Abstract
The infection status of Clonorchis sinensis metacercariae (CsMc) was examined in freshwater fish from a highly prevalent site, Wicheon (a branch of Nakdong-gang), which is located in Gunwi-gun, Gyeongsangbuk-do, the Republic of Korea. Total 1,162 fish in 32 species were examined by the artificial digestion method through 6 years. CsMc were detected in 720 (67.5%) out of 1,067 fish (26 spp.) and their density was 610 per fish infected. In the susceptible gobioninid fish group, i.e., Pungtungia herzi, Squalidus gracilis majimae, Squalidus japonicus coreanus, Sarcocheilichthys variegatus wakiyae and Pseudorasbora parva, all of 323 fish were infected with an average of 1,310 CsMc. Total 23 (95.8%) gobioninid fish, i.e., Pseudogobio esocinus, Abbottina springeri, Hemibarbus longirostris, Microphysogobio koreensis, and Microphysogobio jeoni, were infected with 127 CsMc in average. In the acheilognathinid fish (bitterlings) group, the prevalence was 77.0%, and the density was 50 CsMc per fish infected. In the rasborinid fish (chubs) group, i.e., Zacco platypus, Zacco temminckii, Zacco koreanus, and Opsariichthys uncirostris amurensis, 147 (36.5%) out of 403 fish examined were infected with 15 CsMc in average. The susceptibility indices of CsMc were 412 in the overall positive fish group, 1,310 in the gobioninid group-1, 122 in the gobioninid group-2, 38.5 in the acheilognathinid group, and 5.5 in the rasborinid fish group. Conclusively, it was confirmed that CsMc are highly prevalent in fish from Wicheon, and their infection tendency varied according to the subfamily groups in Cyprinidae fish hosts.
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Key words: Clonorchis sinensis, metacercaria, susceptibility index, gobioninae, acheilognathinae, rasborinae, cyprinidae fish host, Wicheon
INTRODUCTION
Nowadays
Clonorchis sinensis infection is the most endemic parasitic disease in the Republic of Korea (=Korea). The prevalence of this endemic disease was 1.9%, and about 932,540 residents are estimated to be infected, which is the highest value among the prevalences in the nationwide survey on helminthic infections in Korea [
1]. The endemicity of clonorchiasis has maintained at relatively high levels in riverside areas of Korea [
2–
8]. Especially, in 1981, high prevalences were reported from the riverside residents in 7 major rivers, i.e., Nakdong-gang (gang=River) (40.2%), Yeongsan-gang (30.8%), Seomjin-gang (17.3%), Tamjin-gang (15.9%), Han-gang (15.7%), Geum-gang (12.0%), and Mangyeong-gang (8.0%) [
2]. Also in 2006 and 2007, the egg positive rates of
C. sinensis were surveyed from riverside residents in major 5 rivers of Korea [
5,
7]. Recently, Jeong et al. [
8] reported the prevalence of clonorchiasis from the residents of 5 major rivers as Nakdong-gang (11.7%), Seomjin-gang (9.9%), Geum-gang (6.5%), Yeongsan-gang (3.1%), and Han-gang (1.0%).
On the other hand, many Korean workers surveyed on freshwater fish, the infection sources of clonorchiasis, collected from various endemic riverside areas to estimate the endemicities of clonorchiasis. The results revealed that more than 49 fish species in 7 families have been reported as the second intermediate hosts of
C. sinensis [
9–
18]. Especially, Kim et al. [
12] examined 677 freshwater fish (21 spp.) collected from 34 localities to know the infection status of
C. sinensis metacercariae (CsMc). In addition, Cho et al. [
14] surveyed the infection status of CsMc in freshwater fish from 3 wide regions, which are tentatively divided by the latitudinal levels of the Korean peninsula. They examined total 136 freshwater fish (16 spp.) from Wicheon, the same area in this study, in 2008. Later, in 2014, Cho et al. [
16] investigated the prevalence of zoonotic trematode metacercariae in freshwater fish from Gangwon-do (Province), Korea. Recently, Sohn et al. [
17] surveyed the infection status of digenetic trematode metacercariae including
C. sinensis in freshwater fish from the water systems of Hantan-gang and Imjin-gang in northern regions of Korea. Sohn et al. [
