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International Journal of Fisheries Science and Research

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

Abstract Citation Introduction Field Observations and Case Report Discussion Acknowledgements References
Details

Received: 28-Apr-2018

Accepted: 30-Apr-2018

Published: 01-May-2018

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

1Fundación Ecuatoriana para el Estudio de Mamíferos Marinos (FEMM), Guayaquil, Ecuador 2Institute for the Oceans and Fisheries, University of British Columbia, Canada 3Pacific Whale Foundation-Ecuador, Malecón Julio Izurieta, Puerto López, Puerto López, Ecuador 4World Wildlife Fund-Ecuador, Ecuador 5Department of Public Health Science, Medical University of South Carolina, United States

Corresponding Author:

Juan José Alava, Institute for the Oceans and Fisheries, University of British Columbia, Vancouver, BC V6T 1Z4, Canada, Tel: 604-291-0019

Abstract

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.

Citation

Jiménez PJ, Alava JJ, Castro C, Samaniego J and Fair P. Stranding of Small Cetaceans with Missing Fins Raises Concerns on Cetacean Conservation in Ecuador: Bycatch or Targeted Fisheries?. Int J Fisheries Sci Res. 2018; 2(1): 1006.

Introduction

Cetaceans are a key functional group of marine mammals inhabiting Ecuador’s marine waters where they play a crucial role as apex predators controlling top down process [1], but facing several anthropogenic threats at the local, regional and global levels, where bycatch is the top threat [2-4].

Bycatch events of small cetacean species interacting with small-scale (artisanal) fisheries such as gillnets include several species of dolphins such as the common dolphin (Delphinus delphis), spotted dolphin (Stenella attenuata), bottlenose dolphin (Tursiops truncatus) and Risso’s dolphin (Grampus griseus) [5-8]. Other bycatch mortalities of small cetaceans include pilot whales (Globicephala sp.) and the dwarf sperm whale (Kogia sima) [6-8]. For instance, common dolphin is the most frequently bycaught species by fisheries interactions in Ecuador (e.g., Santa Rosa in Santa Elena Province) with an estimate of 98 and 251 dolphins captured from July to October 2009 (i.e. 0.5 dolphins/day) and from February to December 2010 (i.e. 0.76 dolphins/day), respectively [7]. Common dolphins make up of between 70% and 90% of the total composition of bycaught dolphins [5,7]. These estimations are one of the highest bycatch rates for any cetacean species in Ecuador’s marine waters [3].

In addition to bycatch, some species inhabiting Ecuador’s coastal zones such as the vulnerable bottlenose dolphins (T. truncatus) are impacted by other anthropogenic threats including chemical pollution, diseases and habitat disturbances with marked signs of population decline [9-11].

While the stranding of dolphins and other cetaceans are frequently recorded along Ecuador’s coast, little is known about targeted fisheries of dolphins for human consumption and/or bait to be used in illegal fishing activities. During the early 1990’s, the take and market of dolphin carcasses for bait by fishers in Puerto López (Manabí Province) and Puerto Bolívar (El Oro Province), fishing ports located at the central and southern coast of Ecuador, respectively, has previously been reported [5,23]. Currently, due to the lack of surveys and field monitoring, there is no evidence to confirm whether this practice may still persist in Ecuador.

The occurrence of stranded small cetaceans with missing fins raises red flags for the conservation of these species and questions linger on the origin of this event. Here, we communicate recent stranding events involving the presence of two dwarf sperm whales and two species of dolphins from which their fins were apparently removed in coastal Ecuador in 2014, 2015 and 2017 and discuss the possible causes associated to these findings.

Field Observations and Case Report

On 14 August 2017, two species of dolphins were found stranded with either pectoral fins or caudal fin removed, at the beaches of San Joséde Las Nuñez (1.73°S, 80.78°W)and San Pablo (2.15°S, 80.78°W), respectively (Santa Elena Peninsula Province, Ecuador) (Figure 1).

Figure 1: Map of Ecuador illustrating the mainland coast and the fisheries villages, including San Joséde Las Nuñez (1.73°S, 80.78°W) and San Pablo (2.15°S, 80.78°W) in Santa Elena Peninsula Province, where the dolphins were found in August 2017, as well as Puerto López (1°25’S, 79°55’W) and Crucita (0°52’ S, 80°32’W) in Manabí Province, where the two dwarf sperm whales were recorded in July 2014 and August 2015. Other locations, including Puna Island and Puerto Bolívar, where there was respectively evidence of trade, harpooning and use of dolphin as bait in the past [5,24], are also shown in the map.

