SANDARDIZED CATCH-RATES OF WHITE MARLIN (KAJIKIA ALBIDA) FOR THE TAIWANESE DISTANT-WATER TUNA LONGLINE FISHERY IN THE ATLANTIC OCEAN,

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SCRS/2012/056 Collect. Vol. Sci. Pap. ICCAT, 69(3): 1213-1224 (2013) SANDARDIZED CATCH-RATES OF WHITE MARLIN (KAJIKIA ALBIDA) FOR THE TAIWANESE DISTANT-WATER TUNA LONGLINE FISHERY IN THE ATLANTIC OCEAN, 1967-2010 Chi-Lu Sun, Nan-Jay Su, and Su-Zan Yeh 1 SUMMARY The catch and effort data of the Taiwanese distant-water tuna longline fishery were standardized for white marlin in the Atlantic Ocean. Two alternative approaches, i.e., generalized linear and additive models, were applied for the standardization, based on the assumption of lognormal error distribution. All the main effects and the interactions considered in the standardization were statistically significant. Results derived from the two modeling approaches were almost identical, regardless of including or not the interaction terms in the models. The standardized of white marlin for the Taiwanese distant-water longline fishery in the Atlantic Ocean showed a decreasing trend before 1990, but increased substantially in the early 1990s, and then decreased continuously over the past 15 years. RÉSUMÉ Les données de prise et d effort de la pêcherie palangrière thonière du Taipei chinois opérant en eaux lointaines dans l'océan Atlantique ont été standardisées pour le makaire blanc. Deux approches alternatives ont été appliquées (modèle linéaire généralisé et modèle additif) pour la standardisation, sur la base du postulat de distribution d erreur lognormale. L'ensemble des principaux effets et interactions pris en compte dans la standardisation était statistiquement significatif. Les résultats découlant des deux approches de modélisation étaient presque identiques, indépendamment du fait d'inclure ou non les termes d interaction dans les modèles. La standardisée du makaire blanc de la pêcherie palangrière thonière hauturière du Taipei chinois opérant dans l'océan Atlantique dégageait une tendance à la baisse avant 1990, mais a augmenté considérablement au début des années 1990, pour chuter ensuite de manière continue au cours de ces 15 dernières années. RESUMEN Se estandarizaron los datos de captura y esfuerzo de la pesquería de palangre de túnidos de aguas distantes de Taipei Chino para la aguja blanca en el océano Atlántico. Para la estandarización se aplicaron dos enfoques alternativos, es decir, modelos lineales generalizados y aditivos, basándose en un supuesto de distribución de error lognormal. Los principales efectos e interacciones considerados en la estandarización fueron estadísticamente significativos. Los resultados derivados de los dos enfoques de modelación fueron casi idénticos, al margen de que se incluyeran o no los términos de interacción en los modelos. La estandarizada de aguja blanca de la pesquería de palangre de aguas distantes de Taipei Chino en el océano Atlántico mostraba una tendencia decreciente antes de 1990, pero se incrementó notablemente a principios de los noventa, y ha descendido de forma continua durante los 15 últimos años. KEYWORDS White marlin, standardized, GLM, GAM, longline 1 Institute of Oceanography, National Taiwan University, Taipei, 10617 Taiwan. E-mail: chilu@ntu.edu.tw 1213

