Growth rate and natural mortality of the scallop Pecten alba tate in Port Phillip Bay,Australia, and evidence for changes in growth rate after a 20-year period

The instantaneous coefficient of natural mortality of the scallop Pecten alba Tate in Port Phillip Bay (38°S, 145° E) in south-eastern Australia was estimated from tag-recapture experiments as 0.52 year⁻. Values for the parameters k and l₀₀ of the von Bertalanffy growth curve were 1.6 and 86 mm, respectively. Our results indicate that the growth rate of P. alba has increased substantially since the species was first commercially exploited 20 years ago. The scallops now attain a shell length of 70 mm more than 1 year sooner. We suggest that the increase in growth rate is related to density-dependence effects resulting from 20 years of commercial exploitation by scallop dredgers.     

Population dynamics and fishery benefits of a large legal size of a pelagic sportfish,the Talang queenfish,Scomberoides commersonnianus,in northern Australia

The life history of an increasingly important pelagic commercial and sport fish, the Talang queenfish, Scomberoides commersonnianus, was studied in northern Australia to investigate the stock status and assess current management of the species using minimum legal lengths (MLL). Estimated von Bertalanffy growth parameters were L_∞ = 1404 mm FL, K = 0.10 year⁻¹ and t₀ = −1.21 year⁻¹. There was no significant difference in growth between sexes. Ages ranged from 1 to 11 years with age composition differing between the commercial (mainly 6–7 years) and sport fishery (mainly 2–4 years). Females matured (L₅₀) at 635 mm FL and 4–5 years. Spawning occurred between August and March when mature females were estimated to produce 259,488–2,859,935 eggs per spawning. Natural mortality (M) was estimated as 0.16–0.26 year⁻¹, while the combined fishing mortality (F_current) from commercial and sport fisheries was 0.38–0.48 year⁻¹. Yield-per-recruit analyses revealed that under current MLL limits (no MLL or 45 cm TL) and natural mortality (M = 0.16, 0.2 and 0.26 year⁻¹), F_current exceeded the reference points F_max (0.15–0.22 year⁻¹) and F_0.1 (0.10–0.15 year⁻¹), suggesting the stock may be growth overfished if the current situation remains unchanged. Although a stock–recruitment relationship is unknown, spawning stock biomass-per-recruit analysis indicates the stock may also be recruitment overfished since F_current exceeded the reference points F_25% (0.19–0.24 year⁻¹) and F_40% (0.11–0.15 year⁻¹). Increasing the MLL corresponding to L₅₀ of females (70 cm TL) will greatly improve the yield and long-term sustainability of the stock, and also enhance the sport fishery by increasing the number of larger trophy fish.     

Population ecology parameters and biomass of golden grey mullet (Liza aurata) in Iranian waters of the Caspian Sea

This paper examines the changes in the population ecology parameters and biomass of golden grey mullet (Liza aurata) in Iranian waters of the Caspian Sea from 1991 to 2005. For most years during this 14-year period, we estimated the age structure of the catch, length–weight relationship, von Bertalanffy growth parameters, condition factor, natural and fishing mortality and biomass. Growth parameters were estimated as L_∞ = 62.7 cm, K = 0.15 year⁻¹, t₀ = −0.23 year⁻¹. The instantaneous coefficient of natural mortality was estimated as 0.350 year⁻¹ and the instantaneous coefficient of fishing mortality varied during the 14-year period between 0.111 to 0.539 year⁻¹. Biomass estimates of golden grey mullet, from the biomass-based cohort analysis were increased from 13,527 mt in 1991–1992 to 23,992 mt in 2002–2003. In 2004–2005, it was estimated to be 23,658 mt. We concluded that at the present time, the stock of golden grey mullet is not being over-fished.     