The species were identified as the short-beaked common dolphin (Delphinus delphis), from which their pectoral fins were systematically cut and removed, and a bottlenose dolphin (Tursiops truncatus), from which the caudal fin or tail was missing, according to officials of the Ministry of Environment of Ecuador (MAE) and rangers from the El Pelado Marine Reserve (Figure 2) [12].

Figure 2: Two dolphins identified as belonging to the species common (Delphinus delphis) and bottlenose (Tursiops truncatus) dolphins were found dead on the beaches of San Jose de Las Nuñez and San Pablo, Santa Elena Peninsula, on August 15, 2017. The common dolphins were found without pectoral fins, while the bottlenose dolphin was missing its caudal fin or tail (see photo). The photo was originally published by the newspaper Diario EL COMERCIO on 18 August 2017 at the following link [12].

This government entity conducted an investigation to elucidate the cause of the dolphins’ mortality as several conservation concerns were raised by local coastal communities and the general public in the face of this alarming finding.

On July 2014, a dwarf sperm whales (Kogia sima) showing systematic cuts of the caudal fin and external gillnets marks due to entanglement on the body was found in Puerto Lopez (1°25’S, 79°55’W), Manabí Province (Figures 3A and 3B). A second stranded dwarf sperm whale without the dorsal fin was found in Crucita (0°52’ S, 80°32’W), Manabí Province, in 2015 (Figure 3C). These two cases of dwarf sperm whales with removed fins are among the first reports providing evidence of extraction of fins in this particular species in Ecuador.

While questions still remain about the possible causes explaining the mortality of the two dolphins and dwarf sperm whales, we suggest consideration of the following plausible theories:

1. This event may be a possible case of fishing interaction or bycatch with artisanal gill nets, in which the fins were cut to protect the nets instead of giving first priority to rescuing the dolphins. This is further supported by the fact that there are more cases of small cetaceans, in which not only the dorsal fins have been cut, but also the tail, which is usually split in two large parts (Figure 3).

Figure 3: Specimens of dwarf sperm whales (Kogia sima) showing mutilation of fins. A-B) dwarf sperm whale exhibiting lack of caudal fin, which was systematically cut in two portions and removed (white arrows) and marks of entanglements by gillnets on the body (white arrow); this individual was found in the Puerto Lopez (Manabí Province) in July 2014; and, C) juvenile male of dwarf sperm whale missing the dorsal fin found in Crucita (Manabí Province) in August 2015.Photo credits: Pacific Whale Foundation-Ecuador.

These cuts are caused in incidental fisheries, in which the dolphins are trapped and the fishers cut the dorsal fin and tail to save their nets from damage. This is likely to be a common cultural behavior of fishers for lack of environmental education and concern about the ecosystem function role of this species. While remnants of artisanal gillnets were not found near the dolphin bodies to support this possibility, at least one of the dwarf sperm whales showed injuries inflicted by gillnets as indicated by the marks found around the body of the specimens found in Puerto Lopez in 2014 (Figures 3A and 3B). Cetacean bycatch is a grave and chronic conservation problem affecting several species of small dolphins and humpback whales in Ecuador’s waters [3,5-8,13-15].

2. It cannot be ruled out that this finding may well be a case of targeted fisheries to chase and hunt dolphins to extract internal organs or fins by Asian or South American vessels to be traded in international black markets. Dolphins have been hunted in Peru and there is evidence of the use of marine mammal meat (dolphins) used as bait for fishing in marine waters along the Southeastern Tropical Pacific, mainly in waters off Colombia and Peru [16-18].

3. As a possible case of a predatory event, the attack by predators such as sharks or killer whales (Orcinus orca), which can be found in Ecuador’s marine waters, might also be considered. For instance, killer whales attacks on humpback whales have been recorded along coastal waters of Ecuador [19-21]. For instance, a sighting of a killer whale was reported in August 2017 in Santa Elena Puntilla’s waters (P. Jimenez, pers comm., 2017). However, in this case signs of bites and wounds inflicted by a predator were not found in any of the dead specimens.

