Spatially explicit estimates of length and biomass of Micromesistius poutassou (Blue Whiting) from acoustic and trawl surveys in the North-East Atlantic in May 2004

Acoustic estimates of herring and blue whiting abundance were obtained during the surveys using the Simrad ER60 scientific echosounder. The allocation of NASC-values to herring, blue whiting and other acoustic targets were based on the composition of the trawl catches and the appearance of echo recordings. To estimate the abundance, the allocated NASC -values were averaged for ICES-squares (0.5° latitude by 1° longitude). For each statistical square, the unit area density of fish (rA) in number per square nautical mile (N*nm-2) was calculated using standard equations (Foote et al., 1987; Toresen et al., 1998). To estimate the total abundance of fish, the unit area abundance for each statistical square was multiplied by the number of square nautical miles in each statistical square and then summed for all the statistical squares within defined subareas and over the total area. Biomass estimation was calculated by multiplying abundance in numbers by the average weight of the fish in each statistical square then summing all squares within defined subareas and over the total area. The Norwegian BEAM soft-ware (Totland and Godø 2001) was used to make estimates of total biomass.

Spatially explicit estimates of length and biomass of Micromesistius poutassou (Blue Whiting) from acoustic and trawl surveys in the North-East Atlantic in May 2010

Acoustic estimates of herring and blue whiting abundance were obtained during the surveys using the Simrad ER60 scientific echosounder. The allocation of NASC-values to herring, blue whiting and other acoustic targets were based on the composition of the trawl catches and the appearance of echo recordings. To estimate the abundance, the allocated NASC -values were averaged for ICES-squares (0.5° latitude by 1° longitude). For each statistical square, the unit area density of fish (rA) in number per square nautical mile (N*nm-2) was calculated using standard equations (Foote et al., 1987; Toresen et al., 1998). To estimate the total abundance of fish, the unit area abundance for each statistical square was multiplied by the number of square nautical miles in each statistical square and then summed for all the statistical squares within defined subareas and over the total area. Biomass estimation was calculated by multiplying abundance in numbers by the average weight of the fish in each statistical square then summing all squares within defined subareas and over the total area. The Norwegian BEAM soft-ware (Totland and Godø 2001) was used to make estimates of total biomass.

Spatially explicit estimates of length and biomass of Clupea harengus (Norwegian spring spawning herring) from acoustic and trawl surveys in the North-East Atlantic in May 2011

Acoustic estimates of herring and blue whiting abundance were obtained during the surveys using the Simrad ER60 scientific echosounder. The allocation of NASC-values to herring, blue whiting and other acoustic targets were based on the composition of the trawl catches and the appearance of echo recordings. To estimate the abundance, the allocated NASC -values were averaged for ICES-squares (0.5° latitude by 1° longitude). For each statistical square, the unit area density of fish (rA) in number per square nautical mile (N*nm-2) was calculated using standard equations (Foote et al., 1987; Toresen et al., 1998). To estimate the total abundance of fish, the unit area abundance for each statistical square was multiplied by the number of square nautical miles in each statistical square and then summed for all the statistical squares within defined subareas and over the total area. Biomass estimation was calculated by multiplying abundance in numbers by the average weight of the fish in each statistical square then summing all squares within defined subareas and over the total area. The Norwegian BEAM soft-ware (Totland and Godø 2001) was used to make estimates of total biomass.

Spatially explicit estimates of length and biomass of Clupea harengus (Norwegian spring spawning herring) from acoustic and trawl surveys in the North-East Atlantic in May 2007

Acoustic estimates of herring and blue whiting abundance were obtained during the surveys using the Simrad ER60 scientific echosounder. The allocation of NASC-values to herring, blue whiting and other acoustic targets were based on the composition of the trawl catches and the appearance of echo recordings. To estimate the abundance, the allocated NASC -values were averaged for ICES-squares (0.5° latitude by 1° longitude). For each statistical square, the unit area density of fish (rA) in number per square nautical mile (N*nm-2) was calculated using standard equations (Foote et al., 1987; Toresen et al., 1998). To estimate the total abundance of fish, the unit area abundance for each statistical square was multiplied by the number of square nautical miles in each statistical square and then summed for all the statistical squares within defined subareas and over the total area. Biomass estimation was calculated by multiplying abundance in numbers by the average weight of the fish in each statistical square then summing all squares within defined subareas and over the total area. The Norwegian BEAM soft-ware (Totland and Godø 2001) was used to make estimates of total biomass.

