BAYS TUNAS  

1 ATLANTIC BIGEYE TUNA

The SCRS completed a stock assessment of Atlantic bigeye tuna in October 1999. The assessment utilized catch and effort information submitted by ICCAT member and non-member nations. This section provides a summary interpretation of the stock assessment results.

The 1999 SCRS report/stock assessment for bigeye tuna indicates (as have previous SCRS reports) that the catch of undersized fish remains a major problem in the Atlantic bigeye tuna fishery. The share of bigeye tuna less than the ICCAT minimum size (3.2 kg) is approximately 55 percent, by number, of all bigeye tuna harvested. This number has stabilized since with the time/area closure for purse seining in the eastern tropical Atlantic area (detailed in Section 4.2.3), but still remains a concern (SCRS 1999b)

In 1997, SCRS recommended a reduction of overall catch of bigeye tuna to at least the 1992 level (approximately 85,000 mt in the 1997 estimate, but revised to 97,000 mt in 1999). The 1998 catch was 95,000 mt, slightly less than 1992 levels, but still higher than the sustainable catch level. The results of the latest stock assessment indicate an MSY between 79,000 and 94,000 mt. One important component of the 1999 bigeye tuna assessment was the incorporation of revised data from previous years. This resulted in the addition of some 20,000 mt of previously unreported catch. SCRS recommended a reduction of catch to approximately 80,000 mt to reduce the probability of further decline of the stock, although an additional reduction of catch would be required to rebuild the stock to MSY levels. The SCRS was unable to provide recovery projections in 1999 due to lack of data.

1.1 Life History/Species Biology Information

Compared to other tuna and tuna-like species, less research has been conducted on bigeye tuna. The lack of reasonable estimates of some biological parameters considerably hinders the stock assessment process. The Bigeye Tuna Year Program, which calls for extensive research on bigeye tuna, was adopted in 1996 and began its operation in 1999 as funds became available. Additional information on the life history of Atlantic bigeye tuna can be found in the HMS FMP (Sections 2.2.1 and 6.3.1.2).

1.2 Most Recent Stock Assessment Data

ICCAT currently manages Atlantic bigeye tuna based on an Atlantic-wide single stock hypothesis. However, the possibility of other scenarios, including north and south stocks, does exist, and should not be disregarded (SCRS 1999b)

Table 1 Summary Table for Atlantic Bigeye Tuna

Age/size at Maturity Age 3/~100 cm curved fork length
Spawning Sites Tropical waters
Current Relative Biomass Level*

Minimum Stock Size Threshold

SSB98/SSBMSY = 0.57 - 0.63

0.6BMSY (age 2+)

Current Relative Fishing Mortality Rate*

F1998/FMSY

Maximum Fishing Mortality Threshold

F98/FMSY = 1.50 - 1.82



FMSY

Outlook Overfished; overfishing is occurring
Management Measures in Place Minimum sizes; time/area closures for fish aggregating device (FAD) fishing; limit on number of vessels > 24 m length overall (LOA) (not applicable to countries catching less than 2000 mt/year); catch and vessel limit for Chinese Taipei. No specific rebuilding program is in place.

*B/BMSY and F/FMSY ranges are ranges of estimates from different model formulations rather than confidence intervals around an estimate

2 ATLANTIC YELLOWFIN TUNA

The SCRS did not conduct a new stock assessment for Atlantic yellowfin tuna in 1999. The most recent stock assessment was conducted in 1998 and a summary of the status of Atlantic yellowfin tuna can be found in the HMS FMP (Section 2.2.1). The next assessment is scheduled for July 2000.

2.1 Life History/Species Biology Information

No new life history information is available regarding Atlantic yellowfin tuna, although research on the life history of yellowfin and other Atlantic tunas is currently being conducted and/or funded by NMFS. The HMS FMP (Sections 2.2.1 and 6.3.1.5) includes summary information on the life history of yellowfin tuna.

2.2 Most Recent Stock Assessment Data

Based on migration patterns, as well as other information (e.g., time-area size frequency distributions and locations of fishing ground), ICCAT currently manages Atlantic yellowfin tuna based on an Atlantic-wide single stock hypothesis.


