BULLETIN OF MARINE SCIENCE, 69(3): 1109–1119, 2001 GROWTH AND MORTALITY OF THE BIGMOUTH SOLE, HIPPOGLOSSINA STOMATA EIGENMANN & EIGENMANN 1890 (PISCES: PARALICHTHYIDAE), OFF THE WESTERN COAST OF BAJA CALIFORNIA, MEXICO Marco A. Martínez-Muñoz and A. A. Ortega-Salas ABSTRACT Data on growth and mortality were obtained for bigmouth sole, Hippoglossina stomata, collected with otter trawls during 10 cruises off the western coast of Baja California, Mexico, from April 1988 to December 1990. In all, 1115 bigmouth sole were caught and, over the sampling period, in 298 specimens the male to female ratio was 1:1.03. The relationship between weight and length is described for females by W = 0.00000538 SL3.21054 and for males by W = 0.0001963 SL2.48525. Age-groups were estimated from length frequency data, von Bertalanffy growth parameters for all fish combined were the following: L• = 341.34 mm SL, k = 0.1757, t0 = -0.9835; for males, L• = 308.53 mm SL, k = 0.205, t0 = -0.6812, annually; and for females, L• = 359.43 mm SL, k = 0.1924, t0 = 0.769, annually. Males were smaller than females. The age groups allowed to determine a total mortality (Z) rate of 0.69, and estimate the fishing mortality (F) of 0.52 and natural mortality (M) of 0.17. Although the bigmouth sole is not a target species of commercial fisheries, it suffers high mortality as part of the bycatch in the shrimp fishery. Off the western coast of Baja California, flatfishes are the most abundant soft-bottom fishes caught in otter trawls (Martínez-Muñoz and Ramírez-Cruz, 1992). They are an important component of the shrimp fishery bycatch and constitute an important fisheries resource (Castro-Aguirre et al., 1992; Balart, 1996). The bigmouth sole, Hippoglossina stomata (Family Paralichthydae) is one of the more common species, it lives on sandy substrata from Monterey Bay, California, to the northern Gulf of California (Allen and Herbinson, 1991; Hensley et al., 1995). It is usually found in depths of 30 to 237 m (Martínez-Muñoz and Ramírez-Cruz, 1992). Bigmouth sole are relatively small, reaching a maximum total length of 40 cm (Eschmeyer et al., 1983) although fish longer than 35 cm are rare. Larger bigmouth soles could be of commercial importance due to the excellent quality of their meat (Balart, 1996). Bigmouth sole first mature at about 162 mm total length. It is a summer-fall spawner. This species preys on mysids and gammaridean amphipods (Allen, 1982) as well as pelagic red crab, Pleuroncodes planipes (Ramírez-Murillo et al., 1998). Ramírez-Murillo (1995) estimated age and growth parameters for bigmouth sole off the West coast of Baja California, and presented an otolith reading interpretation by the marginal-increment analysis. No data on mortality were available. The purpose of this paper is to provide information on the growth and mortality of bigmouth sole populations in the Mexican Pacific Ocean at Baja California, Mexico, for use in managing this species as a fishery resource. 1109 1110 BULLETIN OF MARINE SCIENCE, VOL. 69, NO. 3, 2001 MATERIALS AND METHODS Fishes were collected from April 1988 to December 1990 from 165 otter trawls conducted during the course of 10 cruises aboard the BO EL PUMA and BI MARSEP XVI. The 34 sampling stations were located off the West coast of Baja California, from Boca del Carrizal (23∞00'N) to Sebastian Vizcaino Bay (28∞51'N) in depths of 10 and 250 m (Fig. 1). The bottom temperature varied between 11 to 19oC. All fish were collected using an otter trawl that measured 20 m wide and 9 m high at the mouth, 24 m in length, with a stretched mesh size of 3 cm and