Back to Journal

International Journal of Fisheries Science and Research

Effect of Photoperiod on Eggs Hatchability, Growth and Survivability of Hybrid Catfish (Heterobranchus bidorsalis X Clarias gariepinus) Larvae

Abstract Citation Introduction Hypothesis Materials and Methods Results Discussion Conclusion References
Details

Received: 09-Dec-2017

Accepted: 09-Feb-2018

Published: 14-Feb-2018

Adebayo IA*

Department of Fisheries and Aquaculture Management, Ekiti State University, Nigeria

Corresponding Author:

Adebayo IA, Department of Fisheries and Aquaculture Management, Faculty of Agricultural Sciences, Ekiti State University, Nigeria, Tel: 234-8066618186

Keywords

Catfish; Hybrid; Hatchlings; Photoperiod; Growth; Light; Darkness

Abstract

This study was conducted to determine the effects of photoperiod on egg hatchability, growth and survivability of hybrid catfish (Heterobranchus bidorsalis X Clarias gariepinus) larvae, using hormone-induced spawning method. Eggs were stripped from two sexually matured and healthy female Clarias gariepinus of average weight of 1kg/each and fertilized with milt from two sexually matured male Heterobranchus bidorsalis of average weight of 2kg/each. An average of five hundred (500) eggs were introduced into each ten aquaria tanks of size 70cm x 45cm x 40cm/tank, using a pre- determined spoonful estimation at five photoperiod regimes: (T1) 24L:00D (Light:Darkness); (T2) 18L:6D; (T3) 12L:12D; (T4) 6L:18D and (T5) 00L:24D in two replicates. Aquaria tanks were arranged in a flow- through system at a flow rate of 1.5L/min with aerators to maintain good water condition. Provision of light during the night for illumination of the aquaria tanks was kept constant at 1200 1x, using solar panel (Mono)/inverter (Microtex) light energy. Growth and survivability of the fish larvae were monitored for six weeks. They were fed with laboratory-cultured live feed (Daphnia) to achieve maximum feed utilization. Percentage hatchability of eggs and best growth performance of fish larvae were significantly (p<0.05) highest (92.5%, 91.2 ± 0.21mg) respectively in T5 (00L:24D), while percentage survivability of hatchlings was significantly (p<0.05) highest (94.4%) in T3 (12L:12D). It was observed in this study that the highest hatchability of eggs and optimum growth performance of hatchlings were under complete darkness, with reduced survivability of fish, as a result of observed cannibalism. The fish were photophobic. To achieve a balance result in terms of hatchability of eggs, growth and survivability of fish fry, it is suggested that incubation and hatching of eggs should be done under complete darkness, while rearing of fry should be under equal light and darkness exposure.

Citation

Adebayo IA. Effect of Photoperiod on Eggs Hatchability, Growth and Survivability of Hybrid Catfish (Heterobranchus bidorsalis X Clarias gariepinus) Larvae. Int J Fisheries Sci Res. 2018; 2(1): 1004.

Introduction

Aquaculture in Nigeria is dominated by catfish farming through hypophysation, thus leading to increase of farm -raised catfish [1]. The favoured catfish species include Clarias gariepinus, Heterobranchus bidorsalis and their hybrid (Hetero-clarias). Catfish grows faster in fresh water, and has become popular due to their ease of cultivation, resistance to diseases and tolerance to high- density culture [2]. Despite the popularity of the African catfish and its great market potentials, the production is still at subsistence level due to inadequate availability of fish seeds for stocking. Currently in Nigeria, the fingerlings supplied from viable hatcheries are not enough to meet the needs of the catfish farmers, while supply of fingerlings from the wild is faced with poor patronage due to unpredictable genetic potentials for fast growth [3].

Artificial propagation of catfishes is carried out in hatcheries using hormonal induction method. Farmers have found this approach to be cheap, practical and highly reliable than the wild source [4]. Adequate qualitative and quantitative sexual gametes are prerequisites for a successful artificial propagation exercise, hence the need to use sexually matured and healthy breeders [5]. Parent fish must also be kept in suitable environmental conditions with good feeding to ensure quality gametes. Hybridization between Clarias gariepinus and Heterobranchus bidorsalis combines the early maturing trait in Clarias gariepinus with fast growth trait in Heterobranchus bidorsalis to produce hybrid (Hetero-clarias). The emergence of hybrid catfish, with good potentials for fast growth and high acceptability led to rapid development of catfish farming in most part of Nigeria. Production of table size hybrid catfish was widely embraced by farmers as it gave better internal rate of return on investment due to rapid growth [2].