18] also investigated the infection status with
C. sinensis metacercariae in fish from water systems of Seomjin-gang.
Wicheon is one of the branch streams of Nakdong-gang, which arises from a mountainous area of Goro-myeon (myeon =township) in Gunwi-gun (gun=county), flows via Gunwigun and Euiseong-gun, and unites with the main stream at Sangju-si (si=city), Gyeongsangbuk-do. The water ecosystem of this stream is more or less healthy but the ecological conditions for fish is not so good [
19]. However, it has been known that freshwater fish such as
Pungtungia herzi, Squalidus gracilis majimae, S. japonicus coreanus, and
Pseudogobio esocinus from this stream were heavily infected with CsMc [
14]. Therefore, for a period of 7 years, we focused on the infection status of CsMc in fish from a highly prevalent site of Wicheon, Gyeongsangbukdo, Korea, and analyzed the infection status of CsMc according to the subfamily groups of Cyprinidae fish hosts of
C. sinensis.
MATERIALS AND METHODS
Fish collection site and freshwater fish examined
We collected total 1,162 freshwater fish in 32 species in Wicheon (a stream of Nakdong-gang), which is located in Woobo-myeon, Gunwi-gun (latitude: 38.43268; longitude: 127.4375), Gyeongsangbuk-do, Korea. The numbers and species of fish examined in each year were as follows:
In 2011, total 105 freshwater fish in 13 species (no. of fish examined), i.e., Zacco platypus (49), Squalidus japonicus coreanus (10), Zacco temminckii (10), Squalidus gracilis majimae (8), Pungtungia herzi (5), Acheilognathus majusculus (5), Opsariichthys uncirostris amurensis (5), Carassius auratus (3), Pseudogobio esocinus (3), Acanthorhodeus macropterus (3), Sarcocheilichthys variegatus wakiyae (2), and Acheilognathus koreensis (1), Cobitis sinensis (1), were examined. In 2013, total 107 freshwater fish in 12 species, i.e., P. herzi (20), Z. platypus (20), Acheilognathus yamatsutae (16), Z. temminckii (15), A. koreensis (10), S. gracilis majimae (9), S. variegatus wakiyae (6), Coreoperca herzi (5), Abbottina springeri (2), C. sinensis (2), C. auratus (1), and Lepomis macrochirus (1), were examined.
In 2014, total 338 freshwater fish in 24 species, i.e., Z. platypus (60), Z. temminckii (50), P. herzi (47), A. koreensis (29), A. yamatsutae (25), S. japonicus coreanus (14), C. auratus (13), S. gracilis majimae (13), Acheilognathus rhombeus (11), S. variegatus wakiyae (11), A. majusculus (10), Micropterus salmoides (8), C. sinensis (8), C. herzi (7), P. esocinus (7), Misgurnus anguillicaudatus (6), Odontobutis platycephala (4), Pseudorasbora parva (4), L. macrochirus (4), Cobitis lutheri (3), Acheilognathus lanceolatus (2), Microphysogobio jeoni (1), and Microphysogobio koeensis (1), were examined. In 2015, total 245 freshwater fish in 19 species, i.e., Z. platypus (50), Z. temminckii (49), P. herzi (41), A. koreensis (29), A. yamatsutae (16), S. japonicus coreanus (15), S. gracilis majimae (11), C. auratus (10), A. rhombeus (7), A. springeri (4), S. variegatus wakiyae (3), O. uncirostris amurensis (3), P. parva (1), Rhynchocypris oxycephalus (1), A. macropterus (1), P. esocinus (1), C. herzi (1), M. koeensis (1), and A. lanceolatus (1), were examined.
