IUCN/SCC Otter Specialist Group Bulletin
©IUCN/SCC Otter Specialist Group
Volume 25 pages 75 - 123 (October 2008)
Citation: Recharte, M., Bowler, M. and Bodmer, R. (2008). Potential Conflict between Fishermen and Giant Otter (Pteronura brasiliensis) Populations by Fishermen in Response to Declining Stocks of Arowana Fish (Osteoglossum bicirrhosum) in Northeastern Peru. IUCN Otter Spec. Group Bull. 25 (2): 89 - 93
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Potential Conflict between Fishermen and Giant Otter (Pteronura brasiliensis) Populations by Fishermen in Response to Declining Stocks of Arowana Fish (Osteoglossum bicirrhosum) in Northeastern Peru
Maribel Recharte1, Mark Bowler2 and Richard Bodmer2
1Universidad Nacional de la Amazon Peruvian (UNAP), Calle Garcia Sanz #346, Iquitos, Peru; e-mail: maribel_recharte@yahoo.com
2Durrell Institute of Conservation and Ecology, University of Kent, Canterbury, UK |
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(received 3rd December 2008, accepted 13th January 2009) |
Abstract: Giant otter (Pteronura brasiliensis)
populations are increasing in many parts of the Peruvian Amazon,
and are coming into contact with people more regularly. Giant
otters are piscivores and fishermen often see them as potential
competitors for fish stocks. We report on giant otter - fisherman
conflict on the River Yanayacu. During informal discussions,
we found that fishermen considered the giant otter a competitor
for fish, and one of their main concerns was for the fisheries
of arowana (Osteoglossum bicirrhosum). This fishery,
for young arowanas for sale to the ornamental fish trade, is
very important for the communities in the Pacaya-Samiria National
Reserve, and fishermen believe that stocks of this species are
declining. Although arowana can be preyed upon by giant otter,
smaller fish are preferred and there is no evidence for giant
otters impacting on populations of this species. We identify
a need for more research into giant otter populations, arowana
populations, the exploitation of arowana, and the diet of giant
otters in northeastern Peru, to support conservation initiatives
aimed at changing the perception of giant otters as competitors
for fish. |
Keywords: fishing, trade, conflict, arahuana, conservation |
Française | Español |
Giant otters (Pteronura brasiliensis) are increasing in number
in many parts of their range and are returning to many areas where
they have not been seen for many years (Recharte,
2007; Van Damme et
al., 2001; Hajek and Groenendijk, 2006). This is bringing the giant
otter into contact with people. While otters are not generally hunted
(Recharte, 2007), their predominantly piscivore diet (Duplaix,
1980;
Laidler 1984; Carter and Rosas,
1997; Gonzáles, 1997; Carrasquilla,
2002; Velasco, 2004; Staib,
2005) may bring them into conflict with
fishermen. Fishing is an important subsistence and commercial activity
in most parts of the giant otters range, and giant otter-fisherman
conflict has been considered in Colombia by Gómez and Jorgenson
(1999) and Velasco (2004), and in Brazil by Calvimontes
and Marmontel (2006) and Zucco and Tomas (2004). Gómez and Jorgenson (1999) concluded that although there is overlap in the diet of giant otters
and the fish taken by fishermen, giant otters have little effect on
fisheries in Colombia. Giant otter-fisherman conflict has not yet been
evaluated in northeastern Peru, where extremely low populations of
giant otter have meant that the issue has not been important. As giant
otter populations increase and repopulate rivers near human habitation,
conflict may be inevitable. This paper describes a possible conflict
between fishermen harvesting ornamental arowana fish (Osteoglossum
bicirrhosum) and giant otters observed on the Yanayacu River in
the Pacaya-Samiria National Reserve (PSNR), where giant otter populations
have increased between censuses by Schenck et
al. (1996) and Isola
(2000).
The Yanayacu River is 158km long and 40m wide, and joins the Marañon River
about 30km upstream from the city of Nauta. The area is composed of white-water
várzea forests that flood between November and May each year, leaving
only high areas of ground exposed. We visited two communities on the Yanayacu.
The Community of Arequipa near the mouth had 57 inhabitants in 15 families, and
the community of Yarina on the middle section of the river had 118 inhabitants
in 25 families. Fishing for subsistence and sale in markets, including fishing
for various species of ornamental fish, is overseen by a management group; ‘Organización
Social de Pescadores y Pescadores Artesanales’ (OSPPA UPC Yarina).
This management group is assisted by biologists from ‘Pro Naturaleza’,
a Peruvian NGO. Some low-level tourism is also conducted in the area.