The success of artificial propagation of fish is determined by the number of fish larva produced at a given time [6]. Photoperiod, which is the daily cycle of light and darkness, plays a major role in the hatchability of eggs, growth and survivability of fish [7]. Photoperiod has been found to have a significant effect on the survivability of fish larva by exerting a definite influence on fish metabolism, maturation, behaviour and even coloration [8]. There must be a minimum and maximum amount of exposure to light or darkness that should be allowed for certain fish larva production [7]. Batty (1992) found that long exposure to light caused a decrease in hatchability of eggs, less nutrients intake and consequently poor growth rate in some freshwater fishes [9]. Also, light or darkness has direct impact on water temperature, turbidity, pH, ammonia which may either positively or negatively affects fish larva. To this regards, it is important to determine the influence of photoperiod on water parameters and the effect on fish larva in the hatchery. It was observed that fifty percent (50%) of fish fry mortality occurred at the larva stage due to fluctuations in photoperiod [10]. If fish do not receive the correct amount of light or darkness, they can be crippled and may not develop properly [8]. Light helps larva to determine the location of its food in water through Photoreception [7]. The amount of light and darkness require is species specific and must be determined to achieve maximum larva production [6]. Therefore, the objective of this study was to know the effect of varying levels of light and darkness on eggs hatchability, growth and survivability of hybrid catfish (Hetero- clarias) larva under laboratory conditions.

Hypothesis

1) There will be no significant difference (p>0.05) in eggs hatchability of hybrid catfish under different photoperiod regimes.

2) There will be no significant difference (p>0.05) in growth, survivability of hybrid catfish larvae under different photoperiod regimes.

3) Water quality will not affect the performance of the eggs hatchability, growth and survivability of the fish larvae.

Materials and Methods

Procurement of broodstocks

A pair each of sexually matured and healthy female Clarias gariepinus and male Heterobranchus bidorsalis of average weight of 1kg and 2kg respectively were purchased from a reputable fish farm in Offa, Kwara State, Nigeria two weeks before the commencement of the experiment. The male and female fish were kept separately in earthen nursery ponds of size 4m x 3m x 1.5m/each to ensure suitable environmental conditions. During this period, fish were fed with commercial diets (40% CP) at 5% body weight to maintain good quality gametes before and during breeding operation.

Experimental set up

The experiment was conducted at the Department of Fisheries and Aquaculture Management, Ekiti State University, Ado-Ekiti. Ten glass aquaria tanks of size 70cm x 45cm x 40cm/each filled with borehole water to 70L capacity were used for the experiment. The five photoperiod regimes at two replicates per treatment were: (T1) 24L:00D (Light:Darkness); (T2) 18L:06D; (T3) 12L:12D; (T4) 6L:18D and (T5 ) 00L:24D respectively. The glass aquaria tanks were arranged in a flow-through system at 1.5L/min water discharge. Aerators were installed to complement the flow-through system to maintain good water quality throughout the experiment. Light for illumination of the aquaria tanks was kept constant at 1200 lx using solar panel (Mono)/inverter (Microtex) light energy.

Hormonal induction of parent fish

Two hatchery-raised gravid Clarias gariepinus brood stocks (Av. Weight of 1kg/one) were kept singly in aerated concrete tanks size 2m x 2m x 1m/each with 200 litres of water prior to injection. Fish were weighed with an electric sensitive weighing balance to determine the amount of hormone to be used. 0.5ml of Ovaprim hormone was used for each 1kg of fish at 0.5ml/kg. The injection was done intramuscularly above the lateral line toward the anterior end of the fish at 19.00 GMT. The injected fish were returned into their tanks to complete the ovulation period.

Stripping, fertilization and incubation of eggs

Stripping of eggs took place after the completion of the ovulation period of 12 hours (7.00 GMT) at room temperature (27°C). One of the male fish (Heterobranchus bidorsalis) was sacrificed and the milt was collected for the fertilization of the stripped eggs. With the addition of normal saline water (0.9% Choride), eggs were carefully stirred using feather to complete the fertilization process. Using a pre-determined spoonful estimation [11], an average of five hundred eggs (500 eggs) were spread evenly on kakaban in each experimental tank under controlled levels of light and darkness exposure regimes (photoperiod). After 24 hours, hatched eggs were seen, while the fry were not fed until the third day to complete endogenous feeding.

Monitoring of water quality parameters

The physico-chemical parameters of water were closely monitored using standardized YSI DO Meter (YSI model 57), electronic pH meter (Metler Toledo 320 model) and Mercury-in glass thermometer, for Dissolve oxygen, pH and Temperature respectively. Nitrate in water was determined weekly.

Determination of eggs hatchability

Gamete quality in female C. gariepinus was determined by fecundity/Gonado-Somatic Index Ratio (GIS). Hatchability rate of the eggs was determined on the basis of the percentage of the unhatched as used by Aluko and Ali, 2001 [11]. An estimation which assumed hatching rate of flow through water system to be calculated on live/dead ratio of incubated eggs as follows:

% Hatchability = (Number of hatched eggs/Total number of eggs) x 100%

Survival rate = (Number of hatchlings alive up to larvae stage/Total number of hatchlings) x 100%

Survival rate was determined based on Jensen (1996) method [12]. The normal healthy larvae were estimated on percentage basis of dead and deformed hatchlings.

Determination of growth performance

Growth responses were determined as described by Olvera Novoa et al. (1990).

Statistical analysis

Data from each treatment were pooled and subjected to one way Analysis of Variance (ANOVA) test using the Statistical Package for Social Science (SPSS) 1998 version). Individual differences (P = 0.05) among treatment means were separated using Duncan’s multiple range test [13].

Results

The result of percentage hatchability of eggs in each photoperiod regime is shown in Table 1. Average numerical estimation for both the hatched and unhatched eggs was cautiously and manually done and percentage hatchability calculated. Treatment (T5) had the highest hatchability value of 92.5% followed by T4 (86%) and least in T1 (58.5%), the Control.

