The Effects of the Trematode Bucephalus Polymorphus on the Reproductive Cycle of the Zebra Mussel Dreissena Polymorpha in the Drava River

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The Effects of the Trematode Bucephalus Polymorphus on the Reproductive Cycle of the Zebra Mussel Dreissena Polymorpha in the Drava River DOI: 10.2478/s11686-008-0011-1 © 2008 W. Stefañski Institute of Parasitology, PAS Acta Parasitologica, 2008, 53(1), 85–92; ISSN 1230-2821 The effects of the trematode Bucephalus polymorphus on the reproductive cycle of the zebra mussel Dreissena polymorpha in the Drava River Jasna Lajtner1*, Andreja Luciæ1, Miljenko Marušiæ2 and Radovan Erben1 1Department of Zoology, Faculty of Science, University of Zagreb, Rooseveltov trg 6, HR-10000 Zagreb; 2Department of Mathematics, University of Zagreb, Bijenièka 30, HR-10000 Zagreb; Croatia Abstract The effects of the trematode Bucephalus polymorphus on the reproductive cycle of the zebra mussel Dreissena polymorpha were examined in mussel populations from the Drava River. The reproductive cycle was studied by histological examination of the gonads and quantified by an image analysing system to determine changes in volume of the entire visceral mass, gonads, digestive glands and in particular the volume of trematodes. Results confirmed that (1) gonads of D. polymorpha were affect- ed by B. polymorphus infection more than any other organ and (2) development of cercariae in sporocysts of B. polymorphus coincides with host gonad maturation. This is the first study in which the image analysing system was used to determine the effect of trematodes on the reproductive cycle of D. polymorpha. Also, this is the first record of sporocysts of B. polymorphus in D. polymorpha in this part of Europe. Keywords Bucephalus polymorphus, Dreissena polymorpha, sporocyst, cercariae, Drava River, Croatia Introduction Many studies of biology and ecology of D. polymorpha have been conducted (Morton 1969, Walz 1973, Stañczykow- The freshwater mussel Dreissena polymorpha (Pallas, 1771) ska 1977, Lewandowski 1982). However, investigations of has become one of the most dominant species in many lakes diversity, distribution and significance of endoparasites of and rivers of Europe, since it began spreading from the Cas- D. polymorpha have become important only during the past pian area in the early 19th century (Stañczykowska 1977). In decade. These studies include Dreissena’s mantle-cavity cili- the mid-1980s, it could occasionally be found in the Great ates (Laruelle et al. 1999, Burlakova et al. 2000, Karatayev et Lakes of North America where it is suspected to have entered al. 2000), intracytoplasmic prokaryotes (Molloy et al. 2001) via ballast water discharge (Hebert et al. 1989), and today and endosymbiont assemblages detected in Dreissena popu- D. polymorpha spreads rapidly over the Nearctic region. This lations in Russia (Kuperman et al. 1994, Molloy et al. 1996) success of D. polymorpha could be attributed to the ability of and Belarus (Karatayev et al. 2000). adults to adhere to hard surfaces with their byssus, to devel- To date, seven genera of trematodes parasitic in D. poly- opment by free-swimming veliger larvae, and to their extraor- morpha have been described: Bucephalus (Digenea, Buce- dinarily high fecundity (Stañczykowska 1977, Borcherding phalidae), Phyllodistomum (Gorgoderidae), Echinoparyphium 1991). and Echinostoma (Echinostomatidae), Sanguinicola (Sangui- In Croatia, D. polymorpha is a new species which began to nicolidae), Leucochloridiomorpha (Brachylaemidae) and As- colonize the Drava River ecosystem during the 1980s (Erben pidogaster (Aspidogastrea, Aspidogastridae) (Conn and Conn et al. 2000, Lajtner et al. 2004). Since then, it has spread 1995, Molloy et al. 1997, Laruelle et al. 2002). upstream to the town of Varaždin and this process is still in In the life cycle of Bucephalus polymorphus (Baer, 1827), progress (Lajtner et al. 2004). D. polymorpha is the first intermediate host (Molloy et al. *Corresponding author: [email protected] 86 Jasna Lajtner et al. Œl¹ski 1997). The life cycle starts with the development of the earli- digestive gland, byssus gland, foot, parts of the adductor mus- est larval stage, the miracidium, which enters the mantle cav- cle) were separated from the remaining tissues (gills, mantle, ity of the mussel via water and penetrates the visceral mass, heart, kidneys, parts of adductor muscle), fixed in Bouin’s fix- especially in the gonad area. Here, the miracidium develops ative, dehydrated in an ascending alcohol series and chloro- into the sporocyst which is of irregular shape with many form and embedded in Paraplast Plus (Sigma P-3683, melt- branches. The next developmental stage, the cercaria, devel- ing point 56°C). Each visceral mass was completely cut in ops within the sporocyst. After completing their development, transverse sections (10 µm); thereby enabling us to record the the cercariae exit the mussel mantle cavity and enter the sec- length of the visceral mass (distance from the first to the last ond intermediate host via water. Most frequently, these hosts section). During this process, 20 sections were taken along the are cyprinid fishes, in which the