Warning: mkdir(): Permission denied in /home/virtual/lib/view_data.php on line 81

Warning: fopen(upload/ip_log/ip_log_2024-12.txt): failed to open stream: No such file or directory in /home/virtual/lib/view_data.php on line 83

Warning: fwrite() expects parameter 1 to be resource, boolean given in /home/virtual/lib/view_data.php on line 84
Epidemiological Investigation of Tick Species from Near Domestic Animal Farms and Cattle, Goat, and Wild Boar in Korea

Epidemiological Investigation of Tick Species from Near Domestic Animal Farms and Cattle, Goat, and Wild Boar in Korea

Article information

Korean J Parasito. 2019;57(3):319-324
Publication date (electronic) : 2019 June 30
doi : https://doi.org/10.3347/kjp.2019.57.3.319
1Laboratory of Veterinary Internal Medicine, BK21 PLUS Program for Creative Veterinary Science Research, Research Institute for Veterinary Science and College of Veterinary Medicine, Seoul National University, Seoul 08826, Korea
2Laboratory of Zoo and Wildlife Medicine, College of Veterinary Medicine, Seoul National University, Seoul 08826, Korea
*Corresponding author (jschae@snu.ac.kr)
Received 2018 August 21; Revised 2019 April 7; Accepted 2019 April 9.

Abstract

This study aimed to investigate the tick species and give background for tick-borne investigations in Korea. Ticks were collected from the area within 2 km radius of the 4 domestic animal farms, where they were located in mountainous areas and raising animals on pasture, and from animal bodies in 2014 and 2015. In total, 7,973 nymphal and adult ticks were collected from the farms - 7,758 Haemaphysalis longicornis, 198 Haemaphysalis flava, and 17 Ixodes nipponensis, and 1,763 were collected from animals - 729 H. longicornis from cattle; 569 H. longicornis from goats; and 297 H. longicornis, 118 H. flava, 1 I. nipponensis, and 49 Amblyomma testudinarium from wild boars. As more species of ticks were collected from wild boars than domesticated animals and their habitats, various animal hosts should be considered while investigating tick species.

Keywords: Tick; distribution; animal

Ticks are external parasites that suck blood from several animal species and also important vectors for various pathogens [1]. There are many genera of hard ticks in the world including Ixodes, Amblyomma, Haemaphysalis, Boophilus, Rhipicephalus, Dermacentor, and Anocentor. For various reasons, the distribution of ticks has been continuously investigated worldwide. The majority of ixodid ticks in China are from the genera Haemaphysalis (44 species) and Ixodes (24 species) [2]. Nationwide surveys in mainland Portugal listed 20 tick species [3] and more than 30 tick species, including soft ticks, were collected nationwide in Turkey [4]. In Iran, Boophilus, Dermacentor, Haemaphysalis, Hyalomma, Ixodes, and Rhipicephalus were isolated from approximately 1,500 sheep, 1,200 goats, and 500 cattle of 12 herds [5]. In addition, 25,566 ticks from 9 species of domesticated animals and 1,385 ticks from 20 animal species were collected in Sri Lanka [6].

In Korea, concerns related to ticks and tick-borne pathogens have been increasing and many studies on tick population and tick-borne diseases were conducted. Especially, tick surveillance studies related to host species (small mammals, migratory birds, wild boars, etc.) [79] or provinces [10,11], and tick-borne pathogens including Anaplasma spp., Bartonella spp., Borrelia spp., and a newly emerging pathogen called severe fever with thrombocytopenia syndrome virus, were conducted [8,12].

Given that the current climate is in constant change in Korea as well as in other countries, there may be changes in the habitats of existing organisms and the influx of new species [1315]. As tick distribution can be influenced by many factors, including local host populations [16], the host population should be considered while surveying tick population. The current study aimed to investigate the distribution of ticks, by collecting them from near animal farms and animals located throughout Korea.