Effects of exploitation on age, growth and mortality of the blackspot snapper, Lutjanus fulviflamma, at Mafia Island, Tanzania

Abstract Estimates of the growth parameters (L_∞ and K), mortality coefficients (Z, M and F) and exploitation rate (E) for the blackspot snapper, Lutjanus fulviflamma (Forsskål) from the Mafia Island Marine Park (MIMP) and adjacent intensively fished areas in Tanzania were determined. Sectioned otoliths showed that L. fulviflamma in the MIMP attained a maximum age of 18 years, with a high proportion of fish between 6 and 10 years old. The maximum age was 8 years in the intensively fished areas, with a preponderance of 2‐ and 4‐year‐old fish. The size structures of the populations in the MIMP and that in the intensively fished areas were markedly different, with the MIMP fish averaging (±SE) 211.4 ± 0.38 mm TL, but 154.6 ± 0.32 mm TL in the intensively fished areas. The von Bertalanffy growth parameters were L_∞ = 290.3 mm TL, K = 0.15 year^?1 and t₀ = ?2.7 years. There was no significant difference in growth between the four populations (L_∞: F‐stat = 0.14, P = 1.000, and K: F‐stat = 0.26, P = 0.992). Total mortality was 0.55 and 1.64 year^?1 in the MIMP and intensively fished areas, respectively, natural mortality 0.27 year^?1 and fishing mortality 0.18 and 1.37 year^?1 in the MIMP and intensively fished areas, respectively. The exploitation rate was 0.51 and 0.84 in the MIMP and intensively fished areas, respectively. The artisanal seine net fishery is directed mainly at younger fish in the intensively fished areas resulting in growth overfishing. The protracted life span, the slow growth and natural mortality rates imply that L. fulviflamma is vulnerable to overfishing and that the protection provided by the park, although limited, is vital for sustaining the fishery at Mafia Island.     

Spawning per recruit analysis of the pelagic thresher shark,Alopias pelagicus,in the eastern Taiwan waters

The pelagic thresher shark, Alopias pelagicus, is a cosmopolitan species and abundant in Taiwan waters. Some of its biological information has been documented yet its population dynamics are poorly known. The purpose of this study is to assess the pelagic thresher shark stock status in the eastern Taiwan waters. The whole weights (W) of 51,748 individuals of the pelagic thresher shark landed at Nanfanao and Chengkung fish markets, eastern Taiwan from 1990 to 2004 were converted to precaudal length (PCL) based on the W–PCL relationship (W = 2.25 × 10⁻⁴ × PCL^2.533, n = 2165). The sexes combined VBGE L_t = 189.5 × (1 − e^{−0.10(t+6.47)}) was used to estimate the age for each length group. Total mortality rates (Z) obtained with length-converted catch curves ranged from 0.208 to 0.277 year⁻¹. Natural mortality rate (M) estimated from Hoenig method was 0.132 year⁻¹, and exploitation rate (E) ranged from 0.069 to 0.127 for 1990–2004. Annual abundance was estimated to range from 97,551 in 2000 to 153,331 in 2003 from virtual population analysis, and the highest fishing mortality occurred in ages 8–18 years. There were four different scenarios being simulated in this study. Scenario 1 indicated that spawning per recruit (SPR) ranged from 23.07% in 2001 to 47.71% in 1990 with a mean of 36.41% for the period of 1990–2004. The mean SPR of pelagic thresher for 1990–2004 was below the BRP of SPR = 35% in scenarios 2–4 suggesting that this stock was slightly overexploited. Therefore, to ensure sustainable utilization of this stock, reduction of fishing effort and close monitoring on A. pelagicus are needed.     

Age and growth of yellowtail snapper and queen triggerfish collected from the U.S. Virgin Islands and Puerto Rico

Opaque rings on sectioned otoliths and sectioned dorsal spines were used to age yellowtail snapper, Ocyurus chrysurus (N = 654) and queen triggerfish, Balistes vetula (N = 665), taken from U.S Virgin Islands and Puerto Rico trap and hook-and-line fisheries in 1983 and 1984. Annulus formation, validated by marginal increment analysis, occurred from March to May for yellowtail snapper and from February through March for queen triggerfish.The maximum age for yellowtail snapper was 17 years, compared with only 7 years for queen triggerfish. Mean back-calculated fork lengths (FL, mm) of yellowtail snapper aged 1, 5, 10, 15 and 17 years were 117, 287, 375, 455 and 505, respectively. Mean back-calculated lengths for queen triggerfish aged 1–7 years were 161, 229, 274, 307, 332, 356 and 378 mm FL, respectively. The von Bertalanffy growth equations for yellowtail snapper and queen triggerfish were L_t=502.5 (1−e^{−0.139(t + 0.955)}) and L_t=415(1−e^{−0.30(t + 0.600)}) respectively, where t = age in years. The length-weight relationship for yellowtail snapper was W = 0.000117FL^2.6504, where W = weight in grams and was W = 0.000101FL^2.750 for queen triggerfish. Data revealed that yellowtail snapper live longer than previously reported and grow at a rate similar to other western Atlantic lutjanids. Queen triggerfish studied were not as old as expected, probably because of fishing gear selectivity.     