Fishermen on the Yanayacu have noted the expansion of the ranges of giant otters
and are concerned about increasing competition with otters for fish. During separate
informal discussions, seven fishermen expressed concern that the giant otters
were competing with them for fish, and thought that the otters were reducing
fish populations. Five fishermen said they believed that giant otters predated
arowana fish, and were impacting on numbers of these fish. Community members
said that the collection of arowana fry for sale to the ornamental fish trade
was very important for them economically, and was one of the main sources of
income for many families. The harvest of the young of this fish is managed by
community groups in the area. However, one community member claimed that the
harvest of this species had fallen from around 15,000 fry to 2,000 in recent
years and thought that the increase in numbers of giant otters was one of the
main factors in the reduction in size of recent harvests of arowana fry. One
interviewee requested verification that the giant otters were indeed feeding
on arowana from biologists, and said that a solution is necessary because the
arowana fishery is of such economic importance to the communities.
Arowana are large fish growing up to 1m in length (Goulding,
1980).
The male arowana broods 180-210 eggs in its mouth after spawning,
and keeps the young in its mouth for several weeks after hatching
(Goulding, 1980). Fishermen catch the male fish at this stage and
remove the young for sale (Moreau and Coomes, 2006; Figure
1). Harvesting
practices vary in different fishing grounds. In many areas the parent
fish is killed in the process of harvesting the young, while on some
rivers, especially within the Pacaya-Samiria National Reserve, brooding
adults are released alive after the young are collected (Figure
2).
This is a result of participation by local communities in projects
that aim to sustainably harvest the fish (Moreau
and Coomes, 2006;
Durand and McCaffrey, 1999). Moreau
and Coomes (2006) highlighted
the importance of the trade in Arowana to the economy of Iquitos
in northeastern Peru. Just over one million juvenile arowanas were
legally exported in 2001 for a value of 559,615 USD. The species was
the most commercially important to the Peruvian Amazon aquarium trade,
representing 42% of the total export value (Moreau
and Coomes, 2006).
At a community level, Moreau and Coomes (2006) and Kvist
et al., (2001) demonstrated that the arowana fishery was of considerable
importance to local people, with earnings from arowana making up
20.7% of the mean household income in some communities.
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Figure 1.
Arowana fry being removed from an adult male, Rio Yanayacu, Pacaya
Samiria National Park, Peru. Photograph: Mark Bowler. (click
for larger version) |
Figure
2. Adult male arowana
being released after removal of fry, Rio Yanayacu. Pacaya-Samiria
National Park, Peru. Photograph: Mark Bowler (click for larger
version) |
There have been no extensive studies on the diet of the giant otter
in northeastern Peru, but the diet of giant otters has been recorded
in several other sites where arowana do not occur (e.g Schenck,
1999;
Staib, 2005). Although the diet in Madre de Dios consists mainly of
fish ranging from 10cm to 30cm in size, larger fish are sometimes taken
(Schenck, 1999; Staib, 2005). Gómez (1999), Roopsind
(2002) and Recharte (2007) recorded arowana in diet of giant otters in Colombia,
Suriname and northeastern Peru respectively, but smaller fish species
were generally preferred. We therefore believe that the impact of giant
otters on arowana populations is likely to be negligible, and suspect
that overexploitation of Arowana for the aquarium trade is more likely
to be the cause if stocks of this species have declined. Arowana are
large and slow to mature, and fecundity is very low (Goulding,
1980).
This makes the species vulnerable to overexploitation when fishing
by humans is intensive (Moreau and Coomes, 2006). The related Asian
arowana (Scleropages formosus) was listed on Appendix I of
CITES in 1975 as a result of over collection for the aquarium trade.
Our discussions on the Yanayacu suggest that otters may be blamed for
falling stocks of arowana, even though there is no evidence for such
a relationship. A perceived increase in giant otter populations on
the Yanayacu River has coincided with a decline in the numbers of
arowana harvested by some households. Considering the importance
of the arowana fisheries to the people in the Pacaya-Samiria National
Reserve, it is conceivable that communities may take action to protect their
fisheries from the perceived threat by shooting giant otters. Better understanding
of giant otter populations, arowana populations, the exploitation of arowana,
and the diet of giant otters in northeastern Peru are required. A dialog with
communities and fisherman is also needed to determine how attitudes to giant
otters might affect their conservation. Communities on the Yanayacu River have
shown a willingness to work with biologists and may accept a scientific assessment
of the giant otter’s impact on the arowana fishery.
