Open Access
Issue
Parasite
Volume 23, 2016
Article Number 16
Number of page(s) 14
DOI https://doi.org/10.1051/parasite/2016016
Published online 07 April 2016

© Y. Kondo et al., published by EDP Sciences, 2016

Licence Creative CommonsThis is an Open Access article distributed under the terms of the Creative Commons Attribution License (http://creativecommons.org/licenses/by/4.0), which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.

Introduction

Jellyfish not only play an important role as predators in the marine ecosystem, but they also function as prey and hosts for a wide variety of organisms [1, 2, 38, 39, 41]. Interactions between jellyfish and fish have long been known and have been comprehensively reviewed by many authors [1, 3, 17, 19, 24, 41, 51, 52]. Jellyfish are utilized by fish for school formation, food collection, and prey [29, 30]. In addition, endoparasitic helminths are transmitted from intermediate host jellyfish to definitive host fish via predation [25]. Some digenean trematodes are known to use cnidarians as their second intermediate hosts [15, 28, 33] and/or paratenic hosts [20, 4749]. Medusivorous fish become infected by trematodes through predation of infected jellyfish and act as definitive hosts [7, 39].

In the Seto Inland Sea of western Japan, some large scyphozoan jellyfish, such as the moon jellyfish Aurelia aurita (Linnaeus, 1758) s.l., Japanese sea nettle Chrysaora pacifica (Goette, 1836), and ghost jellyfish Cyanea nozakii Kishinouye, 1891, are infected by the metacercariae of trematodes [39]. Unencysted metacercariae of three species, Lepotrema clavatum Ozaki, 1932, Cephalolepidapedon saba Yamaguti, 1970, and Opechona olssoni (Yamaguti, 1934), have been found in the mesoglea of A. aurita s.l. [39]. In addition, these jellyfish are usually accompanied by other symbionts, including juveniles of the Japanese butterfish Psenopsis anomala (Temminck and Schlegel, 1844), black scraper Thamnaconus modestus (Günther, 1877), and Japanese jack mackerel Trachurus japonicus (Temminck and Schlegel, 1844) [30, 39].

The present study aimed to investigate seasonal changes in the prevalence and intensity of metacercariae of three trematode species in host jellyfish in the Seto Inland Sea from March 2010 to September 2012, and to clarify transmission of these trematodes to their definitive host fish.

Materials and methods

Seasonal changes in prevalence and intensity of metacercariae in jellyfish

Scyphozoan jellyfish were collected with a scoop net (diameter 50 cm; mesh size 2 mm) from a fishing boat in the central part of the Seto Inland Sea of western Japan (34°10′17′′–34°19′27′′ N, 132°53′49′′–132°57′45′′ E) (shaded area inserted in Fig. 1) from March 2010 to September 2012. Collections were conducted at least twice a month throughout the study period. Surface water temperature and salinity at each sampling site were measured in situ using a CTD (D-400F, JFE Advantech Co., Ltd.). The bell diameter of each specimen of jellyfish was measured in the laboratory immediately after collection. The presence or absence of metacercariae in the mesoglea was examined under a compound stereomicroscope (SZ6045, Olympus). Bell measurements are presented as the mean ± standard deviation (SD).

thumbnail Figure 1.

Sampling sites for jellyfish and juvenile fish in Japan. The shaded area indicates the sampling location in the Seto Inland Sea from March 2010 to September 2012. St-A indicates the supplementary sampling site in the Ariake Sea.

Metacercariae found in jellyfish and juvenile fish, and adult trematodes found in the guts of associated juvenile fish were carefully removed from the host’s tissues with fine forceps, and then fixed in hot 10% formalin, stained with Mayer’s haemalum, dehydrated in an ethanol series, cleared in a xylene series, and mounted in Canada balsam. Trematodes were identified using Bartoli and Bray [4], Bray [6], Ozaki [40], and Yamaguti [5457]. Body length measurements are presented as the mean ± SD.

Seasonal changes in prevalence and intensity of trematodes in each species of jellyfish examined were calculated following Bush et al. [9]. The mean intensity of trematodes in each of the host jellyfish throughout the study period was tested using the Steel-Dwass test because our data was not in normal distribution and homoscedasticity. Spearman’s rank correlation coefficient between host size (bell diameter and wet weight) and intensity of trematodes was tested. Statistical analyses were performed using R software (version 3.0.1).