Ticks were collected from 9 provinces in Korea (Gangwon-do, Gyeonggi-do, Chungcheongbuk-do, Chungcheongnam-do, Jeollabuk-do, Jeollanam-do, Gyeongsangbuk-do, Gyeongsangnam-do, and Jeju-do) from June to November in 2014 and March to November in 2015. To locate animal farms in mountain areas, we conducted an internet search and obtained information from Korean Ministry of Agriculture and Forestry, and working local veterinarians. After contacting farm owners, we obtained informed consents to investigate their farms and nearby areas. In total, 78 farms (29 cattle, 9 chicken, 27 goat, and 14 pig farms) that were in the mountainous areas and allowed their animals to graze were selected for investigation. The farms investigated in this study did not overlap. The areas around the farms, where ticks could live, were investigated, and the marginal areas were defined within a radius of 2 km using GPS system. Among the various farms, the defined areas of investigation were almost consistent, comprising of vegetation and some grasses less than 0.5 m in height. Ticks were collected from the fields using the flagging method (flags were made using a wooden stick attached to a 1×1 m white flannel cloth). Only nymphal and adult ticks were collected. Collected ticks were stored in a 15 ml centrifuge tube, with a grass leaf to maintain the humidity, and transported to the laboratory. The ticks were stored at 4°C until identification.

Nymphal and adult ticks were collected from restrained (cattle and goat) or captured (wild boar) animals using fine forceps. For animal welfare and ethical issues, tick investigation was performed while animals were restrained for their health checkup. Wild boars were captured and hunted following the guidelines for the capture of hazardous wild animals published by the Korean Ministry of Environment with the help of the Korean Wildlife Management Association. In the guidelines for the capture of hazardous wild animals performed by Korean Ministry of Environment, the Korean Wildlife Management Association might carry out the guidelines to adjust the number of wild boars by hunting. Collected ticks from each animal were stored at 4°C in a 15 ml centrifuge tube with a grass leaf and transported to the laboratory.

The species and developmental stage of all collected ticks were identified using a stereo microscope (SZH10, Olympus, Japan), following identification standards [21]. Each identified tick was stored at −20°C in a 2 ml microcentrifuge tube for further study.

In total, 7,973 nymphal and adult ticks (2,215 in 2014; 5,758 in 2015) belonging to 2 genera and 3 species were collected from the areas around the farms. Among the tick species, 7,758 (97.3%) were Haemaphysalis longicornis (2,072 in 2014; 5,686 in 2015; 496 adult males [243 in 2014; 253 in 2015], 845 adult females [333 in 2014, 512 in 2015], and 6,417 nymphs [1,496 in 2014; 4,921 in 2015]). Of the remaining ticks, 198 (2.5%) were Haemaphysalis flava (143 in 2014; 55 in 2015; 38 adult males [33 in 2014; 5 in 2015], 25 adult females [21 in 2014; 4 in 2015], and 135 nymphs [89 in 2014; 46 in 2015]), and 17 (0.2%) were Ixodes nipponensis (none in 2014; 17 in 2015; 2 adult males, 7 adult females, and 8 nymphs).

For each province, 1,128 ticks from Gangwon-do (1,093 H. longicornis [30 adult males, 49 adult females, and 1,014 nymphs], 31 H. flava [1 adult male, 2 adult females, and 28 nymphs], and 4 I. nipponensis [2 adult females, and 2 nymphs]), 1,171 ticks from Gyeonggi-do (1,168 H. longicornis [36 adult males, 32 adult females, and 1,100 nymphs], and 3 H. flava nymphs), 268 ticks from Chungcheongbuk-do (263 H. longicornis [23 adult males, 51 adult females, and 189 nymphs], and 5 H. flava [1 adult male, and 4 nymphs]), 532 ticks from Chungcheongnam-do (511 H. longicornis [55 adult males, 94 adult females, and 362 nymphs], 17 H. flava [9 adult males, 2 adult females, and 6 nymphs], and 4 I. nipponensis [2 adult males, and 2 adult females]), 1,061 ticks from Gyeongsangbuk-do (1,061 H. longicornis [12 adult males, 56 adult females, and 993 nymphs]), 818 ticks from Gyeongsangnam-do (796 H. longicornis [59 adult males, 80 adult females, and 657 nymphs], 21 H. flava [6 adult females, and 15 nymphs], and 1 I. nipponensis nymph), 1,075 ticks from Jeollabuk-do (1,032 H. longicornis [15 adult males, 42 adult females, and 975 nymphs], 35 H. flava [4 adult males, 5 adult females, and 26 nymphs], and 8 I. nipponensis [3 adult females, and 5 nymphs]), 595 ticks from Jeollanam-do (548 H. longicornis [23 adult males, 35 adult females, and 490 nymphs], and 47 H. flava [11 adult males, 8 adult females, and 28 nymphs]), and 1,325 ticks from Jeju-do (1,286 H. longicornis [243 adult males, 406 adult females, and 637 nymphs], and 39 H. flava [12 adult males, 2 adult females, and 25 nymphs]) were collected (Fig. 1).

