Proceedings of the Zoological Institute RAS
Vol. 316, No. 4, 2012, рр. 361–368
УДК 597.211
LOCAL MIGRATION AND FEEDING HABITS OF CARPATHIAN LAMPREY
EUDONTOMYZON DANFORDI (PETROMYZONTES: PETROMYZONTIDAE)
IN TISZA RIVER SYSTEM (DANUBE DRAINAGE, UKRAINE)
E.M. Talabishka1, N.G. Bogutskaya2 and A.M. Naseka2*
1
Transcarpathian Salmonids and Endangered Fish Reproduction Research Station of Institute of Fisheries of Ukrainian
National Academy of Agrarian Science, Uzhgorodska Str. 165, 89600 Mukachevo, Ukraine; e-mail: talabishka@online.ua
2
Zoological Institute of the Russian Academy of Sciences, Universitetskaya Emb. 1, 199034 Saint Petersburg, Russia;
e-mail: dr_naseka@rambler.ru
ABSTRACT
The paper presents data on the feeding habits and migratory activity of Carpathian lamprey Eudontomyzon danfordi
Regan, 1911, one of the few predatory lampreys resident in rivers. Observations made in winter revealed some
feeding activity though it was commonly supposed that the lampreys cease feeding by the end of autumn. The most
intensive feeding occurs from May till August; during the same period, the lampreys actively migrate upstream.
Observations made at the rapids revealed that E. danfordi actively preys and feeds during day time when and where
the concentration of its prey is high, not only in the evening or at night as was believed earlier.
Key words: fecundity, feeding, migrations, parasitic lampreys
О ЛОКАЛЬНОЙ МИГРАЦИИ И ПИТАНИИ КАРПАТСКОЙ МИНОГИ
EUDONTOMYZON DANFORDI (PETROMYZONTES: PETROMYZONTIDAE)
В СИСТЕМЕ РЕКИ ТИССЫ (БАССЕЙН ДУНАЯ, УКРАИНА)
Е.М. Талабишка1, Н.Г. Богуцкая2 и А.М. Насека2*
1
Закарпатская научно-исследовательская станция лососеводства и воспроизводства исчезающих видов рыб
Института рыбного хозяйства Национальной академии аграрных наук Украины, Ужгородская ул. 165, 89600
Мукачево, Украина; e-mail: talabishka@online.ua
2
Зоологический институт Российской академии наук, Университетская наб. 1, 199034 Санкт-Петербург, Россия;
e-mail: dr_naseka@rambler.ru
РЕЗЮМЕ
В статье представлены данные наблюдений за пищевой и миграционной активностью взрослых особей карпатской миноги Eudontomyzon danfordi Regan, 1911, которая является одним из немногих видов жилых паразитических миног. В отличие от данных из литературы, отмечавших прекращение питания в конце осени,
показано, что минога продолжает питаться и зимой, хотя и менее активно. Пик пищевой активности наблюдается в мае–августе; в этот же период минога активно мигрирует вверх по течению. Наблюдения на порогах
впервые показали, что карпатская минога активно охотится и питается не только вечером и ночью, но и в
дневное время в местах концентрации доступных пищевых объектов.
Ключевые слова: плодовитость, питание, миграции, паразитические миноги
*Corresponding author / Автор-корреспондент
362
INTRODUCTION
Lampreys (Petromyzontidae Bonaparte, 1831)
are a group of primitive vertebrates, that includes
anadromous, landlocked, and purely freshwater taxa.
Over half of the known species are non-parasitic,
or brook forms, which never feed during their brief
adult lives. The remainder feed as adults in a parasitic, or more correctly, predatory manner in the case
of Carpathian lamprey Eudontomyzon danfordi Regan, 1911, mainly on teleost fishes (Hardisty 1986a).
