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Threatened fishes of the world: Stenodus leucichthys leucichthys Guldenstadt, 1772 (Salmonidae).

INTRODUCTION

The Inconnu (Stenodus leucichthys leucichthys Guldenstadt) is the largest and fastest-growing member of the whitefish subfamily Coregoninae (Salmonidae). Two subspecies of Inconnu are recognized, with S. l. leucichthys isolated in the Caspian Sea drainage of western Asia, while S. l. nelma (Pallas) is found in the Arctic and subarctic regions of north-western North America and northern Eurasia (Stephenson et al. 2005). It is known by a range of common names: Inconnu (English), Belorybitsa (Russian), Mahi Ziba (Persian), Stenode Blanc (French), Salmon Blanco (Spanish) Ak balyk (Kazakh) and Azatmahy (Turkmenian).

Stenodus leucichthys leucichthys is the Caspian endemic subspecies and mainly occurs along the western and eastern coasts of the middle Caspian Sea at depths of 60-65 m (Berg 1948). Declining natural populations in the Caspian Sea due to heavy fishing pressure, increasing water pollution and habitat alteration and destruction have resulted in S. l.leucichthys being listed as "Extinct in the wild" (IUCN Red List 2010). Concerns about the decline of Stenodus l. leucichthys populations led Volga River hatcheries to carry out artificial reproduction and restocking in the Caspian Sea (Belyaeva & Milstein 1959). The Arctic subspecies, Stenodus leucichthys nelma, was introduced into the northern Volga River drainage and is now expanding, so may threaten surviving populations and cultivated stocks through hybridization (Freyhof & Kottelat 2008).

Despite the ecological and economic importance of this fish, very little is known about it in the Caspian Sea. Therefore, the aim of this study is to introduce and better understand the ecological and biological characteristics of this valuable species.

Identification: D II-VI (9-13), A II-IV 9-15, dorsal fin high and pointed, adipose fin present, pelvic fins with well developed axillary process, vertebrae 65-68, manubrium absent, with hook-shaped processes on the capitulum, anterior edge of hyomandibular round, only 19 to 26 gill rakers present on lower limb of first gill arch. Scales large, 99-120 in lateral line. Body fusiform and moderately slender, head relatively small, mouth large and terminal, lower jaw long, tip projecting, hind end reaching back behind eye, upper jaw reaching to level of pupil, teeth present on jaws, vomer, palatines and tongue. Pyloric caeca 191-193. Maximum length and weight 130 cm and 35 kg respectively; much larger individuals have been recorded. Sides of body silvery, belly silvery white without spots, dorsum usually green, blue or pale brown (Fig. 1). Sexual dimorphism develops during spawning period, when epithelial tubercles appear on head and side of body of males (Berg 1948; Shariaty 2001).

Distribution: Stenodus l. leucichthys is found only in rivers draining to the Caspian Sea, from which it mainly ascends the Volga, while very few fish ascend the Ural, and it is rarely found in the Terek. It is widely found along the western coast north of Makhachkala and along the eastern coast (Mangyshlak). Its closest relative, Stenodus leucichthys nelma, penetrates into the Caspian Sea from the Arctic Ocean basin through the Post-Glacial ponded lakes which are situated between the basins of the Volga and the Kama, on the one hand, and of the Baltic Sea and the Arctic Ocean, on the other (Berg 1948). Stenodus l. leucichthys spends the warm season in the central and southern regions of the Caspian Sea (Kottelat & Freyhof 2007) mainly in Guilan and no record of this species has been reported from the Mazandaran and Golestan coasts (FAO 1991). Figure 2 shows the distribution of S. l. leucichthys in the Caspian Sea basin.

