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Journal of Threatened Taxa | www.threatenedtaxa.org | 26 July 2017 | 9(7): 10380–10385

 

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Captive breeding for conservation of Dussumier’s Catfish (Actinopterygii: Siluriformes: Clariidae: Clarias dussumieri) a Near Threatened endemic catfish of peninsular India

 

K.G. Padmakumar 1, L. Bindu 2, P.S. Sreerekha 3, Nitta Joseph 4, Anuradha Krishnan 5, P.S. Manu 6 & V.S. Basheer 7

 

1 International Research and Training Centre for Below Sea Level Farming, Kuttanad, Kerala 688561, India

2 Post Graduate Department of Zoology, M.S.M. College, Kayamkulam, Alappuzha District, Kerala 690502, India

3,4,5,6 Kerala Agricultural University, Regional Agricultural Research Station, Kumarakom, Kerala 686566, India

7 PMFGR Centre, National Bureau of Fish Genetic Resources CMFRI Campus, Post Box No. 1603, Ernakulam North P.O., Kochi, Kerala 682018, India

1 kgpadman@gmail.com, 2 bindukylm@gmail.com (corresponding author), 3 surajsree@gmail.com, 4 rarskum@kau.in, 5 arkrishnan@rediffmail.com, 6 psmanuposhickal@gmail.com, 7 vsbasheer@gmail.com

 

 

doi: http://doi.org/10.11609/jott.2444.9.7.10380-10385

Editor: Rajeev Raghavan, Kerala University of Fisheries and Ocean Studies (KUFOS), Kochi, India. Date of publication: 26 July 2017 (online & print)

Manuscript details: Ms # 2444 | Received 05 March 2017 | Final received 03 July 2017 | Finally accepted 07 July 2017

Citation: Padmakumar, K.G., L. Bindu, P.S. Sreerekha, N. Joseph, A. Krishnan, P.S. Manu & V.S. Basheer (2017). Captive breeding for conservation of Dussumier’s Catfish (Actinopterygii: Siluriformes: Clariidae: Clarias dussumieri) a Near Threatened endemic catfish of peninsular India. Journal of Threatened Taxa 9(7): 10380–10385; http://doi.org/10.11609/jott.2444.9.7.10380-10385

Copyright: © Padmakumar et al. 2017. Creative Commons Attribution 4.0 International License. JoTT allows unrestricted use of this article in any medium, reproduction and distribution by providing adequate credit to the authors and the source of publication.

Funding: Indian Council of Agricultural Research(ICAR), New Delhi, Project- ICAR-NATP-Germplasm Inventory, Evaluation and Gene Banking of Freshwater Fishes (F.No.27 (28)/98/NATP/MM-III-18)

Competing interests: The authors declare no competing interests.

Author Contribution: KGP: design the work, supervised the data collection and wrote the manuscript; BL: data collection, data analysis and manuscript preparation; PSS, NJ, PSM and AK: Sample collection and data analysis; VSB contributed in the data analysis and edited the manuscript. All authors read and approved the final version of the manuscript.

Acknowledgements: We would like to thank the Indian Council of Agricultural Research (ICAR) for financial support and Kerala Agricultural University (KAU) for the facilities provided during the investigation period.

 

 

 

 

 

Abstract: The peninsular Indian endemic Dussumier’s Catfish Clarias dussumieri once abundant in the wetlands and other water bodies of Kerala is now in rapid decline. The present paper focuses on an approach towards the conservation of this rare catfish through artificial propagation. Fishes were bred in captivity by the administration of fish pituitary extract at the rate of 20–40 mg.kg-1. Spawning occurred after 12–14 hr of injection and fertilized eggs hatched after 16:30hr. Larval rearing was carried out in cement cisterns and the larvae attained a mean size of 51.6±1.6mm in 60 days. Since brooders of this species have become extremely rare in nature, the present study on captive breeding by hormonal manipulation methods without sacrificing the male fishes, assumes significance for conserving this endemic species.

 

Keywords: Clarias dussumieri, endemic catfish, fish pituitary extract, hatching, induced breeding.