Age and growth of sea perch (Helicolenus percoides) from two adjacent areas off the east coast of South Island,New Zealand

A validated ageing methodology using otolith thin sections is presented for sea perch (Helicolenus percoides) in two adjacent areas off the east coast of South Island, New Zealand. Oxytetracycline marking of two adult fish held in captivity for 1 year suggested that a single dark growth increment formed during winter, commencing May or June. The annual formation of growth increments was confirmed by the observed progression of year classes in comparable samples from three different years, and the progression of length modes in several consecutive years that matched the estimated growth curves. Otolith interpretation was difficult because of a central dense region and the presence of many fine bands within each growth increment, but the latter could be counted, and it is considered that a validated ageing procedure is presented. Von Bertalanffy growth parameters were calculated for east coast South Island (ECSI) and Chatham Rise males and females. In both areas the growth rate of males is slightly but significantly faster than for females. Growth is relatively slow throughout life. From the maximum observed ages for ECSI and Chatham Rise fish of 35 and 59 years, the respective natural mortality rates are estimated to be 0.12 and 0.07 year^?1, but the most plausible value for the species is likely to be at the lower end of this range. Some stock differentiation between the two areas is indicated, based primarily on differences in length-frequency distributions implying different patterns of year class strengths, but also on apparent differences in growth rates between areas. This supports the present management regime of separate commercial catch quotas.     

Changes in growth characteristics of the small abalone Haliotis diversicolor (Reeve, 1846) after one decade in a closed culture system: a comparison with wild populations

Small abalone Haliotis diversicolor (Reeve, 1846) is one of the smallest commercial abalone in the world. The successful application of artificial propagation and mass seed production techniques since the 1980s have resulted in the establishment of well-developed culture systems for small abalone in Taiwan. In the study reported here, we estimated the growth of a population of small abalone after a decade in a closed culture system and its growth characteristics with those of wild populations reported in previous studies. The von Bertalanffy growth equations of the shell length (L) and body weight (W) of cultured abalone were L _t  = 71.73 (1 ? e^{?0.84 (t?0.16)}) and W _t  = 47.70 (1 ? e^{?0.84 (t?0.16)})^3.180, respectively. The instantaneous rate of change for weight had an inflection point at the age of 1.54 years, indicating that cultured abalones reach their apex of body growth around this age. Compared with the wild populations, the cultured population exhibits a significantly smaller maximal shell length (L _∞) and a significantly larger growth coefficient (k). Based on our results, it appears that the artificial culture of generations of small albalone for one decade or more in a closed system could be one of the major factors causing the observed minimization of size in the cultured abalone; this may be an adaptation in which growth is traded off for the larger k.     

Yield, growth and mortality rate of the Thai river sprat, Clupeichthys aesarnensis, in Sirinthorn Reservoir, Thailand

The Thai river sprat, Clupeichthys aesarnensis Wongratana, is a clupeid with a short life span, and supports artisanal fisheries in a number of reservoirs in the Mekong Basin. The growth parameters, mortality rates and the status of the Thai river sprat in Sirinthorn Reservoir (28 800 ha), NE Thailand (15°N; 105°E), are presented. The fishery is based on lured lift‐nets, operated 7–14 days in the new moon period, September to April each year. It was shown that the von Bertalanffy growth function (VBGF) model was L_t (mm) = 78.43[1 ? exp{?0.211[t ? (?0.7996)]}] and its growth conformed to an isometric pattern. Natural mortality rate (month^?1) was 0.13 month^?1. Total mortality rates ranged from 0.69 to 1.53 month^?1 depending on the weather and the fishing season. Recruitment was continuous throughout the year but peaked in June and July. The yield per recruit model indicated that the exploitation rate of this fishery is probably too high.     

