Abstract

Sixteen marine fish species (populations) exploited by Chinese fisheries were assessed, using published time series of catch and the CMSY and BSM methods. Given the catch times series as inputs, some ancillary information and reasonable constraints, carrying capacity, maximum sustainable yield, and likely time series of biomass and exploitation rate were estimated. The results show that one (7%) of the assessed species was severely depleted, four species (27%) were fully/overfished, six (40%) were outside of safe biological limits, one species (7%) was recovering and three species (20%) were in a healthy state at the end year of their assessment. However, one species, Pacific sardine (Sardinops sagax), could not be assessed using CMSY, as the exceedingly large fluctuations of its biomass were mainly environmentally driven. These results correspond with previous knowledge on the status of fish populations along the coast of China, where overfishing is rampant. Based on these assessments, some of the benefits that would result from a reduction of the excessive fishing effort are outlined.

Highlights

  • IntroductionIt is widely agreed that China’s domestic fisheries resources are overexploited (Shen and Heino, 2014)

  • China is the country with the world’s largest marine fisheries catch (FAO, 2018)

  • 16 fish populations were analyzed by CMSY method, with 13 assessed using the BSM methods, as CPUE/biomass data were available for them

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Summary

Introduction

It is widely agreed that China’s domestic fisheries resources are overexploited (Shen and Heino, 2014). It seems that overfishing has gradually changed the structure and function of marine ecosystems of China’s coastal seas (Zhai and Pauly, 2020) and that the state of its domestic resources is the main reason for its current emphasis on distant-water fishing (Mallory, 2013). Its most powerful regulations are the “double control” system and summer fishing moratoria (Shen and Heino, 2014) The former are regulations of both the total number of marine engine-powered fishing vessels and their total engine power; the latter have been implemented since 1995 and extended from 3 to 4 months and more in many areas (Ministry of Agriculture and Rural Affairs of the People’s Republic of China [MARA], 2018). Some other regulations and programs are being implemented including vessel buyback, alternative employment opportunities for fishers (Song, 2007) and a 10 year fishing ban in the Yangtze River Basin (Ministry of Agriculture and Rural Affairs of the People’s Republic of China [MARA], 2019)

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