Eudontomyzon danfordi is an endemic species distributed only in the left-hand tributaries of the Lower
Danube – Tisza, Timiş, Cerna, and, probably, Nera
(Bănărescu 1969; Renaud and Holčík 1986). The first
record of E. danfordi in the upper Tisza River system
(in the area of the Transcarpathian Province of the
present-day Ukraine) belongs to Vladykov (1925,
1926), who described it as a new species Lampetra
bergi that was synonymised with E. danfordi in a
subsequent publication (Vladykov 1931). Details
of its distribution in the Ukrainian part of the Tisza
River system and adjacent Romanian territory can
be found in a number of publications (Vlasova 1956;
Kolyushev 1949, 1959; Movchan 1993, 2000, 2005,
2009; Harka and Bănărescu 1999; Koŝĉo et al. 2004;
Harka 2006).
Eudontomyzon danfordi is one of the few predatory lampreys that do not migrate to sea or a large
lake during their adult stage. Some data on its ecology can be found in two summarising publications
(Renaud and Holčík 1986; Renaud 2011). However,
there are still many aspects to be investigated with
regards to its feeding habits, migratory activity and
spawning. In this paper we present data on feeding
and migration of adult Carpathian lamprey in the
Tisza River system.
MATERIAL AND METHODS
Field observations and collections were made by
the first author in 2004–2009 in the Vecha River
(a left-hand tributary of the Latorica River in the
Tisza system) along a one kilometre long stretch of
the river, where a shallow riffle section is located
(48°34´2´´N 23°2´38´´E). In this section, occurrence
of E. danfordi was monitored daily from early spring
till late autumn, and also in winter, but more intermittently. In summer, observations were also done
E.M. Talabishka et al.
along the whole Vecha River as well as in adjacent
Latorica River sections and in the Tisza River in
2004–2010. Observations of migratory activity of
Carpathian lamprey and other fishes were made at
the rapids, where rocks of a considerable size (Fig. 1)
impede their movement. Shallow water in the monitored sections of the river made it possible to visually observe the lampreys’ movements and feeding as
well as conditions and movements of its prey. Some
observations on feeding habits were performed in an
aquarium; all lamprey individuals were then released
back into the river. A few samples were fixed in 4%
formalin and deposited in the fish collection of the
National Museum of Natural History of the National
Academy of Sciences of Ukraine in Kiev (NHMU).
RESULTS
Description of adult E. danfordi. Observed individuals were adult post-metamorphosed pre-spawning lamprey in the parasitic phase of the life cycle
judging by morphological characters summarised, for
example, in Renaud and Holčík (1986). The size of
the lamprey increases from spring to the end of summer. In a sample (NHMU No 8650) collected on May
23, 2007 at the Vecha River rapids, the total length of
10 specimens is 169–230 mm and the weight is 6.1–
13.2 g (Table 1); the gonads were poorly developed,
and their sex could not be determined. A sample
(NHMU No 8647), collected on August 20, 2005
at the same locality, includes five females (Table 2)
199–270 mm long with well-developed gonads and
clearly distinguishable oocytes. The gonado-somatic
index in three of the females was 4.6, 4.7, and 5.6%.
However, in two of the females it was difficult to
determine with any accuracy the number of eggs
because of their smaller size. All measurements were
made after fixation in formalin. Specimens in both
samples possess well-developed intestinal tracts entirely filled up with food remains.
Migration. The rapids were used as an observation point to examine the direction of the lampreys’
movement along the river. A pronounced downstream migration, if it occurs, was not observed. An
active run upstream of relatively large schools of
lamprey was recorded at the rapids from May till
August with the peak in June. The earliest appearance of lamprey was recorded on May 23; the latest
record was on August 22 (both in 2007). During the
period May–August, water temperature varied from
363
Ecology of Carpathian lamprey
Fig. 1. Rapids on Vecha River (48°34’2”N 23°2’38”E) – main locality of observations. Arrows show two points, where Carpathian lamprey
moves upstream.
