Article

Meleshko, Kravchenko (2012) Study of green frogs of the Iskov pond

Meleshko O.V., Kravchenko M.O. Investigation of the population system state of green frogs (Pelophylax esculentus complex) of the Iskyi pond of Zmiivskyi district of Kharkiv region // Visnyk Prykarpatskoho natsionalnoho universytetu imeni Vasylia Stefanyka. Seriia - Biolohiia. - Ivano-Frankivsk : Vyd-vo Prykarpatskoho natsionalnoho universytetu imeni Vasylia Stefanyka, 2011. - Vyp. 24. - S. 193-197.

The complex of Central European green frogs, Pelophylax esculentus complex, consists of two parental species — the pool frog, Pelophylax lessonae (Camerano, 1882), the lake frog, Pelophylax ridibundus (Pallas, 1771), and their hybrid (which has a name similar to a species) — the edible frog, Pelophylax esculentus (Linnaeus, 1758) [13]. One of the unusual features of this complex is that for diploid P. esculentus, hemiclonal (semiclonal) inheritance is characteristic: in hybrid frogs, one of the parental genomes passes into the gametes. This is achieved through premeiotic elimination of one genome, endoreduplication of the other (clonal) genome, and gametogenesis with the formation of identical gametes [5;15]. If, when crossing hybrid individuals, the offspring receives clonal genomes from the same parental species, its viability significantly decreases: such individuals do not reach sexual maturity [15].

29.06.2012
51

8

M
92 
25
II

n
92 
30 
7

m
92
25
26.07.2012 
122

N
6
697
224

SE
The obtained data make it possible to approximately establish the sex ratio in the studied HPS. We separately estimated the number of males and females using the Peterson method. Since no females were captured in the sample obtained during the first recapture (Table 1), sex structure was evaluated using data from the second and third recaptures. The obtained data are shown in Table 2.
Table 2. Sex ratio based on recapture results (designations see above)

I  29.06.2012 51 8 4 92 25
II 02.07.2012 74 30 7 286 82
III 26.07.2012 122 39 6 697 224

The three obtained population estimates (92±25, 286±82, and 697±224) differ significantly from each other. This discrepancy can be explained by the short time interval between the release of tagged individuals and the first and second recapture events. Probably, the calculations based on the first and second captures are not reliable: the tagged individuals did not have enough time to mix with other individuals in the population. At the same time, the third capture was carried out three weeks after the last release of tagged individuals, so, from the perspective of meeting the method's conditions (equal probability of capturing tagged and untagged animals), the population estimate obtained from its results can be considered quite correct. The obtained data allow for an approximate determination of the sex ratio in the studied HPS. We separately estimated the number of males and females using the Peterson method. Since females were not included in the sample obtained during the first recapture (Table 1), the sex structure was assessed based on data from the second and third recaptures. The obtained data are shown in Table 2. Table 2. Sex ratio based on recapture results (see above for notation)

Males were significantly predominant, which may be a consequence of the female deficit registered in 2005. Despite this, the sex ratio is consistent across the results of two catches separated by a significant time interval. As already noted, we consider the HPS abundance estimate from the results of the third, final catch to be more reliable. By the time of the second catch, marked individuals did not have time to redistribute evenly throughout the entire HPS (which consists of both individuals in the water body and those that have moved away from the pond and are on land). However, the fact that the sex ratio estimates coincide indicates that mixing occurred equally for females and males. Presumably, the calculated sex ratio is close to the actual one. 8 Thus, the obtained results reflect the trend of the HPS returning to the state recorded by G.A. Lada in 1995 [3;8]. Modeling of green frog HPS transformations shows that for populations including only hybrid forms, a necessary condition for reproduction processes is the distribution and transmission from generation to generation of different clonal genomes (both P. ridibundus and P. lessonae, and both male and female) [4;9]. The crisis of this HPS was probably associated with the loss of all clonal genomes except the male P. lessonae genome [3]. Fortunately, Is'kov pond is not isolated from other water bodies located nearby (Fig. 1). Presumably, the improvement in the HPS state that we observe is the result of the entry of a set of clonal genomes into it, allowing it to transition to a stable state [4].   Coordinates   During the work, an assessment of the demographic state of the scientifically interesting HPS of green frogs was obtained. In the HPS composition, 161 individuals with marks remain, which allow further individual identification. It was established that at the current stage of transformation of the studied HPS, we observe an E-type system (i.e., one consisting mainly of diploid P. esculentus) with a small proportion of P. ridibundus and triploid P. esculentus. The calculated abundance of sexually mature individuals of this HPS is approximately 700, with approximately fivefold male prevalence. The studied HPS is recovering after the crisis associated with pond drainage in 2000.
During the work, the shortcomings of Peterson abundance estimation became apparent, the correctness of which is significantly influenced by the movement of groups of individuals within the pond and its surroundings. For a comprehensive study of green frog HPS transformations of Is'kov pond, further research using the individual marking technique is necessary.
     Nm*  SEm Nf* SEf  
II 2.07.2012 248 82 54 13 ? 5:1
III 26.07.2012 522 178 108 54 ? 5:1