Examination of gut contents of juvenile fish

Juvenile fish associated with jellyfish were captured using a scoop net in the Seto Inland Sea from March 2010 to September 2012. Because juvenile fish were closely associated with their host jellyfish, they were easy to catch by scoop net. The juvenile fish were preserved in 99.5% ethanol soon after collection. The standard length (SL) of all juvenile fish specimens was measured and is presented as the mean ± SD. The gut contents of juvenile fish captured in the Seto Inland Sea were examined under a compound stereomicroscope (SZ6045, Olympus).

Stable isotope analysis of jellyfish and their associated fish

Stable isotope analysis was used to evaluate the trophic interaction between a host jellyfish and associated juvenile fish. Juvenile fish and jellyfish were collected as described above from the Seto Inland Sea, and supplementary collection was made at a station in the Ariake Sea (St-A: 33°01′′25′′ N, 130°18′24′′ E) on October 2, 2011 (Fig. 1). The specimens were preserved in 99.5% ethanol. A marginal part of the bell of the jellyfish and part of the body muscles of the juvenile fish was cut off with clean scissors, dried at 60 °C in an oven (DOV-450P, AS ONE Co.), and pulverized using a mortar and pestle. The dried specimens were transferred to microtubes and subsequently treated with 1 mL methanol and 1 mL dichloromethane/methanol (7:1), and rinsed with distilled water to remove lipids [37]. In addition, carbonate carbon was removed from the specimens with 1 M HCl. The specimens were washed with distilled water and dried again prior to stable isotope analysis. Measurements of carbon and nitrogen isotope compositions were performed using an on-line system of ThermoFinnigan Delta Plus XP isotope-ratio mass spectrometry coupled with a Flash EA 1112 Automatic Elemental Analyzer through a ConFlo III interface modified to sensitive analysis [36]. Isotope compositions were expressed in conventional δ notation against the Peedee Belemnite (PDB) for carbon and atmospheric N2 for nitrogen: δ 13 C   = ( 13 R sample / 13 R standard - 1 )   × 1000 , δ 13 N = ( 15 R sample / 15 R standard - 1 )   × 1000 , $$ \begin{array}{c}{\mathrm{\delta }}^{13}\mathrm{C}\mathrm{\enspace }=\left({}^{13}{R}_{\mathrm{sample}}/{}^{13}{R}_{\mathrm{standard}}-1\right)\enspace \times 1000,\\ {\mathrm{\delta }}^{13}\mathrm{N}=\left({}^{15}{R}_{\mathrm{sample}}/{}^{15}{R}_{\mathrm{standard}}-1\right)\enspace \times 1000,\end{array} $$where 13R and 15R are 13C/12C and 15N/14N ratios, respectively. Analytical errors (95% probability) were estimated to be within 0.3‰ for both carbon and nitrogen based on the repeated measurements of authentic and laboratory standards [36, 50].

Results

Identification of metacercariae in jellyfish

Large-sized scyphozoan jellyfish collected from the sampling area were identified as three species, A. aurita s.l., C. pacifica, and C. nozakii. All jellyfish collected were infected by unencysted metacercariae of three lepocreadiid trematode species, L. clavatum, C. saba, and O. olssoni, in the host mesoglea (Fig. 2). In total, 12,425 metacercariae of L. clavatum were obtained, which was greater than those of C. saba (n = 7,101) and O. olssoni (n = 3,463).

thumbnail Figure 2.

Metacercariae (indicated by black arrowheads) in the mesoglea of Aurelia aurita s.l. collected from the Seto Inland Sea (A, B). Stained metacercariae of Lepotrema clavatum (C), Cephalolepidapedon saba (D), and Opechona olssoni (E) (scale bars: 0.1 mm). Abbreviations: Os, oral sucker; Ph, pharynx; Vs, ventral sucker; Ov, ovary; Te, testis.