In 2016, total 168 freshwater fish in 17 species, i.e., A. koreensis (35), Z. platypus (30), P. herzi (30), A. rhombeus (15), A. yamatsutae (15), Zacco koreanus (14), O. platycephala (6), C. auratus (5), S. japonicus coreanus (4), A. lanceolatus (3), C. herzi (3), P. esocinus (2), S. gracilis majimae (2), Hemibarbus longirostris (1), M. anguillicaudatus (1), Siniperca scherzeri (1), and M. koreensis (1), were examined. In 2017, total 199 freshwater fish in 17 species, i.e., Z. platypus (50), S. japonicus coreanus (31), A. yamatsutae (27), P. herzi (26), A. koreensis (26), Z. temminckii (10), P. parva (7), Acanthorhodeus gracilis (5), S. variegatus wakiyae (3), C. herzi (2), C. auratus (2), Z. koreanus (2), A. rhombeus (2), S. scherzeri (2), M. salmoides (2), C. lutheri (1), and Pseudobagrus fulvidraco (1), were examined.
Examination methods
All collected fish with ice were transferred to the laboratory of the Department of Parasitology and Tropical Medicine, Gyeongsang National University College of Medicine, Jinju, Korea. After 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 with 1×1 mm of mesh, and washed with 0.85% saline until the supernatant became clear. The sediment was carefully examined under a stereomicroscope. The metacercariae of
C. sinensis were separately collected by the general morphological feature [
13,
15], and they were counted to get hold of the infection rate and density by fish species. The susceptibility indices of CsMc were calculated by the formula, prevalence/100× mean metacercarial density per fish infected.
The gobioninid (Gobioninae) group-1 (323 fish) included P. herzi (169), S. gracilis majimae (43), S. japonicus coreanus (74), S. variegatus wakiyae (25), and P. parva (12). The gobioninid group-2 (24 fish) included P. esocinus (13), A. springeri (6), M. koreensis (3), M. jeoni (1), and H. longirostris (1). The acheilognathinid (Acheilognathinae) group (296 fish) included A. koreensis (130), A. yamatsutae (99), A. rhombeus (35), A. majusculus (15), A. macropterus (4), A. lanceolatus (6), and A. gracilis (7). The rasborinid (Rasborinae) group (403 fish) included Z. platypus (259), Z. temminckii (136), and O. uncirostris amurensis (8).
RESULTS
Infection status of CsMc in overall examined fish
CsMc were detected in 720 (62.0%) out of 1,162 fish in 32 species examined, and their average density was 610 per fish infected. The infection status by fish species and surveyed years is shown in
Table 1.
CsMc were detected in all (100%) of 323 fish examined, and their average density was 1,310 per fish infected. The densities were highest in 2014 (1,958), followed by 2015 (1,582), 2016 (1,211), 2013 (972), 2017 (685), and 2011 (516) (
Table 2). The infection status of CsMc by fish species, i.e.,
P. herzi, S. gracilis majimae, S. japonicus coreanus, S. variegatus wakiyae and
P. parva, is revealed in
Table 3.
CsMc were detected in 23 (95.8%) out of 24 fish examined, and their average density was 127 per fish infected. The infection status by fish species, i.e.,
P. esocinus, A. springeri, M. koreensis, M. jeoni and
H. longirostris, is shown in
Table 4.
CsMc were detected in 228 (77.0%) out of 296 fish examined, and their average density was 50 per fish infected. The densities were highest in 2015 (93), followed by 2016 (70), 2014 (43), 2011 (20), 2013 (5), and 2017 (5) (
Table 5). The infection status of CsMc by fish species, i.e.,
A. koreensis, A. yamatsutae, A. rhombeus, A. majusculus, A. macropteru, A. lanceolatus and
A. gracilis, is revealed in
Table 6.
CsMc were detected in 147 (36.5%) out of 403 fish examined, and their average density was 15 per fish infected. The densities were highest in 2015 (25), followed by 2017 (16), 2013 (15), 2014 (11), 2016 (10), and 2011 (7) (
Table 7). The infection status of CsMc by fish species, i.e.,
Z. platypus, Z. temminckii and
O. uncirostris amurensis, is shown in
Table 8.
The susceptibility indices of CsMc were 412 in the overall positive fish group; 1,310 in the gobioninid group-1, 122 in the gobioninid group-2, 38.5 in the acheilognathinid, and 5.5 in the rasborinid fish group (
Table 9).
