Herpetologica Romanica Vol. 2, 2008, pp.21-26 The analysis of the trophic spectrum of a Pelophylax ridibundus population from Vadu area, Constanta county, Romania Anamaria, DAVID1,*, Nicoleta DIMANCEA2, Adrian PAL1 and Katalin CSERVID1 1. University of Oradea, Faculty of Sciences, Department of Biology, Universitatii str.1, Oradea 410087, Romania 2. University of Oradea, Faculty of History and Geography, Department of Geography, Universitatii str.1, Oradea 410087, Romania * Coppersponding author: A. David, E-mail: [email protected] Abstract. The 43 analysed individuals were captured from a habitat near Vadu, Constanta county. All the frogs presented stomachal content, which suggests optimum feeding conditions in the biotope inhabited by this population. The most important categories of prey taxa are represented by the terrestrial Crustacean Isopoda, Arahnidae-Araneidae and Coleopteras. The remains of vegetales and shed-skin were also present in the frogs' stomach. Key words: Pelophylax ridibundus, differences between the sexes, trophic spectrum Introduction Although the components of the trophic spectrum are more or less identical for all of the amphibians, the role of some trophic objects are different. Moreover data of this kind offers valuable information regarding the condition of the habitat, the available resources which can ensure a lasting development of the Amphibian populations which are found here. Pelophylax ridibundus is an almost exclusively aquatic species, a good swimmer, being seen only in the water or in the nearby area (Berger 1973). It lives in permanent waters, prefering especially the deep and big lakes (Rybacki & Berger 1994 ; Cogălniceanu et al. 2000). The trophic spectrum of this species was studied especially in the western part of the country, in this region a series of studies have been conducted regarding the trophic spectrum of some nonhibernating populations of Pelophylax ridibundus (Covaciu-Marcov et al. 2003, 2005; Sas et al. 2004a, Peter et al. 2005). In Constanta county the food composition was also analysed from a frog population from Dobromir locality (Szeibel et al. 2008). In this study we observed the feeding particularities depending on the sex and on the ontogenetic development stage. Materials and methods The study took place in April 2007,when we preserved the stomachal contents of 43 individuals :22 females, 15 juveniles, and only 6 males. The habitat from which we analysed the population is found near the beach, so the altitude is therefor low (5 metres). We also mention that the investigated area is part of the Danube Delta Biosphere Reservation, which is affected by man. We used the stomach-flushing method (Cogalniceanu 1997) in order to preserve the stomachal contents. This method has the advantage that one can perform feeding studies without killing the individuals. The samples were preserved separately, in a 4% formaldehyde solution and stored in airtight test tubes, which contained labels with the frog's sex. After the conservation of the stomachal contents, the studied individuals were released as close as possible to the place where they were captured, in order to reduce the impact of our activity. We analysed and determined the samples in the laboratory using a magnifying glass and scientific literature (Crisan & Cupsa 1999; Radu & Radu 1967). The aim of the study was to determine the differences that appear between the sexes, the amount and the frequency Herpetol. Rom, 2, 2008, Romania 22 of the prey taxa, the feeding intensity and the origin of the prey. Results and discussions From a total of 330 consumed prey, 186 were identified in the stomachal contents of the females, 84 in the case of the juveniles and 60 in that of the males. Besides animal prey, in the stomachal contents were also identified vegetales and shedskin. The amount of the vegetales is 100% in the case of the males, followed by the females with 63.6% and the juveniles with 60%. We consider that the analysed individuals swallowed them together with the animal prey, in the case of the males the high