Fishborne-zoonotic helminths (FZH), including Gnathostoma spp. and trematodes, provoke a remarkable morbidity in residents of some Asian countries, i.e., Lao PDR, Vietnam, Cambodia, Thailand, the Philippines, Taiwan, China, and Korea. This helminth group causes serious economic damage in the industry of fish aquaculture [1–4]. FZH infections in humans are mainly localized in riverside areas, in which riparian residents are vulnerable to be infected by habitual consumption of raw and/or fermented fish containing infective larvae. Especially, the riverside areas in Mekong river basin in Vietnam, Lao PDR, Cambodia, and Thailand are known to be highly endemic with FZH infections [5–9].
Epidemiological studies on helminthic infections have not been actively performed in the Republic of the Union of Myanmar (Myanmar). Most studies if any were surveys on soil-transmitted helminthiases [10–14]. However, Aung et al. [15] and Sohn et al. [16] reported the endemic status of opisthorchiasis in Myanmar. Won et al. [17] molecularly diagnosed 2 cases of Taenia saginata infection in Yangon, Myanmar. Chai et al. [18] surveyed the infection status of zoonotic trematode metacercariae (ZTM) in fish from a local market in Yangon, and they described the morphological characteristics of adult flukes recovered from experimental animals. On the other hand, surveys on larval gnathostome infections in fish hosts were performed 3 times in Myanmar [19–21]. Chai et al. [19] examined 10 freshwater fish in 3 species, i.e., 6 catfish (Parasilurus sp.), 3 freshwater breams (Tilapia sp.), and 1 snakehead (Channa sp.), from Yangon, Myanmar. Jung et al. [20] examined total 15 snakeheads (Channa striata) from a suburban area of Naypyidaw (the capital of Myanmar). Chai et al. [21] surveyed larval gnathostome infections in 37 Asian swamp eels (Monopterus albus) purchased from a local market in Yangon. These studies were performed with limited numbers of fish in limited fish species, and/or probable fish hosts of Gnathostoma spp. Therefore, in the present study, we examined total 486 fish in 13 species to reveal the infection status of zoonotic helminth larvae (ZHL), including larval gnathostomes and ZTM, in Yangon, Myanmar.
We purchased a total of 486 fish of 13 species in a local market in North Dagon District [14], Yangon City, Myanmar, 8 times (December 2015, August and November 2016, November 2017, June and December 2018, 2019). All collected fish were transported with ice to the laboratory of Department of Parasitology and Tropical Medicine, Gyeongsang National University College of Medicine, Jinju, Korea. The length and weight of fish were individually measured and identified the fish species with the aid of the FishBase website (http://www.fishbase.org/search.php) (Table 1) [22]. Individual fish was finely ground with a mortar and pestle, the ground fish meat was mixed with artificial gastric juice and the mixture was incubated at 36°C for about 2 hr. The digested material was filtered through a 5×5 mm2 mesh, and washed with 0.85% saline until the supernatant became clear. The sediment was carefully examined under a stereomicroscope. Larval gnathostomes and ZTM were separately collected viewing from the general feature, and were counted to get hold of the prevalence (%) and intensity of infection (no. of larvae per fish infected) by fish species [18,21].
Larval gnathostomes were detected from 58 (16.0%) out of 362 fish of 6 species (46.2%), i.e., Channa lucius, Anabas testudineus, Chelon macrolepis, Channa striata, Heteropneustes kemratensis, and Channa sp., and their mean intensity was 2.8 per fish infected. The infection status of larval gnathostomes by fish species is presented in Table 2. The advanced third-stage larvae (AdL3) of gnathostomes detected (n=17) from forest snakeheads, C. lucius, and climbing perch, A. testudineus were 2.05–3.90 (av. 2.911) mm long and 0.20–0.36 (av. 0.311) mm wide. They had a characteristic head bulb (av. 0.077×0.187 mm) with 4 rows of hooklets, a muscular long esophagus (av. 0.955 mm long), 2 pairs of cervical sac (av. 0.580 mm long), and a short tail (av. 0.059 mm long). The mean number of hooklets was 40, 43, 46, and 48 on the 1st, 2nd, 3rd, and 4th row, respectively. They were more or less smaller than those (from swamp eels and Chinese edible frogs) of previous studies in Myanmar [21,23].