 

 

 

INTRODUCTION

Freshwater aquaculture development in India has hitherto focused on the Indian major carps, and carp culture accounts for 95% of the total inland fish production (FAO 2016). Although many of the indigenous fishes have local preference and demand, such species have not been incorporated into the culture systems owing to lack of availability of fingerlings. Compared to other Southeast Asian countries, the ‘Index of Biodiversity’in Indian aquaculture is quite low (Kutty 1999). In this context, there is an urgent need to standardize mass production of indigenous fishes by captive breeding so as to replenish and restore them in natural waters, and facilitate their sustainable utilization on commercial scale.

In Kerala, poor consumer preference for carps results in the culture of undesirable exotic species like African Catfish Clarias gariepinus (Burchell, 1822) and carnivorous Pacu Piaractus brachypomus (Cuvier, 1818), despite the ban imposed on its culture and their introduction to natural waters (Binoy 2010). The endemic Catfish Clarias dussumieri Valenciennes, 1840 is a candidate species that has high aquaculture potential, as it has been reported to grow to a maximum size of over 3kg in nature (Padmakumar et al. 2010).

Clarias dussumieri popularly known as ‘naadan mushi’ or ‘naadan muzhi’ (Image 1), is an endemic catfish of peninsular India that has been assessed as ‘Near Threatened’ in the IUCN Red List of Threatened Species (Abraham 2011). The species, once abundant in the rice polders, rivulets and temple ponds of Kerala, has now sharply declined as a result of increased use of pesticides and agrochemicals for intensive rice cultivation practices and land reclamation for construction (Padmakumar et al. 2010; Shaji & Kumar 2016). Clarias dussumieri has very high consumer preference as a food fish with medicinal and nutraceutical properties due to the presence of high concentration of physiologically available iron, necessary for the synthesis of haemoglobin and essential amino acids (Padmakumar et al. 2004). Much of the research in India, has been centred on the breeding and propagation of Clarias magur (Sahoo et al. 2008) and Heteropneustes fossilis (Alok et al. 1998; Bindu et al. 2009), and little work has been carried out on C. dussumieri (Padmakumar et al. 2004; Aneesh et al. 2013). Owing to their close morphological similarity with C. magur, the species is often wrongly identified and reported in publications implying their abundance. The situation calls for very sincere efforts for their propagation and popularization of culture practices. Studies on captive breeding of C. dussumieri was undertaken for the first time at the Regional Agricultural Research Station (R.A.R.S), Kumarakom as part of the National Agricultural Technology Project (Padmakumar et al. 2004) and the studies that followed assumes significance in this context. Present report is on the breeding of C. dussumieri in captivity through near natural means without sacrificing the male for milt collection and artificial breeding.

 

 

MATERIALS AND METHODS

 

Live C. dussumieri were collected from the lowland areas and rivulets (9.3473–9.38350N and 76.3473–76.57410E) of the river Pampa. Male and female fishes were raised separately in experimental tanks (5x3x1m) for one year at R.A.R.S., Kumarakom. During this period they were fed with commercial pellet (Higashi fresh; crude protein content 20%), supplemented with fishmeal and chopped trash fish at the rate of 5–6 % of body weight. The morphometric characteristics and key biological features such as gonadosomatic index, fecundity and egg size were monitored.

Mature fishes having distinct secondary sexual characters were selected as brooders (Padmakumar et al. 2004) and were subjected to intra-muscular administration of hormone. Continuous showering and natural stimulation using filtered river water was provided in the tank with a closely simulated flow regime for 6–8 hr before the hormone injection. Altogether 15 breeding trials were conducted during the years 2001–2005. Both synthetic and natural hormonal extracts were utilized for breeding stimulation and final maturation of gonads. Hormonal analogue Ovaprim® containing 20mg SGnRHa and 10mg Domperidone in 1ml was used at the rate of 0.8–1.0 ml.kg-1 in the first three trials and crude carp fish pituitary extract, at the rate of 20–40 mg.kg-1 was administered for the remaining trials, in a single dose. After the injection, both male and female fishes were kept together in an experimental tank in single and double pairs. They were kept under close observation for breeding behavior. All responses and exact time of egg laying were closely monitored for 12hr post-injection and further up to 20hr for fishes which failed to develop any visible courting responses.

Fertilised eggs were collected and observed continuously and images captured at 15 minute intervals, under a trinocular microscope (CETI, Belgium) at 10X magnification for documenting the embryonic development. This was done with the help of Magnus Imaging System supported by PixelView software, connected to a computer monitor. Time of fertilization was denoted as 0:0h. Dead eggs were removed from the bottom of the spawning tank at each stage of development.

