INTRODUCTION
Centrocestus armatus (Digenea: Heterophyidae) is a small intestinal fluke bearing 42–48 circumoral spines, which mainly inhabits in the small intestines of birds and mammals. This fluke was first recovered from dogs, cats, rabbits, rats and mice experimentally fed with cyprinoid fish with
C. armatus metacercariae (CaMc) in Japan [
1]. Human infections were experimentally proven in Japan, and a natural human case was reported in the Republic of Korea (Korea) [
1,
2]. The freshwater snails,
Semisulcospira spp., are known to be the first intermediate hosts in Japan and Korea [
3,
4]. Various species of freshwater fish, including
Zacco platypus and
Z. temminckii, were reported as the second intermediate hosts in Japan and Korea [
5–
13]. As the natural definitive hosts of this fluke, the large egret,
Egretta alba modesta, and stray cat,
Felis catus, were recorded in Korea [
14–
17].
This species of heterophyid fluke is not clinically important unlike
Clonorchis sinensis and
Metagonimus spp. as fishborne zoonotic trematodes. And so the epidemiological study on the metacercarial infections in fish hosts has been rarely done in Korea [
6–
8,
10,
11]. In Korea, Chun [
6] described more than 11 species of digenetic trematode metacercariae (DTM) together with CaMc detected in 16 fish species from streams and ponds in adjacent areas of Nakdong-gang. Rhee et al. [
8] detected CaMc in 7 out of 32 fish species from Mangyeong-gang and they also found them in 5 out of 33 fish species from Dongjin-gang [
9]. In 1988, Hong et al. [
10] investigated the infection status of CaMc in 2 species of chub,
Z. platypus and
Z. temminckii, collected from 19 sites in 6 major rivers of Korea. Recently, Cho et al. [
12] reported the infection status of zoonotic trematode metacercariae including CaMc in fishes from the water systems in Gangwon-do. Sohn et al. [
13] surveyed the infection status of DTM in fishes from the water systems of Hantan-gang and Imjin-gang. However, most of previous studies were performed in limited areas except for Hong et al. [
10]. Even in Hong et al. [
10], only 2 species of chub,
Z. platypus and
Z. temminckii, collected from 19 sites were examined. Therefore, the present study was performed to estimate the endemisities of CaMc in the freshwater fishes nationwidely and moreover, to expand the fauna on the fish hosts of
C. armatus in Korea.
MATERIALS AND METHODS
Fish collected from water systems of Han-gang
Fishes from Hantan-gang in Cheorwon-gun (2010: 177 fishes in 15 spp.; 2012: 255 fishes in 18 spp.; 2013: 200 fishes in 23 spp.; 2014: 400 fishes in 15 spp.), Suipcheon in Yanggugun (2009: 196 fishes in 14 spp.), Hongcheon-gang in Hongcheon-gun (2010: 186 fishes in 14 spp.), Pyeongchang-gang in Pyeongchang-gun (2013: 230 fishes in 15 spp.), Dong-gang in Yeongwol-gun (2009: 251 fishes in 19 spp.), Seom-gang in Hoengseong-gun (2011: 184 fishes in 20 spp.) and Choyang-gang in Jeongseon-gun (2012: 196 fishes in 15 spp.), Gangwon-do, and Dalcheon in Goesan-gun (2011: 99 fishes in 12 spp.), Chungcheongbuk-do were examined.
Fish collected from water systems of Geum-gang
Fishes from Chogangcheon in Yeongdong-gun (2011: 132 fishes in 15 spp.), Chungcheongbuk-do, Cheonnae-gang in Geumsan-gun (2011: 140 fishes in 20 spp.; 2013: 146 fishes in 13 spp.; 2014: 161 fishes in 17 spp.; 2015: 79 fishes in 14 spp.), Yugucheon in Gongju-si (2013: 146 fishes in 11 spp.; 2015: 165 fishes in 11 spp.) and Jicheon in Cheongyang-gun (2014: 89 fishes in 13 spp.), Chungcheongnam-do, Jujacheon in Jinangun (2012: 208 fishes in 19 spp.) and Namdaecheon in Mujugun (2012: 123 fishes in 14 spp.), Jeollabuk-do were examined.
Fish collected from water systems of Mangyeong-gang and Dongjin-gang
Fishes from Soyangcheon in Wanju-gun (2012: 82 fishes in 8 spp.; 2013: 97 fishes in 12 spp.; 2014: 165 fishes in 9 spp.; 2015: 200 fishes in 12 spp.) and Jungeupcheon in Jungeup-si (2013: 88 fishes in 11 spp.), Jeollabuk-do were examined.