DISCUSSION
By the present study, it was reconfirmed that CsMc are highly prevalent in fish from Wicheon, Gyeongsangbuk-do, Korea. Moreover, the infection status showed a certain tendency according to the subfamily groups of fish hosts, i.e., Gobioninae, Acheilognathinae, and Rasborinae, among the Cyprinidae. The prevalences were 100%, 79.7%, and 35.5%, and metacercarial densities were 1,310, 50, and 15 per fish infected in 3 fish groups, respectively. These findings also suggested that the endemicity of CsMc is closely related to the fish group, and this host-parasite relationship may originate from a long-lasting evolutional process.
The fish sampling is one of the important factors in metacercarial surveys for the epidemiology of fishborne zoonotic trematode infections. Total 1,162 fish in 32 species were collected through 6 years (2011 and 2013–2017) in the same site of Woobo-myeon in Gunwi-gun. Among them, the pale chub (259
Z. platypus: 22.2%) was the most dominant fish species like Sohn et al. [
18] in Seomjin-gang, followed by the striped shinner (169
P. herzi: 14.5%), dark chub and/or Korean chub (136
Z. temminckii and/or
Z. koreanus: 11.7%), oily bitterling (130
A. koreensis: 11.2%), Korean striped bitterling (99
A. yamatsutae: 8.5%), and short barbell gudgeon (74
S. japonicus coreanus: 6.4%). The number of fish examined was 867 (74.4%) in major 6 species and 298 (25.6%) in the remaining 26 species. The disproportion of the fish number examined was dependent upon the ecological conditions of each fish species, and moreover, we collected all fish only by the casting net in the daytime. If we used together with other methods for fish catching like a netting, we could have collected more various species of fish, including nocturnal ones.
Total 49 fish species (in 34 genera 7 families) have been reported as the second intermediate hosts of
C. sinensis in Korea [
9–
18]. In the present study, CsMc were found in 26 fish species, i.e.,
Abbottina springeri, Acanthorhodeus macropterus, A. gracilis, Acheilognathus koreensis, A. lanceolatus, A. majuscules, A. rhombeus, A. yamatsutae, Carassius auratus, Coreoperca herzi, Hemibarbus longirostris, Micropterus salmoides, Microphysogobio koeensis, M. jeoni, Misgurnus anguillicaudatus, Opsariichthys uncirostris, Pseudogobio esocinus, Pungtungia herzi, Pseudorasbora parva, Rhynchocypris oxycephalus, Sarcocheilichthys variegates wakiyae, Siniperca scherzeri, Squalidus gracilis majimae, S. japonicus coreanus, Zacco platypus, and
Z. temminckii. Among them, 2 fish species, i.e.,
M. salmoides (Centrachidae) and
M. anguillicaudatus (Cobitidae), are newly added in the list of the second intermediate hosts of
C. sinensis in Korea [
9–
18]. Accordingly, total 51 fish species in 9 families are listed as the second intermediate hosts of
C. sinensis in Korea.
The large mouth bass,
Micropterus salmoides, was imported from USA as an edible fish species in 1973. However, this fish is widely spread in the water systems of the whole country, and then became notorious as an agitating fish species of the ecosystem in Korea [
20]. In this study, we examined total 10
M. salmoides and detected 1 and 5 CsMc from 2 fish. Although the number of fish examined and metacercariae detected were not so many, the fact, infection with CsMc in foreign fish species, is highly important. Thus, we should pay attention to the fish species from foreign countries in the metacercarial survey for the fishborne zoonotic trematodes.
Fish species, i.e., Mandarin fish (
S. scherzeri), Korean aucha perch (
C. herzi), common carp (
Cyprinus carpio), and crusian carp (
C. auratus), edible in raw conditions practically act as the infection source of clonorchiasis in Korea. Fortunately, these fish species are less prevalent with CsMc. Total 3 (8.8%) out of 34
C. auratus were infected with total 3 CsMc, 2 (11.1%)
C. herzi was infected with a total of 4 CsMc, and only 1 (33.3%)
S. scherzeri was infected with 6 CsMc, respectively, even in such a highly endemic area, Wicheon. In a survey of the fish from Seomjin-gang, no CsMc was detected in 4 fish species, i.e.,
C. herzi (57),
C. auratus (42),
S. scherzeri (11), and
C. carpio (2), edible in raw conditions [
18].