Posibilidades de cultivo de nuevas especies marinas en el área mediterránea

La acuicultura, el cultivo y cría de animales y plantas acuáticas, representa en la actualidad una fuente esencial de proteína animal y vegetal altamente saludable y nutritiva, proporcionando un sistema de vida y de ingresos en todo el mundo. La acuicultura además de ser un motor para el desarrollo social y económico de las áreas costeras marinas y fluviales mundiales, supone en muchas regiones subdesarrolladas una garantía de alimento de alta calidad y es clave en la seguridad alimentaria de sus poblaciones. El desarrollo de la acuicultura se ha realizado fundamentalmente en los últimos 50 años, y ha sido sobre todo en la década de los años 80, cuando la acuicultura ha experimentado un fuerte crecimiento con tasas anuales que superan el 6%. Con el estancamiento de la producción pesquera y el incremento de la población mundial, la acuicultura se presenta como la única fuente posible de suministro de proteínas (vegetales y animales) de alta calidad, ricas en aceites omega 3 (EPA y DHA) de origen acuático. En la actualidad la producción procedente de la acuicultura supera los 95 millones de toneladas anuales, siendo ligeramente superior a los 94 millones de toneladas anuales provenientes de la pesca extractiva. De este total mundial acuícola, la producción asiática representa el 89%, mientras que la europea el 4,2% Aunque el 46% de la producción mundial acuícola se concentra únicamente en solo 10 especies, una de las principales características de la acuicultura es la gran diversidad de especies cultivadas, más de 500, realizándose su cría bajo diferentes tecnologías y sistemas productivos. El ámbito de esta tesis, es únicamente la acuicultura marina que se desarrolla en las aguas del mar mediterráneo, indistintamente de los sistemas y tecnología de producción utilizados. Los principales grupos de cultivo que se realizan en las aguas del Mediterráneo son los moluscos y los peces, siendo muy escasos los cultivos de otros grupos como crustáceos y macroalgas. La piscicultura marina mediterránea está dominada por el cultivo en jaulas flotantes de dos especies, la dorada (Sparus auratus) y la lubina (Dicentrarchus labrax). Estas dos especies y tras 30 años de experiencia de cultivo, mantienen todavía una ineficiencia productiva alta (reducida selección genética, lento crecimiento hasta talla comercial, alto factor de conversón del pienso…) y además ocupan un estrecho nicho de mercado, ya que prácticamente toda la comercialización de la dorada y lubina se realiza en fresco y sin elaborar ni transformar, a una talla media de 500 g. Para dar respuesta desde la acuicultura mediterránea al alto consumo y a la creciente demanda que en la Unión Europea existe de los productos acuícolas, y en especial los productos elaborados y transformados, es necesario de manera urgente, un aumento de la producción de las especies ya cultivadas (dorada y lubina) mediante la mejora de su eficiencia productiva, al mismo tiempo que se debe iniciar la producción industrial de nuevas especies piscícolas, mediante la diversificación de los cultivos. Para llevar a cabo esta diversificación, se hace necesario el establecimiento de una metodología clara, que asegure una selección de especies apropiadas y rentables para la industria acuícola mediterránea, cuyo cultivo sostenible debiera cumplir con los desafíos que el sector tiene. Nuevas especies que complementen y cubran las demandas actuales y futuras del mercado Europeo e Internacional de productos acuícolas. Nuevas especies con parámetros productivos eficientes, que garanticen unos costes productivos competitivos. Nuevas especies que puedan ser cultivadas utilizando como base la tecnología de producción ya existente en el sector. El objetivo de esta tesis es la definición y desarrollo de una metodología sencilla para la selección de nuevas especies piscícolas marinas para su cultivo eficiente y sostenible Y bajo la aplicación de esta metodología, la selección de un grupo de especies piscícolas para su cultivo rentable a corto y medio plazo (6-8 años) en el Mediterráneo. Para ello se ha definido y aplicado una metodología con la que se han evaluado diez especies candidatas, previamente escogidas de una serie de listas previas originadas en los distintos estudios y trabajos de diversificación realizados con anterioridad por otros equipos de