Fish collected from water systems of Yeongsan-gang and Tamjin-gang
Fishes from Hwangryong-gang in Jangseong-gun (2011: 107 fishes in 14 spp.), Jiseokcheon in Hwasun-gun (2011: 54 fishes in 8 spp.) and Naju-si (2013: 86 fishes in 9 spp.), Yeongamcheon in Yeongam-gun (2013: 45 fishes in 8 spp.;), Tamjingang in Jangheung-gun (2014: 167 fishes in 13 spp.; 2015: 243 fishes in 15 spp.; 2016: 302 fishes in 16 spp.; 2017: 420 fishes in 19 spp.) and Gangjin-gum (2014: 110 fishes in 12 spp.; 2017: 407 fishes in 15 spp.), Jeollanam-do were examined.
Fish collected from water systems of Seomjin-gang
Fishes from Osucheon in Imsil-gun (2011: 105 fishes in 10 spp.; 2012: 190 fishes in 10 spp.; 2013: 46 fishes in 5 spp.), Seomjin-gang in Sunchang-gun (2014: 69 fishes in 22 spp.; 2015: 241 fishes in 23 spp.) and Songdaecheon in Namwon-si (2012: 139 fishes in 12 spp.; 2013: 57 fishes in 7 spp.), Jeollabuk-do, Seomjin-gang in Gokseong-gun (2015: 146 fishes in 11 spp.) and in Gurye-gun (2014: 183 fishes in 21 spp.), Jeollanam-do, Hoengcheon (2014: 156 fishes in 13 spp.), Namsancheon (2015 and 2016: 234 fishes in 12 spp.) and Jugyocheon (2011: 54 fishes in 14 spp.) in Hadong-gun, Gyeongsangnam-do were examined.
Fish collected from water systems of Nakdong-gang in Gyeongsangnam-do
Fishes from Yangcheon in Sancheong-gun (2010: 350 fishes in 15 spp.; 2011: 201 fishes in 14 spp.; 2012: 221 fishes in 11 spp.; 2013: 644 fishes in 20 spp.; 2014: 291 fishes in 14 spp.; 2015: 183 fishes in 15 spp.; 2016: 253 fishes in 16 spp.; 2017: 408 fishes in 22 spp.), Jisucheon in Jinju-si (2014: 94 fishes in 11 spp.) and Hamancheon in Haman-gun (2014: 73 fishes in 9 spp.) were examined.
Fish collected from water systems of Nakdong-gang in Gyeongsangbuk-do
Fishes from Naeseongcheon in Bonghwa-gun (2008: 97 fishes in 12 spp.) and Yecheon-gun (2008: 131 fishes in 18 spp.; 2014: 103 fishes in 15 spp.), Nakdong-gang in Andong-si (2008: 118 fishes in 12 spp.; 2009: 56 fishes in 11 spp.), Yeong-gang in Mungyeong-si (2009: 108 fishes in 15 spp.), Banbyeoncheon in Yeongyang-gun (2008: 86 fishes in 12 spp.; 2015: 161 fishes in 12 spp.), Namdaecheon in Uiseong-gun (2009: 83 fishes in 9 spp.), Wicheon in Gunwi-gun (2008: 136 fishes in 16 spp.; 2011: 105 fishes in 13 spp.; 2013: 107 fishes in 12 spp.; 2014: 338 fishes in 24 spp.; 2015: 245 fishes in 19 spp.; 2016: 279 fishes in 24 spp.; 2017: 199 fishes in 17 spp.), Bukcheon in Sangju-si (2008: 45 fishes in 11 spp.), Hoecheon in Goryeonggun (2013: 165 fishes in 13 spp.), Nakdong-gang in Dalseonggun (2009: 63 fishes in 5 spp.) and Baekcheon in Seongju-gun (2009: 71 fishes in 12 spp.) were examined.
Fish collected from water systems in the east coast of Korea
Fishes from Namdaecheon in Yangyang-gun (2009: 174 fishes in 11 spp.; 2015: 140 fishes in 13 spp.), Osipcheon (2009: 155 fishes in 11 spp.; 2015: 143 fishes in 15 spp.) and Gagokcheon (2009: 109 fishes in 8 spp.) in Samcheok-si, Gangwon-do, Osipcheon in Yeongdeok-gun (2008: 104 fishes in 9 spp.; 2015: 122 fishes in 11 spp.), Wangpicheon in Uljin-gun (2015: 239 fishes in 13 spp.) and Hyeongsan-gang in Gyeongju-si (2015: 111 fishes in 12 spp.), Gyeongsangbuk-do, Cheokgwacheon (2015: 221 fishes in 10 spp.) and Taehwa-gang (2015: 89 fishes in 14 spp.) in Ulju-gun, Ulsan Metropolitan City were examined.