The morphology of the metacercariae is briefly described as follows: In L. clavatum (Fig. 2C), the body is pyriform, measuring 0.29–0.40 mm long (0.35 ± 0.03 mm, n = 18). This species is smallest among the three species. The tegument is spinose. The oral sucker (Os in Fig. 2C) and ventral sucker (Vs in Fig. 2C) are rounded. The pharynx (Ph in Fig. 2C) is oval. The ovary (Ov in Fig. 2C) and two testes (Te in Fig. 2C) are seen in the hindbody. The excretory vesicle is I-shaped, extending between the ventral sucker and intestinal bifurcation. The excretory pore terminal opens into dorsal side. In C. saba (Fig. 2D), the body is elongate, measuring 0.38–0.50 mm long (0.44 ± 0.05 mm, n = 19). The oral sucker (Os in Fig. 2D) is short and funnel-shaped. The ventral sucker (Vs in Fig. 2D) is rounded. The prepharynx is long. The pharynx (Ph in Fig. 2D) is oval. The intestines end blindly. The excretory vesicle extends to the pharynx. In addition, in C. saba, the circumoral spines are not seen clearly in the present metacercariae. The excretory vesicle reaches the pharynx in the present metacercariae. In this respect, our findings agree with the description by Yamaguti [56], but differ from those of Bartoli and Bray [4] and Shimazu [43, 44], who found that the excretory vesicle extends to the ovary or posterior testis. In O. olssoni (Fig. 2E), the body is elongate, measuring 0.69–1.15 mm long (0.92 ± 0.18 mm, n = 9), twice as large as the others. The oral sucker (Os in Fig. 2E) is elongate and funnel-shaped. The ventral sucker (Vs in Fig. 2E) is rounded and smaller than the oral sucker. The prepharynx is relatively short. The intestines and excretory vesicle form a uroproct (possibly a cloaca). The excretory vesicle extends slightly anterior to the intestinal bifurcation.

Seasonal changes in prevalence and intensity of metacercariae in jellyfish

Seasonal changes in water temperature and salinity during the present investigation are shown in Figure 3. Water temperatures ranged from 10.2 °C (February 21, 2011) to 27.1 °C (September 18, 2012), and salinity fluctuated from 31.5 (October 12, 2011) to 33.7 (April 14, 2011).

thumbnail Figure 3.

Seasonal changes in water temperature and salinity in the western part of the Seto Inland Sea from March 2010 to September 2012.

Aurelia aurita s.l. occurred from June to September in 2010, April to August in 2011, and May to July in 2012. A total of 174 individuals were investigated. The bell diameter ranged from 5.8 to 29.0 cm (13.3 ± 3.8 cm). Prevalence and mean intensity of metacercariae in A. aurita s.l. clearly showed seasonality (Figs. 4A and 4B), although the number of jellyfish collected varied widely among months. In L. clavatum, prevalence increased from March to June, and exceeded 95% in June of each year (Fig. 4A), excluding the months when only one individual was collected. The mean intensity of L. clavatum in A. aurita s.l. ranged widely from 1.0 to 247.0 individuals, and was consistently high in June of each year, decreasing thereafter (Fig. 4B). An extremely high intensity (440.0) was recorded on June 24, 2010. The mean intensities of C. saba and O. olssoni varied from 1.3 to 51.6 and from 0 to 45.6, respectively. They were much lower than that of L. clavatum, but generally exhibited a similar seasonal pattern (Fig. 4B).

thumbnail Figure 4.

Seasonal changes in the prevalence (A) and mean intensity (B) of metacercariae in Aurelia aurita s.l. from June 2010 to September 2012. Lepotrema clavatum, open square; Cephalolepidapedon saba, open circle; Opechona olssoni, open triangle. n: Number of jellyfish collected. A line was not connected when only one individual was collected.

In C. pacifica, a total of 44 individuals were collected from June and April in 2010 to July in 2011 and 2012. The bell diameter ranged from 4.0 cm to 24.0 cm (14.2 ± 4.7 cm). The prevalence of L. clavatum was 50%–100% throughout the period of host occurrence (Fig. 5A). In C. saba and O. olssoni, the prevalence increased between April and July. The maximum mean intensity of the three trematode species was 21.9 in L. clavatum (Fig. 5B). The intensities of all species of trematodes were much lower than in A. aurita s.l. and C. nozakii (Figs. 4B, 5B, and 6B).

thumbnail Figure 5.

Seasonal changes in the prevalence (A) and mean intensity (B) of metacercariae in Chrysaora pacifica from June 2010 to September 2012. Lepotrema clavatum, open square; Cephalolepidapedon saba, open circle; Opechona olssoni, open triangle. n: Number of jellyfish collected. A line was not connected when only one individual was collected.

thumbnail Figure 6.

