631. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 12.Yang J, Li Y, Liu Z, Liu J, Niu Q, Ren Q, et al. Molecular detection and characterization of Anaplasma spp. in sheep and cattle from Xinjiang, northwest China. Parasite Vector. 2015;8: 108. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 13.Takada N, Masuzawa T, Ishiguro F, Fujita H, Kudeken M, Mitani H, et al. Lyme disease Borrelia spp. in ticks and rodents from northwestern China. Appl Environ Microb. 2001;67: 5161–5165. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 14.Deng G, Jiang Z. Economic insect fauna of China Fasc. 39. Acari: Ixodidae. Beijing: Science Press; 1991. [Google Scholar]
  • 15.Lv J, Wu S, Zhang Y, Chen Y, Feng C, Yuan X, et al. Assessment of four DNA fragments (COI, 16S rDNA, ITS2, 12S rDNA) for species identification of the Ixodida (Acari: Ixodida). Parasite Vector. 2014;7: 93. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 16.Karim S, Budachetri K, Mukherjee N, Williams J, Kausar A, Hassan MJ, et al. A study of ticks and tick-borne livestock pathogens in Pakistan. PLOS Neglect Trop D. 2017;11: e0005681. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 17.Kumsa B, Laroche M, Almeras L, Mediannikov O, Raoult D, Parola P. Morphological, molecular and MALDI-TOF mass spectrometry identification of ixodid tick species collected in Oromia, Ethiopia. Parasitol Res. 2016;115: 4199–4210. 10.1007/s00436-016-5197-9 [DOI] [PubMed] [Google Scholar]
  • 18.de Marco M, Hernandez-Triana LM, Phipps LP, Hansford K, Mitchell ES, Cull B, et al. Emergence of Babesia canis in southern England. Parasite vector. 2017;10: 241. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 19.Park HS, Lee JH, Jeong EJ, Koh SE, Park TK, Jang WJ, et al. Evaluation of groEL gene analysis for identification of Borrelia burgdorferi sensu lato. J Clin Microbiol. 2004;42: 1270–1273. 10.1128/JCM.42.3.1270-1273.2004 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 20.de la Fuente J, Atkinson MW, Naranjo V, Fernandez de Mera IG, Mangold AJ, Keating KA, et al. Sequence analysis of the msp4 gene of Anaplasma ovis strains. Vet Microbiol. 2007;119: 375–381. 10.1016/j.vetmic.2006.09.011 [DOI] [PubMed] [Google Scholar]
  • 21.Kawahara M, Rikihisa Y, Lin Q, Isogai E, Tahara K, Itagaki A, et al. Novel genetic variants of Anaplasma phagocytophilum, Anaplasma bovis, Anaplasma centrale, and a novel Ehrlichia sp. in wild deer and ticks on two major islands in Japan. Appl environ microb.2006;72: 1102–1109. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 22.Guo Y. Established detection methods of Q fever and North—Asian fever and investigation epidemic in northeast and Inner Mongolia. Thesis, Jilin Agricultural University. 2013.
  • 23.Anstead CA, Chilton NB. A novel Rickettsia species detected in Vole Ticks (Ixodes angustus) from Western Canada. Appl environ microb. 2013;79: 7583–7589. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 24.Burland TG. DNASTAR’s Lasergene sequence analysis software. Methods in molecular biology. 2000;132: 71–91. [DOI] [PubMed] [Google Scholar]
  • 25.Tamura K, Peterson D, Peterson N, Stecher G, Nei M, Kumar S. MEGA5: molecular evolutionary genetics analysis using maximum likelihood, evolutionary distance, and maximum parsimony methods. Mol Biol Evol. 2011;28: 2731–2739. 10.1093/molbev/msr121 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 26.Zhao S, Li H, Yin X, Liu Z, Chen C, Wang Y. First detection of Candidatus Rickettsia barbariae in the flea Vermipsylla alakurt from north-western China. Parasite vector. 2016;9: 325. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 27.Tian Z, Liu G, Shen H, Xie J, Luo J, Tian M. First report on the occurrence of Rickettsia slovaca and Rickettsia raoultii in Dermacentor silvarum in China. Parasite vector. 2012;5: 19. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 28.Deng G. Economic insect fauna of China Fasc. 15. Acari: Ixodidea. Beijing: Science Press; 1978. [Google Scholar]