investigación. Estas especies candidatas han sido: Seriola dumerili. (Seriola) , Argyrosomus regius (Corvina), Polyprion americanus (Cherna), Ephinephelus marginatus (Mero), Dentex dentex (Dentón), Pagrus pagrus (Pargo), Solea senegalensis (Lenguado del Senegal), Thunnus thynnus (Atún rojo), Mugil cephalus (Lisa), Coryphaena hippurus (Lampuga). El conjunto de estas especies ocupa un amplio y variado espectro dentro de las distintas áreas de mercado, productiva, tecnológica, y medioambiental . Y en todas ellas existe una experiencia mínima en sus diferentes fases de cultivo. En el desarrollo de la metodología de selección, en esta tesis se han definido diversos parámetros de evaluación, considerados como los más significativos y sencillos de aplicar. Los parámetros se han agrupado en tres bloques, el comercial, el productivo y el medioambiental. El Bloque de Mercado, comprende aquellos criterios que están relacionados con la comercialización de la especie. Calidad de la carne del pescado. Competencia con otras especies en el mercado. Potencial de Transformado. Precio de venta del pescado. El bloque Medioambiental incluye criterios del grado de idoneidad de la especie en la región y del grado de impacto ambiental de su cultivo. Rango de temperaturas del agua óptimo para el cultivo. Potencial impacto ambiental de su cultivo. Eslabón trófico de la especie.. El bloque Productivo, engloba los criterios y parámetros relacionados con el nivel de conocimiento y control que sobre su cultivo existen ( larvario, engorde, tecnología) Grado de control de la fase larvaria. Disponibilidad de alevines en el sector Crecimiento. Factor de conversión Aprovechamiento de la capacidad productiva instalada, Coste de inversión. Previa a la evaluación se han descrito las principales características de las especies candidatas en función del estado y experiencia actual sus cultivos. En la aplicación de estos criterios se han establecido matrices de evaluación y a cada criterio se le ha asignado un valor diferente en función de sus características y propiedades selectivas. Los resultados obtenidos mediante la aplicación de la metodología de evaluación propuesta, han señalado la seriola y la corvina como especies más recomendadas para su puesta en cultivo en el Mediterráneo a corto y medio plazo. Las otras dos especies seleccionadas han sido la lisa y la lampuga. Como conclusión final podemos señalar que el cultivo de nuevas especies es fundamentalmente para el desarrollo sostenible de la acuicultura mediterránea. Esta diversificación debe basarse en la aplicación de una metodología sencilla y práctica, que garantice una selección de especies cuyo cultivo sea rentable y abarquen nuevos segmentos de mercado. ABSTRACT Aquaculture, the cultivation and breeding of aquatic animals and plants, currently represents an essential source of highly nutritious and healthy protein that provides a way of life and income all over the world. Apart from being a social and economic driver in coastal and marine areas, it also entails a guaranteed high quality nourishment in many undeveloped areas being key to the alimentary safety of their population. Aquaculture has developed mainly in the last 50 years and experienced a high growth especially during the Eighties when the annual rates were above 6%. With fishing production stagnating and the global population increasing, aquaculture emerges as the only possible animal and vegetable protein source of aquatic origin, high in quality and omega 3 oils (EPA and DHA). Here and now, aquaculture production is over 95 million tons per year, which is slightly higher than the 94 million tons per year that come from extractive fisheries. From this aquaculture total, Asiatic production represents 89% while Europe´s is only 4.2%. Even though 46% of the global aquaculture production focuses just on 10 species, one of the main characteristics of aquaculture is the wide diversity of cultivated species –over 500– using different technologies and production systems. This PhD’s scope is only marine aquaculture in Mediterranean water, regardless of the technology or systems used. The main crop groups in the Mediterranean sea are molluscs and finfish, while crustacean and macroalgae cultivations are very limited. Mediterranean fish culture is dominated by the cultivation in floating cages of two species: Bream (Sparus auratus) and Bass (Dicentrarchus labrax). After 