code mesh of 1.5 cm. Trawling time and speed were recorded to estimate the area swept by the net. Trawling speed ranged between 1.1 and 1.5 m s–1. Trawls were towed for 30 min along isobaths (10 to 250 m). Specimens of bigmouth sole were measured, to the nearest millimeter standard length (SL), weighed to the nearest gram and sexed visually immediately after being caught. The gonads were examined macroscopically using the staging criteria of Nikolsky (1963). These data were used to calculate length-weight relationships, varying the logarithmic form of the equation: W = aLb for each sex, where W is weight in grams, a is the y-intercept, SL is standard length in millimeters, and b is the slope calculated with FISAT software (Gayanilo et al., 1994). Length frequency histograms of bigmouth sole were used to find the age-groups by the modal progression of Petersen (1939) method to start with, then the FISAT software was used to accurate Figure 1. Trawl stations sampled off Baja California, Mexico, 1988–1990, at depths of 10 to 250 m. MARTÍNEZ AND ORTEGA: GROWTH AND MORTALITY OF THE BIGMOUTH SOLE 1111 Figure 2. Length frequency distributions showing population structure of bigmouth sole, Hippoglossina stomata, during 1988–1990. the age-groups from the length frequency scattergram as seen in Fig. 5. Mean lengths for age groups were fitted using the von Bertalanffy (1938) equation Lt = L•(1-exp-k (t-to)); Ford (1933) and Walford (1949) methods by FISAT software were used to describe theoretical growth and growth parameters where Lt = standard length of fish at t years, L• = theoretical asymptotic length, k = growth coefficient rate of approach to L•, t0 = theoretical age at which Lt = 0. LFDA (Length Frequency Distribution Analysis ver 3.1), Holden and Bravington (1992), and Ortega-Salas (1981) basic programs were also used. Estimation of the instantaneous total mortality rate (Z) was calculated by the Beverton and Holt (1959) catch curve method described in Ricker (1975) using the FISAT software, based on all fishes ≥3 yrs of age. The difference between the total mortality coefficient (Z), which includes migration, and the natural mortality coefficient (M) gave an estimate of fishing mortality (F): F = Z-M. Although bigmouth sole is considered an exploitable species, its natural mortality (M) was estimated as an index from the rate of growth (k) as described by Beverton and Holt (1959). RESULTS Fishes from all trawls were combined, so that 1115 bigmouth soles, ranging in size from 55 to 290 mm SL and weights from 2.9 to 429 g were registered. From 298 fishes, 145 (48.65%) were females, 137 (45.97%) were males, and the sex of 16 (5.36%) was undetermined; hence, the female to male ratio was 1:1.03. A chi square test showed no seasonal difference in numbers of females relative to males (c2 = 0.2268; df = 1; P < 0.01). As with most flatfish, females were considerably larger in length and weight relative to males (Figs. 2,3). The largest female measured 290 mm SL and weighed 429 g, compared with 223 mm and 189 g, respectively, for the largest male. The mean values for females were 160.5 mm SL ± 42.6 SD and 80.7 g ± 63.9 SD weight, and males 142.7 mm SL ± 35.3 SD and 55.1 g ± 41.5 SD, respectively (Table 1). Use of a t-test and mean differences revealed no significant difference between sexes according to the mean length was 17.78; confidence interval (CI) was 95%; df = 280; t = 3.80; and significance level = 1.76 ¥ 10-4 at P< 0.05, not even mean weight revealed significant differences between sexes was 25.65; CI = 95%; df = 280; t = 3.96; and significance level = 9.15 ¥ 10-5. 