Discussion

While the status of the dwarf sperm whale (K. sima) is categorized as Data Deficient (DD) species, both the common (D. delphis) and bottlenose (T. truncatus) dolphins are Vulnerable (VU) species at the national level, according to the Red Book of Mammals of Ecuador [9,22,23]. These three species of small cetaceans are commonly involved in incidental captures with gillnets of artisanal fisheries in Coastal Ecuador [3]. Small cetacean bycatch and the use of dolphins’ meat as bait are pervasive activities along the Pacific coast of South America, mainly in Guatemala, Ecuador, Colombia and Peru [3,4,9,16-18,24-27]. In Ecuador, there is evidence supporting the fact that some fishers were willing to pay up to US $75 for a dolphin carcass to obtain bait in the 1990s [5]. At present, questions linger on whether the trade of bait collected from small cetaceans bycaught continues in Puerto López, but a small scale black market seems to continue in Puerto Bolívar (Figure 1) [5,24], where at least one boat harpooned dolphins in the past [24]. Likewise, at least one bottlenose dolphin was harpooned by fishers nearby Puna Island (Gulf of Guayaquil) (Figure 1) [24]. The use of cast net (a fishing gear locally known as “voladora”) by a fisher from Posorja Habor to directly target and hunt bottlenose dolphins to trade dolphin’s meat in the local markets was anecdotally reported to rangers from the El Morro Mangrove Ecological Reserve in 2017 (Juan Romero, pers. comm., 2017). Meanwhile, the status of this current practice has yet to be fully assessed in coastal Ecuador.

In recent times, the exploitation and occasional hunting of dolphins in fisheries for human consumption in some of these countries have rapidly increased because of the alleged effectiveness of using dolphins’ meat as bait [4,17,18,24-30]. For instance, small cetaceans and sea lions that are incidentally captured in surface gillnets, long-line and purse seiner by fishing operations in Ecuador’s coastal waters are illegally used as bait in Fish Aggregation Devices (FAD) activities [31]. Similarly, fishers use the adipose and fat tissue of dolphins, whales, and porpoises as preferred bait for catching sharks in Brazil [30].

While fisheries targeting or hunting of dolphins for human consumption is currently not a traditional fishing practice by small or large scale fisheries in Ecuador, the occurrence of these stranded dolphins with their fins removed is controversial and raises a red flag in terms of the conservation of cetaceans and illegal fisheries in Ecuadorian marine waters. Conversely, although these episodes may perhaps be considered as isolated cases with a low impact at the population level, the direct hunting of dolphins could signal a more prevalent fishing activity in Ecuador’s waters than previously thought. This illegal activity has the potential to increase because regional fisheries can be depleted by overexploitation [4,32,33]. Thus, a targeted fishery may be developed considering the interactions of some artisanal fleets from Peru and Ecuador that share some fishing zones within the economic exclusive zone. In other words, Ecuadorian fishers could be influenced to pursue this activity because of depleted fish stocks and the need of economical incomes for subsistence.

The new rules and regulations of the US Marine Mammal Protection Act (MMPA) regarding the provisions related to implement import restrictions of fish and fish products from fisheries that have incidental or intentional mortality and serious injury of marine mammals (Federal Register 80 FR 54390 on August 15, 2016, Department of Commerce National Marine Fisheries Service, National Oceanic and Atmospheric Administration [34]) further highlight the need to implement a regulatory program in compliance with the US MMPA regulations to mitigate and reduce cetacean bycatch in Ecuador (e.g., implementation of pingers in the artisanal gillnets fleet [3]). This has tremendous socio-economic implications as Ecuador is in the list of the top 20 exporters of seafood to USA.

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.

Acknowledgements

We specially thank the US Fulbright Award for P. Fair to conduct conservation efforts and research of cetaceans in Ecuador. The authors acknowledge Fundación Ecuatoriana para el Estudio de Mamíferos Marinos (FEMM), Pacific Whale Foundation-Ecuador (PWF), and WWF-Ecuador for their continued commitments to marine mammal conservation and research during the last three decades in Ecuador.

References

1. Alava JJ. Carbon productivity and flux in the marine ecosystems of the Galapagos Marine Reserve based on cetacean abundances and trophic indices. Rev. Biol. Mar.Oceanogr.2009; 44: 109-122.

2. CPPS. Memorias del Taller de Trabajo sobre el impacto de las actividadesantropogénicas en mamíferos marinos en el Pacifico Sudeste. Bogota, Colombia, 28-29 Noviembre 2006. Comisión Permanente del Pacifico Sur, Guayaquil, Ecuador. 2007.