Table 1: Percentage (%) hatchability of incubated eggs.

Photoperiod regimes (Treatments) Average mean number of eggs stripped and Average mean number of hatched and un-  
incubated hatched eggs % Hatchability
Replicate (R1) Replicate (R2) Mean Total Hatched Unhatched  
T1 (24L:00D) 500±0.02 500±0.04 1000±0.03 585±0.01 415±0.02 58.5
T2 (18L:06D) 500±0.01 500±0.02 1000±0.02 680±0.03 320±0.01 68
T3 (12L: 12D) 500±0.00 500±0.01 1000±0.01 735±0.02 265±0.01 73.5
T4 (06L:18D) 500±0.02 500±0.00 1000±0.02 860±0.02 140±0.02 86
T5 (00L:24D) 500±0.03 500±0.01 1000±0.02 925±0.01 75±0.03 92.5

After twenty-one days of the hatching, the live, deformed and dead fish fry were estimated and the percentage mortality and survivability calculated as shown in Table 2. The highest percentage mortalities were recorded in T4 and T5 (15.9%) respectively. It was observed that most of the dead fish fry were not seen may be as a result of cannibalism among the fish fry. Photoperiod regime of 12L:12D (T3) had the highest percentage survivability (94.4%), while the least value was recorded in T5 (77.0%). The percentage of deformed fish fry was highest (13.0%) in T1 and least in T3 (4.9%).

Table 2: Average number and Percentage (%) mortality and survivability of fish fry after twenty one days of hatching.

Photoperiod regimes Average number of Average number and Average number and percentage Average number and
(Treatments) hatched eggs percentage of Live fish larvae of Deformed fish larvae percentage of Dead fish larvae
T1 (24L:0D) 585±0.01 452±0.01 (77.3%) 76 ±0.01 (13.0%) 57±0.02 (9.7%)
T2 (18L:6D) 680±0.03 530±0.02 (77.9%) 52±0.02 (7.6%) 98±0.01 (14.4%)
T3 (12L: 12D) 735±0.02 694±0.03 (94.4%) 36±0.01 (4.9%) 05±0.00 (0.7%)
T4 (6L:18D) 860±0.02 676±0.02 (78.6%) 47±0.02 (5.5%) 137±0.02 (15.9%)
T5 (0L:24D) 925±0.01 712±0.01 (77.0%) 66±0.02 (7.1%) 147±0.02 (15.9%)

The result of the physic-chemical parameters of the aquaria tanks is presented in Table 3. Water temperature was within the range of 26.7-26.9°C throughout the experiment, while mean values obtained for Dissolve Oxygen (DO), pH and nitrate ranged between 6.3-6.5 mg/L, 7.5-7.9 and 0.22-0.23 mg/L respectively. There was no significant difference (p>0.05) in the values obtained for the water parameters among the treatments. Optimal water condition was maintained for the fish throughout the experiment to forestall poor results.

Table 3: Water quality parameters in all treatments during the experiment.

  Photoperiod regimes
Water Parameters T1 (24L:0D) T2 (18L:6D) T3 (12L: 12D) T4 (6L:18D) T5 (0L:24D)
Dissolved oxygen (mg/L) 6.5±0.22 6.3±0.21 6.5±0.20 6.5±0.22 6.3±0.21
pH 7.5±0.20 7.6±0.15 7.9±0.21 7.7±0.22 7.6±0.20
Temperature (0C) 26.7±0.21 26.9±0.17 26. 7±0.21 26.5±0.21 26.7±0.20
Nitrate (mg/L) 0.22 ± 0.002 0.23 ± 0.002 0.22 ±0.001 0.23 ± 0.003 0.23 ± 0.001

Means along the horizontal row are not significantly different (P>0.05).

The growth response of the fish larvae under the five different photoperiod regimes (T1-T5) in six weeks after hatching is presented in Table 4. There were significant differences (p<0.05) in growth performance of hybrid (H. bidorsalis X C. gariepinus) larvae. The mean weight gain value was highest in T5 (91.2±0.21) mg, followed by T4 (86.0±0.20) mg and least in T1 (59.0±0.22) mg respectively. The instantaneous growth rate expressed as Specific Growth Rate (SGR) was significantly highest (p<0.05) in T5 (9.16) and least in T1 (8.22).

Table 4: Growth response of hybrid catfish (hetero-clarias) larvae in six weeks after hatching.

  Photoperiod Regimes
Growth Parameters T1 (24L:0D) T2 (18L:6D) T3 (12L: 12D) T4 (6L:18D) T5 (0L:24D)
Initial Mean Weight (mg) 1.5 ± 0.01 1.5 ± 0.01 1.5 ± 0.01 1.5 ± 0.01 1.5 ± 0.01
Final Mean Weight (mg) 60.5 c ± 0.20 63.6 c ± 0.22 76.8 b ± 0.20 87.5 b ± 0.20 92.7 a ± 0.20
Average Weight gain (mg) 59.0 c ± 0.22 62.1 c ± 0.20 75.3 b ± 0.22 86.0 a ± 0.20 91.2 a ± 0.21
SGR 8.22c 8.33c 8.75 b 9.06b 9.16a

Means values with similar superscripts along the horizontal row are not significantly different (P>0.05).