value of the vegetal fragments is due to the smaller amount of analysed individuals. The accidental consumption of vegetal fragments is suggested by the observation that adult Amphibians are, as far as the feeding habits are concerned, carnivore-insectivore, and that only their larvae are phytophagous-detritivore (Reeder 1964) and stressed by the fact that amphibians consume mainly mobile prey (Zimka 1966). There are theories that state that amphibians consume vegetal fragments for the water found in them, or in order to eliminate intestinal parasites or crush the exoscheleton of the swallowed prey (Evans & Lampo 1996). The amount of stomachal contents with shedskin is higher in the case of the males 16.7%,followed by the juveniles with 13.3%, and the females with 9.09%. The consumption of shed-skin is considered by some authors as a way of recycling epidermal protein (Weldon et al. 1993), these can be easily swallowed from the water, or ingested as a result of the confusion between the prey and other amphibians which are in motion. Shed-skin don't represent a trophic basis that amphibians search, but are rather consumed in the nonfavourable periods, as a result of the absence of other categories of trophic elements. Shed-skin have also been identified in the stomachal contents of other amphibians, such as Rana arvalis (Sas et al. 2003a), Herpetol. Rom, 2, 2008 David, A. et al. Rana dalmatina (Aszalos et al. 2005), Bombina bombina (Sas et al. 2003b), Bombina variegata (Sas et al. 2004b, Peter et al. 2006), Hyla arborea (Kovacs et al. 2007) Pelophylax lessonae (Sas et al. 2005) Pelophylax kl. esculentus (Sas et al. 2007, 2009-online.first). As far as the feeding intensity is concerned, all of the analysed frogs present stomachal contents, the necessary prey being available in order to satisfy the frog's energetic needs. The average number/individual is 10 in the case of the males, which consumed a small number of prey categories (14 categories) in a large amount; in the case of the females this is 8.45 (the prey taxa were grouped in 19 categories), their food being more diverse; and in the case of the juveniles the average number of prey/individual is 5.6 (Table 1). The amount of the prey taxa emphasizes certain differences between the sexes, respectively depending on the stage of ontogenetic development. This fact shows that there are distinctions regarding the way of obtaining food among the males, females and juveniles. In the case of the males the highest value is occupied by the aquatic Gasteropodes and the terrestrial Isopodas with a percentage of 25%. Unlike the males, in the case of the females the aquatic snails have a vey low rate, 0.54%, the majority being held by the terrestrial Isopoda, 27.4% (Table 2), in a whole the females consumed a higher amount of terrestrial-originated taxa. The second place, both in the case of the males and females, is occupied by the Arahnida-Araneida, their value being 20%, and 17.7% in the case of the females. This categorie of prey is mentioned in the scientific literature as important in another population of Pelophylax ridibundus (Ylmaz & Kutrup 2006). In the case of the juveniles, the spiders hold first place with a value of 29.8%.The Araneida represent an important group which can be easily captured from the vegetation from the habitat and therefore are accesible for both adults and juveniles. Heteropteras have a lower value in the case of the males, 5%, followed by other taxons such as Coleopteras Carabidae (6.67%), Arahnidae The analysis of the trophic spectrum of a Pelophylax ridibundus population from Vadu area (Romania) Pseudoscorpionidae (3.33%) and undetermined Coleoptera s ( 3.33%). In the case of the females the majority of the taxons have terrestrial origin. Thus, we determined terrestrial Heteroptera (4.84%), Lepidoptera larvae (3.23%), undetermined Coleoptera (9.68%), Coleoptera Carabidae (3.23%) and Diptera Brahicera (4.84%). It is noticeable the appearance of larger preys in the case of the females, such as Coleopteras, Araneida, Isopoda, but also the presence