* m – males; f – females. Males were found to be significantly predominant, which may be due to the deficit of females recorded in 2005. Despite this, the sex ratio is stable based on the results of two captures separated by a significant time interval. As already indicated, we consider the population estimate based on the results of the third and final capture to be more reliable. At the time of the second capture, the tagged individuals had not yet redistributed evenly throughout the entire HPS (which consists of both individuals in the water body and those that have moved away from the pond and are on land). However, the fact that the sex ratio estimates coincide suggests that mixing occurred equally for females and males. It is likely that the calculated sex ratio is close to the actual one. P. esculentus individuals predominated in species composition, with only 1% represented by individuals of the parental species P. ridibundus. Ploidy was determined in 107 green frogs. Determination of ploidy in the studied hybrids showed that almost all individuals in the sample are diploid (only one triploid individual was recorded). Compared to 2011, the proportion of females in catches has significantly increased. Thus, the obtained results reflect the tendency of the HPS to return to the state recorded by G. A. Lada in 1995 [3; 8]. Modeling of the transformations of the green frog HPS shows that for populations consisting only of hybrid forms, a necessary condition for reproduction is the presence and transmission from generation to generation of various clonal genomes (both P. ridibundus and P. lessonae, including both male and female) [4; 9]. The crisis of this HPS was likely due to the loss of all clonal genomes except the male genome of P. lessonae [3]. Fortunately, the Is'kiv pond is not isolated from other nearby water bodies (Fig. 1). It is likely that the improvement in the HPS condition we observe is a result of the introduction of a set of clonal genomes, allowing it to transition to a stable state [4]. Conclusions In the course of the work, an assessment of the demographic status of a scientifically interesting green frog HPS was obtained. The HPS includes 161 individuals with tags that allow for further individual identification. It was established that at this stage of transformation of the studied HPS, we observe an E-type system (i.e., consisting mainly of diploid P. esculentus) with a small proportion of P. ridibundus and triploid P. esculentus. The calculated number of sexually mature individuals in this HPS is about 700, with males outnumbering females approximately fivefold. The studied HPS is recovering after a crisis caused by the draining of the pond in 2000. The shortcomings of the Peterson population estimation method became apparent during the work, as its accuracy is significantly affected by the movement of groups of individuals within and around the pond. For a comprehensive study of the HPS transformations of the Is'kiv pond green frogs, further research using individual tagging methods is necessary. Acknowledgments The authors express their gratitude to many colleagues who contributed to the study of the Is'kiv pond green frog HPS. G. A. Lada initiated these studies. S. M. Lytvynchuk, L. Ya. Bokin, and Yu. M. Rozanov provided invaluable assistance in identifying the studied frogs. Field studies involved E. Malchenko, R. Myronov, Yu. Kravchenko, S. Ohiyenko, as well as many other students who underwent field practice in vertebrate zoology at the V. N. Karazin Kharkiv National University biological station. O. V. Korshunov and D. A. Shabanov played a key role in all studies of the Is'kiv pond. The authors express their sincere gratitude to all colleagues. Literature 1. Bondareva A. A. Cytogenetic features of green frog erythrocytes from the Seversky Donets center of diversity of the Pelophylax esculentus complex / [A. A. Bondareva, Yu. S. Bibik, S. M. Samylo, D. A. Shabanov] // Visnik of V. N. Karazin Kharkiv National University. Series: Biology. – 2012. – in press. 