ACKNOWLEDGMENTS - We thank The LA Zoo and
Wildlife Conservation Society (WCS-Peru) who provided the financial
support for the research. We also thank Pro Naturaleza, the comunities
Yarina and Arequipa, Pablo Puertas (WCS-Perú), Javier Noriega
Murrieta (NGO Pro Naturaleza) and Javier del Aguila (INRENA). Special
thanks to our field assistants Arbildo Uraco (ORMARENA Yarina) and
Orlando Laiche (OSPPA UPC Yarina).
REFERENCES
Calvimontes, J. and Marmontel, M. (2006). Conflictos actuales y potenciales
entre los lobos de rio (Pteronura brasiliensis) y los pobladores
de las cabeceras del lago Amanã. 11ava Reunión especialistas
de mamíferos acuáticos de América del sur. Quito.
Carrasquilla, M. (2002). Uso de hábitat,
comportamiento y dieta de la nutria gigante (Pteronura brasiliensis)
en el río Orinoco. Tesis de grado. Universidad de los Andes.
Bogotá.
Carter, S. and Rosas, F. (1997). Biology
and conservation of the Giant Otter Pteronura brasiliensis. Mammal
Rev. 27: 1-26.
Duplaix, N. (1980). Observations
on the ecology and behaviour of the giant river otter (Pteronura
brasiliensis) in Suriname. Terre Vie-Rev Ecol a 34 (4):
495-620.
Durand, E. and McCaffrey, D. (1999).
The Pacaya-Samiria Project: enhancing conservation and improving livelihoods
in Amazonian Peru. In: Varzea: Diversity, Development and Conservation
of Amazonia´s Whitewater Floodplain. (eds. C. Padoch, J. M. Ayres,
M. Pinedo-Vasquez, A. Henderson), pp. 233-246.
Gómez, J. (1999). Ecología alimentaria
de la Nutria Gigante (Pteronura brasiliensis), en el bajo río
Bita, Vichada - Colombia. Tesis de grado. Pontificia Universidad
Javeriana. Bogotá,Colombia.
Gómez, J. and Jorgenson, J. (1999). An Overview
of the Giant Otter-Fisherman Problem in the Orinoco Basin of Colombia. IUCN
Otter Spec. Group Bull. 16(2): 90-96.
González, E. (1997). Ecoetología
de la londra (Pteronura brasiliensis), en la Reserva
de Producción del Bajo Paraguá. Tesis de grado. Universidad
Autónoma “Gabriel Rene Moreno”. Facultad de Ciencias
Agrícolas. Bolivia. 62 pp.
Goulding, M. (1980). The fishes and
the forest, Explorations in Amazonian Natural History. University of
California Press, Berkeley, USA.
Hajek, F. and Groenendijk, J. (2006).
Lobos del rio Madre de Dios. Ayuda para la vida silvestre. Amenazada-Sociedad
Zoológica de Francfort Perú.
Isola, S. (2000). Determinación
de la distribución y abundancia de lobo de río (Pteronura
brasiliensis) en la Reserva Nacional Pacaya Samiria. Tesis de
grado. Universidad Nacional Agraria La Molina. Perú.
Kvist, L., Gram, S., Cacares, C. and Ore B. (2001).
Socio-economy of flood plain households in the Peruvian Amazon. Forest
Ecol Manag, 150: 175-186.
Laidler, P. (1984). The behavioural
ecology of the giant otter in Guyana. PhD Thesis. Universidad de Cambridge.
UK.
Moreau, M. and Coomes, O. (2006).
Potential threat of the international aquarium fish trade to silver
arawana Osteoglossum bicirrhosum in the Peruvian
Amazon. Oryx. 40:2
Recharte, M. (2007). Evaluación
poblacional del lobo de río (Pteronura brasiliensis,
Zimmerman, 1780)en la cuenca de los ríos Yavarí, Yavarí Mirín
y Samiria, Loreto-Peru. Tesis de grado. Universidad Nacional de la
Amazonia Peruana.
Roopsind, I. (2002). Fish consumption
by giant otters (Pteronura brasiliensis) in the North Rupununi
Wetlands. Tesis de grado. Smithsonian National Zoo, Washington CD,
US, Jacksonville Zoo, Florida, US, The Guyana Zoological Park, Iwokrama
International Centre, Faculty of Natural Sciences, University of Guyana.
Schenck, C., Estremadoyro F. and Staib, E. (1996).
