STATISTICS OF THE SPANISH ALBACORE (THUNNUS ALALUNGA) FISHERY IN THE NORTH EASTERN ATLANTIC DURING 2001 SUMMER SEASON

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SCRS/2002/084 Col. Vol. Sci. Pap. ICCAT, 55(1): 238-244 (2003) STATISTICS OF THE SPANISH ALBACORE (THUNNUS ALALUNGA) FISHERY IN THE NORTH EASTERN ATLANTIC DURING 2001 SUMMER SEASON V. Ortiz de Zárate 1 and C. Rodriguez-Cabello 1 SUMMARY The aim of this document is to present a brief review of the main features of the Spanish albacore (Thunnus alalunga) fishery in 2001. Landings and nominal effort by the Spanish troll and baitboat fleets are presented. As well the catch at size composition of landings is included. This fishery develops during summer and autumn months in the Northeast Atlantic and Bay of Biscay waters. The development of landings and nominal effort made by those fleets during 2001 shows a sharp decrease mainly for baitboats that could be related to thermal and climatic anomalies in the fishing area. RÉSUMÉ L objectif du présent document est de fournir un bref examen des principales caractéristiques de la pêcherie espagnole de germon (Thunnus alalunga) en 2001. Il fournit les données de capture et d effort nominal des flottilles espagnoles de ligneurs et canneurs qui ont développé leur activité en 2001, de même que la composition par taille des débarquements. Cette pêcherie de germon opère pendant les mois d été et d automne au nord-est de l Atlantique et dans les eaux du Golfe de Gascogne. L évolution des captures et de l effort réalisé par ces flottilles indique une diminution en 2001, notamment de l activité les canneurs, laquelle pourrait être liée à des anomalies thermales et climatiques dans la zone de pêche. RESUMEN Se presentan los datos de las capturas y esfuerzos nominales de las flotas de cacea y cebo vivo españolas que desarrollaron su actividad en 2001 y los datos de composición de tallas de las descargas. Esta pesquería de atún blanco tiene lugar en los meses de verano y otoño en el área del Atlántico nordeste y golfo de Vizcaya. La evolución de las capturas y esfuerzo realizado por estas flotas muestra un descenso en 2001, que afecta a la flota de cebo vivo principalmente y puede estar asociado a anomalías térmicas y climatología en el área de pesca. KEY WORDS Albacore, fishery statistics, size composition, northeast Atlantic. 1. INTRODUCTION The albacore fishery in the north of Spain is one of the most important economical activities carried out by the spanish fleet during summer and autumn seasons (June to October). This marked seasonally is due to the migratory behaviour of immature albacore to the feeding area of Northeast 1 Instituto Español de Oceanografía. Apdo. 240. 39080 Santander. Spain. victoria.zarate@st.ieo.es. 238

Atlantic waters and Bay of Biscay. Two different types of gears target on albacore; baitboat (BB) and troll (TR). The number of boats involve varies among the fishing seasons being the annual average 600 vessels (80% troll and 20% baitboat in 2001). In general the troll vessels are of lesser tonnage and power than those of baitboat. The catch is mainly made up of juveniles of age groups 1 to 4. Albacore is a large pelagic fish with a highly migratory behaviour. A migration pattern for juvenile population has been described based on tag-returns information (Bard, 1981; 2001; Ortiz de Zárate and Cort, 1998). Those albacore followed two main routes at the beginning of summer: one to the south-west of Ireland and the other to the Bay of Biscay area, whose movements are associated to sea surface temperature ranging from 17º C to 21ºC (Havard Duclos, 1973; Leroy, 1990). The aim of this paper is to present a brief review of the main features of the Spanish albacore surface fishery in 2001 and comparison with previous 2000 results. Following the recommendations on statistics by ICCAT, the catch and nominal fishing effort (days) as well as the catch-at size composition of landings are presented for both fleets: bait boat and troll. No quantitative analyses is been done on the data, however a review of past catch and effort data evolution is included in an attempt to explain the lowest records of albacore catches in 2001. 2. MATERIAL AND METHODS The information comprises the scientific estimations on the nominal catch, effort and the catch at size by gear, based on the data obtained by means of the sampling network of IEO, established in the main fishing ports of Galicia (western north coast) and the Cantabrian coast. This seasonal fishery is carried out by trollers and baitboats from June to October and from July to October, respectively. A number of individual trips from both fleets: bait boat and troll are interviewed and the catch landed is sampled to the nearest centimetre (FL = 35 to 120 cm range) according to commercial categories in the fishing markets. Thus catch, nominal effort (fishing days) and lengt h distribution are processed by gear on monthly basis following statistical procedures to estimate Task I and Task II (biological information) statistics of ICCAT (Miyake, 1990). In Figure 1 are represented the fishing grounds for troll and baitboat fleets. The troll vessels extends in a lager area from the coastal waters in the Bay of Biscay to the most northern waters around southwest coast of Ireland while the baitboats are localised mainly in the bay of Biscay waters. This last fleet has confined its activity to the Bay of Biscay area in the last years (Santiago, 1996; Ortiz de Zárate and Rodriguez-Cabello, 2001; 2002) and still continued this tendency in 2001. Considering the different geographical distribution of fleets, two main fishing areas have been identified according to longitude: Gulf (0º-10ºW) and Atlantic (10ºW-30ºW) in order to summarize the catch and effort by fleet on each given area for 2000 and 2001 fishing seasons. A review of averaged catch and fishing effort by gear has been done for the period 1975 to 2000 with the aim of compare the exploitation levels of both fleets during 2001 fishing season with the described time intervals for the period. 3. RESULTS AND DISCUSSION In Table 1 are included the catches and nominal effort for both fleets obtained in 2001 and those corresponding to 2000 for comparison reasons. The most remarkable change is given by the lower catch of bait boat fleet in 2001, representing a decrease of 67 % along with a reduction of 30% of the fishing effort respecting 2000. For the troll fishery there was as well a reduction on catch (15%) with a minor fishing effort (30%) in 2001 as compared to 2000 statistics. In figure 2 it is presented the 239