Examination methods
All collected fishes with ice were transferred to the laboratory of the Department of Parasitology and Tropical Medicine, Gyeongsang National University College of Medicine, Jinju, Korea. After the identification of fish species, they were individually ground with a mortar or grinder. Each ground fish meat was mixed with artificial gastric juice and the mixture was incubated at 36°C for 2 hr. The digested material was filtered through 1×1 mm of mesh, and washed with 0.85% saline untill the supernatant is clear. The sediment was carefully examined under a stereomicroscope. CaMc were separately collected by the general feature [
11] (
Fig. 1), counted and calculated for infection rates (%) and densities (No. of CaMc per fish infected) by fish species.
DISCUSSION
In the present study, we investigated the infection status with CaMc nationwidely in the freshwater fishes from the water systems of major rivers in Korea. Total 89 times in 50 sites (Han-gang: 11 times in 8 sites; Geum-gang: 10 times in 6 sites; Mangyeong-gang and Dongjin-gang: 5 times in 2 sites; Yeongsan-gang and Tamjin-gang: 10 times in 5 sites; Seomjin-gang: 13 times in 8 sites; Nakdong-gang: 29 times in 13 sites; streams in the east coast: 11 times in 8 sites) were surveyed. However, the data from the 12 times surveys performed in 10 sites (Hangang: 9 times in 7 sites; streams in the east coast: 3 times in 3 sites) were already reported in Cho et al. [
12]. At any rate, total 14,977 fish including 2,200
Z. platypus, 1,732
Z. temminckii and 297
O. uncirostris amurensis were examined in this study. The proportion of
Zacco spp. is more or less different by the surveyed sites (19.8–33.0%: 26.3% in average) and fish species (
Z. platypus: 9.2–22.1%;
Z. temminckii: 9.1–14.4%). These differences are due to the fish ecology in surveyed rivers.
The prevalences with CaMc were very high, 93.7–100% (97.1% in average), in
Zacco spp. from all surveyed sites. However, their densities were more or less different by the surveyed areas, and slightly higher in
Z. platypus (2,109 in average) than in
Z. temminckii (1,567). They were most high in Nakdong-gang in Gyeongsangnam-do, (4,201 in average), and followed by Geum-gang (2,343), Nakdong-gang in Gyeongsangbuk-do (1,623), Han-gang (1,564), Tamjin-gang (1,550), Yeongsan-gang (1,493), streams in the east coast (1,028), Seomjin-gang (488) and Mangyeong-gang and Dongjin-gang (170) (
Table 5). The prevalence in another species of rasborinid fish,
O. uncirostris amurensis, was 74.8% (222 out of 297 fish examined) and their density was 278 per fish infected. On the other hand, Hong et al. [
10] reported 86.8% and 78.5% prevalences in
Z. platypus (164 out of 189 fish examined) and
Z. temminckii (142 out of 181 fish examined), from 19 sites in the 6 major rivers of Korea. They also reported that densities with CaMc were more higher in
Z. platypus (224 in average) than in
Z. temminckii (131) [
10]. In Hong et al. [
10], the prevalences with CaMc in
Zacco spp. were more or less different by the surveyed rivers, 60.6–100% (82.7% in average), and their densities were most high in Nakdong-gang (347 in average) and followed by Seomjin-gang (120), Tamjin-gang (59), Yeongsan-gang (44), Han-gang (29) and Geum-gang (27). The endemicities of CaMc in
Zacco spp. in our study is much higher when we compared with those of Hong et al. [
10]. However, the infection trend by fish species, more higher endemicity in
Z. platypus than in
Z. temminckii, is the same in Hong et al. [
10]. Therefore, it appears that the endemicity of CaMc is currently much higher than in the past. It’s reason why is obscure, but we can only suppose with general knowledges in the Parasitology textbook. Recently, the ecological conditions for this heterophyid fluke will be much better than in the past in Korea.