1. Introduction White marlin, Kajikia albida (formerly Tetrapturus Albidus; Collette et al., 2006), is a highly migratory species widely distributed in the Atlantic Ocean (Goodyear, 2003). Several studies have reported that white marlin migrate a long distance more than 1000 km, consisting of both trans-atlantic and trans-equatorial movements (Orbesen et al., 2008). The assessment of white marlin in the Atlantic Ocean was made based on the assumption of a single unit stock (Restrepo et al., 2003). Previous stock assessment conducted by the International Commission for the Conservation of Atlantic Tunas (ICCAT) indicated that the current status of this population was overfished, with estimated exploitable biomass well below the level needed to maintain maximum sustainable yield, and suffering overfishing (Wells et al., 2010; ICCAT, 2012). White marlin are caught as bycatch species in commercial longline fisheries targeting tunas, supporting economically important recreational fisheries throughout the Atlantic Ocean (Prince and Brown, 1991). The Taiwanese distant-water tuna longline fishery has operated throughout the Atlantic Ocean since the early 1960s, and become one of the major longline fleets thereafter. The fishery targeted solely on albacore tuna (Thunnus alalunga) from the beginning through 1980s, but some of fishing effort has shifted to target on bigeye (Thunnus obesus) and yellowfin (Thunnus albacares) since the late 1980s, with the development of the deep longlining (Chang, 2003). (catch per unit of effort) of white marlin for the fleets operating in the Atlantic Ocean is standardized for the use of basic input data in stock assessments (ICCAT, 2011). The objective of this study were to provide (1) the spatial and temporal distributions of fishing effort for the Taiwanese distant-water tuna longline fishery in the Atlantic Ocean and the nominal catch-rates of white marlin from this fishery, and (2) the standardized of white marlin derived from statistical models based on the assumption of a single Atlantic-wide stock for this species. 2. Materials and methods 2.1 Fishery data Task II data (1967-2010) on catch (number of white marlin caught) and effort (number of hooks deployed) of the Taiwanese distant-water tuna longline fishery in the Atlantic Ocean were obtained from the Overseas Fisheries Development Council of the Republic of China (OFDC, Chinese Taipei). Data were aggregated into monthly 5 5 latitude and longitude grids. were expressed as the number of fish caught per 1000 hooks. 2.2 Statistical model Nominal of white marlin were standardized using two alternative approaches, generalized linear models (GLMs) and generalized additive models (GAMs). The lognormal error distribution was assumed in the standardization. GLMs are the most commonly used approach for standardizing catch and effort data, assuming that the expected value of a transformed response variable is related to a linear combination of exploratory variables, whereas GAM is a semi-parametric extension of GLM with the underlying assumption that the response variable is related to smooth additive functions of the explanatory variables (Maunder and Punt 2004)., month, latitude, and longitude were considered in the GLM and GAM analysis as main explanatory variables. The full GLM and GAM models including interactions were expressed as follows: GLM: WHM ~ + Month + Latitude + Longitude; GLMi: WHM ~ + Month + Latitude + Longitude + Interactions; GAM: WHM ~ + s(month) + s(latitude) + s(longitude); GAMi: WHM ~ + s(month) + s(latitude) + s(longitude) + s(interactions) where WHM is the nominal of white marlin with a constant being added to avoid log-transformation problems; s(x) denotes a spline smoother function of the covariate X. No interactions with year effect were considered in GLMs and GAMs for the standardization (Maunder and Punt 2004). 1214

2.3 Model diagnostic Various diagnostic plots, e.g. the distribution of residuals and quantile-quantile plots (Q-Q plots), were used to assess the assumption of error models (here assuming lognormal distribution) for standardizing the nominal of white marlin in the Atlantic Ocean. The improvement of each model that differed in one additional predictor was examined using the change in deviance explained, the proportion of deviance explained to the total explained deviance, the change in R 2, and the Chi-square test. 3. Results and discussion There were in total 22,719 catch-effort records available for the Taiwanese distant-water tuna longline fishery in the Atlantic Ocean for 1967-2010. This fishery operated throughout the entire Atlantic Ocean (Figure 1), but shifted to tropical waters to target bigeye and yellowfin tunas since the late 1980s (Figures A1-A2). Most of high nominal of white marlin distributed in temperate waters of the western Atlantic Ocean around 20 N and 20 S (Figure 2). The residual distributions from both GLM and GAM analyses appeared normal for all of the four candidate models (Figure 3), even if separated by period (results for GLMi were shown in Figure A3). The Q-Q plots also confirmed to the greatest extent the assumption of lognormal error distribution for all the models used to standardize the nominal of white marlin for the fishery (Figure 4). All of the main explanatory variables considered in the modelling and the interactions used in the GLM and GAM analyses were highly significant (P < 0.01; Table 1). The proportion of deviance explained (i.e. R 2 ) in the GLM and GAM modelling with all of the predictors were 0.36 and 0.29, respectively., latitude and longitude explained the largest proportion of deviance, accounting for 75.4% in the GLM and 79.7% in the GAM of the total deviance explained (Table 1). We inferred based on the results that latitude and longitude were the predominant predictors affecting the nominal of white marlin, compared to the month effect (Figure A4). However, environmental factors (e.g. sea surface temperature, chlorophyll-a concentration, and mixed layer depth) could also be important factors to influence the of white marlin, and should be included in further analyses (see the study conducted by Goodyear, 2003). Results showed that the standardized of white marlin derived from the GLM and GAM modeling approaches were almost identical, no matter including or not the interaction terms in the standardization models (Figure 5). In general, the standardized of white marlin for the Taiwanese distant-water longline fishery were high (~0.3 fish per 1000 hooks) in the late 1960s and early 1970s, but decreased sharply in the late 1970s. The standardized trend seemed to stabilize with a slight increase trend in the 1980s, and then substantially increased in the early 1990s. However, the standardized of white marlin have dropped continuously since mid-1990s, and reached the lowest level in recent years (less than 0.1 fish per 1000 hooks) (Figure 5). We suggest using the standardized series derived from the GLMi for the white marlin stock assessment (Table 2), because this model explained the most deviance among the candidate models. References Chang, S.K. 2003, Analysis of Taiwanese white marlin catch data and standardization of catch rates. Collect. Vol. Sci. Pap. ICCAT, 55: 453 466. Collette, B.B., McDowell, J.R. and Graves J.E. 2006, Phylogeny of recent billfishes (Xiphioidei). Bull. Mar. Sci., 79: 455 468. Goodyear, C.P. 2003, Spatio-temporal distribution of longline catch per unit effort, sea surface temperature and Atlantic marlin. Mar. Freshw. Res., 54: 409 417. ICCAT 2012, Report of the 2011 Blue Marlin Stock Assessment and White Marlin Data Preparatory Meeting. April 25-29, 2011, Madrid, Spain. Collect. Vol. Sci. Pap. ICCAT, 68(4)L 1273-1386. Maunder, M.N. and Punt, A.E. 2004, Standardizing catch and effort data: a review of recent approaches. Fish. Res., 70: 141 159. 1215