Seasonal changes in the prevalence (A) and mean intensity (B) of metacercariae in Cyanea nozakii from June 2010 to September 2012. Lepotrema clavatum, open square; Cephalolepidapedon saba, open circle; Opechona olssoni, open triangle. n: Number of jellyfish collected.

Twenty-four individuals of C. nozakii were sampled and examined from August and September in 2010 and 2011, and June to September in 2012. The bell diameter ranged widely from 13.3 cm to 51.0 cm (29.2 ± 10.1 cm). Prevalence of the three trematode species was consistently 100% during the period of the host’s occurrence (Fig. 6A), although it should be noted that replications of the sampled jellyfish were low (n = 2–5). The mean intensity of L. clavatum in C. nozakii ranged from 76.3 to 474.4 individuals. The mean intensities of C. saba and O. olssoni varied from 26.6 to 315.5 and 23.4 to 164.0, respectively (Fig. 6B).

The mean intensity of L. clavatum in C. nozakii throughout the study period was 219.6. In A. aurita s.l. and C. pacifica, the mean intensities of L. clavatum were 46.5 and 8.8, respectively. There was a significant difference among the host jellyfish (Steel-Dwass test, p < 0.05). The mean intensity was highest in C. nozakii (147.8), compared to A. aurita s.l. (28.3) and C. pacifica (7.7). In O. olssoni, the mean intensity was 19.3 in A. aurita s.l., 2.2 in C. pacifica, and 77.0 in C. nozakii. In addition, significant differences in mean intensities among host jellyfish were observed for the other two trematodes (Steel-Dwass test, p < 0.05). The mean intensity of the three trematode species in C. nozakii was highest among the host jellyfish (Fig. 7).

thumbnail Figure 7.

Mean intensity of metacercariae of each species in host jellyfish collected from June 2010 to September 2012. Error bars indicate standard deviations. Different letters denote significant differences among hosts (Steel-Dwass test, p < 0.05).

Spearman’s rank correlation coefficient was calculated to examine any statistical correlation between the host’s bell diameter and the intensity of metacercariae (Fig. 8). Positive correlations between bell diameter and intensity of the metacercariae were significant only in C. nozakii (r = 0.71, p < 0.05) but not in the other two host species (p > 0.05). However, there was no correlation between wet weight and intensity (p > 0.05).

thumbnail Figure 8.

Relationship between bell diameter and intensity of all metacercariae. r: correlation coefficient. (A) Aurelia aurita s.l., (B) Chrysaora pacifica, (C) Cyanea nozakii.

Examination of the gut contents of juvenile fish

The three species of jellyfish were accompanied by juvenile fish of P. anomala, T. modestus, and T. japonicus in the Seto Inland Sea (Fig. 9). Psenopsis anomala co-occurred with C. pacifica and C. nozakii from May to September. Thamnaconus modestus and T. japonicus were associated with A. aurita s.l. and C. nozakii from June to August (Table 1). Psenopsis anomala also co-occurred with C. nozakii in the Ariake Sea.

thumbnail Figure 9.

Juvenile fish associated with jellyfish collected from the Seto Inland Sea. (A) Psenopsis anomala associating with Cyanea nozakii (arrows). (B) Psenopsis anomala. (C) Trachurus japonicus. (D) Thamnaconus modestus.

Table 1.

Number and size of fish juveniles associated with jellyfish in Seto Inland Sea from July 2010 to September 2012. Abbreviations: SL, standard length of associated fish (cm); SD, standard deviation.

Numerous nematocysts of unidentified cnidarians were observed in the guts of P. anomala (SL: range 2.2–9.7 cm; mean ± SD 5.4 ± 2.2 cm; n = 11) and T. modestus (SL: 2.0–2.9 cm; 2.5 ± 0.4 cm; n = 4), implying that P. anomala and T. modestus had fed on jellyfish. In addition, metacercariae and adults of O. olssoni and C. saba, and metacercariae of L. clavatum were detected in the guts of P. anomala. Metacercariae of L. clavatum and O. olssoni were also detected in the guts of T. modestus (Table 2, Fig. 10). In contrast, neither trematodes nor nematocysts were observed in the guts of T. japonicus (SL: 1.0–2.7 cm; 1.8 ± 0.7 cm; n = 5) (Table 2).

thumbnail Figure 10.