Influence of environmental factors,season and size at deployment on growth and retrieval of postlarval lion's paw scallop Nodipecten nodosus (Linnaeus, 1758) from a subtropical environment

The effect of seasonal variation of environmental factors on daily shell growth rates (DGR) of postlarval Nodipecten nodosus was studied at the southern distribution limit of the species in Santa Catarina State, Brazil. Five deployments of hatchery produced postlarvae (initial shell height 0.5 mm) in the sea-based nursery were carried out from August 2000 to September 2001, and DGR and percent retrievals were recorded. Chlorophyll-a, seston, salinity, dissolved oxygen and turbidity were measured weekly, and temperature was recorded hourly. Additionally, DGR and retrievals were compared for postlarvae maintained simultaneously in the sea- and land-based nurseries (initial shell height 0.5 mm), and also for post-larvae deployed in the sea-based nursery at different initial sizes (0.29–1.1 mm). Mean DGR was significantly lower in late winter–early spring 2000 (0.045 mm day⁻¹), intermediate in late winter–early spring 2001 (0.078 mm day⁻¹) and significantly higher in the other seasons (late spring–early summer, 0.152 mm day⁻¹; late summer–early autumn, 0.149 mm day⁻¹ and late–autumn early winter, 0.130 mm day⁻¹). Temperature was the best predictor of growth, which was least at temperatures below 20 °C. Growth rate was also minimal during a period of low salinity and high turbidity. Mean DGR was significantly higher in postlarvae deployed in the sea-based nursery than in those maintained in the land-based nursery. Loss of postlarvae in the sea-based nursery was initially higher in collectors transferred earlier to the sea (ca. 2–3 weeks post-set; shell height 0.5–0.8 mm), but percent retrievals were similar after postlarvae deployed to the sea ca. 4–5 weeks post-set (shell height 1.1 mm) were retrieved simultaneously with those deployed earlier. At retrieval, postlarvae deployed approximately 2 weeks post-set were larger than those deployed subsequently, but spat deployed 1 week post-set attained a similar size to those deployed 2 weeks post-set. A strategy to deploy postlarvae in the sea-based nursery at a size circa 0.5 mm is proposed as more advantageous than keeping them longer in land-based facilities. In southern Brazil, there is a wide window of opportunity to deploy post-larval scallops in the sea-based nursery in which growth is maximized, except when water temperatures drop below 20 °C.     

In situ growth of pearl oysters Pinctada mazatlanica (Hanley 1856) and Pteria sterna (Gould 1851) under repopulation conditions at Bahia de La Paz, Baja California Sur, Mexico

Pearl oysters Pinctada mazatlanica (Hanley 1856) and Pteria sterna (Gould 1851) were studied for an annual cycle of in situ growth from May 1992 to April 1993. Organisms generated from extensive culture were kept under repopulation conditions at Caleta El Merito. Growth measurements of shell height and length were taken monthly. Data were used to build the annual growth curve of both species, to test the temporal relationship between shell height and length, to calculate monthly and total growth rate, to follow the modal progression with the ELEFAN software, and to fit the growth curve to the Von Bertalanffy equation. Growth dimensions increased steadily during the annual cycle, from 7 to 18 months old for P. mazatlanica and from 11 to 22 months for P. sterna. No significant differences were detected between shell height and length during growth, although length seemed to grow faster. The ELEFAN program identified two modes in P. mazatlanica (Rn= 0.205) and a single one for P. sterna (Rn= 0.557). A positive correlation to the Von Bertalanffy equation was seen for both species (r²= 0.97 for both species).     

Size,growth, temperature and the natural mortality of marine fish

The natural mortality of exploited fish populations is often assumed to be a species‐specific constant independent of body size. This assumption has important implications for size‐based fish population models and for predicting the outcome of size‐dependent fisheries management measures such as mesh‐size regulations. To test the assumption, we critically review the empirical estimates of the natural mortality, M (year^?1), of marine and brackish water fish stocks and model them as a function of von Bertalanffy growth parameters, L (cm) and K (year^?1), temperature (Kelvin) and length, L (cm). Using the Arrhenius equation to describe the relationship between M and temperature, we find M to be significantly related to length, L and K, but not to temperature (R² = 0.62, P < 0.0001, n = 168). Temperature and K are significantly correlated and when K is removed from the model the temperature term becomes significant, but the resulting model explains less of the total variance (R² = 0.42, P < 0.0001, n = 168). The relationships between M, L, L, K and temperature are shown to be in general accordance with previous theoretical and empirical investigations. We conclude that natural mortality is significantly related to length and growth characteristics and recommend to use the empirical formula: ln(M) = 0.55 ? 1.61ln(L) + 1.44ln(L) + ln(K), for estimating the natural mortality of marine and brackish water fish.     