Discussion

The effect of photoperiod on the reproduction of fish species is an important factor to be studied [14]. The duration of exposure to light and darkness of fish gametes influences eggs fertility, hatchability and survival of the fish larvae [15]. In this study, eggs incubated under the total darkness of 24 hour had the highest hatchability, while the lowest hatchability was recorded in the 24 hour light exposure. This was in line with the result obtained by Okwiri (2015), on the hatchability of O. niloticus eggs using white light as background, which recorded poor hatchability [16]. This study further showed that larvae of hybrid catfish (Hetero-clarias) were photophobic like Heterobranchus bidorsalis [17]. But contrary to the report of Puvanendran and Brown (2002) that observed highest growth rate and survival of G. Morhua larvae under 24 hour photoperiod (continuous light exposure) [8], this study indicated best growth performance of hetero-clarias larvae under complete darkness. The difference in reaction to photoperiod is most likely attributed to the different conditions of the environments that the fishes were collected from, which may affect the functionality of their visual system to food [18]. G. Morhua is a photoreceptor and marine fish, unlike hetero-clarias that is of freshwater origin. With this in mind, the natural environment of a fish should be taken into consideration when determining the correct photoperiod for its reproduction [19-20].

To improve the reproductive management of the hybrid catfish larvae, especially when rear in captivity, feeding under dark environment would be appropriate since the larvae are photophobic. Also in this study, since hatchability of eggs was very low under long light exposure, high percentage hatchability of eggs of hybrid catfish in hatcheries should be under complete darkness. Despite the highest growth performance recorded at 24hour of darkness in this study, deformed fish larvae were equally highest compared to other photoperiod regimes. This observation could be related to the assertion of El- Sayed and Kawanna, (2007) that fish species exposed to incorrect hour of photoperiod could be severely crippled and may not develop properly [21]. In addition, photoperiod may not be the only variable affecting morphology, feeding, growth and survival rates of fish larvae [22]. Though some tropical fish species thrive in extended photoperiods [23], to have a successful propagation of this species, continuous light exposure should be avoided since it impairs development.

In this study, highest survivability of fish fry at six weeks of experiment was recorded under equal light and dark exposure (12L:12D). This result was close to the findings of Kiyono and Hirano (1981) on Mylio macrocephalus (Black porgy) who reported that under a 13 hour photoperiod there was a higher survival rate than at extended photoperiod [24]. Also, similar to the result obtain in this study, Puvanendran and Brown (2002) reported that larvae of Salmo gairdneri kept under moderate darkness had a significantly higher specific growth rate, survival rate compared with larvae reared at other photoperiod regimes [8]. It is expected that increased photoperiod is often associated with increased activity levels through the amount of exercise the fish larva performs [9]. These effects vary based on the species and larvae stage being studied [23]. Some fish larvae perform considerably better under longer light exposure, while others suffer under the same conditions. Luiz et al (2012) reported that fish larvae that cannot properly identify food due to low light exposure would have decreased survival and growth rate [14]. This report was contrary to the result obtained in this study in support of Adewolu et al (2008) that, photoperiod effects vary on species of fish and stage of growth of the larvae [23]. Feeding prior to utilization of barbells to search for food influences high survival and growth performances [25]. In this study, highest mortality of fish fry at six weeks of experiment was at longest hour of darkness (24h), due to observed cannibalism. Wasiu and Ofelia, (2014) reported cannibalism to be unavoidable in many fish species especially catfishes, therefore suggested adlibitum feeding and low stocking density [17].

Conclusion

The contribution of this study to the growth of aquaculture in Nigeria is the establishment of the appropriate photoperiods for the artificial propagation of hybrid catfish (hetero-clarias). The present knowledge would help in successful propagation of this species by incubating and hatching of eggs under complete darkness, while raising of healthy fish larvae with optimum survivability requires equal light and darkness exposure. In addition, the implications of inappropriate photoperiods from this study contribute to the understanding of the biology of hybrid catfish (Heterobranchus bidorsalis X Clarias gariepinus) to the growth of aquaculture. Exposing fertilized eggs to continuous light worsen hatchability, while longer darkness exposure reduces survivability of fish larvae. Future studies may look at the combine effect of other factors such as water transparency, water source, heat and source of live food with photoperiods on fish performance.

References

1. Adewumi AA, Olaleye VF. Catfish culture in Nigeria: Progress, prospects and problems. African Journal of Agricultural Research. 2011; 6: 1281-1285.

2. Adeogun OA, Ayinla OA, Ajana AM, Ajao EA. Economic impact assessment of hybrid catfish (Hetero-clarias) in Nigeria. Technical Report of National Agricultural Research Project (NARP). NIOMR, Victoria Island, Lagos, Nigeria. 1999: 27.

3. Olaleye VF. A review of reproduction and gamete management in the African catfish, C. gariepinus (Burchell). Ife Journal of Science. 2005; 7: 63-70.

4. Oresegun A, Oguntade OR, Ayinla OA. A review of catfish culture in Nigeria. Nigerian Journal of Fisheries. 2007: 4: 27- 52.