Nematocysts (A) and metacercaria of Opechona olssoni (B) observed in the gut of a juvenile butterfish, Psenopsis anomala (standard length: 6.6 cm), collected in August 27, 2010. Abbreviations: Os, oral sucker; Ph, pharynx; Vs, ventral sucker; In, intestine.

Table 2.

Occurrence of trematodes in fish juveniles associated with jellyfish in Seto Inland Sea from August 2010 to July 2012. Abbreviations: No, Number of examined fish juveniles; +, Nematocysts are contained in guts; −, Nematocysts are not contained in guts; Pm, Prevalence of metacercariae (%); Im, Mean intensity of metacercariae; Pa, Prevalence of adults (%); Ia, Mean intensity of adults.

Stable isotope analysis of jellyfish and their associated fish

The δ13C values of A. aurita s.l. (n = 3) ranged from −17.7‰ to −17.5‰. The δ15 N values were 17.8‰–19.7‰ (Table 3). In C. pacifica (n = 2), δ13C values and δ15N values were −22.3‰, 12.6‰ and −22.0‰, 12.7‰, respectively. The δ13C values ranged from −20.2‰ to −16.5‰, and δ15N values ranged from 12.8‰ to 14.1‰ in C. nozakii (n = 4). Each jellyfish and juvenile fish pair showed a different tendency. The δ13C values of P. anomala (n = 5) ranged from −21.2‰ to −17.2‰ and these values depended on their host jellyfish. Moreover, δ15N values (14.9‰ to 15.9‰) were higher than each host (Fig. 11). In pairs of P. anomala and C. pacifica, the mean δ15N value of P. anomala was 2.3‰ and 2.7‰ higher than those of their hosts, respectively. In contrast, the δ13C and δ15N values of T. modestus (n = 3) were similar among three individuals (−20.4‰ to −18.8‰ and 13.8‰ to 15.8‰). Trachurus japonicus also showed that the δ13C (−19.4‰ to −17.8‰) and δ15N values (13.2‰ to 14.6‰) were similar among the individuals examined. The δ13C and δ15N values of these two species were different from those of the host jellyfish.

thumbnail Figure 11.

Dual isotope plot of δ13C and δ15N. (A) Psenopsis anomala and its host jellyfish, (B) Thamnaconus modestus and its host jellyfish, (C) Trachurus japonicus and its host jellyfish. Dotted lines indicate pairs of an associated fish and its host jellyfish which were collected together. Abbreviations: BD, bell diameter of host jellyfish (cm); SL, standard length of associated fish (cm).

Table 3.

δ13C (‰) and δ15N (‰) contents of members of associations between jellyfish and fish. Abbreviations: BD, bell diameter of host jellyfish (cm); SL, standard length of associated fish (cm).

Discussion

Jellyfish as intermediate and/or paratenic hosts of metacercariae

In the present study, all individuals of the trematodes observed in jellyfish were identified as unencysted metacercariae belonging to the family Lepocreadiidae. No specific information regarding the first intermediate hosts of these trematodes is available. However, sporocysts full of oculate trichocercous cercariae (Lepocreadiidae) in the dove shell, Mitrella bicincta (Gould, 1860) from the Seto Inland Sea in May (Kondo, unpublished data), may be a candidate for one of the three trematodes. In the present study, infection of jellyfish by metacercariae showed distinct seasonal differences in prevalence and mean intensity in the Seto Inland Sea. Martell-Hernández et al. [26] reported the seasonal occurrence of Opechona pyriforme (Linton, 1900) metacercariae in the hydrozoan Eirene tenuis (Browne, 1905) in the western Gulf of Mexico. The host occurred in May, July, and October, whereas the endoparasite was observed in the mesoglea of the host only in July and October, suggesting that the infectious period of the parasite to the host was restricted to July and October. In addition, Yip [58] reported that the prevalence and intensity of Opechona bacillaris (Molin, 1859) metacercariae in the ctenophore Pleurobrachia pileus (O. F. Müller, 1776) were highest in Galway Bay, western Ireland, in early summer. These seasonal changes in prevalence and intensity are related to the life cycle of the trematodes. The trematode Bucephalus sp., which utilizes the Japanese pearl oyster Pinctada fucata martensii (Dunker, 1872) as its first intermediate host, actively releases free-swimming cercariae as water temperature increases [34]. In this study, the prevalence of metacercariae of three species in A. aurita s.l. and C. pacifica increased with a rise in water temperature from early spring to early summer (Figs. 35). Seasonal changes in prevalence and intensity in the second intermediate host seem to be controlled by the seasonal release of infective cercariae related to changes in water temperature.