Fig. 1

A map on distribution of ticks around the farms of 4 kind animals in provinces. Circular graph depicts species and number of ticks in the province.

From the animals, 1,763 ticks were collected (1,084 in 2014; 679 in 2015) belonging to 3 genera and 4 species; 729 (209 in 2014; 520 in 2015; 41.3%) were from cattle, 569 (569 in 2014; none in 2015; 32.3%) were from goats, and 465 (306 in 2014; 159 in 2015; 26.3%) were from wild boars (Table 1). From cattle, 729 H. longicornis were collected (78 adult males [49 in 2014, 29 in 2015], 649 adult females [159 in 2014, 490 in 2015] and 2 nymphs [1 in 2014, 1 in 2015]). From goats, 569 H. longicornis were collected (369 adult males, 162 adult females, and 38 nymphs). From wild boars, 297 H. longicornis (44 adult males [31 in 2014; 13 in 2015], 185 adult females [114 in 2014; 71 in 2015], and 68 nymphs [all in 2014]; 63.9%), 118 H. flava (94 adult males [48 in 2014; 46 in 2015], and 24 adult females [9 in 2014; 15 in 2015]; 25.4%), 1 I. nipponensis (1 adult male in 2014; 0.2%), and 49 Amblyomma testudinarium (30 adult males [22 in 2014; 8 in 2015], and 19 adult females [13 in 2014; 6 in 2015]; 10.5%) were collected.

Tick species collected from cattle, goats and wild boars in 2014 and 2015

In this study, we investigated the distribution of tick species and numbers from all provinces of Korea related to animal hosts. Given that once the larvae hatch, they do not move over a wide range, a large number of larvae can be collected in one flagging, which may skew the results of the overall distribution. Therefore, our collection was limited to the adult and nymph stages. Our results showed that near grazing animal farms, H. longicornis was the most commonly found tick species, followed by H. flava and I. nipponensis. These results are similar to those of previous studies on ticks collected from the environment in Korea [17]. Haemaphysalis and Ixodes are known as typical forest ticks, which have a passive ambush strategy of host seeking [18]. As dragging and flagging method, conducted in the areas around farm in this study, is known as the efficient method for surveying questing ticks, it is natural that only abundant Haemaphysalis spp. and Ixodes spp. were collected near animal farms.

By region, the highest number of ticks was collected in Jeju-do. Different from other provinces, Jeju-do has a subtropical climate, plenty of grasslands and pasturing cow and goat farms. Therefore, their distribution was much higher in the Jeju-do province than other provinces in Korea. Moreover, 3 species were collected in Gangwon-do, Chungcheongnam-do, Gyeongsangnam-do, and Jeollabuk-do, but 2 species were collected in Gyeonggi-do, Chungcheongbuk-do, Jeollanam-do, and Jeju-do, and only 1 species was collected in Gyeongsangbuk-do. However, it is difficult to determine the underlying factor for these differences between the regions.

From animals, adult ticks were collected in larger numbers than nymphs, which is contradictory to the results of tick collected from farms. This might be because most of the nymphs are known to bite small/medium-sized animals and are also difficult to see when covered by animal hair, as they are relatively smaller than adult ticks.

From the cattle and goats, only H. longicornis was collected. However, from the wild boars, 4 species (H. longicornis, H. flava, I. nipponensis, A. testudinarium) were collected, which have been previously reported from wild boar’s bodies and their habitats [7]. A. testudinarium was only found on wild boars in this research. This might be explained by different species of ticks having different habitat preferences depending on various factors such as host type, temperature, humidity, and soil condition [19]. Moreover, unlike grazing animals, which inevitably inhabit smaller areas, wild boars have a wide range of movement and are more likely to be exposed to many kinds of ticks.