The striped shinner,
P. herzi, is appropriate to be an index fish species to check the endemicity of
C. sinensis infection. This fish species broadly lives in the water systems of rivers in Korea and is highly susceptible to CsMc. In the present study, all of 169
P. herzi examined were infected with an average of 1,550 CsMc per fish. The prevalences of CsMc in this fish species were 80.4%, 72.5%, and 30.6%, and metacercarial densities were 15.2, 46.1, and 175.9 per fish infected in the upper, middle, and lower reaches of Seomjin-gang, respectively [
18]. The positive rates of CsMc were 6.2%, 31.8%, and 92.9%, and densities were 2.8, 214, and 409 per fish infected in
P. herzi from the northern, middle, and southern regions of the Korean peninsula, respectively [
14]. Especially, in this fish species from the streams of Nakdong-gang, i.e., Wicheon in Gunwigun, Banbyuncheon in Yeongyang-gun, Gyeongsangbuk-do, and Yangcheon in Sancheong-gun, Gyeongsangnam-do, the endemicities of CsMc were much higher like in this study [
14].
Conclusively, it has been confirmed that the endemicity of CsMc is much higher in fish from Wicheon, and a strong tendency was shown in the prevalence and intensity of CsMc according to the subfamily groups of fish, i.e., Gobioninae, Acheilognathinae, and Rasborinae, in the family Cyprinidae fish hosts. Among the highly susceptible gobioninid fish, P. herzi is recommended as a useful index fish to check the endemicity of clonorchiasis in a certain area of Korea.
Notes
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The authors have no conflicts of interest concerning the work reported in this paper.
ACKNOWLEDGMENTS
This study was supported by an anti-communicable diseases control program, 2014-E54002-00 (Investigation of fish-borne parasites and acquisition of their biological resources in the southern regions of Korea) and 2015-E54001-00 (Investigation of fish-borne parasites and acquisition of their biological resources in the eastern regions of Korea) of National Institute of Health (NIH), Korea Centers for Disease Control and Prevention (KCDCP), Korea. We thank Jung-A Kim and Hee-Joo Kim (Department of Parasitology and Tropical Medicine, Gyeongsang National University College of Medicine, Jinju, Korea), for their help in the examination of fish.
Table 1Infection status of Clonorchis sinensis metacercariae in fish from Wicheon (a stream of Nakdong-gang) in Gunwi-gun, Gyeongsangbuk-do
Table 1
|
Year and fish species |
No. of fish examined |
No. (%) of fish infected |
No. of metacercariae detected |
|
|
Total |
Range |
Average |
|
2011 |
|
Pungtungia herzi
|
5 |
5 (100) |
5,216 |
340–2,420 |
1,043 |
|
Squalidus japonicus coreanus
|
10 |
10 (100) |
818 |
13–295 |
82 |
|
Squalidus gracilis majimae
|
8 |
8 (100) |
4,960 |
9–1,035 |
620 |
|
Sarcocheilichthys variegatus