metacercarial stage develops. whole visceral mass, stained with Mayer’s haemalaun (Merck) The final hosts are also fishes, infected with metacercariae and eosin and mounted in Canada balsam (Romeis 1968). The while eating infected fish. Metacercariae develop into adult stage of gametogenic development was described using a four- trematodes and become sexually mature. After fertilisation, a step qualitative evaluation, as reported by Gist et al. (1997): new life cycle starts (Molloy et al. 1997). stage 0 = gonad inactive; stage 1 = developing; stage 2 = pre- This paper focuses on infections of B. polymorphus in spawn; stage 3 = postspawn. D. polymorpha and is a further contribution towards under- For ten mussels, the areas of the whole visceral mass, go- standing the endoparasites of this mussel. It presents histo- nads, digestive gland and trematodes were measured using an logical photomicrographs illustrating the precise location of image analysing system (LUCIA G 4.81) according to Bor- trematodes in the visceral mass. Also, by measuring the vol- cherding (1991). To calculate volume, the mean tissue areas of ume of the gonads, digestive glands and other organs of the each mussel were multiplied by the corresponding length of visceral mass and comparing these data to data for uninfect- the visceral mass. In addition, indices of gonad, digestive ed mussels, an attempt was made to determine the impact of gland and other tissues of the visceral mass were calculated trematodes on the reproductive cycle of D. polymorpha. as the percentage of tissue to visceral mass volume (Borcherd- ing 1991). Materials and methods Statistical analyses All statistical analyses were carried out using SAS System Field sampling for Windows. The MANOVA test was used to test for differ- Mussels were collected on eight field trips from January to ences between infected and uninfected mussels. The Wilcox- December 2000, each of approximately 35 to 40 days. The on rank sum test was used to establish differences for a par- collecting site was immediately offshore of the Drava River ticular variable. P-values less than 0.05 (p<0.05) were con- (46°19′N, 16°44′E), approximately 1 km downstream of the sidered statistically significant. dam of the Dubrava hydro-electric power plant, at depths ranging from 0.3 to 0.5 m. Current velocity was generally lower than 0.50 m/s. Mussels were scraped from small rocks, Results collected by wading. On each sampling date, 50 specimens of D. polymorpha were collected. Examination of the histological preparations indicated that of Physical and chemical parameters including water tem- 80 analysed mussels, 17 (21.3%) were infected with B. poly- perature, °C (range 8.20–22.00), pH (range 7.70–8.15), dis- morphus. Twelve (70.6%) of these were females, three were solved oxygen, mg/l (range 8.20–16.70), calcium, mg/l (range males (17.6%) and two (11.8%) were hermaphrodites. Infect- 38.40–46.40), total hardness, mg CaCO3/l (range 132.00– ed mussels were found at each sampling date. 168.00), alkalinity, ml 0.1 N HCl/1-m (2.30–2.70) and micro- biological parameters, chlorophyll a, mg/m3 (range 0.06–2.52) Reproductive cycle of Dreissena polymorpha were recorded at each sampling date. Gametogenesis (oogenesis and spermatogenesis) (gonad stage 1) started in autumn and continued through winter and Histological procedures and tissue measurements early spring. Gonad development was accelerated in spring Shell length, shell width and shell height of all mussels were with the rise of water temperature while first mature oocytes measured with vernier callipers. Afterwards, thirty randomly- and spermatozoa were recorded already in March (gonad stage selected mussels were submitted for length-dry mass analysis. 2). Spawning occurred in May and June, which was confirmed The results of these analyses are being prepared separately for by a large number of mussels at gonad stage 3. Temperature publication. Other mussels, with an approximate shell length and sufficient food resources are the main triggers that induce of 26.0 ± 2 mm, were chosen for histological analysis. The synchronized and massive spawning (Borcherding 1991, Gist visceral mass of mussels (containing gonads, stomach, gut, et al. 1997, Wacker and von Elert 2003). Already in April, the The effects of Bucephalus polymorphus on D. polymorpha 87 Stanis³a water temperature in the Drava River was above 12°C, while Site selection of the parasites chlorophyll a values were at the highest level (2.52 mg/m3). Bucephalus polymorphus was identified in histological sec- Mussels in the rest stage (gonad stage 0) were already tions by the shape of its sporocysts, its position in the mussel found in August and some mussels remained in this stage until body and the morphological characteristics of the cercariae January. The greatest number of mussels in the rest stage was according to Laruelle et al. (2002) (Fig. 1). observed in October. Fig. 1. Gonads of Dreissena polymorpha filled with sporocyst branches containing several developmental stages of cercariae of Bucephalus polymorphus: A. Accumulation of haemocytes at the site of first infection. B. Early stage of cercarial development.
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