13.5 to 17 °C, and water transparency was between
5 and 150 cm. Because of heavy rains, the migration
started much later in 2006, when both bony fishes
and lamprey began overcoming the rapids only in the
middle of summer. In general, the migration of the
lamprey coincides with that of other fishes. However,
in 2006, when the run started only on July 20th, the
first fishes that appeared at the rapids were several
individuals of minnow and bullhead; the following
day many more fishes came through, but no lamprey
was recorded during an hour of observations. On the
third day of the migration there were already many
fishes and lampreys at the rapids.
Diurnal activity was rather stable; lamprey individuals coming upstream were commonly recorded
throughout the whole day with a peak from 14:00–
15:00 until 17:00. However, during the evening and
night the movement activity was minimal or absent.
During the peak of the migration, there could be seen
Table 1. Total length and weight of Eudontomyzon danfordi adults,
Vecha River, May 23, 2007.
No
Total length, mm
Body weight, g
1
169.0
6.1
2
171.4
8.3
3
191.3
8.5
4
230.0
12.4
5
215.2
11.7
6
204.4
12.5
7
218.1
13.2
8
216.9
11.0
9
200.7
9.7
10
205.5
10.5
364
E.M. Talabishka et al.
Table 2. Data on Eudontomyzon danfordi females, Vecha River, August 20, 2005.
No
Total length,
mm
Intestine external
diameter, mm
Body weight,
g
Weight of gonads,
g
Absolute fecundity,
eggs
Relative fecundity,
eggs per 1 g of body weight
1
270.0
3.0
33.3
1.88
19390
582
2
257.3
5.2
26.6
1.26
12300
462
3
231.7
4.4
18.4
0.85
8770
477
4
243.0
6.1
22.9
0.67
–
–
5
199.0
4.0
14.3
0.15
–
–
Fig. 2. Carpathian lamprey attached to rocks while running upstream over rapids.
up to 13 individuals during 15 minutes, up to seven
simultaneously.
For getting over the barrier, E. danfordi uses its
oral disc for attachment to rocks. First, a lamprey
swims rapidly to a higher place on a rock and attaches
to it, then, after some time, it swims further upstream,
reaching another rock or moving to a deeper place
under rocks from where it reappears later to attach to
another rock located further upstream. The lampreys
often climb out of the water onto wet rocks and crawl
in an upstream direction along the cracks in rocks in
order to overcome an obstacle. Sometimes, up to four
or five E. danfordi individuals could be seen attached
together on a single rock in very shallow water with a
high velocity (Fig. 2). They could be easily taken by
hand. After overcoming the rapids, lamprey swim fast
upstream to deeper places of the river bed.
Feeding habits. Our observations show that
adult E. danfordi feed during the entire year of their
feeding phase. However, there are limitations to com-
365
Ecology of Carpathian lamprey
parisons between seasons because our observations
were dependent on weather and water conditions;
flooding and high water turbidity prevented us from
conducting observations in the early spring at the
same level as during the rest of the year. The peak
of feeding (the greatest number of prey collected and
feeding lamprey observed) was in late May–August;
the earliest record of several intensively feeding postmetamorphosed individuals was done at night May
1–2, 2010, in the Tisza River. In September–November the feeding activity declined to a very low level.
Thus, in November only three fishes partly eaten by
lamprey were collected. In December–beginning of
March, few observations of feeding lamprey were
done or prey found.
During the daily excursions along the investigated section of the river, excluding the rapids, prey
of the lamprey were only found in the morning and
never during the second inspection of the same river
section in the afternoon. This probably indicates that
the lampreys feed during the night or early morning,
and that the prey were then swept downstream with
the current. Additionally, there were observations
made at night in Vecha and Latorica rivers of feeding lamprey in different biotopes, from quiet shallows
to riffles with exposed rock, but usually in sections
between calm water and fast current. The attached
lamprey did not react to scattered light but, when
illuminated by bright torch light, immediately detached from the prey and tried to hide under a stone
or in a deeper place.
The only exception to this feeding behaviour was
at the rapids on the Vecha River, where many lamprey individuals were observed preying upon other
fishes during the day time while migrating upstream.