|
2 |
2 (100) |
1,901 |
2–12 |
951 |
|
Pseudogobio esocinus
|
3 |
3 (100) |
16 |
- |
5 |
|
Acheilognathus majusculus
|
5 |
1 (20.0) |
1 |
2 |
1 |
|
Acanthorhodeus macropterus
|
3 |
3 (100) |
91 |
87 |
30 |
|
Acheilognathus koreensis
|
1 |
1 (100) |
9 |
- |
9 |
|
Zacco platypus
|
49 |
18 (59.3) |
129 |
1–32 |
7 |
|
Subtotal |
86 |
51 (59.3) |
13,141 |
1–2,420 |
258 |
|
|
2013 |
|
Pungtungia herzi
|
20 |
20 (100) |
22,790 |
27–11,290 |
1,140 |
|
Squalidus gracilis majimae
|
9 |
9 (100) |
8,687 |
33–2,720 |
965 |
|
Sarcocheilichthys variegatus
|
6 |
6 (100) |
2,545 |
26–1,245 |
424 |
|
Abbottina springeri
|
2 |
2 (100) |
95 |
44–51 |
48 |
|
Acheilognathus koreensis
|
10 |
10 (100) |
58 |
1–14 |
6 |
|
Acheilognathus yamatsutae
|
16 |
6 (37.5) |
23 |
1–10 |
4 |
|
Zacco platypus
|
20 |
8 (40.0) |
129 |
1–70 |
16 |
|
Zacco temminckii
|
15 |
1 (6.7) |
2 |
- |
2 |
|
Subtotal |
98 |
62 (63.3) |
34,329 |
1–11,290 |
554 |
|
|
2014 |
|
Pungtungia herzi
|
47 |
47 (100) |
116,805 |
6–31,250 |
2,485 |
|
Squalidus japonicus coreanus
|
14 |
14 (100) |
25,291 |
140–8,460 |
1,807 |
|
Squalidus gracilis majimae
|
13 |
13 (100) |
20,285 |
132–6,130 |
1,560 |
|
Sarcocheilichthys variegatus
|
11 |
11 (100) |
8,936 |
13–2,730 |
812 |
|
Pseudorasbora parva
|
4 |
4 (100) |
2,911 |
483–1,180 |
728 |
|
Microphysogobio jeoni
|
1 |
1 (100) |
365 |
- |
365 |
|
Acheilognathus koreensis
|
29 |
29 (100) |
1,099 |
1–184 |
38 |
|
Microphysogobio koeensis
|
1 |
1 (100) |
12 |
- |
12 |
|
Acheilognathus yamatsutae
|
25 |
22 (88.0) |
560 |
1–136 |
26 |
|
Acheilognathus rhombeus
|
11 |
9 (81.8) |
782 |
1–290 |
87 |
|
Acheilognathus majusculus
|
10 |
2 (20.0) |
3 |
1–2 |
2 |
|
Acheilognathus lanceolatus
|
2 |
1 (50.0) |
283 |
- |
283 |
|
Zacco platypus
|
60 |
40 (66.7) |
447 |
1–66 |
11 |
|
Zacco temminckii
|
50 |
1 (2.0) |
1 |
- |
1 |
|
Carassius auratus
|
13 |
1 (7.7) |
1 |
- |
1 |
|
Micropterus salmoides
|
8 |
1 (12.5) |
1 |
- |
1 |
|
Coreoperca herzi
|
7 |
1 (14.3) |
3 |
- |
3 |
|
Misgurnus anguillicaudatus
|
6 |
2 (33.3) |
2 |
- |
1 |
|
Subtotal |
319 |
206 (64.6) |
178,007 |
1–31,250 |
864 |
|
|
2016 |
|
Pungtungia herzi
|
30 |
30 (100) |
36,686 |
28–9,870 |
1,223 |
|
Squalidus japonicus coreanus
|
4 |
4 (100) |
3,603 |
210–1,480 |
901 |
|
Squalidus gracilis majimae
|
2 |
2 (100) |
3,323 |
653–2,670 |
1,662 |
|
Pseudogobio esocinus
|
2 |
2 (100) |
540 |
36–504 |
270 |
|
Microphysogobio koreensis
|
1 |
1 (100) |
40 |
- |
40 |
|
Hemibarbus longirostris
|
1 |
1 (100) |
13 |
- |
13 |
|
Acheilognathus koreensis
|
35 |
34 (97.1) |
871 |
2–287 |
26 |
|
Acheilognathus rhombeus
|
15 |
15 (100) |
3,006 |
64–329 |
200 |
|
Acheilognathus yamatsutae
|
15 |
8 (53.3) |
25 |
1–9 |
3 |
|
Acheilognathus lanceolatus
|
3 |
3 (100) |
327 |
4–255 |
109 |
|
Zacco platypus
|
30 |
19 (63.3) |
192 |
1–30 |
10 |
|
Siniperca scherzeri
