Pelagic Fishery Research Program (PFRP)
Joint Institute for Marine and Atmospheric Research
School of Ocean and Earth Science and Technology
University of Hawaii
June 1996
2. Establish a meaningful time series of pelagic fish availability and fishing pressure in Hawaii. Compute time series (1948-1992) of catch per unit effort (CPUE) and standardized fishing effort, at monthly resolution, for yellowfin and bigeye tuna
s, blue and striped marlins, mahimahi, and ono (wahoo).
3. Develop analytical models for variation in pelagic fish availability (CPUE) in Hawaii. Analyze the CPUE time series in relation to potential influences including total local fishing effort and effort by specific fishery components.
Frequency distributions of CPDF for any one species are sometimes highly skewed and include substantial frequencies of zero CPDF. A modified negative binomial distribution fit to the CPDF provided mean catch rates that differed very little from simple a
rithmetic means. Other analyses showed that mean CPDF, excluding days which caught no species at all, was highly predictive of mean CPDF including zero catch days (Fig. 2). Thus, lack of data on fishing days with no catch throughout much of the time ser
ies does not invalidate the use of CPDF as an index of fishery performance.
The HDAR data were appended with individual licensee identifiers to enable us to track fishermen individually or as groups through time. Cluster analysis was used to classify fishermen by gear use and species composition of catch. Individual long-term f
ishermen with consistent reporting habits were also identified for contact during a survey of operational characteristics of different fishery sectors.
Comparative information on handline and troll catch was available for only three years (1980, 1981, and 1988). These years showed that under-reporting by handline and troll fishermen was not too severe with reported catches to HDAR representing about 80%
of actual total catch. Only a few years of comparative data for handline and troll fisheries exists making any quantification of trends in under-reporting difficult. Since the possible comparisons did show that reported catches were not grossly inaccura
te, we focused our under-reporting study on the longline sector of Hawaii's pelagic fishery.
A set of raising factors were estimated to correct for under-reporting by longliners to HDAR. Total catches of six species were estimated from HDAR-independent data and compared with existing HDAR catch reports to determine suggested raising factors (Tabl
e 1). Individual species comparisons were not available for all years, forcing us to base estimates on a single species or on a species grouping. From 1984 to 1986 no comparative data were available and suggested raising factors were interpolated for ea
ch species. Bigeye tuna and yellowfin tuna raising factors were interpolated from 1984 to 1987.
The simulation models were run at monthly time steps for 30 years. The models include stochastic processes in migration rates, fishing mortality, and catchability. Each scenario was run 1000 times. Total catches of yellowfin tuna from 1962 to 1994 were
estimated for three fishing gear types: longline, troll, and handline. Results indicated that total catches by Hawaii's fishery sectors have low probabilities of affecting local CPUE for yellowfin tuna. Further analysis is focusing on the same data, b
ut at finer spatial and temporal scales.
He, X., C. H. Boggs, and K. A. Bigelow, 1996. Cluster analysis of longline sets and fishing strategies within the Hawaii-based Fishery. Submitted to the journal Fisheries Research.
He, X., and C. H. Boggs, 1996. Time Series Analysis on Hawaii's Tuna Fisheries: Do Local Catches Affect Local Abundance? Second FAO Expert Consultation on Interactions of Pacific Tuna Fisheries. Shimizu, Japan. Paper No: 5-24 (In press).
He, X., and C. H. Boggs, 1996. Estimating Fisheries Impacts Using Commercial Fisheries Data: Simulation Models and Time Series Analysis of Hawaii's Yellowfin Tuna Fisheries. For the Proceedings of the Second World Fisheries Congress July 28-August 1, 19
96, Brisbane, Australia.
Table 1.--Suggested raising factors for HDAR longline catch data, by year and taxa, compared with raising factors derived from previous NMFS estimates of longline catch. When no ratio was calculated for the raising factor, raising factors based on other taxa or combined taxa are suggested, as indicated by an asterisk. For species not listed, the factor for combined taxa is recommended. In some years raising factors were derived by interpolation between years as indicated by parentheses.
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Year Bigeye Yellowfin Billfish Mahimahi Wahoo Combined taxa
This study NMFS
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1970-78 1.19 1.19* 1.19* 1.19* 1.19* 1.19* 1.00
1979 1.72* 1.72* 1.68 2.41 1.76 1.72 2.76
1980 7.47* 7.47* 8.11 5.20 2.74 7.47 6.90
1981 11.46* 11.46* 11.85 9.81 4.60 11.46 10.50
1982 12.50 20.29 22.90 19.29 8.83 14.35 11.38
1983 5.28 5.46 8.46 6.37 6.02 5.81 5.68
1984 (6.17) (6.27) (7.84) (5.97) (5.74) (5.99) 7.92
1985 (7.10) (7.08) (7.22) (5.57) (5.47) (6.17) 9.00
1986 (7.96) (7.88) 6.60 5.17 5.19 6.35 5.28
1987 8.85 8.69 14.83 7.12 6.58 10.09 11.03
1988 9.42 5.94 7.22 6.21 7.36 9.04 8.86
1989 2.25 1.75 2.05 2.06 2.13 2.05 2.19
1990 1.26 1.11 1.31 1.14 1.48 1.25 1.38
1991 1.25 1.06 1.09 1.63 1.40 1.15 1.31
1992 1.34 1.04 1.00 1.62 1.24 1.10 1.41
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