Table 2 Summary Table for Atlantic Yellowfin Tuna

Age/size at Maturity Age 3/~110 cm curved fork length
Spawning Sites Tropical waters
Current Relative Biomass Level

Minimum Stock Size Threshold

unknown

0.5BMSY (age 2+)

Current Relative Fishing Mortality Rate

F1997/FMSY

Maximum Fishing Mortality Threshold

F97/FMSY = 0.97-1.35



FMSY

Outlook Stock not overfished, overfishing may be occurring
Management Measures in Place Minimum sizes; ICCAT recommendation for effective fishing effort not to exceed 1992 levels; recreational retention limit in the United States.

3 NORTH ATLANTIC ALBACORE TUNA

The SCRS did not conduct a new stock assessment for Atlantic (northern, southern, or Mediterranean) albacore tuna in 1999. The latest stock assessment was conducted in 1998. The HMS FMP includes a summary of the status of the stock of northern Atlantic albacore tuna (Section 2.2.1). The next assessment for both North Atlantic and South Atlantic albacore tuna is scheduled for October 2000.

3.1 Life History/Species Biology Information

No new life history information is available regarding Atlantic albacore tuna. Please refer to the HMS FMP (Sections 2.2.1 and 6.3.1.4) for more information on the life history of albacore tuna.


3.2 Most Recent Stock Assessment Data

On the basis of the available biological information, the existence of three stocks of albacore tuna is assumed for assessment and management purposes; northern and southern Atlantic stocks (separated at 5 N) and a Mediterranean stock. The United States primarily fishes on the north Atlantic stock/management unit, with very minor catches (~ 1 mt) of south Atlantic albacore.


Table 3 Summary Table for the North Atlantic Albacore Tuna

Age/size at Maturity Age 5/~90 cm curved fork length
Spawning Sites Subtropical western waters of the Northern Hemisphere
Current Relative Biomass Level





Minimum Stock Size Threshold

B97/BMSY = 0.47 (0.34 - 0.63)

B90-94/B75-80 = 0.72



0.7BMSY

Current Relative Fishing Mortality Rate

F1997/FMSY





Maximum Fishing Mortality Threshold

F97/FMSY = 1.39 (uncertain)

F97/FMAX = 0.91

F97/F0.1 = 1.60



FMSY

Outlook Overfished; overfishing is occurring
Management Measures in Place Limit number of vessels to average number 1993-1995


4 WEST ATLANTIC SKIPJACK TUNA

The characteristics of Atlantic skipjack tuna stocks and fisheries make it extremely difficult to conduct stock assessments using current models. Continuous recruitment occurring throughout the year, but heterogeneous in time and area, makes it impossible to identify and monitor individual cohorts. Apparent variable growth between areas makes it difficult to interpret size distributions and their conversion to ages. For these reasons, SCRS did not conduct a stock assessment for Atlantic (west or east) skipjack tuna in 1999, although some estimates were made (SCRS 1999b).

2.3.4.1 Life History/Species Biology Information

No new life history information is available regarding Atlantic skipjack tuna. Please refer to the HMS FMP (Sections 2.2.1 and 6.3.1.4) for more information on the life history of skipjack tuna.

2.3.4.2 Most Recent Stock Assessment Data

The stock structure of Atlantic skipjack tuna is not well known, and two management units (east and west) have been established due to the development of fisheries on both sides of the Atlantic and the lack of transatlantic recoveries of tagged skipjack tuna. U.S. vessels fish on the west Atlantic stock/management unit.

Table 4 Summary Table for West Atlantic Skipjack Tuna

Age/size at Maturity Age 1 to 2/~50 cm curved fork length
Spawning Sites Opportunistically in tropical and subtropical waters
Current Relative Biomass Level

Minimum Stock Size Threshold

unknown

unknown

Current Relative Fishing Mortality Rate

F1998/FMSY

Maximum Fishing Mortality Threshold

unknown


FMSY

Outlook unknown

Source :

2000 Stock Assessment and Fishery Evaluation for Atlantic Highly Migratory Species

U.S. Department of Commerce
National Oceanic and Atmospheric Administration
National Marine Fisheries Service
Office of Sustainable Fisheries
Highly Migratory Species Management Division
1315 East-West Highway
Silver Spring, MD 20910

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