Use of stochastic models to estimate the growth of the Port Jackson shark,Heterodontus portusjacksoni,off eastern Victoria,Australia

Three stochastic models were used to describe the growth of Heterodontus portusjacksoni off eastern Victoria, Australia. The models are based on a reparametrization of the von Bertalanffy growth model to take account of length-at-age heterogeneity, and incorporate random variation of the von Bertalanffy growth coefficient (k), using three different probability distribution functions (pdfs): Weibull, gamma and log-normal. They were fitted to the lengths of 179 specimens (79 females and 100 males), and associated age estimates obtained by counting growth bands in the inner trunk dentine layer of the dorsal-fin spines. The species is relatively long-lived (maximum estimated age of 35 years for females and 28 years for males) and slow growing, but has rapid growth during the early stages of life. All the models provided similar growth parameters and length-at-age quantiles. However, Kullbac?s information mean indicated that the stochastic model assuming a log-normal distribution fitted the length-at-age data better for both females (L∞ = 1337, E(k) = 0.059, t₀ = 5.294) and males (L∞ = 1125, E(k) = 0.075, t₀ = 4.944) than the models assuming other distributions. The χ² likelihood ratio test indicated that females and males grow differently.     

Evolutionary assembly rules for fish life histories

We revisit the empirical equation of Gislason et al. (2010, Fish and Fisheries 11 :149–158) for predicting natural mortality (M, year^?1) of marine fish. We show it to be equivalent to , where L_∞ (cm) and K (year^?1) are the von Bertalanffy growth equation (VBGE) parameters, and L (cm) is fish length along the growth trajectory within the species. We then interpret K in terms of the VBGE in mass , and show that the previous equation is itself equivalent to a ?? power function rule between M and the mass at first reproduction (W_α); this new ?? power function emerges directly from the life history that maximizes Darwinian fitness in non‐growing populations. We merge this M, W_α power function with other power functions to produce general across‐species scaling rules for yearly reproductive allocation, reproductive effort and age at first reproduction in fish. We then suggest a new way to classify habitats (or lifestyles) as to the life histories they should contain, and we contrast our scheme with the widely used Winemiller–Rose fish lifestyle classification.     

The potential for aquaculture of the bearded horse mussel (Modiolus barbatus) and Noah’s Ark shell (Arca noae) in southern Croatia

To assess the potential of the bearded horse mussel (Modiolus barbatus) and Noah’s Ark shell (Arca noae) for aquaculture in southern Croatia, we analyzed their survival and growth rates under two experimental conditions—suspended culture and on-bottom culture. Furthermore, we investigated feeding on zooplankton by these two species in suspended culture conditions and compared them with previously published results of their feeding on zooplankton in the natural benthic environment. Experimental studies were conducted in Mali Ston Bay (Adriatic Sea) from December 2009 to December 2010. Differences were observed in terms of survival of tagged M. barbatus and A. noae—specimens of M. barbatus exhibited much better survival rates both in suspended culture and in on-bottom cages than did A. noae. Growth of A. noae under both culture conditions was essentially negligible, while M. barbatus grew several times faster in suspended culture than on the bottom. Values for the growth constant K and L _inf for M. barbatus in suspended culture were 0.45 year^?1 and 55.9 mm, while corresponding values for on-bottom culture were 0.09 year^?1 and 58.6 mm, respectively. Zooplankters were present in the stomachs of 86.3 % of M. barbatus and 86.4 % of A. noae. Most abundant taxa were bivalve larvae followed by tintinnids, copepods, unidentified eggs and gastropod larvae. In conclusion, this study clearly shows that M. barbatus is a promising candidate for suspended aquaculture in southern Croatia.     

Growth of the oyster Crassostrea corteziensis (Hertlein, 1951) in Sonora, Mexico

This is the first evaluation of growth and survival of spat of the Cortez oyster Crassostrea corteziensis (Hertlein) produced under controlled conditions in a coastal area in the state of Sonora, Mexico for aquaculture purposes. A suspended culture technique, used for the Pacific oyster C. gigas, was used. The Cortez oyster has an isometric shell growth during the first 13 months, reaching 71.3±1.9 mm length, 52.6±1.3 mm thickness and 25.1±0.8 mm width. Allometric growth was found between total weight and length, thickness and width (survival was 70%). The relationships between particulate organic, inorganic material, chlorophyll a and environmental parameters with growth are described. Growth rates of C. corteziensis were affected by temperature with retardation at less than 18°C. For aquaculture purposes, it is recommended that spat be sowed after winter, and oyster harvest occur at the end of autumn. According to the von Bertalanffy equation, Cortez oysters would reach the traditional exploitation size of 65 mm (mean length) at harvest. Finally, the results of this study have shown that C. corteziensis is a good candidate for aquaculture projects in this region.     