 

 

RESULTS AND DISCUSSION

 

 

The total length (TL) and total weight (TW)of the fishes that appeared in the collections (n=52) ranged from 17–54.0 cm (38.85±10.5 cm) and 40g to 1130g (432.9±293.7 g) respectively. The highest G.S.I observed in this species was 24.4 and fecundity was 65,258 eggs.

Induced breeding

Mature males having an average size of 299.67±96.4g and females having 326±100.6g were observed to be suitable for breeding. Ripe females were identified by easy extrusion of uniform sized eggs when pressed on the abdomen. Being a monogamous fish forming a ‘one to one’ mating pair, one male and one female was observed to be a suitable set for breeding. Whenever more females or more males were placed together in one breeding pool, the fishes were observed to be seriously injured and even resulted in mortality. Hence a 1:1 ratio was strictly maintained in subsequent trials. Breeding trials were undertaken close to the onset of monsoon coinciding with first monsoonal showers-the identified spawning season in nature (Padmakumar et al. 2010). In the breeding trials using ovaprim as inducing agents, even fully matured and gravid females failed to respond, although the fish exhibited vigorous sex play. The broodfishes underwent mortality in all such trials. There were many reports on breeding other clariids using diverse hormonal regimes, viz., ovaprim (Mahapatra et al. 2000), carp pituitary extract (Clemens & Sneed 1971; Hogendoorn & Vismans 1980), HCG (Mollah & Tan 1983; Zairin et al. 1992; Szyper et al. 2001). Hence for further trials, a varying dose of pituitary alone was administered to the females while male received half of the female dose. Fertilization was successful in six trials and hatching was successful in three (Table 1). Recently, Aneesh et al. (2013) reported breeding of this endemic catfish using synthetic hormone Wova-FH.

Clariids have a natural tendency to hide in dark corners away from light (Offem et al. 2010) utilizing any hideouts available within the tank, a tendency seen even in the broodfish. Hence a PVC pipe (0.4m long and 4” diameter) was provided as hideout in the spawning tank. After hormonal administration, the male chases the female and swims underneath her and due to their natural affinity to dark corners settle in the hideouts. In trials when more than one hideout was provided the stimulated fishes enter into separate hideouts with occasional union with the prospective mate, again returning to their respective chosen hideouts. With elapse of time in all such instances, the spawning response was negative. Hence in subsequent trials, only a single hideout was placed in the spawning tank. Both the hypophysed fishes, i.e., male and female went into the same hideout chamber. The diameter of the hideout was so chosen, as just enough for the mating pair to wriggle in. When larger sized hideouts were provided, the fish was found to freely move in and out, most restlessly prior to spawning and with elapse of time response was negative. The selection of a single hideout with diameter sufficient enough for the mating pair to wriggle in with no free space, the response was positive. It appeared that the hideouts facilitated immediate physical contacts of the hypophysed brooders resulting in courting and successful natural spawning. Hence, in all the subsequent trials, this method was meticulously employed with success. In all previous reports of induced breeding of clariids, the standard procedure has been stripping the ripe eggs after hormonal manipulation and fertilization of the stripped eggs utilizing milt from the male fish. As the males among clariids do not exude milt by usual procedures, the common method employed is to surgically collect the testis of the hypophysed male, prepare sperm extract and utilize the suspension for in situ fertilization of stripped eggs from the hypophysed females. This procedure necessitates sacrificing male fishes for artificial fertilization of the eggs (Rao et al.1994). Among catfishes, males are generally not free milting and most of them are considered not amenable to stripping (Pandian & Koteeswaran 1998) probably due to the unique anatomy of their tubular testis. Violent juxtaposition of the mating pair and wriggling of the body of male and female fishes facilitated by contraction and relaxation of successive myotomes, recall the act of stripping of gametes (Pandian et al.2001).