30 years of farming, these two species still keep a high productive inefficiency –reduced genetic selection, slow growth to marketable size, high feed conversion rate– and fill a narrow niche market as practically all bream and bass is sold fresh and whole, unprocessed and untransformed, with an average size of 500 grams. To meet the high consumption and growing demand of aquaculture products, in the European Union (especially those prepared and transformed), Mediterranean aquaculture needs to urgently increase the production of the species already under cultivation (Bass and Bream) by means of improving its productive efficiency and at the same time begin initiating industrial production of new species by diversifying the cultivation. To carry out this diversification it is necessary to establish a clear methodology that ensures the selection of adapted and profitable species for the Mediterranean aquaculture industry. The sustainable farming of these new species needs to meet the challenges this sector faces: New species that complement and meet the current and future needs of the European and International markets for aquaculture products. New species with efficient production parameters that ensure competitive production costs. New species that can be cultivated using already existing production technologies. The aim of this PhD is to define and develop a simple methodology for the selection of new marine fish species for their efficient and sustainable cultivation. And by applying this methodology, to select a group of fish species for its profitable crop in the short and medium term (6-8 years) in the Mediterranean. For this, a methodology has been defined and applied evaluating ten candidate species selected from a series of lists originated from different studies and from diversification works previously conducted by other research teams. These candidate species are: Seriola dumerili. (Greater amberjack), Argyrosomus regius (Meagre), Polyprion americanus (Wreckfish), Ephinephelus marginatus (Dusky grouper), Dentex dentex (Common dentex), Pagrus pagrus (Red porgy), Solea senegalensis (Senegal sole), Thunnus thynnus (Bluefin tuna), Mugil cephalus (Grey mullet), Coryphaena hippurus (Dolphinfish). All these species occupy a broad and varied spectrum within different productive, technological and environmental market areas. There is minimal experience in their different stages of cultivation for all of them. While developing the selection methodology several evaluation parameters have been defined in this PhD, considered the most significant and simple to apply. The parameters are grouped in three blocks: commercial, productivity and environmental. Market block comprises criteria related to the marketing of the species. Quality of the fish meatCompetition with other species in the marketTransformation potentialFish selling price Environment block includes criteria related to the degree of suitability of the species in the region and the degree of environmental impact of their cultivation. Optimal water temperature range for cultivationPotential environmental impact of their cultivationTrophic chain level. Productivity block includes criteria and parameters related to the level of knowledge and control over their cultivation (larval, ongrowing, technology) Degree of control of the larval stageAvailability of alevin in the sector GrowthFeed conversion rate. Exploitation of installed capacityInvestment cost Prior to the evaluation, the main characteristics of the candidate species have been described based on the current status and experience of their cultivations. When applying these criteria evaluation matrices have been established assigning to each criteria a different value depending on their characteristics and selective properties. The results obtained by applying the proposed assessment methodology have identified the Greater Amberjack and Meagre as the most recommended species for farming in the Mediterranean in the short and medium term. The other two selected species were the Grey Mullet and the Dolphinfish. In conclusion, the cultivation of new species is crucial for the sustainable development of Mediterranean aquaculture. This diversification has to be based on the application of a simple and practical methodology that guarantees a selection of species whose cultivation is profitable and covers new market segments.