of Lepidoptera larvae. These are more profitable from an energetic point of view. On the other hand, the larvae are richer in lipide contents and thus have a higher nutritive value (Brooks et al. 1996). In the case of the males the terrestrial Crustacean Isopoda have the highest frequency, which were easily captured from the wet ares near the pond, followed by the Arahnidae Araneidae, aquatic Heteropteras, undetermined Coleopteras and Coleopteras Carabidae, which have a lower frequency. In the case of the females first place is occupied by the Arahnidae Araneidae, which are followed by the undetermined Coleopteras and the terrestrial Heteropteras. The Crustacean Isopoda have a very low frequency rate. This fact presents great interest because of the first place held by them in the case of the amount of taxons. They were consumed in a 23 large quantity only by certain individuals from the population, and the spiders are available for a larger number of frogs, but in a smaller amount. In the case of the juveniles the situation is simmilar to that of the adults, thus in the first place one can find the Arahnidae Araneidae, followed by the undetermined Coleopteras, the Nematocera Diptera and the aquatic Heteropteras. The Arahnidae Araneidae have the highest value in the case of the females, 72.7%. The same category holds first place in the case of the juveniles, 86.7% and the terrestrial Crustacean Isopoda in the case of the males, 83.3%. In the third place we can find the terrestrial Crustacean Isopoda with a relatively high frequency, 37.2%, followed by the aquatic Heteropteras, 25.6%, terrestrial Heteropteras, 23.3%, Coleopterae Carabidae, 20.9%. The relation between the frequency and the amount of the prey taxa emphasizes an almost homogeneous distribution of the trophic resources, which are relatively abundant in the habitat and are accesible for most of the individuals, and the fact that they don't select a certain prey taxa, but the most abundant one.The high value of both the frequency and the amount of the same taxa indicates that the whole population depends on the same feeding resources (Cogălniceanu et al. 2000b). Table 1. The total number of prey and the average number of prey/individual, the amount of the aquatic and terrestrial prey, the frequency of the vegetales and shed-skin Males Females Juveniles The total no. of prey/individual 60 186 84 The average no. of prey/individual 10 8.45 5.6 % aquatic prey 35.01 20.97 17.85 % terrestrial prey 65.01 79 82.16 vegetales 100 63.6 60 shed-skin 16.7 9.09 13.3 Herpetol. Rom, 2, 2008 David, A. et al. 24 Table 2. The amount prey taxa in the case of the males, females and juveniles Males Females Juveniles Gasteropode-melci(t) 1.67 2.69 - Gasteropode-melci(a) 25 0.54 - Crustacee-Gamaride - 4.3 8.33 Crustacee-Izopode(a) - 7.53 1.19 Crustacee-Izopode(t) 25 27.4 10.7 3.33 - - Arahnide-Acarieni - - 1.19 Arahnide-Araneide 20 17.7 29.8 Colembole - 0.54 2.38 Heteroptere(a) 5 2.69 4.76 Heteroptere(t) - 4.84 2.38 Homoptere-Afidine - - 1.19 Lepidoptere (L) 1.67 3.23 2.38 Coleoptere-Dytiscide 1.67 5.91 1.19 Coleoptere-Dytiscidae (L) 1.67 - - Coleoptere-nedet. 3.33 9.68 13.1 Coleoptere-Carabide 6.67 3.23 1.19 Coleoptere-Coccinelide 1.67 - - Coleoptere-Curculionide - 1.08 - Coleoptere-Scarabeide - 0.54 - Coleoptere-Stafilinide - 1.61 1.19 1.67 - 2.38 Diptere-Nematocere - 1.08 8.33 Diptere-Brahicere - 4.84 7.14 1.67 0.54 1.19 Arahnide-Pseudoscorpionide Diptere-Nematocere (L) Hymenoptere-Formicide As far as the origin of the environment of the prey is concerned, we can observe that most of the prey have a terrestrial origin, despite the fact that this species is considered to be the most aquatic of the Ranide (Fuhn 1960). The capturing of the prey is not necessarely made from the terrestrial environment, these being accesible from the plants on the water, or even from the lustre of the water, or from its shores. In our study, the amount of the prey taxa is high in the cases when they are accesible from the plants (Araneida, Curculionidae). The Herpetol. Rom, 2, 2008 majority of terrestrial