3. Alava JJ, Tatar B, Barragán MJ, Castro C, Rosero P, Denkinger J, et al. Mitigating cetacean bycatch in coastal Ecuador: Governance challenges for small-scale fisheries. Mar. Policy. 2017.

4. Avila IC, Kaschner K, Dormann CF. Current global risks to marine mammals: Taking stock of the threats. Biol.Conser.2018; 221: 44-58.

5. Félix F, Samaniego J. Incidental catches of small cetaceans in the artisanal f isheries of Ecuador. Rep. Int.Whal.Comm. 1994; 15: 475-480.

6. Castro C, Rosero P. Interacción de cetáceos menores con artes de pesca artesanalen el Parque Nacional Machalilla, Ecuador, In: Comisión Permanente del PacíficoSur - CPPS. Plan de acción para la protección del medio marino y áreas costeras delPacífico Sudeste, 2010.

7. Coello D, Herrera M, Calle M, Castro R, Medina C, Chalén X. Incidencia deTiburones, Rayas, Aves, Tortugas y Mamíferos Marinos en la Pesquería Artesanalcon Enmalle de Superficie en la caleta pesquera de Santa Rosa (Provincia de SantaElena) Ecuador, Instituto Nacional de Pesca (Boletín Especial). 2011; 2: 1-51.

8. Rosero P. Tasa de captura incidental de mamíferos, aves, reptiles y peces cartilaginosos con pesca artesanal en el Área Marina del Parque Nacional Machalilla - Ecuador, Tésis de Licenciatura en Ciencias Biológicas, Universidad Central del Ecuador. 2010.

9. Jiménez P, Alava JJ, Castro C, Denkinger J, Haase B, Utreras V, et al. Delfín nariz de botella, Tursiopstruncatus. In:Tirira DG.Libro rojo de los mamíferos de Ecuador. 2nd edición. IUCN. Fundación Mamíferos y Conservación, Pontificia Universidad Católica del Ecuador (PUCE), Ministerio del Ambiente, Quito, Ecuador.2011; 239-240.

10. Jiménez PJ, Alava JJ. Population Ecology and Anthropogenic Stressors of the Coastal Bottlenose Dolphin (Tursiopstruncatus) in the El Morro Mangrove and Wildlife Refuge, Guayaquil Gulf, Ecuador: Toward Conservation and Management Actions. In: Samuels JB. Dolphins: Ecology, Behavior and Conservation Strategies. Series: Marine Biology. Nova Science Publishers, Inc. Hauppauge, NY, USA. 2014; 131-163.

11. Félix F, Calderón A, Vintimilla M, Bayas-Rea Rosa A. Decreasing population trend in coastal bottlenose dolphin (Tursiops truncatus) from the Gulf of Guayaquil, Ecuador.Aquat.Conserv. Mar.FreshwaterEcosyst.2017; 27: 856-866.

12. EL Comercio. Dos delfines sin aletas fueron hallados en playas de Santa. 2017; 2107. http://www.elcomercio.com/tendencias/delfines-aletas-playas santaelena-ministeriodelambiente.html

13. Alava JJ, Barragan MJ, Castro C, Carvajal R. A note on strandings and entanglements of humpback whales (Megaptera novaeangliae) in Ecuador, J. Cetacea. Res. Manag. 2005; 7:163-168.

14. Alava JJ, Barragan MJ, Denkinger J. Assessing the impact of bycatch on Ecuadorian humpback whale breeding stock: a review with management recommendations.Ocean Coast. Manag. 2012; 57: 34-43.

15. Félix F, Muñoz M, Falconi J, Botero N, Haase B. Entanglement of humpback whales in artisanal fishing gear in Ecuador, J. Cetacea. Res. Manag. 2011; 3: 285-290.

16. Van Waerebeek K, Van Bressem MF, Reyes JC, Alfaro JA, Bello R, Echegaray M, et al. Illegal Exploitation of Small Cetaceans in Peru. Final Report to United Nations Environment Programme, Nairobi, and the Whale and Dolphin Conservation Society, UK. 1994.

17. Avila IC, Garcia C, Bastidas, JC. A note on the use of dolphins for bait in the artisanal fisheries off Bahia Solano, Choco, Columbia. J.Cetac. Res. Manage. 2008; 10: 179-182.

18. Mangel JC, Alfaro-Shigueto J, Van Waerebeek K, Cáceres C, Bearhop S, Witt MJ, et al. Small cetacean captures in Peruvian artisanal fisheries: high despite protective legislation. Biol.Conser. 2010; 143: 136-143.