Spatially explicit estimates of length and biomass of Micromesistius poutassou (Blue Whiting) from acoustic and trawl surveys in the North-East Atlantic in May 2012

Acoustic estimates of herring and blue whiting abundance were obtained during the surveys using the Simrad ER60 scientific echosounder. The allocation of NASC-values to herring, blue whiting and other acoustic targets were based on the composition of the trawl catches and the appearance of echo recordings. To estimate the abundance, the allocated NASC -values were averaged for ICES-squares (0.5° latitude by 1° longitude). For each statistical square, the unit area density of fish (rA) in number per square nautical mile (N*nm-2) was calculated using standard equations (Foote et al., 1987; Toresen et al., 1998). To estimate the total abundance of fish, the unit area abundance for each statistical square was multiplied by the number of square nautical miles in each statistical square and then summed for all the statistical squares within defined subareas and over the total area. Biomass estimation was calculated by multiplying abundance in numbers by the average weight of the fish in each statistical square then summing all squares within defined subareas and over the total area. The Norwegian BEAM soft-ware (Totland and Godø 2001) was used to make estimates of total biomass.

Micromesistius poutassou (blue whiting) abundance and biomass data in Bay of Biscay estimated from acoustic surveys (2000-2012)

Acoustic and pelagic trawl data were collected during various pelagic surveys carried out by IFREMER in May between 2000 and 2012 (except 2001), on the eastern continental shelf of the Bay of Biscay (Pelgas series). The acoustic data were collected with a Simrad EK60 echosounder operating at 38 kHz (beam angle at -3 dB: 7°, pulse length set to 1.024 ms). The echosounder transducer was mounted on the vessel keel, at 6 m below the sea surface. The sampling design were parallel transects spaced 12 nm apart which were orientated perpendicular to the coast line from 20 m to about 200 m bottom depth. The nominal sailing speed was 10 knots and 3 knots on average during fishing operations. The scrutinising (species identification) of acoustic data was done by first characterising acoustic schools by type and then linking these types with the species composition of specific trawl hauls. The data set contains nautical area backscattering values, biomass and abundance estimates for blue whiting for one nautical mile long transect lines. Further information on the survey design, scrutinising and biomass estimation can be found in Doray et al. 2012.

Survey bottom trawl data of Micromesistius poutassou (blue whiting) in Bay of Biscay and Celtic Sea from the EVHOE time series (1997-2011)

Data were collected during various groundfish surveys carried out by IFREMER from October to December between 1997 and 2011, on the eastern continental shelf of the Bay of Biscay and in the Celtic Sea (EVHOE series). The sampling design was stratified according to latitude and depth. A 36/47 GOV trawl was used with a 20 mm mesh codend liner. Haul duration was 30 minutes at a towing speed of 4 knots. Fishing was restricted to daylight hours. Catch weights and catch numbers were recorded for all species and body size measured. The weights and numbers per haul were transformed into abundances per km**2 by considering the swept area of a standard haul (0.069 km**2).

Cardicola Short, 1953 and Braya n. gen. (Digenea : Sanguinicolidae) from five families of tropical Indo-Pacific fishes

A survey of Pacific coral reef fishes for sanguinicolids revealed that two species of Lutjanidae (Lutjanus argentimaculatus, L. bohar), six species of Siganidae (Siganus corallinus, S. fuscescens, S. lineatus, S. margaritiferus, S. punctatus, S. vulpinus), seven species of Chaetodontidae (Chaetodon aureofasciatus, C. citrinellus, C. flavirostris, C. lineolatus, C. reticulatus, C. ulietensis, C. unimaculatus), three species of Scombridae (Euthynnus affinis, Scomberomorus commerson, S. munroi) and three species of Scaridae (Chlorurus microrhinos, Scarus frenatus, S. ghobban) were infected with morphologically similar sanguinicolids. These flukes have a flat elliptical body, a vestigial oral sucker, a single testis, separate genital pores and a post-ovarian uterus. However, these species clearly belong in two genera based on the position of the testis and genital pores. Sanguinicolids from Lutjanidae, Siganidae, Chaetodontidae and Scombridae belong in Cardicola Short, 1953; the testis originates anteriorly to, or at the anterior end of, the intercaecal field and does not extend posteriorly to it, the male genital pore opens laterally to the sinistral lateral nerve chord and the female pore opens near the level of the ootype ( may be anterior, lateral or posterior to it) antero-dextral to the male pore. Those from Scaridae are placed in a new genus, Braya; the testis originates near the posterior end of the intercaecal field and extends posteriorly to it, the male pore opens medially at the posterior end of the body and the female pore opens posterior to the ootype, antero-sinistral to the male pore. The second internal transcribed spacer (ITS2) of ribosomal DNA from these sanguinicolids and a known species, Cardicola forsteri Cribb, Daintith & Munday, 2000, were sequenced, aligned and analysed to test the distinctness of the putative new species. Results from morphological comparisons and molecular analyses suggest the presence of 18 putative species; 11 are described on the basis of combined morphological and molecular data and seven are not because they are characterised solely by molecular sequences or to few morphological specimens (n= one). There was usually a correlation between levels of morphological and genetic distinction in that pairs of species with the greatest genetic separation were also the least morphologically similar. The exception in this regard was the combination of Cardicola tantabiddii n. sp. from S. fuscescens from Ningaloo Reef ( Western Australia) and Cardicola sp. 2 from the same host from Heron Island ( Great Barrier Reef). These two parasite/ host/location combinations had identical ITS2 sequences but appeared to differ morphologically ( however, this could simply be due to a lack of morphological material for Cardicola sp. 2). Only one putative species ( Cardicola sp. 1) was found in more than one location; most host species harboured distinct species in each geographical location surveyed ( for example, S. corallinus from Heron and Lizard Islands) and some ( for example, S. punctatus, S. fuscescens and Chlorurus microrhinos) harboured two species at a single location. Distance analysis of ITS2 showed that nine species from siganids, three from scombrids and five from scarids formed monophyletic clades to the exclusion of sanguinicolids from the other host families. Cardicola milleri n. sp. and C. chaetodontis Yamaguti, 1970 from lutjanids and chaetodontids, respectively, were the only representatives from those families that were sequenced. Within the clade formed by sanguinicolids from Siganidae there wasa further division of species; species from the morphologically similar S. fuscescens and S. margaritiferus formed a monophyletic group to the exclusion of sanguinicolids from all other siganid species.

