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1 December 2011 Frequency of black spot disease in Cobitis cf. turcica from Pınarbaşı Springs (Haymana, Turkey)
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During a survey on the biology of Cobitis cf. turcica living in Pınarbaşı Springs (Haymana district, Turkey), symptoms of black spot disease were frequently observed on the specimens. Of the 1295 loach collected, 240 (19 %) specimens were found to be infected with metacercaria of Posthodiplostomum cuticola, a common digenean parasite causing black spot disease in freshwater fish in Eurasia. During spring and autumn, the infection rate was significantly higher than during winter and summer, most probably due to the increasing density of migration of birds in this area. No statistically significant difference was found in condition, weight and length between infected and non-infected specimens; indicating low physiological effects of the encysted metacercaria on the host specimens. However, the prevalence of black spot had a tendency to decrease with age, remarking a higher mortality rate of infected specimens. This increased mortality rate seems to be the most important impact of an infection with metacercaria for a Cobitis population.


Parasites may have considerable impacts on many fish populations and parasitic infections are among the significant factors that may affect host natural populations (Barber & Poulin 2002). However, studies on parasite fauna of fish are more often focused on commercially important species. Spined loaches are widespread through Eurasia and known to be host for numerous parasite species and important secondary hosts for many other parasites (Zrnčić et al. 2009). Parasitological examinations of loach populations in Europe revealed infections caused by trematode species Diplostomum sp., Tylodelphys clavata, Allocreadium transversale, Posthodiplostomum cuticola, Metorchis xanthosomus, Echinostomatidae gen. sp., (Robotham & Thomas 1982, Halačka et al. 2000, Popiołek & Kotusz 2003, 2004); nematode species Rhabdochona ergensi (Popiołek & Kotusz 2003); cestodes Ligula colymbi and Neogryporhynchus cheilancristrosus (Halačka et al. 2000, Scholz et al. 2004, Kessler et al. 2009).

Black spot is a common fish disease easily recognisable by the presence of encysted metacercariae surrounded by an accumulation of blackspots of melanin in the skin, muscle and fin (Lasee 1995). Many species of digenean trematodes cause blackspot disease in most freshwater fish species. The life cycle of these trematodes is complex and involves a series of hosts; fish serve as an intermediate host in the development of parasites. Infection occurs when a fish encounters free swimming cercariae that penetrate its integument and await the opportunity to pass to the final host (bird) when the fish is eaten (Laase 1995). In response to the metacercarial cyst, the fish forms a capsule of connective tissue that contains melanophores. In Europe, the most common agent of blackspot disease is Posthodiplostomum cuticola (Ondračková et al. 2002). Blackspot disease caused by metacercaria of P. cuticola in loach populations were reported by Halačka et al. (2000) and Popiołek & Kotusz (2003). Studies on the parasites of Cobitis are very rare in Turkey. Kartal & Öztürk (2009) reportedthe occurrence of Gyrodactylus cobitis from C. simplicispina, and Keskin & Özeren (2002) has presented that blackspot was frequently found on C. simplicispina from Sakarya River Basin. But in this study P. cuticola was found on Cobitis cf. turcica from the closed basin of Central Anatolia.

Cobitis cf. turcica is an endemic loach distributed throughout the Tuz Lake Basin in Central Anatolia. Although this species is listed as endangered in the IUCN Red List since 2005, there is no detailed information about its ecology and biology. We frequently observed black spots on the fish body, and the main goal of this study is to point out high prevalence of black spot disease, which could be regarded as a potential future threat for this endangered loach species.

Study Area, Material and Methods

Fish samples were collected from a semiarid area where continental climate prevails. The species is dwelling in a small brook fed by Pıarbaşı Springs (39°14′21″ N 32°44′59″ E) and flowing into Kozanlı-Gök (Saz) Lake which is an important bird area (Magnin & Yarar 1997).