|
1 |
1 (100) |
6 |
- |
6 |
|
Subtotal |
139 |
120 (86.3) |
48,632 |
1–9,870 |
405 |
|
|
2017 |
|
Pungtungia herzi
|
26 |
26 (100) |
26,736 |
22–8,950 |
1,028 |
|
Squalidus japonicus coreanus
|
31 |
31 (100) |
13,161 |
4–2,750 |
425 |
|
Sarcocheilichthys variegatus
|
3 |
3 (100) |
759 |
156–352 |
253 |
|
Pseudorasbora parva
|
7 |
7 (100) |
5,260 |
365–2,225 |
751 |
|
Acheilognathus yamatsutae
|
27 |
15 (55.6) |
45 |
1–2,030 |
7 |
|
Acheilognathus koreensis
|
26 |
19 (73.1) |
129 |
1–30 |
5 |
|
Acanthorhodeus gracilis
|
5 |
5 (100) |
26 |
2–12 |
1 |
|
Acheilognathus rhombeus
|
2 |
1 (50.0) |
1 |
- |
16 |
|
Zacco platypus
|
50 |
21 (42.0) |
345 |
1–205 |
1 |
|
Coreoperca herzi
|
2 |
1 (50.0) |
1 |
- |
5 |
|
Micropterus salmoides
|
2 |
1 (50.0) |
5 |
- |
387 |
|
Subtotal |
181 |
120 (66.3) |
46,468 |
1–8,950 |
|
|
|
Total |
1,067 |
720 (67.5) |
439,439 |
1–31,250 |
610 |
Table 2Infection status of Clonorchis sinensis metacercariae in susceptible gobioninid fish from Wicheon in Gunwi-gun, Gyeongsangbuk-do
Table 2
|
Year examined |
No. of fish examined |
No. (%) of fish infected |
No. of metacercariae detected |
|
Total |
Range |
Average |
|
2011 |
25 |
25 (100) |
12,895 |
9–2,420 |
516 |
|
2013 |
35 |
35 (100) |
34,022 |
26–11,290 |
972 |
|
2014 |
89 |
89 (100) |
174,228 |
6–31,250 |
1,958 |
|
2015 |
71 |
71 (100) |
112,342 |
24–7,750 |
1,582 |
|
2016 |
36 |
36 (100) |
43,612 |
28–9,870 |
1,211 |
|
2017 |
67 |
67 (100) |
45,916 |
4–8,950 |
685 |
|
Total |
323 |
323 (100) |
423,015 |
4–31,250 |
1,310 |
Table 3Infection status of Clonorchis sinensis metacercariae by fish species in the gobioninid group-1
Table 3
|
Species of fish |
No. of fish examined |
No. (%) of fish infected |
No. of metacercariae detected |
|
Total |
Range |
Average |
|
Pungtungia herzi
|
169 |
169 (100) |
261,986 |
6–31,250 |
1,550 |
|
Squalidus japonicus coreanus
|
74 |
74 (100) |
64,037 |
4–8,460 |
865 |
|
Squalidus gracilis majimae
|
43 |
43 (100) |
71,510 |
9–7,680 |
1,663 |
|
Sarcocheilichthys variegatus
|
25 |
25 (100) |
15,773 |
13–2,730 |
631 |
|
Pseudorasbora parva
|
12 |
12 (100) |
9,709 |
365–2,225 |
809 |
|
Total |
323 |
323 (100) |
423,015 |
4–31,250 |
1,310 |
Table 4Infection status of Clonorchis sinensis metacercariae by fish species in the gobioninid group-2
Table 4
|
Species of fish |
No. of fish examined |
No. (%) of fish infected |
No. of metacercariae detected |
|
Total |
Range |
Average |
|
Pseudogobio esocinus
|
13 |
12 (92.3) |
2,101 |
1–1,325 |
175 |
|
Abbottina springeri
|
6 |
6 (100) |
250 |
10–80 |
42 |
|
Hemibarbus longirostris
|
1 |
1 (100) |
13 |
- |
13 |
|
Microphysogobio koreensis
|
3 |
3 (100) |
191 |
12–139 |
64 |
|
Microphysogobio jeoni
|
1 |
1 (100) |
365 |
- |
365 |
|
Total |
24 |
23 (95.8) |
2,920 |
1–1,325 |
127 |