Primeras evaluaciones para determinar la existencia del “lobo
de río” (Pteronura brasiliensis) en el ámbito
de la Reserva Nacional Pacaya - Samiria, Loreto, Perú, SZF -
Pro Naturaleza. Perú. Pag. Irreg.
Schenck, C. (1999). Lobo
de río Pteronura
brasiliensis, presencia, uso del hábitat y protección
en el Perú. Agencia de Cooperación Técnica Alemana
(GTZ), Instituto Nacional
de Áreas Naturales Protegidas (INRENA). Perú.
Staib, E. (2005). Eco-etología
del lobo de río (Pteronura brasiliensis) en el sureste
del Perú. Primera edición. Perú. 195 pp.
Van Damme, P., Wallace, R., Painter, L.. Taber,
A., Gonzales, R., Fraser, A., Rumiz, D., Tapia, C., Michels, H., Delaunoy,
Y., Saravia J., Vargas, J and Torres L. (2001). Distribución y estado de las poblaciones de lontra (Pteronura
brasiliensis) en Bolivia. Revista Boliviana de Ecología y Conservación
Ambiental, 9: 3-13.
Velasco, D. (2004). Valoración biológica
y cultural de la nutria gigante (Pteronura brasiliensis), en elárea
de influencia de Puerto Carreño, Vichada, Colombia (Ríos Orinoco,
Bita, Caños Juriepe y Negro). Tesis de grado. Pontificia Universidad
Javeriana. Colombia.
Zucco C. and Tomas W. (2004) Diagnostico do conflicto entre os pescadores
profissionais artesanais e as populações de jacares (Caiman
yacare) e ariranhas (Pteronura brasiliensis) no pantanal. IV
Simposio sobre Recursos Naturais e Socio-economicos do Pantanal Corumba/MS 23
a 26 Nov 2004. SIMPAN2004 Sustentabilidade Regional
Résumé: Conflit Potentiel
entre les Pêcheurs et les Populations de Loutre Géante (Pteronura
brasiliensis) Suite au Déclin du
Stock d’Arowana (Osteoglossum bicirrhosum) dans
le Nord-Est du Pérou.
L’enquête sur la distribution de la Loutre (Lutra lutra L.) en République de Macédoine a été menée au printemps 2007 grâce à la recherche de ses indices de présence. Durant l’enquête, 36 sites répartis sur l’ensemble du territoire ont été contrôlés. Au total, 70% des sites se sont avérés positifs et la majorité du pays semble occupé par la l’espèce. Deux zones importantes montrent peu ou aucun indice d’occurrence : la partie amont du bassin hydrographique de la rivière Crna paraît inoccupée et le bassin de la Strumica comporte de très rares sites occupés. Les barrières à la présence de la Loutre sont probablement dues à la pollution d’origine industrielle sur la rivière Kriva Lakavica et agricole sur les rivières Crna et Strumica. Au final, aucune tendance d’évolution de la population peut être avancée puisque aucune donnée historique n’est disponible.
Revenez au dessus
Resumen: Conflicto
entre los Pescadores y las Poblaciones de Lobos de Rio (Pteronura
Brasiliensis) en Respuesta a la Reduccion
de Stocks de Arowana (Osteoglossum Bicirrhosum) en
el Noreste de Peru.
Los lobos de rio (Pteronura brasiliensis) han aumentado
en muchos lugares de la Amazonia peruana, y están entrando
en contacto con la gente más frecuentemente. Esta especie
es piscívora y los pescadores a menudo los ven como una competencia
por los peces. En este trabajo, nosotros reportamos el conflicto
de lobo de rio-pescadores en el rio Yanayacu. Durante entrevistas
realizadas en el área de manejo, encontramos que los pescadores
consideran a los lobos de rio como un competidor por los peces, y
principalmente arahuana (Osteoglossum bicirrhosum). El comercio
de alevinos de arahuana como pez ornamental es muy importante para
las comunidades en la Reserva Nacional Pacaya-Samiria, los pescadores
dicen que la población de arahuana está disminuyendo
durante los últimos años. Aunque la arahuana está incluida
en la dieta de lobo de rio, se observo que tiene preferencia por
peces más pequeños y no hay evidencia que el lobo de
rio esta impactando de forma negativa en las poblaciones de esas
especies. Nosotros identificamos una necesidad de información
acerca de las poblaciones de lobo de rio, poblaciones de arahuana,
explotación de arahuana, dieta de lobo de rio en el noreste
de Perú y los cambios de percepción de los pescadores
hacia el lobo de rio como competidores por los peces para mantener
las iniciativas de conservación.
Vuelva a la tapa
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