Sampling was performed along 100 m of the watercourse, where depth ranged from 50 to 80 cm, width was about 2 to 3 m and the current was low. The bottom was mainly sandy, muddy and covered with aquatic vegetation and willows. The water temperature ranged between 8.2 °C (March) and 19.3 °C (June) (Fig. 1). The minimum and maximum dissolved oxygen contents were 4.35 mg/1 and 11.49 mg/1 respectively. Samples of Cobitis cf. turcica were collected by a dip net with a mesh size of 1 mm. A total of 1295 specimens were caught on a monthly basis between March 2003 and August 2004. Total and standard lengths of anaesthetized fish were measured in mm and weighed in mg. Scales were used for age determination. The condition factor was determined from the length and weight of each specimen using Fulton's condition factor (KF) given as KF= W105/TL3 (W: body weight in mg and TL: total length in mm). Uninfected specimens were released back into the water after all measurements were completed, the infected specimens were preserved in 4% buffered formaldehyde for laboratory examination.

The number of cysts on fish was counted and recorded. To identify the parasite species, some parasites were preserved in 70 % ethyl alcohol. Fixed parasite specimens were stained with aceto-carmine and they were dehydrated into alcohol series and mounted in slides with Canada balsam. The determination of parasites was performed according to Bykhovskaya-Pavlovskaya et al. (1962) and Markevich (1951).

The level of parasite infection was estimated according to Bush et al. (1997). The parasitological indices prevalence (percentage of infected hosts), mean intensity (average intensity of the parasite species among the infected members of the host species) and mean abundance (number of parasite in a sample of host divided by the total number of hosts) were calculated. Total length, weight and condition of infected and non-infected specimens in each age class were compared by the Mann-Whitney U-test. Statistical analyses were carried out by SPSS™ 16 package program. The p < 0.05 was considered as significant.

Fig. 1.

Monthly variations in water temperature, number of infected and non-infected specimens.


Results and Discussion

Diagnosis of blackspot disease is usually by presence of dark areas on the surface of the fish. In the present case, cysts from the skin of Cobitis cf. turcica were elliptical with about 1 mm in diameter. The metacercaria body consisted of a wide anterior segment and a small, narrow posterior segment. The oral sucker measured 0.065 × 0.060 mm and the ventral sucker measured 0.080 × 0.080 mm. The ventral sucker is located at the middle of the body. The Brandes' organ was round and bigger than the ventral sucker. There were two intestinal trunks ending in the posterior part of body. The excretory system opening is located at the posterior body tip. On the base of these characters, we identified the parasite as Posthodiplostomum cuticola.

In this study, metacercaria of P. cuticola in black cysts were observed primarily on the skin, fins and gills of fish. A total of 240 infected individuals by P. cuticola were found in 1295 examined specimens of Cobitis cf. turcica. Monthly variation of water temperature and both the number of infected and non-infected specimens were depicted on Fig. 1. Although cold Continental climatic conditions prevail in the study area, due to the nature of spring water the temperature of stream never decreases under 8 °C during the winter and even in very hot days of summer the water temperature did not reach up to 20 °C.

Environmental conditions of the study area were convenient for the occurrence of blackspot disease. The sampling area is a small stream with slow water flow, soft muddy bottom and abundant vegetation, a suitable microenvironment for both snails and Cobitis cf. turcica, since the snails are the intermediate hosts for P. cuticola, cercariae that leave the snail may easily infect this benthic fish. Moreover, Pınarbaşı Springs is close to Kozanlı-Gök (Saz) Lake, which is considered as an important bird area and the piscivorous birds (definitive hosts of P. cuticola) may be one of the major causes for spreading the parasitological infections in this area.

The prevalence of P. cuticola was about 19 % for all specimens. It was determined that the prevalence of black spot had a general tendency to decrease with age (Fig. 2). However, this may be due to the fact that massively infected individuals may have died and not be represented in samples as noted by Berra & Au (1978). On the other hand, the prevalence was 27 % at age of 0, this figure reached to 7 % at V age group (Fig. 2). Although age VI seemed to have the highest prevalence, it should be taken into consideration that the number of samples at this age is only four and half of those specimens that were infected. As the number of samples at age VI is not sufficient, this group is not taken into account during evaluation. It is still a matter of debate on whether the intensity of strigeoid trematode infection increases in older fish (Steedman 1991).

Juvenile fish are more susceptible to blackspot disease. Severe infections of young fish may cause spinal curvature, abnormal muscle development or death and infected adults may be susceptible to secondary infections (Steedman 1991). However, we observed a single sample with spinal abnormality among 1295 specimens.

Fig. 2.

Variations in prevalence of blackspot in different age groups of Cobitis cf. turcica.