To conclude, H. longicornis was the most common species collected from animals and the areas around the farms in this study. H. longicornis is the most dominant species of hard ticks in Korea, and almost all tick-borne diseases in Korea are known to originate from H. longicornis [7,20,21]. Moreover, studies on tick-borne diseases from many other kinds of animals have also detected H. longicornis [2224]. Apart from H. longicornis, other species were also collected from wild boars, and there might be more species of ticks than those detected in this study in Korea [17]. Thus, our study emphasizes that ticks may appear differently depending on the host, so ticks should be investigated considering the various animal hosts.

ACKNOWLEDGMENT

This research was supported by a fund (no. Z-1543085-2014-14-0102) from Research of Animal and Plant Quarantine Agency, Korea and was also partially supported by the Research Institute for Veterinary Science, Seoul National University. I would like to thanks to the Korean Wildlife Management Association for help with collecting ticks from wild boars.

Notes

CONFLICT OF INTEREST

The authors have no conflict of interest.

References

1. de la Fuente J, Estrada-Pena A, Venzal JM, Kocan KM, Sonenshine DE. Overview: ticks as vectors of pathogens that cause disease in humans and animals. Front Biosci 2008;13:6938–6946.
2. Yu Z, Wang H, Wang T, Sun W, Yang X, Liu J. Tick-borne pathogens and the vector potential of ticks in China. Parasit Vectors 2015;8:24.
3. Santos-Silva MM, Beati L, Santos AS, De Sousa R, Núncio MS, Melo P, Santos-Reis M, Fonseca C, Formoshinho P, Vilela C, Bacellar F. The hard-tick fauna of mainland Portugal (Acari: Ixodidae): an update on geographical distribution and known associations with hosts and pathogens. Exp Appl Acarol 2011;55:85–121.
4. Bursali A, Keskin A, Tekin S. A review of the ticks (Acari: Ixodida) of Turkey: species diversity, hosts and geographical distribution. Exp Appl Acarol 2012;57:91–104.
5. Rahbari S, Nabian S, Shayan P. Primary report on distribution of tick fauna in Iran. Parasitol Res 2007;101:175–177.
6. Liyanaarachchi DR, Rajakaruna RS, Dikkumbura AW, Rajapakse RP. Ticks infesting wild and domestic animals and humans of Sri Lanka with new host records. Acta Trop 2015;142:64–70.
7. Chae JB, Kang JG, Kim HC, Chong ST, Lee IY, Shin NS, Chae JS. Identification of tick species collected from wild boars and habitats of wild boars and domestic pigs in the Republic of Korea. Korean J Parasitol 2017;55:185–191.
8. Kang JG, Kim HC, Choi CY, Nam HY, Chae HY, Chong ST, Klein TA, Ko S, Chae JS. Molecular detection of Anaplasma, Bartonella, and Borrelia species in ticks collected from migratory birds from Hong-do Island, Republic of Korea. Vector Borne Zoonotic Dis 2013;13:215–225.
9. Kim CM, Yi YH, Yu DH, Lee MJ, Cho MR, Desai AR, Shringi S, Klein TA, Kim HC, Song JW, Baek LJ, Chong ST, O’guinn ML, Lee JS, Lee IY, Park JH, Foley J, Chae JS. Tick-borne rickettsial pathogens in ticks and small mammals in Korea. Appl Environ Microbiol 2006;72:5766–5776.
10. Chong ST, Kim HC, Lee IY, Kollars TM Jr, Sancho AR, Sames WJ, Chae JS, Klein TA. Seasonal distribution of ticks in four habitats near the demilitarized zone, Gyeonggi-do (Province), Republic of Korea. Korean J Parasitol 2013;51:319–325.
11. Kim HC, Chong ST, Sames WJ, Nunn PV, Wolf SP, Robbins RG, Klein TA. Tick surveillance of small mammals captured in Gyeonggi and Gangwon Provinces, Republic of Korea, 2004–2008. Syst Appl Acarol 2010;15:100–108.
12. Kim KH, Yi J, Kim G, Choi SJ, Jun KI, Kim NH, Choe PG, Kim NJ, Lee JK, Oh MD. Severe fever with thrombocytopenia syndrome, South Korea, 2012. Emerg Infect Dis 2013;19:1892–1894.
13. Berry PM, Dawson TP, Harrison PA, Pearson RG. Modelling potential impacts of climate change on the bioclimatic envelope of species in Britain and Ireland. Glob Ecol Biogeogr 2002;11:453–462.
14. Choi CY, Kang CW, Kim EM, Lee S, Moon KH, Oh MR, Yamauchi T, Yun YM. Ticks collected from migratory birds, including a new record of Haemaphysalis formosensis, on Jeju Island, Korea. Exp Appl Acarol 2014;62:557–566.
15. Forman S, Hungerford N, Yamakawa M, Yanase T, Tsai HJ, Joo YS, Yang DK, Nha JJ. Climate change impacts and risks for animal health in Asia. Rev Sci Tech 2008;27:581–597.
16. Léger E, Vourc’h G, Vial L, Chevillon C, McCoy KD. Changing distributions of ticks: causes and consequences. Exp Appl Acarol 2013;59:219–244.
17. Chong ST, Kim HC, Lee IY, Kollars TM Jr, Sancho AR, Sames WJ, Klein TA. Comparison of dragging and sweeping methods for collecting ticks and determining their seasonal distributions for various habitats, Gyeonggi Province, Republic of Korea. J Med Entomol 2013;50:611–618.
18. Uspensky I. Preliminary observations on specific adaptations of exophilic ixodid ticks to forests or open country habitats. Exp Appl Acarol 2002;28:147–154.
19. Trout Fryxell RT, Moore JE, Collins MD, Kwon Y, Jean-Philippe SR, Schaeffer SM, Odoi A, Kennedy M, Houston AE. Habitat and vegetation variables are not enough when predicting tick populations in the southeastern United States. PLoS One 2015;10:e0144092.
20. Yun SM, Lee YJ, Choi W, Kim HC, Chong ST, Chang KS, Coburn JM, Klein TA, Lee WJ. Molecular detection of severe fever with thrombocytopenia syndrome and tick-borne encephalitis viruses in ixodid ticks collected from vegetation, Republic of Korea, 2014. Ticks Tick Borne Dis 2014;7:970–978.
21. Yamaguti N, Tipton VJ, Keegan HL, Toshioka S. Ticks of Japan, Korea, and the Ryukyu islands. Brigham Young Univ Sci Bull Biol Ser 1971;15:1–226.
22. Doan HT, Noh JH, Choe SE, Yoo MS, Kim YH, Reddy KE, Van Quyen D, Nguyen LTK, Nguyen TTD, Kweon CH, Jung SC, Chang KY, Kang SW. Molecular detection and phylogenetic analysis of Anaplasma bovis from Haemaphysalis longicornis feeding on grazing cattle in Korea. Vet Parasitol 2013;196:478–481.
23. Seong G, Han YJ, Chae JB, Chae JS, Yu DH, Lee YS, Park J, Park BK, Yoo JG, Choi KS. Detection of Anaplasma sp. in Korean native goats (Capra aegagrus hircus) on Jeju Island, Korea. Korean J Parasitol 2015;53:765–769.
24. Lee SH, Yun SH, Choi E, Park YS, Lee SE, Cho GJ, Kwon OD, Kwak D. Serological detection of Borrelia burgdorferi among horses in Korea. Korean J Parasitol 2016;54:97–101.