Habitat and ecology: Stenodus l. leucichthys is a pelagic species which inhabits open waters to the depth 65 m, and has not been found below 65m (its optimum depths are 25-45 m). This fish is an oxyphilic species and prefers waters with temperature below 20[degrees]C. It is heterotrophic and an active predator. At 30 days after hatching, fingerlings begin to feed on invertebrates and larvae and small juveniles of other fishes. In the sea, adult S. l. leucichthys feeds mainly on small fish (clupeids, engraulids, juvenile cyprinids, atherinids, gobiids etc) (Podlesny 1947; Svetovidov 1984; Shariaty 2001). Stenodus l. leucichthys is amphidromous. However, amphidromy is not obligatory and nonamphidromous populations have been described in some locations (Petrova 1976). Mature adults migrate from sea to the delta of the Volga in the fall, winter and the early spring. Therefore, the species has two seasonal forms, spring and autumn, which are differentiated in time of entry to the Volga for spawning (Berg 1948). Adults migrate downward to the sea after spawning, but many of them die (Freyhof & Kottelat 2008). The alevins immediately descend to the sea after hatching.

Reproduction: The main spawning sites of S. l. leucichthys are located in the basin of the Kama, in the Ufa River, 3000 km upstream from the mouth of the Volga (Shariaty 2001). The secondary spawning grounds are situated in the Belaya between Ufa and Sterlitamak. The spawning season in the Ufa begins from the middle of October to the beginning of November. Males mature at +5 to +6 years while females reach maturity at the age of +6 to +7 years (Freyhof & Kottelat 2008). Stenodus l. leucichthys spawns twice during its life cycle with an interval of two years (Berg 1948). Its optimum temperature for reproduction is 0.1 to 6[degrees]C. Semi-adhesive eggs are deposited on the gravel and rock substrate (Kottelat & Freyhof 2007). The sex ratio of brooders in the natural spawning grounds is almost 1:1 as for the subspecies Stenodus leucichthys nelma (Brown 2000). The average fecundity is 250 x [10.sup.3] eggs per individual (104.5-400 x [10.sup.3]). On average, about 26% of the total weight of each fish is egg weight (Berg 1948). Embryonic development takes about 180-200 days. Fry hatch from March up to the early May (mostly the second half of April). From the seventh day onward, fry begin to feed on plankton. The fry stage lasts around two months and then they develop into fingerlings (Berg 1948).

Threats: The sharp decline in their abundance due to the construction of dams, insufficient spawning areas, increasing illegal fishing, unstable hydrological conditions, river contamination and damage caused by other fish (especially kilka) and crustaceans has resulted in this species being listed as extinct in the wild (Letichevski 1983; IUCN 2010).

BRIEF DISCUSSION

Unfortunately, the published data on different aspects of S. l. leucichthys is limited and most studies on the species has been carried out on North American and Eurasian populations of Stenodus leucichthys nelma (Scott & Crossman 1973; Alt 1977; Morrow 1980; Brown 2000; Howland et al. 2000; Underwood et al. 2000; Stephenson et al. 2005). Therefore, much effort from scientists and governments should be made in understanding the biology, ecology and behaviour for managing this valuable species. One key objective in working with endangered species is to increase the number of individuals of the species concerned by artificially/controlled reproduction in captivity. Unfortunately, there is no policy for preserving this species in the Caspian Sea from illegal fishermen by countries bordering the Sea and this should be done according to fishing methods, size of net mesh and time/place prohibition. Previously, the Russian federation enhanced the spawning areas in the lower parts of the Volgograd hydroelectric power station for increased efficiency of natural reproduction.

In connection with the present study, the negative influences of the modern environment needs to be studied (i.e. all possible causes of stress, environmental changes, destruction of spawning grounds) in order to better organize protection of this species and thus develop the necessary strategies for action.

Findings from this preliminary data suggest that further research is needed for the future, including population genetics, artificial spawning, domestication for future aquaculture activities, natural behaviour during migration and spawning, as well as ionic balance and osmoregulation. The collective goal of this research should enhance the effectiveness of breeding programs, increase populations of remaining wild stock, and to improve our understanding of the biological knowledge of this species. Since stocks have declined, much effort is needed to rehabilitate the wild populations by all countries around the Caspian Sea.

Received: 24 April 2011 - Accepted: 30 July 2011

REFERENCES

ALT, K. T. 1977. Inconnu, Stenodus leucichthys, migration studies in Alaska 1961-1977. Journal of the Fisheries Research Board of Canada 34: 129-133.