5. Phelps RP. Recent advances in fish hatchery management. Brazilian Journal of Animal Science. 2010; 39: 95-101.

6. Zheng W. Review, culture of catfish in China. Aquaculture. 1988; 75: 35-44.

7. Pena R, Dumas S, Saldivar-Lucio R, Garcia G, Trasvina A, Hemandez Ceballos D. The effect of light intensity on first feeding of the spotted sand bass Paralabrax maculatofasciatus (steindachner) larvae. Aquaculture Research. 2004; 35: 345-349.

8. Puvanendran V, Brown J. Foraging, growth and survival of Atlantic cod larvae in different light intensities and photoperiods. Aquaculture. 2002; 214: 131 151.

9. Batty R. Effect of light intensity on activity and food- searching of larval herring, Clupea harengus: A laboratory study. Marine biology. 1987; 94: 323 327.

10. Brown J, Puvanendran V. Effect of light intensity on the forging and growth of Atlantic Cod larva: Inter-population differences? Marine Ecology Progress Series, 1998; 167: 207-214.

11. Aluko PO, Ali MH. Production of eight types of fast growing intergeneric hybrids from four Clariid species. J. Aqua. Trop. 2001: 16: 139-147.

12. Jensen AL. Berverton and Holt life history invariants results from optimal trade-off of reproduction and survival. Can J Fish. Aquat.Sci. 1996; 53: 820 822.

13. Duncan DB. Multiple ranges and multiple F-tests. Biometrics. 1955; 11:1-42.

14. Luiz GG, Haluko M, Joao BKF. Effect of photoperiod on reproduction of Siamese fighting fish (Betta splendens) R. Bras. Zootec. 2012; 41: 821-826.

15. Watanabe WO, Woolridge CA, Daniels HV. Progress toward year-round spawning of southern flounder broodstock by manipulation of photoperiod and temperature. Journal of the World Aquaculture Society. 2006; 37: 256 272.

16. Okwiri B. Effect of tank background color on the hatchability of O. Niloticu eggs and survival of fry. International Journal of Fisheries and Aquatic Studies.2015; 2: 81-86.

17. Wasiu AO, Ofelia GO. Embryonic and larval developmental stages of African catfish Heterobranchus bidorsalis (Geoffroy Saint Hilaire, 1809) Teleostei, Clariidae). Springerplus.2014; 3: 677.

18. Downing G, Litvak MK. The effect of photoperiod, tank colour and light intensity on growth of larval haddock. Aquaculture International. 2000; 7: 369-382.

19. Bromage NR, Porter M, Randall C. The environmental regulation of maturation in farmed finfish with special reference to the role of photoperiod and melatonin. Aquaculture. 2001; 197: 63-98.

20. Appelbaum S, Kamler E. Survival, growth, metabolism and behaviour of Clarias gariepinus (Burchell) early stages under different light conditions. Aquacult. Eng. 2000; 22: 269-287.

21. El-Sayed AFM, Kawanna M. Effects of photoperiod on growth and spawning efficiency of Nile tilapia (Oreochromis niloticus L.) broodstock in a recycling system. Aquac Res 2007; 38: 1242-1247.

22. Boeuf G, Le Bail PY. Does light have an influence on fish growth? Aquaculture. 1999; 177: 129-152.

23. Adewolu MA, Adeniji CA, Adejobi AB. Feed utilization, growth and survival of Clarias gariepinus (Burchell 1822) fingerlings cultured under different photoperiods. Aquaculture. 2008; 283: 64-67.

24. Kiyono M, Hirano, R. Effects of light on feeding and growth of black porgy Mylio macrocephalus (Basilewsky), post larvae and juveniles. Cons. Int. Explo Mer. 1981:178: 334-336.

25. Olaniyi WA, Omitogun OG. Stages in the early and larval development of the African catfish Clarias gariepinus (Teleostei Clariidae). Zygote. 2013; 22: 314-330.

Other Articles

Article Image 1

Massive Chinese Fleet Jeopardizes Threatened Shark Species around the Galápagos Marine Reserve and Waters off Ecuador: Implications for National and International Fisheries Policy

Being a UNESCO-World Heritage Site, the Galápagos harbors the largest global shark biomass in the world’s oceans and a unique marine biodiversity.

Alava JJ1,2*, Barragán-Paladines MJ3, Denkinger J4, Muñoz-Abril L4, Jiménez PJ2, Paladines F5, Valle CA4, Tirapé A6, Gaibor N7, Calle M6, Calle P6, Reyes H8, Espinoza E8 and Grove JS9


Article Image 1

The Relationship between Behavior Responses and Brain Acetylcholinesterase (AChE) Activity of Zebrafish (Danio rerio) in Cadmium Stress

In this research, the toxic effects of Cadmium chloride (CdCl2 ), which can seriously pollute aquatic environment and threaten human health, are evaluated based on the behavior responses and the brain Acetylcholinesterase (AChE) activity of zebrafish (Danio rerio). The results showed that Behavior Strength (BS) of test groups (changed from 0.15 to 0.65), which was recorded using an online behavior monitoring system, was lower than the control groups (changed from 0.65 to 0.85). The behavior responses of zebrafish suggested that both dose and time effect relationships existed between Cd2+ stress and zebrafish BS. Meanwhile, the brain Acetylcholinesterase (AChE) activity of zebrafish were strongly inhibited by Cd2+: the AChE activities were lower than 60% after 0.5h Cd2+ exposure in both 1 TU (Toxic Unit) and 2 TU. The AChE activities in 0.1 TU Cd2+ treatment were about 60% in the first 2h and then increased to about 100% in 4h with a decrease tendency in the following exposure time (8h to 48h), which changed from 100% to 70%-80%. Totally, the brain AChE activities of zebrafish showed similar rules with BS after correlation analysis, which might provide an understanding of the ecotoxicological assessment of heavy metal Cd based on zebrafish.