Orbesen, E.S., Hoolihan, J.P., Serafy, J.E., Snodgrass, D., Peel, E.M., and Prince, E.D. 2008, Transboundary movement of Atlantic istiophorid billfishes among international and U.S. domestic management areas inferred from mark-recapture studies. Mar. Fish. Rev., 70: 14 23. Prince, E.D. and Brown, B.E. 1991, Coordination of the ICCAT Enhanced Research Program for Billfish. In: Guthrie, D., Hoenig, J.M., Holliday, M., Jones, C.M., Mills, M.J., Moberly, S.A., Pollock, K.H., and Talhelm, D.R. (Eds.), Fisheries Management, American Fisheries Society Symposium 12, pp13 18. Restrepo, V., Prince, E.D., Scott, G.P., and Uozumi Y. 2003, ICCAT stock assessments of Atlantic billfish. Mar. Freshw. Res., 54: 361 367. Wells, R.J.D., Rooker, J.R., Prince, E.D. 2010, Regional variation in the otolith chemistry of blue marlin (Makaira nigricans) and white marlin (Tetrapturus albidus) from the western North Atlantic Ocean. Fish. Res., 106: 430 435. Table 1. Analysis table for the models selected to standardize the catch and effort data of Taiwanese distant-water tuna longline fishery for white marlin in the Atlantic Ocean using generalized linear models and generalized additive models. (a) Generalized linear models Predictor Residual deviance Deviance explained % of total deviance explained P-value R 2 Model NULL 26598 + 23744 2853 29.9 <0.01 0.107 +Month 22990 755 7.9 <0.01 0.136 +Latitude 20278 2711 28.4 <0.01 0.238 +Longitude 18644 1634 17.1 <0.01 0.299 GLM +Latitude:Longitude 17054 1590 16.7 <0.01 0.359 GLMi (b) Generalized additive models Predictor Residual deviance Deviance explained % of total deviance explained P-value R 2 Model NULL 26598 +s() 23744 2853 36.8 <0.01 0.107 +s(month) 23125 619 8.0 <0.01 0.131 +s(latitude) 21503 1622 20.9 <0.01 0.192 +s(longitude) 19804 1700 21.9 <0.01 0.255 GAM +s(latitude:longitude) 18852 952 12.3 <0.01 0.291 GAMi The P-values indicate the level of significance based on the Chi-square test. 1216