1112 BULLETIN OF MARINE SCIENCE, VOL. 69, NO. 3, 2001 Figure 3. Weight frequency distributions showing population structure of bigmouth sole, Hippoglossina stomata, during 1988–1990. Length and weight were closely correlated with the determination coefficients ranging from 0.96 in females to 0.74 in males (Fig. 4). The slope shows that females are heavier than males for the same length. Age-groups were estimated from the length frequency scattergram of the bigmouth sole and the von Bertalanffy parameters calculated are the following: L• = 341.34 mm SL, k = 0.1757, t0 = -0.9835 as shown in Figure 5. Theoretical growth of males and females of the bigmouth sole is shown in Figures 6 and 7. After age 3 (210 mm), females were consistently longer and heavier than males due to differences in reproductive condition or general robustness of fish, although the rate of growth (k) for the two sexes was similar. Females attained an older age and longer length than males. The growth rate of the different age-groups (4 yrs and older) declined with age. Assuming no size- or age-selective catchability, the mean annual total mortality was calculated as Z = 0.69 and, apparently, constant for the age-groups considered (Fig. 8). Age-groups 0 to 2 were excluded because of poor efficiency of the sampling net for the smaller fishes. Hence, the natural mortality coefficient (M) according to Beverton and Holt (1959) was estimated as 0.17. The estimated mortality rates were the following: Z = 0.69; M = 0.17; F = 0.52, where F = 0.52 is an estimate for fishing mortality. Table 1. Weight and standard length data of bigmouth sole, Hippoglossina stomata, males and females. Sex Females Standard length (mm) Weight (g) Males Standard length (mm) Weight (g) n Minimum Maximum Mean SD 145 55 2.9 290 429 160.4 80.7 42.6 63.9 137 55 2.9 223 189 142.7 55.1 35.3 41.5 MARTÍNEZ AND ORTEGA: GROWTH AND MORTALITY OF THE BIGMOUTH SOLE 1113 Figure 4. Length-weight relationships of male and female bigmouth sole, Hippoglossina stomata, from Baja California. Scatter of points are from 1115 fish. Figure 5. Length frequency scattergram of the bigmouth sole, Hippoglossina stomata, to find the age groups. 1114 BULLETIN OF MARINE SCIENCE, VOL. 69, NO. 3, 2001 Figure 6. Growth curve of female and male bigmouth sole, Hippoglossina stomata, in standard length, showing standard dispersion error at 95% confidence. Figure 7. Weight curve of female and male bigmouth sole, Hippoglossina stomata, showing the standard dispersion error at 95% confidence. MARTÍNEZ AND ORTEGA: GROWTH AND MORTALITY OF THE BIGMOUTH SOLE 1115 Figure 8. Catch curve for bigmouth sole, Hippoglossina stomata, caught off Baja California, Mexico. The curve is slightly nonlinear but regression analysis suggests a value of Z = 0.69. The FISAT program was used. DISCUSSION The sex ratio in the flatfish species is generally 1:1 (Kramer, 1991; Minami and Tanaka, 1992) as found in this paper. Ramírez-Murillo (1995) calculated age in bigmouth sole by the Cassie method (1954) and by reading otoliths (Table 2), which compared with the present results of L• = 341.34 mm SL, k = 0.1757, t0 = -0.9835, reveal a bigger L•, possibly because maximum lengths were of 290 mm SL, compared with their measurement of 258 mm SL, although the rate of growth (k) was similar; in both papers a maximum age of 9 to 10 yrs has been estimated. Few previous studies on the biology of the bigmouth sole exist; hence, the growth and mortality parameters estimated here can only be compared to those obtained from studies made in other flatfish species (Tables 3,4). Growth