We observed seasonal variation for prevalence such as an increase during spring and autumn (Fig. 3). Lowest prevalence was observed in summer with 14.47 %. There is little evidence to suggest strong seasonality in the abundance of black spot disease in fish populations (Steedman 1991). There may be a relation with the bird migrations and the seasonality in abundance, as many migratory birds use both Gök Lake and remains of Samsam Lake adjacent to the study area intensively during migration in spring and autumn, and may act as a vector of this parasite.

Fig. 3.

Seasonal variations in prevalence of blackspot in Cobitis cf. turcica.


The condition factor, weight and length of infected and non-infected individuals in the same age groups were compared and statistically no significant difference was found (Mann-Whitney U-Test, p > 0.05). Total length, weight and condition factor of the infected and non-infected specimens are given in Table 1. Ondračková et al. (2006) claimed that condition factor was more poor in fish with higher prevalence of P. cuticola. However, in contrary to our expectations, the result of this study revealed that the condition factor was not significantly different between infected and non-infected individuals. Despite of the high prevalence, insignificance of correlation coefficient (TL, W and KF) may be explained by low mean intensity and mean abundance.

The length-weight relationship for infected specimens (W =0.1 × 10-4TL2.82) was not statistically different that of non-infected fish ( W = 0.1 × 10-4 TL2.77) (Student's t-test, p > 0.05). Both data are presented in Table 1 and length-weight relationship equations indicated that growth rate of infected fish were similar to non-infected individuals.

Table 1.

Total length (TL), weight (W) and condition factor (KF) with mean values, standard deviation (SD) for infected and non-infected Cobitis cf. turcica specimens and mean intensity (MI) and mean abundance (MA) values in different age groups (N: number of specimens).


Mean intensity and mean abundance were found as 4.68 and 0.86 respectively for all specimens (Table 1). It was determined that both mean intensity and mean abundance had the tendency to decrease with age. Due to the high number of infected specimens, more intense parasite infection may be expected in the studied population. But our results revealed that the infection intensity was relatively low, this may be due to the lost of black spots caused by the friction between the fish skin and substratum.

Males were predominant with ratio of 1 : 0.59 (822 male and 483 female). Although males were more abundant in the population, the prevalence of black spot in males was lower (16%) than in females (30%). The presence of parasites has great influence on the longevity of the organism so the prevalence of blackspot should be considered carefully. In his review, Steedman (1991) reported that several studies have shown that black spot infections were most severe in stream fishes that inhabited pool areas, as we have observed in the presented case. Pollution may have effects on the abundance of snails, which are the intermediate host of P. cuticolci. Although we do not have any quantitative data on the pollution, we observed organic material discharging from the farms that may cause to the pollution in the creek. Presence of blackspot disease not only reduces the aesthetic value of the fish, it may also cause mortality especially when infections are heavy and water temperature declines (Lasee 1995) and changes in fish behaviour (Mikheev & Pasternak 2006). On the other hand, fish infected by P. cuticola appear to be easier prey for predators due to the formation of clearly visible black spots (Ondračková et al. 2006). But this claim does not seem to be acceptable for the case of Cobitis cf. turcica as this is a bottom dwelling species.


We thank Ms. Alexandra Newlon for checking the language of the text as a native speaker and two anonymous referees and associate editor for their constructive critics and comments. The samples could not be caught without valuable efforts of Dr. Mehmet Ekmekçi.



Barber I. & Poulin R. 2002: Interactions between fish, parasites and disease In: Hart P.J.B. & Reynolds J.D. (eds.), Handbook of fish biology and fisheries Vol. I: Fish biology. Blackwell Sciences Ltd. : 359–385. Google Scholar


Berra T.M. & Au R. 1978: Incidence of black spot disease in fishes in Cedar Frok Creek, Ohio. Ohio J. Sci. 78: 318–322. Google Scholar


Bush A.O., Lafferty K.D., Lotz J.M. & Shostak A.W. 1997: Parasitology meets ecology on its own terms: Morgolis et al. revisited. J. Parasitol. 83: 575–583. Google Scholar