Article information Continued

Fig. 1

A map on distribution of ticks around the farms of 4 kind animals in provinces. Circular graph depicts species and number of ticks in the province.

Table 1

Tick species collected from cattle, goats and wild boars in 2014 and 2015

Animals Tick species Developmental stages Number of ticks

2014 2015 Total
Cattle Haemaphysalis longicornis Adult male 49 29 78
Adult female 159 490 649
Nymph 1 1 2
Subtotal 209 520 729
Subtotal 209 520 729

Goat Haemaphysalis longicornis Adult male 369 0 369
Adult female 162 0 162
Nymph 38 0 38
Subtotal 569 0 569
Subtotal 569 0 569

Wild boar Haemaphysalis longicornis Adult male 31 13 44
Adult female 114 71 185
Nymph 68 0 68
Subtotal 213 84 297
Haemaphysalis flava Adult male 48 46 94
Adult female 9 15 24
Nymph 0 0 0
Subtotal 57 61 118
Ixodes nipponensis Adult male 1 0 1
Adult female 0 0 0
Nymph 0 0 0
Subtotal 1 0 1
Amblyomma testudinarium Adult male 22 8 30
Adult female 13 6 19
Nymph 0 0 0
Subtotal 35 14 49
Subtotal 306 159 465

Grand Total 1,084 679 1,763