of the bigmouth sole shows the same features as other flatfishes: females growing faster than males, adult females being heavier (La = 359.43 mm SL) than males for the same length (La = 308.53 mm SL). In comparison with other flatfish species for which growth data are available, the growth rate of the bigmouth sole is comparatively high and the species attains a size large enough for commercial exploitation at 3 yrs. Table 2. Growth parameters of bigmouth sole, Hippoglossina stomata by Cassie method and by reading otoliths in 1990. Taken from Ramí rez-Murillo (1995). Growth parameters L• k t0 March 426.4 0.004 -3.91 Cassie method September 392 0.004 -4.99 Otoliths reading December 226 0.0009 -2.42 289.09 0.184 -0.209 Location Baja California, Mexico Baja California, Mexico Diamond turbot, Hypsopsetta guttulata Anaheim Bay, USA Dover sole, Microstomus pacificus Northern California, USA Pacific sanddab, Citharichthys sordidus Southern California, USA Starry flounder, Platichthys stellatus Monterrey Bay, USA Bigmouth sole, Hippoglossina stomata Baja California, Mexico Bigmouth sole, Hippoglossina stomata Species Fantail sole, Xystreurys liolepis L• (mm) 443.00 SL 354.85 SL 444.68 SL 289.09 SL 198.50 SL 431.49 LT 494.58 LT 294.80 LT 297.50 LT 443.44 SL 592.86 SL 341.34 SL 308.53 SL 359.43 SL Sex Combined Male Female Combined Combined Male Female Male Female Male Female Combined Male Female Table 3. Comparison of the von Bertalanffy parameters in seven different flatfish species. 0.294 0.241 0.244 0.317 0.441 0.281 0.1757 0.205 0.192 0.10 0.16 0.151 0.163 0.1843 k Source Martí nez-Muñoz and Ortega-Salas (1999) 0.540 0.753 -0.98 -0.336 0.42 0.33 -0.983 -0.681 -0.769 0.31 Present Paper Orcutt (1950) Arora (1951) Hagerman (1952) Lane (1975) -0.098 -0.918 -0.423 0.2096 Ramí rez-Murillo (1995) t0 1116 BULLETIN OF MARINE SCIENCE, VOL. 69, NO. 3, 2001 MARTÍNEZ AND ORTEGA: GROWTH AND MORTALITY OF THE BIGMOUTH SOLE 1117 Table 4. Comparison of total mortality (Z) in five different flatfish species. Species Diamond turbot, Hypsopsetta guttulata Dab, Limanda limanda Lepidorhombus boscii Fantail sole, Xystreurys liolepis Bigmouth sole, Hippoglossina stomata Location Anaheim Bay, USA Isle of Man, UK Portuguese Coast, Portugal Baja California, Mexico Baja California, Mexico Z 2.6 M: 1.39 F: 1.06 0.45 0.62 0.69 Source Lane (1975) Ortega-Salas (1981) Santos (1994) Martí nez-Muñoz and Ortega-Salas (1999) Present paper The age composition for both sexes of the same stock are clearly different and males generally have a shorter life span than females. Thus, whereas males dominate the younger age-groups, females are more abundant in the older groups. The values obtained for annual total mortality, Z = 0.69, natural mortality, M = 0.17, and fishing mortality, F = 0.52, are first estimations for the bigmouth sole population from the western coast of Baja California. In spite of the consistency among those age classes included, the mortality should be further investigated, especially with respect to the younger age classes and by using direct methods. Off the western coast of Baja California, a high fishing mortality of flatfishes, including bigmouth sole, occurs resulting from intensive trawl fishing for shrimp according to Ehrhardt et al., (1982); van der Heiden et al., (1985). Although bigmouth sole is not a target species of commercial fisheries, the rate of fishing mortality is higher than natural mortality, possibly due to the large bycatch of flatfishes, including California halibut (Paralichthys californicus), Fantail sole (Xystreurys liolepis), Longfin sanddab (Citharichthys