Clarias dussumieri is a broadcast spawner and no parental care was observed in these trials. Spawning occurred after a latency period of 12–14 hr with 40–96.5 % fertilization. The fertilized eggs were spherical, heavily yolked and orange in colour. The diameter of mature eggs varied between 1.3 and 1.6 mm (1.5±0.096), closer to the lower limit of most other catfishes like C. magur, Pangassius sutchi, H. fossilis, Horabagrus brachysoma and C. gariepinus (Thakur & Das 1985; Rao et al. 1994; Islam 2005; Bindu et al. 2009; Padmakumar et al. 2011; Olaniyi & Omitogun 2014). The mating pair always keeps away from the released eggs and this helps to protect the eggs from damages. The eggs are slightly sticky and adhesive but can easily be separated by gentle water flow. The fertilized eggs were transferred to a flow-through incubation system in shallow trays with a feeble flow of water, approximately 5cm sec-1. Better aeration facilities and timely removal of dead and unfertilized eggs improve hatching rate and hatchling survival by preventing the deterioration of water quality.

 

 

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Embryonic and larval development

In C. dussumieri, yolk occupies 75% of the egg mass. The blastodisc appears 2–3 hr after fertilization and the germinal ring appeared as a ridge encircling the globular yolk in 4–5 hr (Table 2). As the development advances, the embryo appear more and more elongated and the tail appeared overlapping the head. The embryonic stages recorded in the present study are found to be similar to other tropical catfishes (Thakur & Das 1985; Arockiaraj et al. 2003; Islam 2005). Incubation was completed in 16.30hr at temperature 27±10C and pH 6.5 to 7.0 and within 20hr after fertilization all the eggs hatched. By this time, the egg membrane becomes conspicuously thinner and tail emergedout first by its vigorous twitching movements (Image 2). Hatching time among catfishes showed wide variations (Arratia et al. 2003). In catfishes like C. magur, H. fossilis and H. brachysoma it varied between 16–24hr (Thakur & Das 1985; Bindu et al. 2009), whereas in C. gariepinus and P. sutchi it ranged between 21–36hr (Bruton 1979; Islam 2005).

Size of the hatchlings varied between 4.9–5.1 mm (5.0±0.1mm) and was larger than most other catfishes, viz., Mystus montanus, M. cavasius, C. gariepinus, H. fossilis and H. brachysoma (Arockiaraj et al. 2003; Rahman et al. 2004; Islam 2005; Bindu et al. 2009; Padmakumar et al. 2011) but smaller than C. magur (Sahoo et al. 2010). Hatchlings appeared rolling on the bottom with their attached spherical yolk sac on the ventral side. The early hatchlings look slender and transparent with unpigmented eyes and without a distinct mouth. They congregate in the tank corners, away from the aeration points. As the hatchling development proceeds (Image 3a–c), heavy pigmentation begin to appear on the dorsal portion of the head from the second day of hatching. The yolk gets fully absorbed by the 3rd day and the young fry were fed with freshly hatched nauplii of Artemia salina. This was followed till 10th day and then gradually weaned to tubifex worms, powdered pellets and minced prawn meat suspension. Mixed zooplankton, Artemia nauplii, tubifex and egg custard were found to be acceptable as larval diets during hatchery rearing of catfish larvae. These feed items containing 41–65 % protein (Sahoo et al. 2010) were reported as good diets. In two months, the hatchlings reached 51.6±1.6 mm and were transferred to open nurseries and fed on pellet feed (Higashi starter). Fish meal is the major ingredient of this commercial pellet. The survival rate of larvae can be improved if boiled egg yolk and live feed are provided (Table 3). Early feeding is most crucial in survival rate of hatchlings. As the youngone reaches fry stage, i.e., 25mm in size they were gradually weaned to commercial feed formulations. Since cannibalism is most common among catfishes sufficient supplementary food and rapid transfer of larger young ones by periodic sorting was found essential for success in fry nursing of this species.

 

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CONCLUSION

 

 

In the context of their rapid population decline in the wild (Shaji & Kumar 2016), it has become imperative to develop suitable conservation strategies for C. dussumieri. Development of artificial breeding protocol for C. dussumieri assumes relevance in this context. A novel method for near natural spawning was evolved by providing horizontal hideouts that ensured intimate physical contact for the monogamous mating pairs. This method avoids the necessity of sacrificing the male fish for artificial fertilization of the stripped eggs in clariids. It is also crucial to take up studies on population structure and dynamics of this species. In the context of ambiguity in correct identification and taxonomy, studies on genetic characterization of this species (Devassy et al. 2016) assume relevance. Further population genetic studies coupled with captive breeding for successful translocation and reintroduction of this species is essential (Cohn 2001; Null & Lund 2011). More importantly, there is an urgent need for restoration of the natural habitats of this threatened species, as habitat disturbances and intrusion of exotics has largely contributed to the current state of decline. Standardization of simple protocol for hatchery production of seeds is a breakthrough not only for conservation management of this endemic species but also for their potential use as a candidate species in aquaculture systems.