2. Borkin L. Ya. Mass polyploidy in the hybridogenic complex Rana esculenta (Ranidae, Anura, Amphibia) in Eastern Ukraine / [Borkin L. Ya., Zinenko A. I., Korshunov A. V., et al.] // Materials of the I conf. of the Ukrainian Herpetological Society. — K.: Zoological Museum of the National Museum of Natural History of the National Academy of Sciences of Ukraine, 2005. — pp. 23–26. 3. Study of population systems of green frogs ( Rana esculenta complex) in the Kharkiv region: history, current state, and prospects / [D. A. Shabanov, A. I. Zinenko, A. V. Korshunov, et al.] // Visnik of V. N. Karazin Kharkiv National University. Series: Biology. — 2006. — Issue 3 (No. 729). — pp. 208—220. 4. Study of the stability of hemiclonal population systems of the hybridogenic complex of green frogs using simulation modeling / [Kravchenko M. A., Shabanov D.A., Vladimirova M.V., et al.] // Visnik of Dnipropetrovsk University. Biology. Ecology. – 2011. – Issue 19, Vol. 1. – pp. 51–64. 5. Green frogs: life without rules or a special way of evolution? / D. A. Shabanov, S. N. Lytvynchuk // Priroda. – 2010. – No. 3 (1135). – pp. 29–36. 6. Koli G. Analysis of vertebrate populations / G. Koli. – M.: Mir, 1979. – 362 p. 7. Korshunov A. V. Ecological patterns of distribution of the Pelophylax esculentus complex in the biotopes of the upper reaches of the Seversky Donets River: abstract of dissertation ... Candidate of Biological Sciences: 03.00.16 "Ecology" / A.V. Korshunov // Dnipropetrovsk, 2010. – 24 p. 8. Lada G. A. On the necessity of preserving unique "pure" populations of the diploid edible frog ( Rana esculenta Linnaeus, 1758) in the Belgorod and Kharkiv regions / G. A. Lada // Problems of conservation and rational use of natural ecosystems and biological resources. — Penza, 1998. — pp. 333 – 335. 9. Modeling of transformations of hemiclonal population systems of green frogs ( Pelophylax esculentus complex; Amphibia, Ranidae) using recurrence difference equations / M.A. Kravchenko, D.A. Shabanov, et al. // Visnik of V. N. Karazin Kharkiv National University. Series: Biology. – 2010. – Issue 12 (No. 920). – pp. 70–82. 10. Population system of green frogs Pelophylax esculentus complex of the Is'kiv pond in the Zmiiv district of Kharkiv region: history of study and population size estimation / [E. V. Meleshko, A. D. Suvorova, M. A. Kravchenko, D.A. Shabanov] // Biological Bulletin. – Kharkiv, 2012. – Vol. 14, No. 1, 2010. – pp. 63–68. 11. Diversity of green frogs ( Pelophylax esculentus complex) in the Kharkiv region: morphological aspect of study / [O.V. Korshunov, T.V. Babinich, O.I. Zinenko, et al.] // Biology and Valeology – Issue 6 Kharkiv: KhDPU, 2004. – pp. 24-30. 12. Size structure of the population of common toads ( Bufo bufo ) / [Achkasova I. V., Dyachenko L. A., Myakota Ya. Yu., et al.] // Biology and Valeology. Collection of scientific works. – 2001. – Kharkiv: KhDPU, – Issue 4. – pp. 41–46. 13. What green frogs inhabit the Kharkiv region? Terminological and nomenclatural aspects of the problem / D. A. Shabanov, O. V. Korshunov, M. O. Kravchenko // Biology and Valeology. — 2009 — Issue 11. — Kharkiv: KhDPU. — pp. 164–125. 14. Mass occurrence of polyploid green frogs ( Rana esculenta complex) in Eastern Ukraine / L. J. Borkin, A. V. Korshunov, G. A. Lada [et al.] // Russian Journal of Herpetology. — 2004. — Vol. 11, No 3. — pp. 194—213. 15. Plotner J. Die westpalaarktichen Wasserfrosche. Bielefeld: Laurenti-Verlag, 2005. — 161 p. Article submitted to the editorial office on 10/15/2012; accepted for publication on 10/24/2012.