When an individual of E. danfordi was hunting,
it swam slowly in the water column mostly near the
bottom, but when approaching a prey it rapidly attacked the fish and attached to any part of the body.
Then it usually slowly moved to the prey’s abdomen,
penetrated the body cavity, and started sucking the
blood while simultaneously eating the heart and other
visceral organs. This mode of predation was also demonstrated in the aquarium. If there were a lot of fishes
concentrated at the rapids, lampreys left their prey
without eating the muscular tissue (Fig. 3A) or ate the
muscles and skin only just behind the head (Fig. 3B,
C). Some lampreys moved more actively and attacked
any nearby prey, consuming even their vertebrae (Fig.
3D). However, E. danfordi never ate the entire fish –
they usually left the head and the vertebral column
intact (Fig. 3E). Carpathian lamprey often hunted
at places with high water velocity, where prey were
more vulnerable. After a successful attack, a lamprey
swam with its prey to an adjacent part of the river
with a slowed current. Several times two individuals
of E. danfordi were observed eating and fighting over
the same fish. However, the lamprey never exhibited
agonistic behavior towards each other.
We observed Carpathian lamprey preying upon
the following fish species: Alburnoides bipunctatus
(Bloch, 1782), Squalius cephalus (Linnaeus, 1758),
Barbus carpathicus Kotlik, Tsigenopoulos, Ráb
and Berrebi, 2002, Chondrostoma nasus (Linnaeus,
1758), Cottus gobio Linnaeus, 1758, Cottus poecilopus
Heckel, 1837, Barbatula barbatula (Linnaeus, 1758),
Phoxinus phoxinus (Linnaeus, 1758), and Gobio
carpathicus Vladykov, 1925. At the rapids, the most
common prey are P. phoxinus, C. poecilopus, B. carpathicus and B. barbatula. In the fish farm ponds on
the Krasna River (a tributary of the Teresva River),
the lamprey feeds on rainbow trout Oncorhynchus
mykiss (Walbaum, 1792).
DISCUSSION
Our data on fecundity and gonad weight in E. danfordi, though limited, may be useful for comparisons
with other lamprey species. In our study, the absolute
fecundity in a 270 mm long female collected in August
was 19,390 eggs, much higher than the count given
in the literature. Hardisty (1964) reported the estimated absolute fecundity of E. danfordi to be 7,500 to
10,350 eggs in females of 210–215 mm in total length.
The absolute fecundity in adult E. danfordi is higher
than in other resident but non-parasitic lampreys:
573–2,175 in Lampetra planeri (Bloch, 1784) reported in Hardisty (1986a, 1986c) and 1,950–7,106
in Eudontomyzon mariae (Berg, 1931) reported in
Holčík and Renaud (1986), but lower that in the
anadromous parasitic lampreys: 4,000–42,500 in
Lampetra fluviatilis (Linnaeus, 1758) reported in
Hardisty (1986b). It is interesting that a rather similar absolute fecundity of 10,000–16,000 was found
in the landlocked parasitic morph ladogensis of L.
fluviatilis (Ivanova-Berg 1933). In the literature, we
found no data on relative fecundity in E. danfordi; in
three other freshwater (resident) parasitic lampreys,
Tetrapleurodon spadiceus, landlocked Petromyzon
marinus and Ichthyomyzon unicuspis the estimated
366
E.M. Talabishka et al.
Fig. 3. Prey of Carpathian lamprey: A, C – Barbus carpathicus; B – Phoxinus phoxinus; D – Alburnoides bipunctatus; E – Cottus poecilopus.
Ecology of Carpathian lamprey
relative fecundity was respectively, 318, 344 and 410
eggs per g body weight (Hardisty 1971, 1986a). Our
estimates of 462–582 for E. danfordi are thus significantly higher than those reported for other resident
parasitic species and closer to estimates found in nonparasitic species (Hardisty 1986a).