 

 

 

REFERENCES

 

 

Abraham, R. (2011). Clarias dussumieri. The IUCN Red List of Threatened Species 2011 <www.iucnredlist.org> Downloaded on 13 April 2014. http://doi.org/10.2305/IUCN.UK.2011-1.RLTS.T172332A6870008.en

Alok, D., T. Krishnan, G.D. Talwar & L.C. Garg (1998). Multiple induced spawning of the Indian Catfish Heteropneustes fossilis (Bloch) within a prolonged spawning season. Journal of the World Aquaculture Society 29(2): 252–254.

Aneesh, B., K.R. Salin & C.M. Nair (2013). Breeding for conservation: case of an endangered Catfish Clarias dussumieri (Valenciennes, 1840). Fishery Technology 50: 101–109.

Arockiaraj, A.J., M.A. Haniffa, S. Seetharaman & S.P. Singh (2003). Early development of a threatened freshwater Catfish Mystus montanus (Jerdon). Acta Zoologica Taiwanica 14(1): 23–32.

Arratia, G., B.G. Kapoor, M. Chardon & R. Diogo (2003). Catfishes Vol. 1 & 2. Science Publishers, Inc. Enfield (NH), USA, 812pp.

Bindu, L., S. Salini, M.V. Moni, P.S. Manu & K.G. Padmakumar (2009). Indian Catfish (Heteropneustes fossilis) Breeding and embryonic development. Fishing Chimes 29(1): 188–191.

Binoy, V.V. (2010). Catfish Clarias is vanishing from the waters of Kerala. Current Science 99(6): 714

Bruton, M.N. (1979). The breeding biology and early development of Clarias gariepinus (Pisces: Clariidae) in lake Sibaya, South Africa with a review of breeding in species of subgenus Clarias (Clarias). Transactions of the Zoological Society of London 35: 1–45.

Clemens, H.B. & E.K. Sneed (1971). Bioassay and use of pituitary materials to spawn warm - water fishes. U.S. Fish and Wildlife Service Res. Rep., No: 61, 30pp.

Cohn, J.P. (2001). Resurrecting the Dammed: A Look at Colorado River Restoration. BioScience 51(12): 998­–1003; http://doi.org/10.1641/0006-3568(2001)051[0998:RTDALA]2.0.CO;2

Devassy, A, R. Kumar, P.P. Shajitha, R. John, K.G. Padmakumar, V.S. Basheer, A. Gopalakrishnan & L. Mathew (2016). Genetic identification and phylogenetic relationships of Indian clariids based on mitochondrial COI sequences. Mitochondrial DNA Part A: DNA Mapping, Sequencing, and Analysis 27(5): 3777–3780.

FAO (2016). Assessing water availability and economic social and nutritional contributions from inland capture fisheries and aquaculture: an indicator-based framework - A compilation of water-related indicators in selected African and Asian countries, by Daniela Ottaviani, Cassandra De Young & Sachiko Tsuji. FAO Fisheries and Aquaculture Circular Paper No. 1116, Rome, 310pp.

Hogendoorn, H. & M.M. Vismans (1980). Controlled propagation of the African catfish C. gariepinus II. Artificial Reproduction. Aquaculture 21: 39–53.

Islam, A. (2005). Embryonic and larval development of Thai Pangas (Pangasius sutchi Fowler, 1937). Development Growth and Differentiation 47(1): 1–6.

Kutty, M.N. (1999). Aquaculture development in India from a global perspective. Current Science 76(3): 333–341 .

Mahapatra, B.K., K.K. Sengupta, U.K. De, G.C. Rana, A. Datta, A. Basu & S. Saha (2000). Controlled breeding and larval rearing of Clarias batrachus (Linn.) for mass scale propagation. Fishing Chimes 19(10&11): 97–102.

Mollah, M.F.A & E.S.P. Tan (1983). HCG - induced spawning of the catfish Clarias macrocephalus (Gunther). Aquaculture 35: 239–247.