Bykhovskaya-Pavlovskaya I.E., Gussev A.V., Dubinina M.N., Izyumov N.A., Simimova T.S., Sokolovskaya I.L., Shtein G.A., Shulman S.S. & Ephstein V.M. 1962: Key to parasites of freshwater fish of the USSR. Izdatel'stvo Akademi Nauk SSSR Moskva-Leningrad. Israel Program for Scientific Translation , Jerusalem . ( Traslated from RussianGoogle Scholar


Halačka K., Lusková V. & Lusk S. 2000: Contribution to the occurrence of parasites in Cobitis elongatoides and Cobitis elongatoides x C. sp. Folia Zool. 49 (Suppl. 1): 215–218. Google Scholar


Kartal K. & Öztürk M.O. 2009. Investigations of ectoparasite fauna of some fish species (Cyprinus carpio Linnaeus, 1758; Cobitis simplicispina Hanko, 1924) from Lake Akşehir (Konya). Türkiye Parazitoloji Dergisi 33: 101–106. ( in TurkishGoogle Scholar


Keskin N. & Özeren C. 2002: The occurrence of blackspot disease in Cobitis simplicispina from the Kirmir Stream, Turkey. 2nd international conference on loaches of the genus Cobitis and related genera, September 9-13, 2002 , Olsztyn, Poland : 37. Google Scholar


Kessler M., Vetemaa M., Saks L. & Saat T. 2009: Occurrence of Ligula colymbi (Cestoda) in spined loach (Cobitis taenia) and its effects on reproduction and growth of the host. Boreal Environ. Res. 14: 932–936. Google Scholar


Lasee B.A. 1995: Introduction to fish health managemet, 2nd edit. U.S. Fish and Wildlife Service : 55. Google Scholar


Magnin G. & Yarar M. 1997: Important bird areas in Turkey. Dogğal Hayati Koruma Derneği , İstanbul, Turkey.  Google Scholar


Markevich A.P. 1951: Parasitic fauna of freshwater fish of the Ukrania. Israel Program for Scientific Translation.  Google Scholar


Mikheev V.N. & Pasternak A.F. 2006: Defense behavior of fish against predators and parasites. J. Ichthyol. 46 (Suppl. 2): 173–179. Google Scholar


Ondračková M., Dávidová M., Gelnar M. & Jurajda P. 2006: Susceptibility of Prussian carp infected by metacercariae of Posthodiplostomum cuticola (v. Nordmann, 1832) to fish predation. Ecol. Res. 21: 526– 529. Google Scholar


Ondračková M., Jurajda P. & Gelnar M. 2002: The distribution of Posthodiplostomum cuticola metacercariae in young-of-the-year cyprinid fishes. J. Fish Biol. 60: 1355–1357. Google Scholar


Popiołek M. & Kotusz J. 2003: Endoparasitic helminthes of fishes of the genus Cobitis from Poland. Folia Biol. Kraków 51: 173–178. Google Scholar


Popiołek M. & Kotusz J. 2004: Metacercariae of digeneans occurring in Cobitis elongatoides Bacescu et Maier, 1969 (Pisces: Cobitidae). Wiad. Parazytol. 50: 609–613. ( in PolishGoogle Scholar


Robotham P.W.J. & Thomas J.S. 1982: Infection of the spined loach, Cobitis taenia (L.) by the digenean Allocreadium transversale (Rud.) J. Fish Biol. 21: 699–234. Google Scholar


Scholz T., Bray R.A., Kuchta R. & Repova R. 2004: Larvae of gryporhynchid cestodes (Cyclophyllidea) from fish: a review. Folia Parasitol. 51: 131–152. Google Scholar


Steedman R.J. 1991: Occurrence and environmental correlates of black spot disease in streem fishes near Toronto, Ontario. Trans. Am. Fish. Soc. 120: 494–499. Google Scholar


Zrnčić D., Šoštarić B., Caleta M., Buj I., Zanella D. & Šurmanović D. 2009: Occurrence of parasites in Cobitidae from Croatian rivers draining into two different watersheds. J. Appl. Ichthyol. 25: 447–450. Google Scholar
Şerife Gülsün Kirankaya and Fitnat Güler Ekmekçı "Frequency of black spot disease in Cobitis cf. turcica from Pınarbaşı Springs (Haymana, Turkey)," Folia Zoologica 60(4), 350-354, (1 December 2011).
Received: 25 November 2010; Accepted: 1 May 2011; Published: 1 December 2011

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