Meiyi Yang1,2#, Lizhen Ji1,2#, Xu Zhang2, Yuqi Fan1,2* and Zongming Ren1,2*


Article Image 1

Neritic Larval Fish Distribution in the Oceanic Area of the Campeche Bay, Gulf of Mexico

Composition and abundance of larval fishes in Campeche Bay were studied during two seasons, winter, 2013 (24 stations) and summer, 2014 (31 stations). Sampling was carried out with open-close nets, mouth 75 cm and 505 µm mesh. The data of salinity and temperature allowed distinguishing three oceanic sub-regions: North, East, and West. There were 236 taxa, belonging to 74 families, 168 species, 154 taxa occurred in winter and 171 in summer; the composition in both cruises was similar with around 70 % of oceanic and 30 % of neritic larvae. The larval density was almost three times larger in summer than winter. The Campeche Bay hydrodynamics fits well with the results; the West sub-region is located where a cyclonic gyre takes place, the North and East sub regions are located in the area of influence of warm currents over the Yucatan shelf. The hydrodynamics also allows understanding the differences in the proportion of neritic larvae among the three oceanic sub-regions, the West and East with the lower and higher number of neritic larvae, respectively. The large difference among regions is related to some neritic taxa occurring exclusively in some of them. Of the total taxa, 55 neritic occurred only once and it means that more than a half of neritic taxa were represented by one organism, 31 from 85 neritic taxa occurred in the layers of 600 to 1000 m depth. Of the neritic larvae, only Syacium papillosum and Apogon sp. appear among the 20 more abundant.

Flores-Coto C*, Zavala-García F and Sanvicente-Añorve L


Article Image 1

Empirical Assessment of Fish Diversity of Uttar Pradesh, India: Current Status, Implications and Strategies for Management

About 60-70% of world’s biological resourcesis contributed by India, of which fish represents 80% of the global fishes. Uttar Pradesh blessed with vivid aquatic bioresources in innumerable forms contributes about 14.68% of Indian fish biodiversity with substantial scope of inland fisheries development and aquaculture. Ganga, the mighty river of this state reportsabout 265 freshwater species from its river system [1]. Besides, other rivers viz. Ramganga, Gomti, Ghaghara, Yamuna, Gandak, Kosi and Damodaract as reservoir of different f ish stocks. In past, no study highlights the assessment of the fish biodiversity of this state in holistic way except by Khan (2000) who justreported a compilation of 129 fishes under 27 families [2]. To substantiate and revise the assessment, the fish diversity of this state was assessed by investigating these rivers, analyzing and documenting the information on different fisheries measurements including biology, distribution and conservation status. About 10,000 individuals were collected and the analysis of individuals revealed 126 fish species under 28 families and 74 genera nearly mitigating the earlier reports. The highest species diversity was recorded in the river Ganga (90) followed by Gerua (87) and then Gomati (68). 37 species were found common in Gomati, Ghaghara, Ganges, Son, Tons and Yamuna. Out of 90 species, 6 species were recorded from the river Ganga. In addition, the new distribution of a threatened torrent catfish Amblyceps mango is was recorded from the rivers Gomati, Ganga and Ramganga. The economical assessment unravels nearly 33% as ornamental, 87% as food and 10% as sport fishes.

Pathak AK*


Article Image 1

Stranding of Small Cetaceans with Missing Fins Raises Concerns on Cetacean Conservation in Ecuador: Bycatch or Targeted Fisheries?

Among anthropogenic threats to marine mammals, bycatch is one of the major and increasing concerns. This report describes three species of small cetaceans, including a short-beaked common dolphin (Delphinus delphis), a bottlenose dolphin (Tursiops truncatus), and two dwarf sperm whales (Kogia sima), which were found stranded with pectoral fins, dorsal fins and caudal fin removed. The dolphins were found at the beaches of San José de Las Nuñez and San Pablo, respectively (Santa Elena Peninsula Province on 14 August 2017), while the dwarf sperm whales were found in Puerto Lopéz and Crucita (Manabí Province) in July 2014 and August 2015, respectively. Possible explanation for the dolphins and dwarf sperm whales missing fins support the event as a possible case of fishery interaction or bycatch with systematic removal of their fins. Although remnants of artisanal gillnets were not found near the two dolphin species, one of the dwarf sperm whales showed marks of artisanal gillnets on the body as evidence of bycatch. Trade of dolphin carcasses and their parts for bait by fishers cannot be ruled out as there is some evidence of this practice in the past. Both dolphins species are vulnerable species at the national level and commonly involved in incidental captures with gillnets of artisanal fisheries in Coastal Ecuador. Cetacean bycatch is a grave conservation problem affecting several cetacean species in Ecuador’s waters. Fisheries and environmental authorities must be vigilant and enforce actions to proactively mitigate possible anthropogenic impacts and promote environmental education activities in fishing communities to conserve vulnerable dolphin species in Ecuador’s waters. Further, to comply with new rules and regulations of the US Marine Mammal Protection Act (MMPA) intended to reduce the bycatch of marine mammals in foreign commercial fishing operations that export fish and fish products to the United States, a regulatory program is urgently needed to mitigate and reduce fisheries interactions with marine mammals in Ecuador.