More than 8 species, i.e., Opisthorchis viverrini, Haplorchis taichui, H. pumilio, H. yokogawai, Centrocestus spp., Stellantchasmus falcatus, Pygidiopsis cambodiensis, and Procerovum sp., of ZTM were detected. The metacercariae of O. viverrini were found in 10 (2.9%) out of 349 fish in 5 species (38.5%), i.e., C. lucius, A. testudineus, Thynnichthys thynnoides, C. striata, and Puntioplites sp. and their mean intensity was 16.9 per fish infected (Table 3). The metacercariae of H. taichui were detected from 45 (16.8%) out of 268 fish in 7 species (53.9%), and their mean intensity was 63.3 per fish infected (Table 4). The metacercariae of H. pumilio were found in 102 (26.0%) out of 393 fish in 10 species (76.9%), and their mean intensity was 26.8 per fish infected (Table 5). H. yokogawai metacercariae were detected in 13 (12.5%) out of 104 fish in 3 species (23.1%), and their mean intensity was 86.2 per fish infected. Centrocestus spp. metacercariae were found in 54 (15.0%) out of 359 fish in 6 species (46.2%), and their mean intensity was 8.7 per fish infected. The infection status of H. yokogawai and Centrocestus spp. metacercariae by fish species are presented in detail in Tables 6 and 7. The metacercariae of S. falcatus and P. cambodiensis were detected in 8 (10.3%) and 11 (14.1%) out of 78 mullet, C. macrolepis, examined, and their mean intensities were 9.9 per fish infected each. Procerovum sp. metacercariae were found in 4 (7.3%) striped snakehead, C. striata, and 1 (1.0%) climbing perch, A. testudineus, and their mean intensities were 44.0 and 21.0 per fish infected.
In the present study, more than 9 species, i.e., Gnathostoma sp., O. viverrini, H. taichui, H. pumilio, H. yokogawai, S. falcatus, P. cambodiensis, Procerovum sp., and Centrocestus spp., including C. formosanus, of ZHL were detected in fish from a local market of North Dagon District in Yangon City, Myanmar. The presence of these ZHL in fish hosts were already reported in Myanmar [18–21]. However, large-scale surveys with lots of fish samples had not been performed in Myanmar. Therefore, by the present study, it has been reconfirmed that more than 9 etiologic agents of fishborne zoonotic helminthiases are distributed in Yangon, Myanmar. Their infection status, i.e., prevalence and intensity of infection, was clarified in the aspect of host-parasite relationship.
Gnathostomiasis caused by larval Gnathostoma species is clinically characterized by creeping eruption in subcutaneous and intermuscular tissues due to migrating larvae. The larval gnathostomes also occasionally invade the visceral organs, including livers and lungs, eyes, and even the central nerve system including brain [4]. Human cases of gnathostomiasis have occurred sporadically in Myanmar. More than 42 cutaneous cases and over 10 ocular cases have been reported since the first case in 1960 [24–28]. The infection status with larval gnathostomes were investigated in fish and frog hosts 4 times in Myanmar [19–21,23]. Chai et al. [19] found 2 AdL3 of G. spinigerum from 2 catfish in the examination of 10 freshwater fish in 3 species, i.e., Parasilurus sp., Tilapia sp., and Channa sp., from Yangon. Jung et al. [20] also detected 2 AdL3 of G. spinigerum in 2 snakeheads, C. striata, from a suburban area of Naypyidaw. Chai et al. [21] detected a total of 401 G. spinigerum AdL3 in 33 (89.2%) out of 37 Asian swamp eels purchased in a local market of Yangon. Recently, Chai et al. [23] also detected 158 larval gnathostomes in 15 (75.0%) out of 20 Chinese edible frogs, Hoplobatrachus rugulosus, from a local market of Yangon. In this study, larval gnathostomes were found in 58 (16.0%) out of 362 fish in 6 species, i.e., C. lucius, C. striata, A. testudineus, C. macrolepis, H. kemratensis, and unidentified snakehead, and the forest snakehead, C. lucius, was the most prevalent fish host. Thus, 8 fish species, including catfish and swamp eel, already reported, and Chinese edible frogs are suggested to be the potential risk of human gnathostomiasis in Myanmar.
The endemicity of O. viverrini metacercariae (prevalence below 3.0%; intensity of infection about 17 per fish infected) was very low like in Sohn et al. [16]. Among 5 positive fish species, 4, i.e., C. lucius, C. striata, A. testudineus, and unspecified Puntioplites sp., were previously reported [16], and only 1 species, T. thynnoides, is newly added to the second intermediate hosts of O. viverrini in Myanmar. The low-grade endemicity for opisthorchiasis in Myanmar was also confirmed by fecal examinations of people [15,16]. Aung et al. [15] found small trematode eggs in 34 (9.3%) out of 364 fecal samples of residents, and molecularly confirmed 18 cases to be opisthorchiasis infections. Sohn et al. [16] also detected small trematode eggs from 14 (0.7%) out of 2,057 fecal samples in 3 regions in Yangon. Accordingly, it is suggested that opisthorchiasis is maintained in low grade in the second intermediate fish host as well as in the definitive human host in Myanmar.