xanthostigma), Fourspot sole (Hippoglossina tetrophthalma), Spotted turbot (Hypsopsetta guttulata) and California tonguefish (Symphurus atricauda), among others, in the shrimp fishery. The bigmouth sole is considered a potentially exploitable flatfish but needs to be managed as a fishery resource. ACKNOWLEDGMENTS This study was partially supported by the Consejo Nacional de Ciencia y Tecnología de México (CONACyT), grant P22OCC0R880518, and the Universidad Nacional Autónoma de México, which provided the BO EL PUMA from 1988 to 1991. We also thank the Instituto de Ciencias del Mar y Limnología (UNAM) for analyzing the data and the Centro de Investigaciones Biológicas del Noroeste for processing the raw material. And to A. Nuñez and R. Ramírez for their collaboration. LITERATURE CITED Allen, M. J. 1982. Functional structure of soft-bottom fish communities of the Southern California shelf. Ph.D. Dissertation. Univ. California, San Diego. 577 p. 1118 BULLETIN OF MARINE SCIENCE, VOL. 69, NO. 3, 2001 __________ and K. T. Herbinson. 1991. Beam-trawl survey of bay and nearshore fishes of softbottom habitat of southern California in 1989. Calif. Coop. Oceanic. Fish. Invest. Rpt. 32: 112– 127. Arora, H. L. 1951. An investigation of the California Sanddab Citharichthys sordidus (Girard) Calif. Fish Game 37 (1): 3–42. Balart, E. F. 1996. Pesquería de lenguados. In M. Casas Valdez y G. Ponce Díaz, eds. Estudio del Potencial Pesquero y Acuícola de Baja California Sur. Beverton, R. J. H. and S. J. Holt. 1959. A review of the life span and mortality rates of fish in nature, and their relation to growth and other physiological characteristics. CIBA Fdn. Colloq. Ageing 5: 142–177. Cassie, R. M. 1954. Some uses of probability paper in the analysis of the size frequency distributions. Aust. J. Mar. Freshw. Res. 5: 513–522. Castro-Aguirre, J. L., J. C. Ramírez-Cruz and M. A. Martínez-Muñoz. 1992. Nuevos datos sobre la distribución de lenguados (Pisces: Pleuronectiformes) en la costa oeste de Baja California, México con aspectos biológicos y zoogeográficos. An. Esc. Nac. Cienc. Biol., Méx. 37: 97– 119. Dagang, C., L. Changan and D. Shuozeng. 1992. The biology of flatfish (Pleuronectinae) in the coastal waters of China. Neth. J. Sea Res. 29(1–3): 25–33. Ehrhardt, N. M., E. M. Ramírez, P. Aguilera, P. Jacquemin, M. Lozano and I. Romo. 1982. Evaluación de los recursos demersales accesibles a redes de arrastre de la plataforma continental de la costa occidental de la península de Baja California, México, durante 1979 y 1980. INP/Ser. Ciencias 22: 1–47. Eschmeyer, W. N., E. S. Herald and H. Hammann. 1983. A field guide to Pacific coast fishes of North America from the Gulf of Alaska to Baja California. The Peterson Field Guide Series, Houghton Mifflin Co., Boston. 28: 336. Ford, E. 1933. An account of the herring investigations conducted at Plymouth during the years from 1924 to 1933. J. Mar. Biol. Ass. U.K, NS. 19: 305–384. Gayanilo, F. C., Jr., P. Sparre and D. Pauly. 1994. The FAO-ICLARM stock assessment tools (FISAT) user’s guide. FAO Computerized Information Series (Fisheries) no. 6. Rome. 186 p. Hagerman, B. F. 1952. The biology of the Dover Sole Microstomus pacificus (Lockington). Calif. Dept. Fish. Game. Fish Bull. U.S. (85): 3–48. Hensley, D. A. 1995. Paralichthyidae. Pages 1349–1380–in W. Fischer, F. Krupp, W. Schneider, C. Sommer, K. E. Carpenter and V. H. Niem, eds. Guía para la identificación de especies para los fines de pesca. Pacífico centro-oriental, vol 2. Vertebrados-Parte 1. Vol. 3 Parte 2. FAO, Rome. Holden, S. and M. V. Bravington. 