When compared with data of previous authors
summarised in Renaud and Holčík (1986), our observations confirm the fact that the adult trophic
phase in E. danfordi lasts for most of the first year of
adult life. However, our observations of some winter
feeding activity, albeit at a reduced level, is contrary
to the observations of some authors, who found that
after October or November the intestine atrophies
and adults cease feeding (Mihail 1962a, 1962b; Kux
1965). It was supposed that the prey are usually attacked in the evening or at night (Renaud and Holčík
1986); our data revealed that E. danfordi also actively
prey and feed during the day time when and where
the concentration of its prey is high.
Chappuis (1939), Grossu et al. (1962), Holčík
(1963), and Bănărescu (1969) reported that E.
danfordi fed on Barbatula barbatula, Barbus barbus
(Linnaeus, 1758), B. petenyi (recently described as B.
carpathicus in the area in consideration), Cottus gobio,
C. poecilopus, Salmo sp., and Squalius cephalus. Other
species known to be attacked by E. danfordi in aquaria (Kux 1967) are Carasssius carassius (Linnaeus,
1758), Gobio gobio (now G. carpathicus in the area in
consideration), Phoxinus phoxinus and Rutilus rutilus
(Linnaeus, 1758). Therefore, A. bipunctatus and C.
nasus are reported here as prey for the first time.
ACKNOWLEDGEMENTS
The study was partly supported by a grant from the
Russian Foundation for Basic Research, no. 09-04-01584.
We are thankful to C. Renaud for his valuable comments on
an earlier version of the manuscript.
REFERENCES
Bănărescu P. 1969. Fauna Republicii Socialiste Romania.
Vol. 12. Cyclostomata şi Chondrichthyes. Editura
Academiei Republicii Populare Romine, Bucuresti,
104 p.
Chappuis P.A. 1939. Über die Lebensweise von Eudontomyzon danfordi Regan. Archiv für Hydrobiologie, 34:
645–658.
Grossu A., Homei V., Barbu P. and Popescu A. 1962.
Contribution à 1‘étude des pétromyzonides de la
367
République Populaire Roumaine. Travaux du Museum
d’Histoire Naturelle «G. Antipa», 3: 253–279.
Hardisty M.W. 1964. The fecundity of lampreys. Archiv
für Hydrobiologie, 60: 340–357.
Hardisty M.W. 1971. Gonadogenesis, sex differentiation
and gametogenesis. In: M.W. Hardisty and I.C. Potter
(eds). The biology of lampreys. Vol. 1. Academic Press,
London: 295–359.
Hardisty M.W. 1986a. General introduction to lampreys.
In: J. Holčík (Ed.) Freshwater fishes of Europe. Vol. 1,
part 1. Petromyzontiformes. AULA-Verlag, Wiesbaden:
19–83.
Hardisty M.W. 1986b. Lampetra fluviatilis. In: J. Holčík
(Ed.) Freshwater fishes of Europe. Vol. 1, part 1. Petromyzontiformes. AULA-Verlag, Wiesbaden: 249–278.
Hardisty M.W. 1986c. Lampetra planeri. In: J. Holčík
(Ed.) Freshwater fishes of Europe. Vol. 1, part 1. Petromyzontiformes. AULA-Verlag, Wiesbaden: 279–304.
Harka Á. 2006. Changes in the fish fauna of the River
Tisza. Tiscia, 35: 65–72.
Harka Á. and Bănărescu P. 1999. Fish fauna of the Upper
Tisza. In: J. Hamar and A. Sarkany-Kiss (Eds). Tiscia
monograph series. The Upper Tisa Valley. Szolnok–
Szeged–Tirgu Mures: 439–454.
Holčík J. 1963. Notes on the Czechoslovakian lampreys
with redescription of Lampetra (Eudontomyzon)
vladykovi (Oliva and Zanandrea, 1959). Věstník
Československé Společnosti Zoologické, 27: 51–61.
Holčík J. and Renaud C.B. 1986. Eudontomyzon mariae.
In: J. Holčík (Ed.) Freshwater fishes of Europe. Vol. 1,
part 1. Petromyzontiformes. AULA-Verlag, Wiesbaden:
165–185.
