Interacción trófica merluza-anchoveta: ¿existe realmente impacto por predación?

Se analiza la importancia de la anchoveta en la dieta de la merluza durante el periodo 1996-1999, en términos de biomasa, para discutir los efectos de la interaccion merluza-anchoveta. Los resultados obtenidos indican que las anchovetas >10 cm constituyen una de las presas mas importantes en la dieta de merluzas que miden 31 a 40 cm de longitud. Esta interacción se presenta generalmente en años normales, es decir, sin un evento EI Niño. Cuando no hay predación sobre la anchoveta, se incrementa el canibalismo dentro de las poblaciones de merluza, lo que se grafica en una regresión potencial inversa entre ambos casos. Considerando que las áreas principales de distribución de ambos recursos no coinciden totalmente, se discute si la predación por parte de la merluza pueda estar impactando realmente a la población de anchoveta.

Ecología trófica del pulpo Octopus mimus Gould 1852 (Cephalopoda: Octopodidae) invierno 2013-2014 en la bahía del Callao

El pulpo Octopus mimus es un importante recurso de la pesquería artesanal bentónica, que se distribuye desde el norte del Perú a San Vicente, Chile. Se analizaron contenidos gástricos de 741 ejemplares obtenidos de la captura comercial en la bahía del Callao, durante agosto 2013-agosto 2014. Se determinó que las presas más importantes fueron crustáceos Decapoda: Petrolisthes desmarestii (%FO=24,13; %P=21,29%; N=27,10), Cycloxanthops sexdecimdentatus (%FO=16,35; %P=12,16%; N=15,99) y Allopetrolisthes angulosus (%FO=6,17; %P=6,05; %N=25,20). No hubo diferencias en la dieta entre machos y hembras en %FO y %P (Mann -Whitney U-test, p>0,05). Se observaron diferencias en el IR asociado a las fases de desarrollo gonadal en hembras, ejemplares madurantes/maduros mostraron mayor IR (0,17±0,17) que los desovados (0,08± 0,06), en machos no se observaron diferencias. El IR fue mayor en otoño (0,21±0,17) (Kruskal-Wallis test, p < 0,05). Los índices ecológicos mostraron que O. mimus es un depredador generalista (B’>3), observándose traslapo entre la dieta de machos y hembras (Cλ>0,6), por lo que se concluye que su alimentación está influenciada por una combinación de factores fisiológicos y ambientales.

Chrysaora plocamia lesson, 1830 (cnidaria, scyphozoa), frente a Pisco, Perú

Observa una generalizada proliferación de medusas, que llegan a formar “blooms” o poblaciones de alta densidad que podrían reemplazar organismos tradicionalmente dominantes en la cadena trófica.

Distribución horizontal de los Amphipoda (crustacea) en el mar peruano durante el fenómeno "El niño" verano 1983

Los anfípodos hepéridos son microcrustáceos marinos que tienen un rol importante en la ecología trófica de especies pesqueras, se caracterizan por su voraz comportamiento predador sobre otros componentes del zooplancton (NELSON, 1979) y debido a su abundancia constituyen una fuente de alimento para niveles tróficos superiores (ALVAREZ y VIÑAS, 1994). El área de estudio comprende desde 03°29.80´S hasta los 12°54.50´S, abarcando los perfiles de Puerto Pizarro, Cabo Blanco, Talara, Paita, Punta Falsa, Pimentel, Chicama, Salaverry, Chimbote, Huarmey, Supe, Guacho, Chancay, Callao, Pucusana y Cerro Azul, cubriendo de esta manera la parte norte y centro del litoral peruano hasta las 100 millas náuticas de la costa y 50 metros de profundidad. Se determinan 34 especies de anfípodos, con 26 nuevos registros para el país y 2 especies nuevas. La familia Hyperridae es la que registra mayor representatividad a nivel específico destacando por su abundancia las especies Hyperioides sibaginis e Hyperietta vossleri. El presente trabajo, contribuye principalmente a ampliar el conocimiento de especies de anfípodos y asociarlas con las características ambientales, así las especies Vibilia chuni, Partaphronima gracilis, Hemithiphys tenuimanuss, Euscelus robustus y Schizoscelus ornatus, se encuentran relacionados con salinidades que fluctuan entre 34.8 y 35.1‰ y temperaturas de 25.4 hasta 28.2°C, rangos correspondientes a aguas de mezcla de Aguas Ecuatoriales Superficiales (AES) y Aguas Subtropicales superficiales (ASS).