19. Scheidat M, Castro C, Denkinger J, González J, Adelung D. A breeding area for humpback whales (Megaptera novaeangliae) off Ecuador. J.Cetac. Res. Manage. 2000; 2: 165-172.

20. Castro C, González J. Población de la ballena jorobada Megaptera novaeangliae Balaenopteridae, en el Parque Nacional Machalilla, Ecuador. DoctorateThesis, Universidad Central del Ecuador. 2002.

21. Alava JJ, Smith KJ, O’Hern J, Alarcόn D, Merlen G. Denkinger J. Observations of killer whale (Orcinus orca) attacks on Bryde’s whales (Balaenoptera edeni) in the Galapagos Islands. Aquat.Mamm. 2013: 39: 196-201.

22. Alava JJ, Castro C, Denkinger J, Haase B, Utreras V, Tirira DG, et al. Delfín común de hocico largo (Delphinusdelphis). In:Tirira DG.Libro rojo de los mamíferos de Ecuador.2da edición. IUCN. Fundación Mamíferos y Conservación, Pontificia Universidad Católica del Ecuador, Ministerio del Ambiente, Quito, Ecuador.2011; 235-236.

23. Castro C, Denkinger J, Haase B, Utreras V, Alava JJ, Tirira DG. Cachalote enano (Kogia sima). In: Tirira DG. Libro rojo de los mamíferos de Ecuador.2da edición. IUCN. Fundación Mamíferos y Conservación, Pontificia Universidad Católica del Ecuador y Ministerio del Ambiente del Ecuador. Quito, Ecuador. 2011.

24. Van Waerebeek K, Van Bressem MF, Félix F, Alfaro-Shigueto J, García GodosA, Chávez-Lisambart L, et al. Mortality of dolphins and porpoises in coastal fisheries off Peru and southern Ecuador in 1994. Biol.Conser. 1997; 81: 43-49.

25. Majluf P, Babcock EA, Riveros JC, Arias Schreiber M, Alderete W. Catch and bycatch of sea birds and marine mammals in the small-scale fishery of Punta San Juan, Peru. Conser. Biol. 2002; 16: 1333-1343.

26. Quintana-Rizzo E. Harpooning and entanglement of wild dolphins in the Pacific coast of Guatemala. Lat. Am. J.Aquat.Mamm. (LAJAM). 2014: 9: 179-182.

27. Read A, Van Waerebeek K, Reyes J, Mckinnon JS, Lehman LC. The exploitation of small cetaceans in coastal Peru. Biol.Conser. 1988; 46: 53-70.

28. Van Waerebeek K, Reyes J. Catch of small cetaceans at Pucusana port, central Peru, during 1987. Biol.Conser. 1990; 51: 15-22.

29. Goodall RNP, Galeazzi AR, Lichter AA. Exploitation of small cetaceans off Argentina 1979-1986. Rep. Int.Whal. Comm.1988; 38: 407-410.

30. Barbosa-Filho MLV, Barreto RMF, Siciliano S, Seminara CI, Costa-Neto EM 2018. Use of Cetaceans as Bait in Southern Bahia, Brazil, by Expert Fishermen that Market Shark Fins: A Lucrative Trade and Two Threatened Zoological Groups. Ethnobiol. Lett. 2018; 9: 12-18.

31. Castro C, Cardenas D, Kaufman, G. First records of marine mammals takes in fisheries on the Ecuadorian Continental Coast.Document presented to International Whaling Commission: Workshop on Poorly Documented Takes of Small Cetaceans, SC/M18/SAW08. SouthAmerica, Santos, Brasil, March 2018.

32. Alava JJ, Paladines F. Illegal fishing on the Galapagos high seas. Science 2017; 357: 1362.

33. Alava JJ, Barragán-Paladines MJ, Denkinger J, Muñoz-Abril L, Jiménez PJ, Paladines F, et al. Massive Chinese Fleet Jeopardizes Threatened Shark Species around the Galápagos Marine Reserve and Waters off Ecuador: Implications for National and International Fisheries Policy. Int. J. Fish. Sci. Res. 2017; 1: 1001.

34. Department of Commerce, National Oceanic and Atmospheric Administration. Fish and Fish Product Import Provisions of the Marine Mammal Protection Act; Final Rule. Federal Register 81 FR 54389, Document # 2016-19158; 2016; 81: 54389-54419.

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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


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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*


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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


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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


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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*