monthly catch distribution for the troll and bait boat fleets in 2001. As shown there is a seasonal component on the catch for both fleets. In 2001 the bait boat catch was concentrated on July and August being very scarce the activity in the autumn months. Meanwhile for troll fleet the catch was more spread along the summer and autumn months with a peak of catches also on July and August. In Table 2 is presented the evolution of catches and fishing effort (fishing days) averaged over different periods of time beginning with 1975 up to 2000 year. Those results show the decreasing tendency in the average catch and effort for both fleets along the decades and the lowest catch and effort level reached in 2001 for both fisheries: troll and bait boat. Considering the two geographical areas described as Gulf and Atlantic, in table 3 it is observed the different catch and effort obtained by the two fleets in respect to the two fishing grounds. In 2001 there was a reduction in the catch taken in the Gulf area (Bay of Biscay) that affected both fleets but it had a larger impact on the bait boat catch hence the total catch in this area was largely reduced in 2001 respecting the catch level in 2000 and as being presented the largest proportion of the bait boat fishing activity was carried out in the Bay of Biscay. This decrease on the fishing activity of bait boats was due to adverse climatic conditions in the Bay of Biscay area at the beginning of the autumn season. On the other hand the catch level for trollers diminished 15 % in 2001 having been done most of the fishing activity in the Atlantic area. The total catch at size distribution landed by both fleets in 2001 is represented in Figure 3.a and 3.b for bait boat and troll, respectively, the length selectivity is about the same for both gears. Three main modes, more clearly identified in baitboat length distribution catches, apparently correspond to age groups 1 to 3 and fewer fish older (> 80 cm). Immature albacore followed two main routes at the beginning of summer when migrating to the feeding areas in the north hemisphere: one to the south-west of Ireland and the other to the Bay of Biscay area, whose movements are associated to waters of temperature between 17ºC and 21ºC. Annual changes on the sea surface temperature in the fishing areas along with climatic conditions might influenced the distribution of immature albacore in the Bay of Biscay area during 2001 among other possible factors. The warming caused by the NAO positive anomalies has influenced the sea surface temperature in the northern latitudes of the northeast At lantic (Hurrel and Dickson, 2001). REFERENCES BARD, F.X., 1981. Le thon germon (Thunnus alalunga) de l Ocean Atlantique. De la dynamique de population à la stratégie démographique. Thèse Doctorat ès Sciences Naturelles, Universitè de Paris VI, 330 p. BARD, F.X., 2001. Extension of geographical and vertical habitat of albacore (T. alalunga) in the North Atlantic. Possible consequences on true rate of exploitation of this stock. ICCAT, Col. Sci. Pap. Vol. LII, pp 1447-1456. SCRS/00/119. HAVARD DUCLOS, F. 1973. La pêche au germon (Thunnus alalunga) dans le Golfe de Gascogne. Influence de la tèmperature sue le déplacement des mattes. ICCAT Rec.Doc.Sci.1: 341-370. HURREL, J.W. and R.R. Dickson, 2001. Climate variability over the North Atlantic. On Ecological effects of climate variations in the North Atlantic. Oxford University Press. Eds. (N.C. Stenseth, G. Ottersen, J.W.Hurrel and A.Belgrano). LEROY, C., 1990. Teledeteccion satellitaire et pêche du germon Thunnus alalunga dans le NE atlantique. ICCAT Rec. Doc. Sci. SCRS/89/59. 240