Pedro J Jiménez1, Juan José Alava1,2*, Cristina Castro3, Jorge Samaniego4 and Patricia Fair5


Article Image 1

Sodium Arsenite-induced Morphological, Behavioral, Hematological and Histopathological abnormalities in Labeo Rohita

Toxic metals have contaminated the aquatic ecosystems to a large scale, and they eventually enter human systems by contaminated air, food, water and soil. Recently, arsenic toxicity has become an alarming concern around the globe. Major areas of North-Eastern states of India have been demarcated with an arsenic content of 50-1000 µg/l in drinking water sources and aquatic ecosystems. Arsenic range in Barak Valley is many folds higher than the permissible limit of WHO and BIS as 10µg/l and 50µg/l respectively, which is present in the form of Sodium Arsenite in water. Fishes are the major dwellers of aquatic ecosystem and serves as good bio-indicators for determination of health status of an aquatic ecosystem. They also form the staple diet of North Eastern people. Labeo rohita is one of the most commonly available and consumed in large scale. The present study was carried out in Labeo rohita in vivo. Labeo rohita (n=10) of similar size and weight were exposed to sodium aresnite at concentrations 100 µg/l and 250 µg/l along with controlled set up for 10 days. The morphological, behavioral, hematological and histopathological changes were evaluated. Fishes exposed to Sodium arsenite showed irregular ocular movement, fin movement, swimming pattern and loss in scales with higher prominence in 250 µg/l of arsenic group than those at 100 µg/l. The hematological indices revealed decrease in RBC count and increase in WBC count in both sodium arsenite exposed groups. The histopathological study of liver revealed parenchymal disorganization and atypical residual body in both sodium arsenite treated groups. Results obtained showed major damages to fishes due to contamination with sodium arsenite. These fishes, when consumed by humans, leads to increase in several thousand folds of sodium arsenite by means of biomagnification. High exposure of arsenic in human through fishes leads to several disorders. The possible way of eradicating sodium arsenite entry into humans is banning fishing activities in highly contaminated aquatic ecosystems. Community education and local participation are also essential to get a fruitful outcome.

Rajib Biswas1* and Soumitra Nath2


Article Image 1

Reconstruction of Historical Fisheries Profile of Cameroon

This work attempts to reconstruct historical fisheries profile by filling in the missed underestimated catch information for some reasons of industrial fishing, artisanal fishing, inland fishing, illegal fishing, discards and aquaculture production of Cameroon from 1950 to 2016.This reconstruction was carried out based on data published by various authors, the Ministry of Fisheries and Livestock (MINEPIA), the Limbe Research Center on Fisheries and Oceans and FAO reports. The dataset allowed us to reconstruct the fishing profile of Cameroon by completing the missing data by interpolation. Then we compare the data obtained with those of FAO. Reconstructed catches were estimated at 13,834 tons and aquaculture production was estimated at 19 tons in 1950 compared to 12,000 tons and 14 tons published by FAO, With the agricultural reforms and development of projects focused on the primary industry, catches increased around 94,122 tons in 1977(compared to 70,167 tons reported by the FAO) to 102,975 tons in 1981(compared to 79,761 tons reported by the FAO), declined to 78,790 tons in 1986 because of the reduction of the Exclusive Economic Zone of Cameroon (EEZ) by the geographical presence of the insular part of Equatorial Guinea (Malabo Island), then increased to 186,204 tons in 2005(compared to 142,345 tons reported by the FAO), declined to 154,800 tons in 2008(compared to 129,000 tons reported by the FAO). Since 2011 it became stable and reached around 240,000 tons against 220,000 tons published by FAO. Overall, there are discrepancies between the reconstructed data and the data provided to FAO: the reconstructed data is 30% higher than the FAO data. This information about fisheries production in Cameroonian waters shows that many locals, fisheries managers and stakeholders depends on fish products for either incomes or food safety; therefore, the recent decline of fish production in Cameroon is of no good sign to the abovementioned persons. These observed fish production decline indirectly threatens the food security of the people of Cameroon and low financial income to the state coffers.