Trophic ecology of jumbo squid and predatory fishes in the Northern Humboldt Current System

This work provides a contribution to a better understanding of the trophic ecology of important predators in the Northern Humboldt Current System, the jack mackerel (Trachurus murphyi), the chub mackerel (Scomber japonicus) and the jumbo squid (Dosidicus gigas) by the characterization of the highly variable feeding patterns of these species at different spatiotemporal scales. We provided new knowledge on the comparative trophic behaviour of these species, defined as opportunistic in previous investigations. For that purpose we applied a variety of statistical methods to an extensive dataset of 27,188 non-empty stomachs. We defined the spatial organization of the forage fauna of these predators and documented changes in prey composition according to predators’ size and spatiotemporal features of environment. Our results highligh the key role played by the dissolved oxygen. We also deciphered an important paradox on the jumbo squid diet: why do they hardly forage on the huge anchovy (Engraulis ringens) biomass distributed of coastal Peru? We showed that the shallow oxygen minimum zone present off coastal Peru could hamper the co-occurrence of jumbo squids and anchovies. In addition, we proposed a conceptual model on jumbo squid trophic ecology including the ontogenetic cycle, oxygen and prey availability. Moreover we showed that the trophic behaviour of jack mackerel and chub mackerel is adapted to forage on more accessible species such as for example the squat lobster Pleurocondes monodon and Zoea larvae. Besides, both predators present a trophic overlap. But jack mackerel was not as oracious as chub mackerel, contradictorily to what was observed by others authors. Fish diet presented a high spatiotemporal variability, and the shelf break appeared as a strong biogeographical frontier. Diet composition of our fish predators was not necessarily a consistent indicator of changes in prey biomass. El Niño events had a weak effect on the stomach fullness and diet composition of chub mackerel and jack mackerel. Moreover, decadal changes in diet diversity challenged the classic paradigm of positive correlation between species richness and temperature. Finally, the global patterns that we described in this work, illustrated the opportunistic foraging behaviour, life strategies and the high degree of plasticity of these species. Such behaviour allows adaptation to changes in the environment.

End-to-end modelling for an ecosystem approach to fisheries in the Northern Humboldt Current Ecosystem

This work represents an original contribution to the methodology for ecosystem models' development as well as the rst attempt of an end-to-end (E2E) model of the Northern Humboldt Current Ecosystem (NHCE). The main purpose of the developed model is to build a tool for ecosystem-based management and decision making, reason why the credibility of the model is essential, and this can be assessed through confrontation to data. Additionally, the NHCE exhibits a high climatic and oceanographic variability at several scales, the major source of interannual variability being the interruption of the upwelling seasonality by the El Niño Southern Oscillation, which has direct e ects on larval survival and sh recruitment success. Fishing activity can also be highly variable, depending on the abundance and accessibility of the main shery resources. This context brings the two main methodological questions addressed in this thesis, through the development of an end-to-end model coupling the high trophic level model OSMOSE to the hydrodynamics and biogeochemical model ROMS-PISCES: i) how to calibrate ecosystem models using time series data and ii) how to incorporate the impact of the interannual variability of the environment and shing. First, this thesis highlights some issues related to the confrontation of complex ecosystem models to data and proposes a methodology for a sequential multi-phases calibration of ecosystem models. We propose two criteria to classify the parameters of a model: the model dependency and the time variability of the parameters. Then, these criteria along with the availability of approximate initial estimates are used as decision rules to determine which parameters need to be estimated, and their precedence order in the sequential calibration process. Additionally, a new Evolutionary Algorithm designed for the calibration of stochastic models (e.g Individual Based Model) and optimized for maximum likelihood estimation has been developed and applied to the calibration of the OSMOSE model to time series data. The environmental variability is explicit in the model: the ROMS-PISCES model forces the OSMOSE model and drives potential bottom-up e ects up the foodweb through plankton and sh trophic interactions, as well as through changes in the spatial distribution of sh. The latter e ect was taken into account using presence/ absence species distribution models which are traditionally assessed through a confusion matrix and the statistical metrics associated to it. However, when considering the prediction of the habitat against time, the variability in the spatial distribution of the habitat can be summarized and validated using the emerging patterns from the shape of the spatial distributions. We modeled the potential habitat of the main species of the Humboldt Current Ecosystem using several sources of information ( sheries, scienti c surveys and satellite monitoring of vessels) jointly with environmental data from remote sensing and in situ observations, from 1992 to 2008. The potential habitat was predicted over the study period with monthly resolution, and the model was validated using quantitative and qualitative information of the system using a pattern oriented approach. The nal ROMS-PISCES-OSMOSE E2E ecosystem model for the NHCE was calibrated using our evolutionary algorithm and a likelihood approach to t monthly time series data of landings, abundance indices and catch at length distributions from 1992 to 2008. To conclude, some potential applications of the model for shery management are presented and their limitations and perspectives discussed.