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Sustainable Development and Subsidies in the Fisheries Sector A Case in Japan

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Title: Sustainable Development and Subsidies in the Fisheries Sector A Case in Japan


1
Sustainable Development and Subsidies in the
Fisheries Sector- A Case in Japan -
  • Nobuyuki Yagi
  • Fisheries Agency

2
Objectives of this presentation are
  • To Describe the Current Status of Fishery
    Subsidies in Japan.
  • To Examine their Implications for the Fishing
    Capacity and Fishery Production in Japan.
  • Discussion and Conclusion

3
OECD estimation of government financial transfers
to marine capture fisheries in 1998
4
Declining Fishing Capacity in Japan
5
Declining Domestic Fishery Production in Japan
6
Increasing Imported Products
(unit in billion yens)
Source Japans trade statistics.
7
Tighter regulations in pelagic and offshore
fisheries have contributed to the production
decline. (unit in million tons)
8
Fishery Management Schemes In Japan
  • Umbrella measures Vessel registration and
    licensing systems
  • Coastal Fisheries Traditional Right Based
    Management
  • Offshore Fisheries (EEZ) TAC and TAE
  • Pelagic Fisheries International Regulations

9
Use of Subsidies (JPY 291 Billion in 2002)
10
Use of Infrastructure Subsidy Safety of Coastal
Villages
11
Some points of consideration
  • Long coastal line in Japan (The length of
    Japanese coastal lines are longer than that of
    mainland USA).
  • The number of coastal communities is relatively
    high in Japan if compared with other developed
    countries.
  • Japans report includes infrastructure subsidy
    while some others do not (Japan is in a unique
    situation that fishery resource management
    authority also handles coastal infrastructure
    budgets.)

12
Use of Infrastructure Subsidy Improvement of
Coastal Life
13
OECD estimation of government financial transfers
to marine capture fisheries in 1998 (with
Japanese infrastructure information incorporated)
14
Findings
  • No obvious relationship was observed between the
    amount of subsidy and fishing capacity. (Fishing
    capacity is controlled under fishery management
    schemes in the case of Japan.)
  • Fishery production would have been more directly
    affected by resource management and market
    conditions, rather than the amount of subsidies.
  • The use of the subsidies, rather than their total
    amount, would be a key factor for further
    assessments on the effects caused by subsidies.

15
Conclusions
  • Policy filters (information on capacity control
    and resource management) are necessary to assess
    the impacts of subsidies.
  • Standardized rules for the coverage of subsidies
    (in particular infrastructure subsidies) would be
    critical for international comparisons.
  • Fair improvement of disciplines on fishery
    subsidy for the purpose of solving the problem on
    over-capacity and IUU fishing is important, and
    Japan is committed to contribute to the process
    of WTO so that a fair conclusion could be
    achieved.
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