Age,growth and demographic characteristics of <Emphasis Type="Italic">Sillago flindersi</Emphasis> exploited in a multi-species trawl fishery

This study investigated variability in the growth, length, and age compositions and the rates of mortality of Flinders’ sillago Sillago flindersi exploited in a demersal trawl fishery in eastern Australia. Sampling was done over 2 years across three depth strata at two locations approximately 400 km apart. Ageing of sectioned sagittal otoliths indicated that the observed maximum age of females was 6 years and that of males 5 years, that growth was variable and that the von Bertalanffy growth parameters significantly differed according to gender and location. Females attained a greater L _∞ than males, but males displayed greater k values. The L _∞ values of both sexes and the mean length-at-age for fish aged 3–5 years were greater at the location of highest latitude. Length and age compositions differed according to depth, with smaller (<15 cm FL) and younger (<2 years) fish generally more predominant in the shallow (<30 m) strata than in the deeper (>31 m) strata. S. flindersi appear to use the shallow strata as a juvenile habitat, moving to deeper waters as they grow. This depth stratification between cohorts may reduce intraspecific competition and could potentially be used as a spatial management tool to reduce any fishing-associated impacts on juveniles. Fish between 1 and 3 years old dominated the age compositions of populations combined across all depths, with estimated total mortality ranging between 2.24 and 2.40. Fishing mortality ranged between 1.54 and 1.70 and was more than twice the derived natural mortality. Exploitation rates were approximately 0.70, indicating that the species was heavily fished.     

Experiments on the culture in the sea of the butterfish Venerupis decussata L.

Eight batches of hatchery reared V. decussata were reared to market size at two sites in England and one in Wales. The mortality rate varied between 10 and 40% per year in different populations with an average of 23% per year. The growth rates were rather similar at the three sites and it was estimated that after 3 years a population planted at 10 mm shell length would have reached about 50 mm. Calculations on the yield of market sized animals showed that at the average mortality rate it would be necessary to plant 10⁵ 10-mm spat to yield 1 tonne of V. decussata after 3 years; at a mortality rate of 40% per year it would be necessary to plant 2 × 10⁵ 10-mm spat to achieve the same yield. Growth started in late April and ceased by mid-October; the condition factor was at its highest in June and July. Samples planted at different densities suggested that V. decussata could be cultivated at up to 500/m².     

Estimation of natural mortality using statistical analysis of fisheries catch-at-age data

This study utilized the fisheries catch-at-age data combined with the auxiliary information of effort data to calculate natural mortality rate (M), and the other population parameters such as catchability and recruitment. The method used in the paper was the standard statistical catch-at-age (SCA) model. Monte Carlo simulation data were used to test this method under four fishery scenarios (good contrast, one-way trip, recovery and status quo). This study showed that the quality of the annual recruitment greatly affected the estimated Ms. When the white noises (CVs) of recruitments reached 10% the estimated Ms were biased, even when the CVs of catch-at-age and effort data were low. CVs in catch-at-age and effort data were also important factors to affect the estimated M, and the results of the simulation analysis of three CV scenarios (CV in both of the catch-at-age and effort with the same level, CV in the catch-at-age (CV_C) was half of CV in the effort (CV_E) and CV_E was half of CV_C) indicated that CV_C made more effects than CV_E on the quality of the estimated M. Among the four fisheries, the one-way trip fishery outperformed the other three, since it obtained the lowest relative estimate error (REE) values of the estimated M for all the scenarios, while the recovery fishery had the worst performance. When M varied through ages, von-Bertalanffy growth function (VBGF) was introduced into the SCA model to estimate the age-dependent M, and the one-way trip and good contrast fisheries obtained more viable estimated Ms than the recovery and status quo fisheries. The method was also applied to the published data of North Atlantic albacore (Thunnus alalunga), and the estimated M was 0.186 year⁻¹, which was lower than previously assumed (0.3 year⁻¹) and may be viable in view of the high fishing effort imposed on the species.