Table 5Infection status of Clonorchis sinensis metacercariae in acheilognathinid fish from Wicheon in Gunwi-gun, Gyeongsangbuk-do
Table 5
|
Year examined |
No. of fish examined |
No. (%) of fish infected |
No. of metacercariae detected |
|
Total |
Range |
Average |
|
2011 |
9 |
5 (55.6) |
101 |
1–87 |
20 |
|
2013 |
26 |
16 (61.5) |
81 |
1–14 |
5 |
|
2014 |
77 |
63 (81.8) |
2,727 |
1–290 |
43 |
|
2015 |
54 |
42 (77.8) |
3,897 |
1–678 |
93 |
|
2016 |
68 |
60 (88.2) |
4,229 |
1–329 |
70 |
|
2017 |
60 |
40 (66.7) |
201 |
1–30 |
5 |
|
Total |
296 |
228 (77.0) |
11,372 |
1–678 |
50 |
Table 6Infection status of Clonorchis sinensis metacercariae by fish species in the acheilognathinid group
Table 6
|
Species of fish |
No. of fish examined |
No. (%) of fish infected |
No. of metacercariae detected |
|
Total |
Range |
Average |
|
Acheilognathus koreensis
|
130 |
122 (93.9) |
4,620 |
1–678 |
38 |
|
Acheilognathus yamatsutae
|
99 |
55 (55.6) |
691 |
1–136 |
13 |
|
Acheilognathus rhombeus
|
35 |
32 (91.4) |
4,870 |
1–295 |
152 |
|
Acheilognathus majusculus
|
15 |
3 (20.0) |
4 |
1–2 |
1.3 |
|
Acanthorhodeus macropterus
|
4 |
4 (100) |
170 |
2–87 |
43 |
|
Acheilognathus lanceolatus
|
6 |
5 (83.3) |
855 |
4–283 |
171 |
|
Acanthorhodeus gracilis
|
7 |
7 (100) |
162 |
2–82 |
23 |
|
Total |
296 |
228 (77.0) |
11,372 |
1–678 |
50 |
Table 7Infection status of Clonorchis sinensis metacercariae in rasborinid fish from Wicheon in Gunwi-gun, Gyeongsangbuk-do
Table 7
|
Year examined |
No. of fish examined |
No. (%) of fish infected |
No. of metacercariae detected |
|
Total |
Range |
Average |
|
2011 |
64 |
18 (28.1) |
129 |
1–32 |
7 |
|
2013 |
35 |
9 (25.7) |
131 |
1–70 |
15 |
|
2014 |
110 |
41 (37.3) |
448 |
1–66 |
11 |
|
2015 |
102 |
39 (38.2) |
974 |
1–420 |
25 |
|
2016 |
44 |
19 (43.2) |
192 |
1–30 |
10 |
|
2017 |
62 |
21 (33.9) |
345 |
1–205 |
16 |
|
Total |
403 |
147 (36.5) |
2,219 |
1–420 |
15 |
Table 8Infection status of Clonorchis sinensis metacercariae by fish species in the rasborinid group
Table 8
|
Species of fish |
No. of fish examined |
No. (%) of fish infected |
No. of metacercariae detected |
|
Total |
Range |
Average |
|
Zacco platypus
|
259 |
139 (53.7) |
2,207 |
1–420 |
16 |
|
Zacco temminckii
|
136 |
6 (4.4) |
10 |
1–4 |
2 |
|
Opsariichthys uncirostris
|
8 |
2 (25.0) |
2 |
- |
1 |
|
Total |
403 |
147 (36.5) |
2,219 |
1–420 |
15 |
Table 9Susceptibility index of Clonorchis sinensis metacercariae by surveyed year and fish groups
Table 9
|
Group |
Susceptibility indexa
|
|
2011 |
2013 |
2014 |
2015 |
2016 |
2017 |
Total |
|
Overall positive fish group |
153 |
351 |
558 |
487 |
350 |
257 |
412 |
|
Gobioninid group-1 |
516 |
972 |
1,958 |
1,582 |
1,211 |
685 |
1,310 |
|
Acheilognathinid group |
11.2 |
3.1 |
35.2 |
72.4 |
61.7 |
3.3 |
38.5 |
|
Rasborinid group |
2 |
3.9 |
4.1 |
9.6 |
4.3 |
5.4 |
5.5 |
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