prey has been observed in other populations of Pelophylax ridibundus (Cicek & Mermer 2006, 2007). The males are those that consumed a larger amount of aquatic prey, 35.01%, this fact is due to the high value of aquatic Gasteropodes, which have been swallowed by these. The differences that appear in the feeding rate of the males, females and juveniles of Pelophylax ridibundus, indicate a more intensive feeding in the case of the females, respectively a higher fluctuation The analysis of the trophic spectrum of a Pelophylax ridibundus population from Vadu area (Romania) of the prey taxa in their contents, in comparison to the males and juveniles. This situation is due to the fact that the females need more energy in the laying of the eggs. Because of the larger body dimensions, they can consume different types of prey. They also have a higher mobility than the juveniles, which, due to the smaller size are limited to the consumption of prey of certain categories and which don't have capturing strategies as performed as the adults do. Conclusions The Crustacean Isopoda, Arahnidae, aquatic Gasteropoda and Coleopteras represent the most important prey taxa for the analysed population. The composition of the food is influenced by the environmental conditions, which can affect the developing rate of the potential prey, thus determining the constituing elements of the trophic spectrum of the analysed population. The similarities of the males, females and juveniles trophic spectrum indicate that the lake frog has a time-serving method of feeding, capturing the most abundant preys from the habitat. With regards to the origin of the prey taxa's environment we established that the majority of the studied individuals consumed terrestrial prey captured from the surface of the vegetation, or from the near-situated ares of the shore. As a result of the study, we concluded that the Pelophylax ridibundus population presents optimum feeding conditions in this habitat. Considering the fact that the habitat, from which the studied individuals belong to, is situated near a beach, the development of the turistic zones could lead to the disappearance of the Amphibian populated habitats, which will afterwards result in the extinction of them, thus studies dedicated to the analysis of the ecological requirements will help in understanding the necessities that they have, in order to ensure a lasting development. 25 References Aszalós, L., Bogdan, H., Kovács, É. H., Peter, V. I. ( 2005): Food composition of two Rana species on a forest habitat (Livada Plain, Romania), North-Western Journal of Zoology 1: 25-30. Berger, L. (1973): Some charachteristics of backcrosses within forms of Rana esculenta complex. Genetica Polonica 14 (4): 413-430. Brooks, J. S., Calver, C. M., Dickman, R. C., Meathrel, E. C., Bradley, S. J. (1996): Does intraspecific variation in the energy value of a prey species to its predators matter in studies of ecological energetics? A case study using insectivorous vertebrates. Ecoscience 3 (3): 247-251. Çiçek, K., Mermer, A. (2006): Feeding Biology of the Marsh Frog, Rana ridibunda Pallas 1771, (Anura, Ranidae) In Turkey’s Lake District. North-Western Journal of Zoology 2 (2): 57-72. Çiçek, K., Mermer, A. (2007): Food composition of the Marsh Frog, Rana ridibunda Pallas 1771, in Thrace. Turkish Journal Zoology 31: 83-90. Cogălniceanu, D. (1997): Practicum de ecologie a Amfibienilor – metode şi tehnici în studiul ecologiei Amfibienilor. Ed. Universităţii din Bucureşti. Cogălniceanu, D., Aioanei, F., Bogdan, M. (2000 a): Amfibienii din România, Determinator. Ed. Ars Docendi, Bucureşti. Cogălniceanu, D., Palmer, M. W., Ciubuc, C. (2000 b): Feeding in Anuran comunities on islands in the Danube floodplain, Amphibia-Reptilia, 22: 1-19. Covaciu–Marcov, S.D., Cupşa, D., Sas, I, Zsurka, R., CicortLucaciu, A.