  • 29.Yamaguti N, Clifford CM, Tipton VJ. Argas (Argas) japonicus, new species, associated with swallows in Japan and Korea. (Ixodoidea Argasidae). J Med Entomol. 1968;5: 453–459. [DOI] [PubMed] [Google Scholar]
  • 30.Chen M, Fan MY, Bi DZ, Zhang JZ, Huang YP. Detection of Rickettsia sibirica in ticks and small mammals collected in three different regions of China. Acta Virol. 1998;42: 61–64. [PubMed] [Google Scholar]
  • 31.Abdullah S, Helps C, Tasker S, Newbury H, Wall R. Ticks infesting domestic dogs in the UK: a large-scale surveillance programme. Parasite vector. 2016;9: 391. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 32.Fan MY, Wang JG, Jiang YX, Zong DG, Lenz B, Walker DH. Isolation of a spotted fever group rickettsia from a patient and related ecologic investigations in Xinjiang Uygur Autonomous Region of China. J Clin Microbiol. 1987;25: 628–632. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 33.Tavassoli M, Malekifard F, Soleimanzadeh A, Pourseyed SH, Bernousi I, Mardani K. Susceptibility of different life stages of Ornithodoros lahorensis to entomopathogenic fungi Metarhizium anisopliae and Beauveria bassiana. Parasitology Res. 2012;111: 1779–1783. [DOI] [PubMed] [Google Scholar]
  • 34.Yu X, Ye R, Gong Z. Ticks fauna of Xinjiang. Urumqi: Xinjiang Science Technology Hygiene Publishing House; 1997. [Google Scholar]
  • 35.Wu ZT, Zhang HJ, Krause CM, Cobb NS. Climate change and human activities: a case study in Xinjiang, China. Climatic Change. 2010;99: 457–472. [Google Scholar]
  • 36.Gray JS, Dautel H, Estrada-Pena A, Kahl O, Lindgren E. Effects of climate change on ticks and tick-borne diseases in europe. Interdisciplinary perspectives on infectious diseases. 2009;2009: 593232 10.1155/2009/593232 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 37.Li WX, Du XJ, Zhong D. Investigation on human dermatitis caused by Argas japonicasin bedroom. Chinese Journal of parasitology and parasitic diseases. 1986;4: 77. [Google Scholar]
  • 38.Parola P, Paddock CD, Raoult D. Tick-borne rickettsioses around the world: emerging diseases challenging old concepts. Clin Microbiol Rev. 2005;18: 719–756. 10.1128/CMR.18.4.719-756.2005 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 39.Parola P, Rovery C, Rolain JM, Brouqui P, Davoust B, Raoult D. Rickettsia slovaca and R. raoultii in tick-borne Rickettsioses. Emerg Infect Dis. 2009;15: 1105–1108. 10.3201/eid1507.081449 [DOI] [PMC free article] [PubMed] [Google Scholar]

Associated Data

This section collects any data citations, data availability statements, or supplementary materials included in this article.

Supplementary Materials

S1 Fig. Seasonal population dynamics of argasid ticks associated with livestock during a one-year period (A, Ornithodoros lahorensis; B, Argas japonicus).

(TIF)

S1 Table. Primers used for identification of tick species and screening of pathogens.

(DOC)

S2 Table. Genbank Accession numbers for sequences of ticks and tick-borne pathogens.

(DOC)

Data Availability Statement

The sequences of 12S rRNA of ticks obtained in this study were deposited in GenBank under accession numbers MG651960 to MG651967 and MG668793 to MG668795. The sequences of 16S rRNA of ticks obtained in this study were deposited in GenBank under accession numbers MG651950 to MG651959, and MH782636.


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