BELYAEVA, V. N. & MILSTEIN, V. V. 1959. Rearing of Inconnu fingerlings in the Volga river delta. Moscow: "Rybnoye Khozyaistvo". Fish Industry Journal: 1-18.

BERG, L. S. 1948. Fishes of freshwaters of USSR and adjacent countries. Vol I. USSR Academy of Sciences publishers, Moscow-Leningrad.

BROWN, R. J. 2000. Migratory patterns of Yukon River Inconnu as determined with otolith microchemistry and radio telemetry. MSc thesis. Fairbanks, Alaska, 73 pp.

FAO. 1991. New species of freshwater fish from Iranian coast of the Caspian Sea. FI: UNDP/IRA/88/001, Rome, Italy.

FREYHOF, J. & KOTTELAT, M. 2008. Stenodus leucichthys. In: IUCN 2010. IUCN Red List of Threatened Species. Version 2010.4. <www.iucnredlist.org>. Downloaded on 31 January 2011.

HOWLAND, K. L., TALLMAN, R. F. & TONN, W. M. 2000. Migration patterns of freshwater and anadromous Inconnu in the Mackenzie River system. Transactions of the American Fisheries Society 129: 41-59.

IUCN. 2010. IUCN Red List of Threatened Species. www.iucnredlist.org. Downloaded on 31 January 2011.

KOTTELAT, M. & FREYHOF, J. 2007. Handbook of European Freshwater Fishes. Publications Kottelat, Cornol, Switzerland: 646 pp.

LETICHEVSKI, M. A. 1983. Reproduction of Inconnu. Moscow. "Lyogkaya I pischevaya promyshlennost" (Light and Food Industry): 30-112.

MORROW, J. E. 1980. The Freshwater Fishes of Alaska. Alaska Northwest Publishing Company, Anchorage, Alaska, 248 pp.

PETROVA, N. A. 1976. The biology of the Inconnu, Stenodus leucichthys nelma, from the Irtysh River basin. Journal of Ichthyology 16: 17-27.

PODLESNY, A. V. 1947. Inconnu Stenodus leucichthys Guld. Bioecological outline essay. Proc. Siberian Department VNIORKh (All-Union Research Institute of Lake and Riverine Fisheries) 7: 1:3-195.

SCOTT, W. B. & CROSSMAN, E. J. 1973. Freshwater Fishes of Canada. Fisheries Research Board of Canada, Bulletin 184, Ottawa, Ontario. 966 pp.

SHARIATY, A. 2001. Breeding and rearing Stenodus leucichthys. Shahr Sabz Publication, Rasht, Iran, 82 pp.

STEPHENSON, S. A., BURROWS, J. A. & BABALUK, J. A. 2005. Long-distance migrations by Inconnu (Stenodus leucichthys) in the Mackenzie River System. Arctic 58: 21-25.

SVETOVIDOV, A. N. 1984. Salmonidae. In: Fishes of the north-eastern Atlantic and the Mediterranean 1. (Eds P. J. P. WHITEHEAD, M. L. BAUCHOT, J. C. HUREAU, J. NIELSEN & E. TORTONESE.): 373-385.

UNDERWOOD, T. J. 2000. Abundance, length composition, and migration of spawning inconnu in the Selawik River, Alaska. North American Journal of Fisheries Management 20: 386-393.

Samaneh Poursaeid & Bahram Falahatkar *

Fisheries Department, Faculty of Natural Resources, University of Guilan, Sowmeh Sara, Guilan, Iran * Corresponding author. Fisheries Dept., Faculty of Natural Resources, University of Guilan, Sowmeh Sara, P.O. Box 1144, Iran. Tel.: +98 182 322 3599; Fax: +98 182 322 2102.

E-mail: falahatkar@guilan.ac.ir
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Author:Poursaeid, Samaneh; Falahatkar, Bahram
Publication:aqua: International Journal of Ichthyology
Date:Jan 15, 2012
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