Table 2. Nominal and standardized of white marlin for the Taiwanese distant-water tuna longline fishery in the Atlantic Ocean. Nominal Standardized Nominal Standardized 1967 0.145 0.165 1989 0.559 0.190 1968 0.631 0.304 1990 0.152 0.128 1969 0.363 0.311 1991 0.047 0.084 1970 0.530 0.324 1992 0.049 0.108 1971 0.323 0.345 1993 0.250 0.226 1972 0.203 0.214 1994 0.285 0.332 1973 0.449 0.259 1995 0.201 0.219 1974 0.492 0.317 1996 0.191 0.214 1975 0.343 0.249 1997 0.158 0.199 1976 0.018 0.094 1998 0.046 0.134 1977 0.009 0.094 1999 0.050 0.131 1978 0.026 0.099 2000 0.056 0.122 1979 0.093 0.119 2001 0.043 0.128 1980 0.182 0.178 2002 0.064 0.137 1981 0.250 0.187 2003 0.039 0.109 1982 0.116 0.147 2004 0.020 0.090 1983 0.118 0.171 2005 0.026 0.099 1984 0.131 0.141 2006 0.027 0.111 1985 0.109 0.142 2007 0.025 0.095 1986 0.234 0.186 2008 0.017 0.084 1987 0.218 0.210 2009 0.011 0.082 1988 0.232 0.178 2010 0.007 0.083 1217

Figure 1. Distributions of fishing effort (10 6 hooks) of the Taiwanese distant-water tuna longline fleet in the Atlantic Ocean for 1967-79, 1980-89, 1990-99, and 2000-10. 1218

Figure 2. Distributions of nominal (number of fish caught per 1000 hooks) for white marlin caught in the Taiwanese distant-water tuna longline fishery in the Atlantic Ocean for 1967-79, 1980-89, 1990-99, and 2000-10. 1219

Density GLM GLMi Density GAM GAMi Residuals Residuals Figure 3. Diagnostic plots (residual distributions) for the GLMs and GAMs used to standardize the catch-rates of white marlin for the Taiwanese distant-water tuna longline fishery in the Atlantic Ocean for 1967-2010. Figure 4. Diagnostic plots (Q-Q plots) for the GLMs and GAMs used to standardize the catch-rates of white marlin for the Taiwanese distant-water tuna longline fishery in the Atlantic Ocean for 1967-2010. 1220

GLM GLMi GAM GAMi Figure 5. The nominal (open circles) and standardized (black lines) (number of fish caught per 1000 hooks) of white marlin for the Taiwanese distant-water tuna longline fishery in the Atlantic Ocean for 1967-2010 using GLM and GAM modeling approaches. The shadowed areas indicate the point-wise standard errors for the standardized of white marlin. 1221

Appendix 1 st Quarter 2 nd Quarter Jan Apr Feb May Mar Jun 3 rd Quarter 4 th Quarter Jul Oct Aug Nov Sep Dec Figure A1. Fishing effort (in 10 6 hooks) of the Taiwanese distant-water longline fishery in the Atlantic Ocean (0-30 S) during 1967-2010 by month. 1222

Catch 0.0 1.0 2.0 3.0 (a) BET 0 2 4 6 8 (a) BET Catch 0.0 0.4 0.8 1.2 (b) YFT 0 2 4 6 8 12 (b) YFT Catch 0 10 20 30 40 50 (c) SWO 0.8 1.0 (c) SWO Catch (d) WHM 0.0 0.4 0.8 (d) WHM Figure A2. Annual catches (in 10 5 fish) and (number of fish caught per 1000 hooks) by species: (a) bigeye tuna (BET), (b) yellowfin tuna (YFT), (c) swordfish (SWO), and (d) white marlin (WHM) for the Taiwanese distant-water longline fleet in the Atlantic Ocean (0-30 S). 1223

Density 1967-1979 1980-1989 Density Residuals Residuals Density 1990-1999 2000-2010 Density Residuals Residuals Figure A3. Residual distributions for the selected standardization model (GLMi) by period, 1967-79, 1980-89, 1990-99, and 2000-10. Effect () 1 0.5 0-0.5 (a) Effect (Month) 0.6 0.4 0.2 0-0.2-0.4 (b) -1 1965 1975 1985 1995 2005-0.6 J F M A M J J A S O N D Month Effect (Latitude) 2 1 0-1 -2-3 (c) Effect (Longitude) 4 3 2 1 0-1 (d) -4-2 S -60-40 -20 0 20 40 60 N W -100-80 -60-40 -20 0 20 40 E Latitude Longitude Figure A4. Estimated effects of (a) year, (b) month, (c) latitude, and (d) longitude on the of white marlin for the selected standardization model (GLMi). 1224