In C. nozakii, which occurred from July to September, the prevalence and mean intensity of metacercariae were highest among the jellyfish examined in the present study, although the low samples sizes should be noted (Figs. 6 and 7). Cyanea nozakii is known as a medusivore [21]. Metacercariae of the family Lepocreadiidae have been reported to infect many species of gelatinous zooplankters, including ctenophores, hydrozoans, and scyphozoans [8, 33, 35]. In the Seto Inland Sea, C. nozakii has been observed feeding on ctenophores, hydrozoans, and scyphozoans (Kondo, personal observation). Therefore, the high prevalence and intensity of metacercariae on C. nozakii may be partly attributable to medusivory. Such an accumulation of metacercariae in paratenic hosts is known in other trematodes. In the trematode Pharyngostomum cordatum (Diesing, 1850) Ciurea, 1922, the intermediate, definitive, and paratenic hosts are frogs, cats, and snakes, respectively; in paratenic frog-eating hosts, metacercariae accumulate [14]. Moreover, a positive relationship was observed between bell diameter and intensity only in C. nozakii (Fig. 8C). Generally, it is not unusual for parasites to occur in greater abundance in larger hosts [22]. However, A. aurita s.l. and C. pacifica did not show significant positive relationships (Figs. 8A and 8B). It appears that accumulation may be due to medusivory by C. nozakii. Hansson [16] reported that predation by the lion’s mane jellyfish Cyanea capillata (Linnaeus, 1758) on A. aurita is enhanced as the bell diameter of the predator increases. In addition, such a tendency was also detected in the medusivorous scyphozoan fried egg jellyfish Phacellophora camtschatica (Brandt, 1835) [46]. Metacercariae are accumulated by predation of larger C. nozakii because large medusivorous jellyfish can catch a higher number of gelatinous zooplankters than small ones. Thus, it is presumed that C. nozakii plays a role as a paratenic host rather than a second intermediate host.

Transmission of trematodes to definitive host fish via predation of infected jellyfish

In Japanese waters, it has been previously found that T. modestus, the thread-sail filefish Stephanolepis cirrhifer (Temminck and Schlegel, 1850), the lagoon triggerfish Rhinecanthus aculeatus (Linnaeus, 1758), and the fivespot flounder Pseudorhombus cinnamoneus Günther, 1862 are definitive hosts for L. clavatum [12, 39, 40, 54]; P. anomala and T. modestus are hosts for O. olssoni [39], and P. anomala and the chub mackerel Scomber japonicus Houttuyn, 1782, are hosts for C. saba [39, 44]. The definitive hosts of trematodes that use jellyfish as a second intermediate host have been summarized in previous studies [8, 35]. Infection from the intermediate or paratenic host jellyfish to the definitive host fish most likely occurs via predation by the definitive host [25, present study]. In the present study, three species of juvenile fish, P. anomala, T. modestus, and T. japonicus were collected along with associated jellyfish throughout the investigation (Table 1). Juveniles of these fish are known to be closely associated with jellyfish [17, 20, 24, 27, 29, 30, 38, 39, 41, 51, 52]. It seems that transmission of the metacercariae in the second intermediate and/or paratenic host to the definitive host also occurred via predation by the associated juvenile fish of infected jellyfish in the Seto Inland Sea.