Şt. (2003): Spectrul trofic al unei populaţii nehibernante de Rana ridibunda (Amphibia) din apele termale de la Chişlaz, judeţul Bihor. Analele Universităţii din Oradea, Fasc Biologie 10: 97-109. Covaciu-Marcov, S. D., Sas, I., Cupşa, D., Bogdan, H., Lukács, J. (2005): The seasonal variation of the food of a nonhibernated Rana ridibunda Pallas 1771 population from the thermal lake from 1 Mai Spa, Romania. Analele Universităţii din Oradea, Fasc Biologie 12: 75-85. Crişan, A., Cupşa, D. (1999): Biologie animală I: Nevertebrate, Ed. Convex S.A, Oradea. Evans, M., Lampo, M., (1996): Diet of Bufo marinus in Venezuela, Journal of Herpetology 30: 73-76. Fuhn, I. (1960): Fauna R.P.R., Vol. XIV, Fasc. I, Amphibia. Editura Academiei R.P.R., Bucureşti. Kovács, E.H., Sas, I., Covaciu-Marcov, S.D., Hartel, T., Cupsa, D., Groza, M. (2007): Seasonal variation in the diet of a population of Hyla arborea from Romania. Amphibia-Reptilia 28: 485-491. Peter, V.I., Sas, I., Cupşa, D., Kovács, E.H., Bányai, G. (2005): Spectrul trofic al broaştei de lac, Rana ridibunda Pall. 1771 pe pârâul Peţea (jud. Bihor, România). Oltenia, Studii şi Comunicări, Ştiinţele Naturii 21: 157-162. Peter, V.I., Citrea, L., Aszaló, Á., Batta, Z., Szabó, M., Cioara, C. (2006): Analiza comparativă a spectrului de hrănire a două populaţii de Bombina variegata din Băiţa Plai (Judeţul Bihor, Romania), Analele Universităţii din Oradea, Fasc Biologie 13: 18-23. Herpetol. Rom, 2, 2008 26 Radu, Gh. V., Radu ,V. V. (1967): Zoologia nevertebratelor, Vol. 2, Ed. Did. şi Ped., Bucureşti. Reeder, W. G., (1964): The digestive tract. pp. 99-149. In Physiology of Amfibia. (Moore, J.A. - eds.). Academic Press, New York. Rybacki, M., Berger, L. (1994): Distribution and ecology of water frogs in Poland. Zoologica Poloniae 39 (3-4): 293-303. Sas, I, Covaciu-Marcov, S.D., Cupşa, D., Aszalos, L., Kovacs, E.H., Telcean, I. (2003a): Data about the trophic spectrum of a population of Rana arvalis of the Andrid area (Satu – Mare county, Romania). Bacău, Studii şi Cercetări Ştiinţifice, Biologie 8: 216-223. Sas, I, Covaciu-Marcov, S.D., Cupşa, D., Schirchanici, A., Aszalos, L. (2003b): Studiul spectrului trofic al unei populaţii de Bombina Bombina (Linnaeus 1761) din zona Resighea (judeţul Satu – Mare, România). Oltenia, Studii şi Comunicări Ştiinţele Naturii 19: 183-188. Sas, I., Kovács, É. H., Peter, V., Cupşa, D., Antal, B. (2004a): Hrănirea al unei populaţii nehibernante de Rana ridibunda Pal.1771. Analele Universităţii din Oradea, Fasc Biologie 9: 83-90. Sas, I, Covaciu-Marcov, S.D., Cupşa, D., Kovacs, E.H., Gabora M. (2004b): Data about the trophic spectrum of a population of Bombina variegata from Vârciorog area (Pădurea Craiului Mountains, Bihor county, Romania. Bacău, Studii şi Cercetări Ştiinţifice, Biologie 9: 124 – 130. Sas, I, Covaciu-Marcov, S.D., Cupşa, D., Cicort-Lucaciu, A.Ş., Antal, B. (2005): Food habits of Rana lessonae and Rana arvalis in Covasna county (Romania). Mediul Cercetare, Herpetol. Rom, 2, 2008 David, A. et al. Protecţie şi Gestiune, Proceedings volume, Cluj –Napoca 5: 359-367. Sas, I., Kovács, E.H., Covaciu-Marcov, S.D., Strugariu, Al., Covaci, R., Ferenţi, S. (2007): Food habits of a Pelophylax lessonae – Pelophylax kl. esculentus population from NorthWestern Romania. Biota – Race 8: 71-78. Sas, I., Covaciu-Marcov, S.D., Strugariu, A., David, A., Ilea, C. (2009-Online.First): Food habit of Pelophyhlax kl. esculentus females in a new recorded E-System population, from a forested habitat in North-Western Romania. Turkish Journal of Zoology 33: 1-5 Szeibel, N., Citrea, L., Memetea, A., Jurj, N., Condure, N. (2008): Feeding ecology of the Pelophylax ridibundus (Anura, Ranidae) in Drobomir, Romania. Biharean Biologist 2: 27-37. Weldon, P. J., Demeter, B. J., Rosscoe, R. (1993): A survey of shed skin-eating (dermatophagy) in amphibians and reptiles. Journal of Herpetology 27: 219-228. Ylmaz, Z.C., Kutrup, B. (2006): Seasonal changes in the diet of Rana ridibunda Pallas 1771 (Anura: Ranidae) from the Gorele river, Giresun, Turkey. Proceedings of the 13th Congress of Societas Europeea Herpetologica: 201-204. Zimka, J.R. (1966): The predacy of the field frog (Rana arvalis Nills.) and food levels in communities of soil macrofauna of forest habitats. Ekol. Pol. 14: 589-605.
© Copyright 2026 Paperzz