In the present study, H. taichui metacercariae were detected from 45 (16.8%) out of 268 fish in 7 (53.8%) species, i.e., C. lucius, C. striata, T. thynnoides, C. cirrhosis, H. lagleri, C. idella, and unspecified Puntioplites sp., and their mean intensity was 63.3 per fish infected. The prevalence was lower than that (42.3%) of Chai et al. [18], but the intensity of infection was more or less higher than that (42.9) of a previous study performed in Yangon, Myanmar [18]. Especially, the prevalences and intensities were relatively high in 2 fish species, C. cirrhosis, and Puntioplites sp. By this study and Chai et al. [18], a total of 11 fish species, i.e., C. lucius, C. striata, T. thynnoides, C. cirrhosis, H. lagleri, C. idella, Puntius aurotaeniatus, Esomus altus, Puntioplites sp., Mystacoleucus sp., and Labeo sp., are recorded as the second intermediate hosts of H. taichui in Myanmar.
The metacercariae of H. pumilio were detected from 102 (26.0%) out of 393 fish in 10 (76.9%) species, i.e., C. lucius, C. striata, A. testudineus, T. thynnoides, C. cirrhosis, H. lagleri, C. idella, P. aurotaeniatus, Puntioplites sp., and Channa sp., and their mean intensity was 26.8 per fish infected. The prevalence and intensity of infection were relatively low like in a previous study [18]. Based on the findings of present and previous studies, total 15 fish species, i.e., C. lucius, C. striata, A. testudineus, T. thynnoides, C. cirrhosis, H. lagleri, C. idella, P. aurotaeniatus, Trichogaster pectoralis, E. altus, Puntioplites sp., Channa sp., Rhynogobius sp., Mystacoleucus sp., and Labeo sp., are the second intermediate hosts of H. pumilio in Myanmar. In Chai et al. [18], H. yokogawai metacercariae were found in 5 fish species, i.e., P. aurotaeniatus, E. altus, T. pectoralis, Mystacoleucus sp., and Labeo sp., from Yangon, Myanmar, and they were heavily infected in 2 fish species, P. aurotaeniatus and Mystacoleucus sp. However, H. yokogawai metacercariae were detected in 3 fish species, Puntioplites sp., P. aurotaeniatus, and T. thynnoides, in this study. Therefore, total 7 fish species, i.e., P. aurotaeniatus, E. altus, T. pectoralis, T. thynnoides, Puntioplites sp., Mystacoleucus sp., and Labeo sp., have been found to be the second intermediate hosts of H. yokogawai in Myanmar.
Centrocestus spp. metacercariae, including C. formosanus, were found in 6 (46.2%) fish species, i.e., C. lucius, C. striata, A. testudineus, T. thynnoides, Puntioplites sp., and Channa sp., and their mean intensity was 8.7 per fish infected. The prevalence (15.0%) and intensity of infection were lower than those (50.8% and 25.8) of Chai et al. [18]. By the present study, 3 fish species, i.e., C. lucius, Puntioplites sp., and Channa sp., are newly added in the second intermediate hosts of Centrocestus spp. in Myanmar. As the second intermediate hosts of Centrocestus spp., a total of 11 fish species, i.e., C. lucius, T. thynnoides, P. aurotaeniatus, E. altus, C. striata, A. testudineus, T. pectoralis, Puntioplites sp., Channa sp., Mystacoleucus sp., and Labeo sp., have been listed in Myanmar.
In the present study, Procerovum sp. metacercariae were detected from 2 fish species, C. striata and A. testudineus, examined in August 2016. The climbing perch, A. testudineus, was previously reported as the second intermediate host of Procerovum spp., including P. varium in Vietnam, Lao PDR, and Myanmar [9,18,29,30]. The metacercariae of S. falcatus and P. cambodiensis were detected only in mullets, Chelon macrolepis, like in previous studies, including Chai et al. [18,31,32]. Chai et al. [18] detected a total of 36 S. falcatus metacercariae in 15 (34.1%) out of 44 mullets examined and they also found 38 metacercariae of P. cambodiensis in only 1 (2.2%) mullet from Yangon, Myanmar. In the present study, the prevalences were 10.3% and 14.1% and intensities of infection of 2 heterophyid flukes were commonly 9.9 per fish infected.
Conclusively, it has been confirmed that larval gnathostomes and more than 8 species of ZTM, i.e., O. viverrini, H. taichui, H. pumilio, H. yokogawai, S. falcatus, P. cambodiensis, Procerovum sp., and Centrocestus spp., including C. formosanus, were infected in fish from Yangon, Myanmar, and they can act as the etiologic agents of fishborne zoonotic helminthiases although their endemicities were not so high. To reveal the detailed epidemiological situation of FZH infections in Myanmar, further studies on the intermediate and definitive hosts (humans and reservoir host animals) of FZH should be performed in the near future.