Juveniles of P. anomala were observed swimming around the tentacles of jellyfish from May to September (Fig. 9A). These young fish are considered to utilize jellyfish as shelter to avoid predation by visual predators [5, 42]. According to Shojima [45], when reaching a total length of 1.5–2.0 cm, the larvae become juveniles. In the present study, the smallest individual (2.2 cm in standard length) was captured in May 2011. Therefore, it is likely that juveniles of P. anomala became associated with jellyfish before or immediately after metamorphosis. Psenopsis anomala is a medusivorous fish, as their guts often contain pieces of jellyfish gonads and tissues even as larvae and juveniles [45]. In the present study, nematocysts were frequently found in the guts of juvenile P. anomala. In addition, our stable isotope analysis also supported that juvenile P. anomala fed on the host jellyfish. Stable isotope ratios generally reflect dietary diversity. When the trophic level rises by one step in the food chain, δ13C and δ15N values increase by about 1‰ and 3‰, respectively [11, 31]. Because stable isotope ratios consistently increased, we can infer trophic relationships between prey and their predators. Recently, stable isotope analyses were used to reveal relationships between jellyfish and their symbionts [13, 53]. D’Ambra et al. [10] obtained evidence with this technique that associated juvenile fish Chloroscombrus chrysurus (Linnaeus, 1766) fed on their hosts jellyfish Aurelia sp. and Drymonema larsoni Bayha and Dawson, 2010. Psenopsis anomala was enriched in δ15N relative to host jellyfish in all pairs (see Table 3, Fig. 11). Furthermore, metacercariae and adults of trematodes were observed in the guts (Table 2), suggesting that these trematodes infected P. anomara via predation.

Thamnaconus modestus has previously been reported as the definitive host of L. clavatum [54]. In this study, the transmission of trematodes is presumed to have been caused through a prey-predator relationship between jellyfish and juveniles of T. modestus, because the nematocysts and metacercariae of trematodes were found together in the guts of the juveniles (Table 2). However, the δ15N value of T. modestus is not suggestive of predation by juvenile T. modestus on jellyfish (Fig. 11). Kim et al. [18] reported that most of the prey items of T. modestus belonged to four groups: hyperiid amphipods, gastropods, ophiuroids, and algae. Minagawa and Yoshioka [32] suggested that when a predator is highly omnivorous, its stable isotope values are estimated to be lower than expected, because they are equalized by the stable isotope values of various food items. Thus the stable isotope analysis suggests T. modestus feeds on jellyfish in addition to other foods, although it is unknown how much each prey item contributed to the results of the stable isotope analysis.

In contrast, the mean δ15N values of T. japonicus were nearly equal to or lower than that of the host jellyfish. The δ13C values of T. japonicus were less than that of the host jellyfish (Table 3, Fig. 11). In T. japonicus, neither nematocysts nor trematodes were detected in the guts (Table 2). Masuda [29] reported that T. japonicus measuring 1.0–2.7 cm in length used jellyfish for shelter, but not for food. The T. japonicus specimens collected in this study fall within the size range recorded by Masuda [29] (Table 1). Masuda [29] suggested that jellyfish function as shelter, rather than as a food source for juveniles of T. japonicus. Therefore, the gut contents and stable isotope analyses indicated no predation by T. japonicus juveniles on jellyfish. Although Machida et al. [23] reported that Opechona sp. was found in the pyloric cecum and intestines of T. japonicus, these fish, which were landed by commercial fishing boats, were adults. All T. japonicus collected in this study were juveniles. Therefore it seems unlikely that juvenile T. japonicus act as a definitive host for trematodes that infect jellyfish.

The present study clearly revealed that transmission of trematodes, from intermediate and paratenic hosts to definitive hosts, occurred over an approximately six-month period, using a wide variety of host jellyfish. The life cycles of the three trematode species examined in the present study were clarified, except for the first intermediate hosts. It seems likely that C. nozakii may act as paratenic hosts through medusivory. The following questions should be investigated in future studies: (1) When are miracidium larvae released from definitive hosts? (2) How do cercariae infect from first intermediate to second intermediate hosts? (3) How long can metacercariae survive in the host jellyfish? and (4) How long do adult trematodes survive in definitive hosts?

Acknowledgments

We would like to thank Dr. S. Sakai for his warm-hearted encouragement through the present study. This study was partially supported by Grants-in-Aid from the Japan Society for the Promotion of Science (JSPS), awarded to SO (No. 25304031), and JN (Nos. 23405031, 26304030) and by a grant from Kuroshio Biological Research Foundation awarded to YK.

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Cite this article as: Kondo Y, Ohtsuka S, Hirabayashi T, Okada S, Ogawa NO, Ohkouchi N, Shimazu T & Nishikawa J: Seasonal changes in infection with trematode species utilizing jellyfish as hosts: evidence of transmission to definitive host fish via medusivory. Parasite, 2016, 23, 16.

All Tables

Table 1.