Chun [
6] detected CaMc in 9 fish species, i.e.,
Z. platypus,
Z. temminckii,
P. altivelis, P. esocinus, P. parva, P. herzi, T. hakonensis, S. gracilis maejimae, S. japonicus coreanus, from the water systems of Nakdong-gang in Gyeongsangnam-do. Rhee et al. [
8] found CaMc in 7 fish species, i.e.,
Aphyocypris chinensis, C. auratus, C. splendidus, Microphysogobio yaluensis, Rhodeus uyekii, P. parva and
Z. platypus, from Mangyeong-gang and they also detected them in 5 fish species, i.e.,
Gnathopogon similis (=
Squalidus intermedius),
Pseudobagrus fulvidraco, P. parva, Rhodeus ocellatus ocellatus and
Z. platypus, from Dongjin-gang [
9]. Cho et al. [
12] reported 15 fish species, i.e.,
A. rhombeus, A. signifier, C. herzi, G. brevibarba, H. longirostris, H. mylodon, K. rotundicaudata, L. andersoni, M. longidorsalis, O. uncirostris amurensis,
Orthrias toni, P. esocinus, P. herzi, R. oxycephalus, and
T. hakonensis, from the water systems of Gangwon-do as the new second intermediate hosts of
C. armatus. Recently, Sohn et al. [
13] detected CaMc in 5 fish species,
Z. platypus,
Z. temminckii,
A. rhombeus, A. yamatsutae, and
A. macropterus from the water systems of Hantan-gang and Imjin-gang. In this study, we found CaMc in total 44 fish species including 3 rasborinid fish,
Z. platypus,
Z. temminckii and
O. uncirostris amurensis. Among them, 25 species were already reported in the previous studies [
6–
13]. Remain 19 species, i.e.,
A. springeri, A. gracilis, A. koreensis, A. majusculus, C. urotaenia, C. lutheri, C. kawamebari, G. strigatus, H. labeo, H. eigenmanni, M. salmoides, O. platycephala, O. masou masou, P. phoxinus, S. nigripinis morii, S. variegatus wakiyae and
S. asotus, are to be the new second intermediate hosts of
C. armatus in Korea. Accordingly, total 50 fish species (33 genera) are listed as the second intermediate hosts of
C. armatus in Korea.
In the genus
Centrocestus, the number of circumoral spines is considered to be the most reliable character in the species identification.
C. armatus, having 42–48 circumoral spines, was first described by Tanabe [
1] in Japan. Kobayashi [
18] classified members in the genus
Centrocestus into 4 groups on the basis of the number of circumoral spines. The group of
C. yokogawai has less than 30 circumoral spines (26–30),
C. formosanus has 32–40 ones,
C. armatus has 42–48 ones, and
C. polyspinosus has more than 50 ones (50–60) respectively. Among
Centrocestus species with 42–48 circumoral spines,
C. armatus is differentiated by characteristic morphological features include a small number of intrauterine eggs, the median location of the ovary, and the side by side location of the 2 testes [
2,
20]. On the other hand, Chai et al. [
21] proposed to consider 6 species, i.e.,
C. cuspidatus,
C. armatus,
C. formosanus, C. kurokawai, C. polyspinosus, and
C. asadai, in the genus
Centrocestus as the valid ones.
In Korea, 3 species of
Centrocestus fluke, i.e.,
C. armatus,
C. asadai and
C. formosanus, were reported in the literatures [
2,
4,
6,
22,
23]. Choi et al. [
22] described
C. asadai adults, which were recovered in the small intestines of mouse experimentally infected with the metacercariae from
Tribolodon taczanowskii. Cho et al. [
23] reported only the presence of
C. formosanus cercariae in Korea. They found these cercariae from
Semisulcospira libertina snails collected around the Jinyang-ho (ho means lake) in Gyeongsangnam-do, Korea. In regard to
C. armatus, a lot of findings on the intermediate and definitive hosts were revealed by many Korean workers [
2,
4,
6–
17]. Adult worms were recovered from a human, the large egret (
Egretta alba modesta) and stray cats (
Felis catus) naturally infected [
2,
14–
17]. Cercariae of this fluke were detected from
Semisulcospira snails collected in Judongcheon in Dalseong-gun, Gyeongsangbuk-do [
4]. Metacercarial infections were verified in the surveys of freshwater fish including
Z. platypus and
Z. temminckii [
5–
13]. Accordingly, we can know that
C. armatus is predominant species in Korea and the presence of another 2 species,
C. asadai and
C. formosanus, is obscure, so there are no reports about those flukes since the first records [
22,
23].
Conclusively, it is confirmed that rasborinid fish, Z. platypus, Z. temminckii, and O. uncirostris amurensis, are highly and heavily infected with CaMc and the densities with CaMc are more or less different by the surveyed areas and fish species. Additionally, 19 fish species are to be the new second intermediate hosts of C. armatus in Korea.