Null, S.E. & J.R. Lund (2011). Fish habitat optimization to prioritize river restoration decisions. River Research and Applications 22(9): 1378–1393; http://doi.org/10.1002/rra.1521

Offem, B.O., Y.A. Samsons & I.T. Omoniyi (2010). Aspects of ecology of Clarias anguillaris (Teleostei: Clariidae) in the Cross River, Nigeria. Turkish Journal of Fisheries and Aquatic Sciences 10: 101–110; http://doi.org/10.4194/trjfas.2010.0115

Olaniyi, W.A. & O.G. Omitogun (2014). Stages in the early and larval development of the African Catfish Clarias gariepinus (Teleostei, Clariidae). Zygote 22(3): 314–330; http://doi.org/10.1017/S0967199413000063

Pandian, T.J. & R. Koteeswaran (1998). Ploidy induction and sex control in fish. Hydrobiologia 384: 167–243.

Pandian, T.J., R. Koteeswaran & S. Kirankumar (2001). Breeding strategies and techniques for ornamental fishes. Paper presented in NBFGR-NATP Workshop, Captive breeding of prioritized cultivable and ornamental fishes for commercial utilization and conservation. 29–30 July, National Bureau of Fish Genetic Resources, Lucknow. U.P., India, 12pp.

Padmakumar, K.G., A. Krishnan, L. Bindu, P.S. Sreerekha & N. Joseph (2004). Captive Breeding for Conservation of Endemic fishes of Western Ghats, India. NATP, Kerala Agricultural University, India, 79pp.

Padmakumar, K.G., L. Bindu, V.S. Basheer & A. Gopalakrishnan (2010). Threatened fishes of the World: Clarias dussumieri dussumieri Valenciennes, 1840 (Clariidae). Environmental Biology of Fishes 87: 297–298.

Padmakumar, K.G., L. Bindu, P.S. Sreerekha, A. Gopalakrishnan, V.S. Basheer, N. Joseph, P.S. Manu & A. Krishnan (2011). Breeding of the endemic Catfish, Horabagrus brachysoma in captive conditions. Current Science 100(8): 1232–1236.

Rahman, M.R., M.A. Rahman, M.N. Khan & M.G. Hussain (2004). Observations on the embryonic and larval development of Silurid Catfish, Gulsha (Mystus cavasius Ham.). Pakistan Journal of Biological Sciences 7(6): 1070–1075.

Rao, G.R., S.D. Tripathi & A.K. Sahu (1994). Breeding and seed production of the Asian Catfish Clarias batrachus (Lin.). Central Institute of Freshwater Aquaculture. Barrackpore, India, 47pp.

Sahoo, S.K, S.S. Giri, S. Chandra & B.C. Mohapatra (2008) Evaluation of breeding performance of Asian Catfish Clarias batrachus at different dose of HCG and Latency period combinations. Turkish Journal of Fisheries and Aquatic Sciences 8: 249–251.

Sahoo, S.K., S.S. Giri, S. Chandra & A.K. Sahu (2010). Management in seed rearing of Asian Catfish, Clarias batrachus, in hatchery conditions. Aquaculture Asia 15(1): 23–25.

Shaji, C.P. & A.B. Kumar (2016). Local extinction of valenciennes Clariid Clarias dussumieri Valenciennes, 1840 from two panchayaths of Thrissur District, Kerala. Journal of Aquatic Biology & Fisheries 4: 125–133.

Szyper, J.P., C.S. Tamaru, R.D. Howerton, K.D. Hopkins, A.W. Fast & R.P. Weidenbach (2001). Maturation, hatchery and nursery techniques for Chinese Catfish, Clarias fuscus, in Hawaii. Aquaculture extension bulletin. Summer 2001: 1–8.

Thakur, N.K. & P. Das (1985). Synopsis on Biological Data on Magur Clarias batrachus (Lin.). Bulletin No. 41. Central Institute of Freshwater Aquaculture. Barrackpore, India, 82pp.

Zairin, M. Jr., K. Furukawa & K. Aida (1992). Induction of ovulation by HCG in the tropical Walking Catfish Clarias batrachus under 23-250C. Bulletin of the Japanese Society for the Science of Fish 59: 1681–1695.