Number and size of fish juveniles associated with jellyfish in Seto Inland Sea from July 2010 to September 2012. Abbreviations: SL, standard length of associated fish (cm); SD, standard deviation.

Table 2.

Occurrence of trematodes in fish juveniles associated with jellyfish in Seto Inland Sea from August 2010 to July 2012. Abbreviations: No, Number of examined fish juveniles; +, Nematocysts are contained in guts; −, Nematocysts are not contained in guts; Pm, Prevalence of metacercariae (%); Im, Mean intensity of metacercariae; Pa, Prevalence of adults (%); Ia, Mean intensity of adults.

Table 3.

δ13C (‰) and δ15N (‰) contents of members of associations between jellyfish and fish. Abbreviations: BD, bell diameter of host jellyfish (cm); SL, standard length of associated fish (cm).

All Figures

thumbnail Figure 1.

Sampling sites for jellyfish and juvenile fish in Japan. The shaded area indicates the sampling location in the Seto Inland Sea from March 2010 to September 2012. St-A indicates the supplementary sampling site in the Ariake Sea.

In the text
thumbnail Figure 2.

Metacercariae (indicated by black arrowheads) in the mesoglea of Aurelia aurita s.l. collected from the Seto Inland Sea (A, B). Stained metacercariae of Lepotrema clavatum (C), Cephalolepidapedon saba (D), and Opechona olssoni (E) (scale bars: 0.1 mm). Abbreviations: Os, oral sucker; Ph, pharynx; Vs, ventral sucker; Ov, ovary; Te, testis.

In the text
thumbnail Figure 3.

Seasonal changes in water temperature and salinity in the western part of the Seto Inland Sea from March 2010 to September 2012.

In the text
thumbnail Figure 4.

Seasonal changes in the prevalence (A) and mean intensity (B) of metacercariae in Aurelia aurita s.l. from June 2010 to September 2012. Lepotrema clavatum, open square; Cephalolepidapedon saba, open circle; Opechona olssoni, open triangle. n: Number of jellyfish collected. A line was not connected when only one individual was collected.

In the text
thumbnail Figure 5.

Seasonal changes in the prevalence (A) and mean intensity (B) of metacercariae in Chrysaora pacifica from June 2010 to September 2012. Lepotrema clavatum, open square; Cephalolepidapedon saba, open circle; Opechona olssoni, open triangle. n: Number of jellyfish collected. A line was not connected when only one individual was collected.

In the text
thumbnail Figure 6.

Seasonal changes in the prevalence (A) and mean intensity (B) of metacercariae in Cyanea nozakii from June 2010 to September 2012. Lepotrema clavatum, open square; Cephalolepidapedon saba, open circle; Opechona olssoni, open triangle. n: Number of jellyfish collected.

In the text
thumbnail Figure 7.

Mean intensity of metacercariae of each species in host jellyfish collected from June 2010 to September 2012. Error bars indicate standard deviations. Different letters denote significant differences among hosts (Steel-Dwass test, p < 0.05).

In the text
thumbnail Figure 8.

Relationship between bell diameter and intensity of all metacercariae. r: correlation coefficient. (A) Aurelia aurita s.l., (B) Chrysaora pacifica, (C) Cyanea nozakii.

In the text
thumbnail Figure 9.

Juvenile fish associated with jellyfish collected from the Seto Inland Sea. (A) Psenopsis anomala associating with Cyanea nozakii (arrows). (B) Psenopsis anomala. (C) Trachurus japonicus. (D) Thamnaconus modestus.

In the text
thumbnail Figure 10.

Nematocysts (A) and metacercaria of Opechona olssoni (B) observed in the gut of a juvenile butterfish, Psenopsis anomala (standard length: 6.6 cm), collected in August 27, 2010. Abbreviations: Os, oral sucker; Ph, pharynx; Vs, ventral sucker; In, intestine.

In the text
thumbnail Figure 11.

Dual isotope plot of δ13C and δ15N. (A) Psenopsis anomala and its host jellyfish, (B) Thamnaconus modestus and its host jellyfish, (C) Trachurus japonicus and its host jellyfish. Dotted lines indicate pairs of an associated fish and its host jellyfish which were collected together. Abbreviations: BD, bell diameter of host jellyfish (cm); SL, standard length of associated fish (cm).

In the text

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