Projecting the fate of fish populations using ecological-economic modeling

Four marine fish species are among the most important on the world market: cod, salmon, tuna, and sea bass. While the supply of North American and European markets for two of these species - Atlantic salmon and European sea bass - mainly comes from fish farming, Atlantic cod and tunas are mainly caught from wild stocks. We address the question what will be the status of these wild stocks in the midterm future, in the year 2048, to be specific. Whereas the effects of climate change and ecological driving forces on fish stocks have already gained much attention, our prime interest is in studying the effects of changing economic drivers, as well as the impact of variable management effectiveness. Using a process-based ecological-economic multispecies optimization model, we assess the future stock status under different scenarios of change. We simulate (i) technological progress in fishing, (ii) increasing demand for fish, and (iii) increasing supply of farmed fish, as well as the interplay of these driving forces under different sce- narios of (limited) fishery management effectiveness. We find that economic change has a substantial effect on fish populations. Increasing aquaculture production can dampen the fishing pressure on wild stocks, but this effect is likely to be overwhelmed by increasing demand and technological progress, both increasing fishing pressure. The only solution to avoid collapse of the majority of stocks is institutional change to improve management effectiveness significantly above the current state. We conclude that full recognition of economic drivers of change will be needed to successfully develop an integrated ecosystem management and to sustain the wild fish stocks until 2048 and beyond.

Disponibilité à des fins d'aquaculture des différents âges de thon rouge en atlantique est

In order to clear up possibilities to get bluefin tuna of various age in Eastern Atlantic, main conclusions on availability of bluefin in Eastern Atalntic are given, using results of International Commission for Conservation of Atlantic Tuna.

Espèces de thonidés d'intérêt potentiel pour l'aquaculture en Méditerranée

Bluefin tuna is particularly concerned in the project of tuna rearing in the Mediterranean sea. However there are no reasons to neglect the other tuna species of the Mediterranean sea which present an interesting material for the development of the research on tuna cultivation.

Markov models and network analysis reveal sex-specific differences in the space-use of a coastal apex predator

Understanding the links between external variables such as habitat and interactions with conspecifics and animal space-use is fundamental to developing effective management measures. In the marine realm, automated acoustic tracking has become a widely used method for monitoring the movement of free-ranging animals, yet researchers generally lack robust methods for analysing the resulting spatial-usage data. In this study, acoustic tracking data from male and female broadnose sevengill sharks Notorynchus cepedianus, collected in a system of coastal embayments in southeast Tasmania were analyzed to examine sex-specific differences in the sharks' coastal space-use and test novel methods for the analysis of acoustic telemetry data. Sex-specific space-use of the broadnose sevengill shark from acoustic telemetry data was analysed in two ways: The recently proposed spatial network analysis of between-receiver movements was employed to identify sex-specific space-use patterns. To include the full breadth of temporal information held in the data, movements between receivers were furthermore considered as transitions between states of a Markov chain, with the resulting transition probability matrix allowing the ranking of the relative importance of different parts of the study area. Both spatial network and Markov chain analysis revealed sex-specific preferences of different sites within the study area. The identification of priority areas differed for the methods, due to the fact that in contrast to network analysis, our Markov chain approach preserves the chronological sequence of detections and accounts for both residency periods and movements. In addition to adding to our knowledge of the ecology of a globally distributed apex predator, this study presents a promising new step towards condensing the vast amounts of information collected with acoustic tracking technology into straightforward results which are directly applicable to the management and conservation of any species that meet the assumptions of our model.