Nyatchouba Nsangue Bruno Thierry, Richard Kindong and Liuxiong Xu*


Article Image 1

Effect of Fishmeal Substitution by Lima Bean Meal on the Zoo Technical Performances of African Catfish (Clarias gariepinus) in the Bati

A study on the effect of the substitution of fishmeal by Lima bean flour was conducted between March and May 2018 within the AIO ICG of the Batié District, with the global objective of contributing to the development of alternative sources of animal protein. Specifically, the aim of the study was to evaluate the effect of the substitution of fishmeal by Lima bean flour on the growth performance, survival and feed cost of Clarias gariepinus. For this purpose, 300 fry of Clarias gariepinus with an average weight of 3 ± 1.41g were divided into five batches and fed three times a day with rations corresponding to 5% of their ichthyo biomass. The rations R0, R25 R50, R75 and R100 respectively corresponded to the substitution rates of 0, 25, 50, 75 and 100% of fish meal by that of Lima bean. The physic-chemical characteristics of the water (pH, temperature, dissolved oxygen, nitrites and nitrates) were measured daily. The following results were obtained: The highest weight gains were obtained with the rations R25 (20.56 ± 0.40 g), R50 (20.64 ± 0.32 g), R75 (20.98 ± 0.46 g) and the lowest with the ration R100 (16.21 ± 0.28 g). For this average daily gain, the highest values were 0.36 ± 0.02 g; 0.37 ± 0.01 g, 0.38 ± 0.01 g respectively for the R0, R50 and R75 rations and the lowest with R100 (0.29 ± 0.01 g). The highest value of the specific growth rate (2.47 ± 0.07%) was obtained with the ration R0 and the lowest (1.61%) with the ration R100. The consumption index reached its highest and lowest values with the rations R100 (4.74 ± 0.42) and R50 (3.57 ± 0.43) respectively, compared to the value of the ration R0 (3.31 ± 0.37) for this parameter. Concerning the condition factor K, the highest value was recorded with the R50 diet (1.11 ± 0.49) while the lowest value was obtained with the R75 diet (0.95 ± 0.45). The cost of producing one kilogram of food was higher with the R25 ration (504.59 FCFA) and lower with the R100 ration (443.20 FCFA). This study found that incorporating 75% Lima bean flour into the feed increases the growth performance of Clarias gariepinus fry and reduces the cost of food production.

Emile Miégoué1*, Pégis Davy Tagning Zebaze2, Fernand Tendonkeng1, Lemoufouet Jules1, Nadège Elvire Njoh2, Ronald Komguep Nganyo2 and Etienne Tedonkeng Pamo1


Article Image 1

Comparative Effect of Monoculture and Polyculture in Two Species of Clariidae: Heterobranchus longifilis and Clarias gariepinus in Post Fingerlings Growth

In order to improve the production of Clariidae, a study on the type of cultivation of Heterobranchus longifilis and Clarias gariepinus in post fingerlings growth phase was carried out in tanks. It took place from March to May 2018 at the IRAD fish station in Koupa-Matapi (LN: 5º 21 ‘to 5º 58’ and LE: 10º 17 ‘to 11º 02’) west region Cameroon. For this fact 180 fry therefore 90 Heterobranchus longifilis and 90 Clarias gariepinus with an average weight 3.55 ± 0.68 g; 8.46 ± 0.41cm of total length and 7.37 ± 0.30 cm of standard length were used. The 180 fry were divided into three treatments of 60 individuals (T1 treatment: Clarias gariepinus, T2 treatment Heterobranchus longifilis and T3 treatment: Clarias gariepinus + Heterobranchus longifilis). Each treatment was repeated twice. The fish were fed twice per day at a rate of 10% of the ichthyobiomass readjusted each month after control fishing with a feed at 42% crude protein. From the results of this trial, it appears that unlike the higher mortality rates (11.66 ± 2.36%) recorded in monoculture Clarias gariepinus, the highest cannibalism rates were obtained in monoculture of Heterobranchus longifilis (13.33 ± 4.71%). The survival rate was not influenced by the type of culture. Nevertheless, the highest rate (94.44 ± 0.00%) was observed in Heterobranchus longifilis in polyculture. The highest growth values were recorded for C. gariepinus in polyculture and the weakest for H. longifilis in polyculture. For linear growth, the highest values were recorded in C. gariepinus in monoculture. In order to reduce the rate of cannibalism and mortalities in Clarias gariepinus and Heterobranchus longifilis in post f ingerlings growth phase, it is preferable to combine these two species.

Nana Towa Algrient¹, Nanmegni Rostand Romeo¹, Tonfackachille Peguy², Efole Ewoukem Thomas¹ and Jouokou Salifou²


Article Image 1

Delayed Fertilization of Landlocked Fall Chinook Salmon Eggs Stored with Oxygen at Two Temperatures

This study examined the use of supplemental oxygen and two temperatures (1° and 11°C) during the four hour storage of unfertilized landlocked fall Chinook salmon (Oncorhynchus tshawytscha) eggs from Lake Oahe, South Dakota, USA. There was a significant and positive effect of oxygen use on egg survival to the eyed-stage and hatch. In addition, survival to egg eye-up and hatch was significantly affected by storage temperature, with decreased survival at 1°C. However, there was no significant interaction observed between the use of oxygen and storage temperature. Mean survival to hatch ranged from 50% for those eggs stored with oxygen at 11°C compared 17.8% for those eggs stored on ice at 1°C in air. To maintain landlocked Chinook salmon egg fertility, storage with supplemental oxygen at 11°C is recommended.

Hunter Eide and Michael E Barnes*