MIYAKE, M. 1990. Manual de Operaciones para estadísticas y muestreo de los túnidos y especies afines en el océano Atlántico. ICCAT, 3ª ed. Madrid. ORTIZ DE ZARATE, V. and J.L. Cort, 1998. Albacore stock structure in the Atlantic Ocean as inferred from distribution and migration patterns?. ICCAT Tunas Symposium. ICCAT, Col. Sci. Pap. Vol L (1), pp 251-260. ORTIZ DE ZARATE, V. and C. Rodriguez-Cabello, 2001. Spatial distribution of spanish baitboat fleet targeting albacore, Thunnus alalunga, in the northeast Atlantic ocean from 1981 to 1999. ICCAT, Col. Sci. Pap. Vol. LII, pp 1429-1434. SCRS/00/116. ORTIZ DE ZARATE, V. and C. Rodriguez-Cabello, 2002. Note on spanish albacore (Thunnus alalunga) surface fisheries in the northeast Atlantic waters in the year 2000. Col. Sci. Pap.. ICCAT Vol. 54 (5): 1508-1514. SANTIAGO, J., 1996. Cpue diaria de la flota vasca de cebo vivo de 1990 a 1993. ICCAT, Col. Doc. Cient. Vol. XLIII, pp: 255-259. 241

Table 1. Catch, nominal effort (fishing days) and number of albacore sampled by the spanish fleet (TR = Troll and BB = Baitboat) in 2000 and 2001. Year Gear Catch (k) Effort Catch (nº) Nº fish sampled % Coverage 2000 2001 BB BB 10498949 3420338 5406 3822 1726156 488788 15231 14157 0.9 2.9 TR TR 5012643 4244596 12023 8512 705903 633918 28237 29711 4.0 4.7 Table 2. Evolution of catch and nominal effort (fishing days) of albacore Spanish fleets: 1975-2001. BAITBOAT FISHERY CATCH ( t) EFFORT (fishing days) years mean st. Error CV (%) mean st. Error CV (%) 1975-1980 12415 2743 22 11271 3108 28 1981-1990 13779 3767 27 10898 2459 23 1991-2000 8362 1191 14 6321 1074 17 2001 3420 3822 TROLL FISHERY CATCH ( t) EFFORT (fishing days) years mean st. Error CV (%) mean st. Error CV (%) 1975-1980 10148 3692 36 20274 5394 27 1981-1990 9767 976 10 19216 3666 19 1991-2000 7094 1644 23 12387 1612 13 2001 4245 8512 Table 3. Catch and nominal effort by fishing areas for troll and baitboat Spanish albacore fishery in 2000 and 2001 years. 2000 TROLL 2000 BAIT BOAT AREA Gulf Atlantic % Gulf Gulf Atlantic % Gulf Nº trips 873 503 63.4 630 19 97.1 EFFORT (fd) 5655 6368 47.0 5163 243 95.5 CATCH (n) 302403 403500 42.8 1685663 40493 97.7 CATCH (w) 1957259 3055384 39.0 10172111 326838 96.9 Mean weigth 6.5 7.6 6.0 8.1 2001 TROLL 2001 BAIT BOAT AREA Gulf Atlantic % Gulf Gulf Atlantic % Gulf Nº trips 432 525 45.1 388 57 87.2 EFFORT (fd) 2520 5992 29.6 3169 653 82.9 CATCH (n) 147599 486319 23.3 436322 52466 89.3 CATCH (w) 720413 3524183 17.0 2945154 475184 86.1 Mean weigth 4.9 7.2 6.7 9.1 242

55 50 45 40 35 Summer baitboat fishery Summer troll fishery 30 30º 25º 20º 15º 10º 5º 0º 5º 10º Figure 1. Albacore troll and baitboat spanish fisheries. Seasonal albacore catch by spanish surface fleet 2000000 1500000 catch (kg) 1000000 500000 Bait boat Troll 0 6 7 8 9 10 Month Figure 2. Monthly albacore catch composition landed by fleet in 2001 year. 243

Albacore length composition of catch in 2001. 48000 42000 36000 age 1 age 2 age 3 Baitboat Nº Fish 30000 24000 18000 N= 488788 12000 6000 0 30 35 40 45 50 55 60 65 70 75 80 85 90 95 100 105 110 115 120 Length (cm) Figure 3.a. Catch length composition of albacore spanish baitboat fishery in 2001. Albacore length composition of catch in 2001. Nº Fish 48000 42000 36000 30000 24000 18000 12000 6000 age 1 age 2 age 3 Troll N = 633918 0 30 35 40 45 50 55 60 65 70 75 80 85 90 95 100 105 110 115 120 Length (cm) Figure 3.b. Catch length composition of albacore Spanish troll fishery in 2001. 244