Migrations of yellowfin tuna tagged off the southern coast of Mexico in 1960 and 1969

ENGLISH: The map method, the Jones method, the variance-covariance method, and the Skellam method were used to study the migrations of tagged yellowfin tuna released off the southern coast of Mexico in 1960 and 1969. The first three methods are all useful, and each presents information which is complementary to that presented by the others. The Skellam method, as used in this report, is less useful. The movements of the tagged fish released in 1960 appeared to have been strongly directed, but this was probably caused principally by the distribution of the fishing effort. The effort was much more widely distributed in 1970, and the movements of the fish released in 1969 appeared to have been much less directed. The correlation coefficients derived from the variance-covariance method showed that it was not random, however. The small fish released in the Acapulco and 10°N-100°W areas in 1969 migrated to the Manzanillo area near the beginning of February 1970. The medium and large fish released in the same areas in the same year tended to migrate to the southeast throughout the first half of 1970, however. SPANISH: El método de mapas, el de Jones, el de la variancia-covariancia y el de Skellam fueron empleados para estudiar las migraciones del atún aleta amarilla marcado y liberado frente a la costa meridional de México en 1960 y 1969. Los tres primeros métodos son todos útiles, y cada uno presenta información que complementa la presentada por los otros. El método de Skellam, conforme se usa en este informe, es menos útil. Parece que los desplazamientos de los peces marcados y liberados en 1960 hubieran sido fuertemente orientados, pero ésto probablemente fue causado principalmente por la distribución del esfuerzo de pesca. El esfuerzo se distribuyó más extensamente en 1970, y parece que los desplazamientos de los peces liberados en 1969 fueran menos orientados. Los coeficientes de correlación derivados del método variancia-covariancia indicaron, sin embargo, que no eran aleatorios. Los peces pequeños liberados en las áreas de Acapulco y los 10°N-100°W en 1969 migraron al área de Manzanillo a principios de febrero 1970. Los peces medianos y grandes liberados en las mismas áreas en el mismo año tuvieron, sin embargo, la tendencia a desplazarse al sudeste durante el primer semestre de 1970. (PDF contains 64 pages.)

Variation in yellowfin tuna (Thunnus albacares) catches related to El Niño-Southern Oscillation events at the entrance to the Gulf of California

Fishery catch data on yellowfin tuna (Thunnus albacares) were examined to study the effects of El Niño events between 1990 and 1999 for an area in the northeastern tropical Pacific (18−24°N, 112−104°W). The data were extracted from a database of logbook records from the Mexican tuna purse-seine f leet. Latitudinal distribution of the catches increased from south to north for the 10-year period. Highest catches and effort were concentrated between 22°N and 23°N. This area accumulated 48% of the total catch over the 10year period. It was strongly correlated with El Niño-Southern Oscillation (ENSO) events. At least two periods of exceptionally high catches occurred following El Niño events in 1991 and 1997. Peaks of catches were triggered by the arrival of positive anomalies of sea surface temperature (SST) to the area. A delay of two to four months was observed between the occurrence of maximum SST anomalies at the equator and peaks of catch. Prior to these two events, negative SST anomalies were the dominant feature in the study area and catch was extremely low. This trend of negative SST anomalies with low catches followed by positive SST anomalies and high catches may be attributed to northward yellowfin tuna migration patterns driven by El Niño forcing, a result that contrasts with the known behavior of decreasing relative abundance of these tuna after El Niño events in the eastern Pacific. However, this decrease in relative abundance may be the result of a local or subregional effect.