Ivanova-Berg M.M. 1933. Zur Biologie des Flussneunauges [Lampetra fluviatilis (L.)]. Archive für Hydrobiologie, 25: 22–27.
Kolyushev I.I. 1949. A short key to fishes of the Transcarpathian Region of USSR. UzNU, Uzhgorod, 53 p. [In
Ukrainian]
Kolyushev I.I. 1959. Fauna of vertebrates of the Soviet
Carpathians. In: Fauna and Animal World of the
Soviet Carpathians. Nauchnyye Zapiski Uzhgorodskogo
Universiteta, 40: 3–20. [In Russian]
Koŝĉo J., Balázs P., Ivanec O., Kovalćuk A., Manko P.
and Terek J. 2004. Príspevok k poznaniu rýb tokov Zakarpatskej oblasti Ukrajuni. Acta facultatis studiorum
Humanitatis et naturae universitatis Prešoviensis.
Prirodne vedy, 40: 138–152.
Kux Z. 1965. Lampetra gracilis, nový neparasitický druh
mihule z východního Slovenska. Časopis Moravskeho
Musea (Brno), 50: 293–302.
Kux Z. 1967. Příspěvek k bionomii mihulovitých (Petromyzonidae) v potisské oblasti východního Slovenska.
Časopis Moravskeho Musea, 52: 209–216.
Mihail N. 1962a. Funktionelle Untersuchungen an den
Verdauungsorganen von Eudontomyzon danfordi. Zoologischer Anzeiger, 168: 130–138.
368
Mihail N. 1962b. Zur Biologie und Ökologie von Eudontomyzon danfordi. Zoologischer Anzeiger, 168: 139–143.
Movchan Yu.V. 1993. Current state of the ichthyofauna of
the Transcarpathia and some actions for its conversation.
In: Fauna of the Eastern Carpathians: current state and
protection. UzU, Uzhgorod: 147–150. [In Ukrainian]
Movchan Yu.V. 2000. Up-to-date species composition of
cyclostomes and fish of the Tisza River basin within
Ukraine. Journal of Ichthyology, 40: 121–123. [In Russian]
Movchan Yu.V. 2005. Contribution to the description
of the fish fauna of fresh waterbodies in Ukraine
(taxonomic composition, distribution in river basins,
current state). Zbirnyk Prats’ Zoologichnogo Muzeyu,
37: 70–82. [In Ukrainian]
Movchan Yu.V. 2009. Fishes of Ukraine (taxonomy, nomenclature, remarks). Zbirnyk Prats’ Zoologichnogo
Muzeyu, 40: 47–86. [In Ukrainian]
Renaud C.B. 2011. Lampreys of the world. An annotated
and illustrated catalogue of lamprey species known to
E.M. Talabishka et al.
date. FAO species catalogue for fishery purposes, no. 5.
Food and Agriculture Organization of the United Nations, Rome, 109 p.
Renaud C.B. and Holčík J. 1986. Eudontomyzon danfordi
Regan, 1911. In: J. Holčík (Ed.) Freshwater fishes of
Europe. Vol. 1, part 1. Petromyzontiformes. AULAVerlag, Wiesbaden: 146–164.
Vladykov V.D. 1925. Über einige neue Fische aus der
Tschechoslowakei (Karpathorussland). Zoologischer
Anzeiger, 64: 248–252.
Vladykov V.D. 1926. Fishes of Subcarpathian Russia and
methods of their capture. Karpatiya, Uzhgorod, 147 p.
[In Russian]
Vladykov V.D. 1931. Poissons de la Russie souscarpathique (Tchécoslovaquie). Mémoires de la Société
Zoologique de France, 29: 217–374.
Vlasova E.K. 1956. Materials to the fish fauna of the
Transcarpathia. Nauchnyje Zapiski Uzhgorodskogo
Universiteta, 16: 3–38. [In Russian]
Submitted May 16, 2012; accepted November 14, 2012.