1992. The LFDA Package user manual. Fish Management Science Programme of the Overseas Development Administration of the U.K Government. London. 66 p. Kramer, S. H. 1991. The shallow-water flatfishes of San Diego County. California Cooperative Oceanic Fisheries Investigations Rpt. 32: 128–142. Lane, E. D. 1975. Quantitative aspects of the life history of diamond turbot, Hypsopsetta guttulata (Girard), in Anaheim Bay. Fish. Bull. U.S. 165: 153–74. Liu, X. 1990. Pages 396–432 In Investigation on the fisheries resources and the division of the Yellow Sea and the Bohai Sea. Ocean Publishing Press. Martínez-Muñoz, M. A. and C. Ramírez-Cruz. 1992. Distribución y Abundancia de Pleuronectiformes (Teleostei), en la costa occidental de Baja California Sur, México. Tesis Facultad Ciencias Univ. Nacional Autónoma de México. 133 p. ___________________ and A. A. Ortega-Salas. 1999. Growth and Mortality of the Fantail sole, Xystreurys liolepis (Jordan and Gilbert 1881) off the Western Coast of Baja California, Mexico. Bull. S. Calif. Acad. Sci. 98(2): 66–74. Minami, T. and M. Tanaka. 1992. Life history cycles in flatfish from the northwest Pacific, with particular reference to their early life histories. Neth. J. Sea Res. 29(1–3): 35–48. Nikolsky, G. V. 1963. The ecology of fishes. Academic Press, London. 352 p. MARTÍNEZ AND ORTEGA: GROWTH AND MORTALITY OF THE BIGMOUTH SOLE 1119 Orcutt, H. G. 1950. The life history of the Starry flounder Platichthys stellatus (Pallas). Calif. Dept. Fish. Game. Fish Bull. 78. 64 p. Ortega-Salas, A. A. 1981. Biology of the dab, Limanda limanda (L) in Isle of Man waters. Ph D. Thesis. Dept. Mar. Biol. Univ. Liv., Port Erin. I of M. 98 p. Petersen, C. G. J. 1939. Fiskenes biologiske forhold og Holbaek Fjord, 1890–91. Beret. Danm. Biol. St. 1890(1) 1: 121–183. Ramírez-Murillo, R. 1995. Determinación de la edad y crecimiento de Hippoglossina stomata Eigenmann and Eigenmann. 1890 (Pisces: Bothidae) en la costa occidental de Baja California Sur, México. Thesis Biol. Univ. Mich. San Nicolás de Hidalgo, Mexico. 44 p. ________________, A. A. Ortega-Salas and M. A. Martínez-Muñoz, 1998. A dietary analysis of Hippoglossina stomata Eigenmann and Eigenmann, 1890 (Pisces: Bothidae) along the Western Coast of Baja California, Mexico. Bull. S. Calif. Acad. Sci. 97(3): 104–109. Ricker, W. E. 1975. Computation and interpretation of biological statistics of fish populations. Bull. Fish. Res. Bd. Can. 191: 382 p. Santos, P. T. 1994. Growth and reproduction of the population of the Four-spot megrim (Lepidorhombus boscii Risso) off the portuguese coast. Neth. J. Sea. Res. 32(3–4): 379–383. van der Heiden, A. M. 1985. Taxonomía, biología y evaluación de la ictiofauna demersal del Golfo de California. Pages 149–200 in A. Yañez-Arancibia, ed. Recursos pesqueros potenciales de México: la pesca acompañante del camarón. Univ. Nal. Autón. México/Secr. Pesca, Mexico. 748 p. von Bertalanffy, L. 1938. A quantitative theory of organic growth of animals. Human Biol. 10(2): 181–213. Walford, L. A. 1949. A new graphic method of describing the growth of animals. Biol. Bull. 90(2): 141–147. DATE SUBMITTED: August 10, 2000. DATE ACCEPTED: June 12, 2001. ADDRESSES: (M.A.M.-M.) Unidad Profesional Interdisciplinaria de Ingeniería y Ciencias Sociales y Administrativas, I.P.N. Hocaba esq. Hopelchen Manz-353 L-1. Torres de Padierna. C.P. 14200, Mexico, D.F., Mexico. E-mail: <[email protected]>. CORRESPONDING AUTHOR: (A.A.O.-S.) Instituto de Ciencias del Mar y Limnología, UNAM, Apdo.Postal 70-305, México 04510, D.F., Mexico. E-mail: <[email protected]>.
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