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Sharing a Fish Stock When Distribution and Harvest Costs are Density Dependent

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Abstract

We studied cooperative and competitive solutions for managing a trans-boundary fish stock that has a stock-size dependent distribution and harvesting costs, using Norwegian spring-spawning (NSS) herring (Clupea harengus) as a case study. This is among the first studies to investigate the effect of a dynamic distribution in a partition function game framework, i.e., including externalities. The special feature of NSS herring is that it comes under the sole ownership of Norway when the stock size is sufficiently low. The three players in our game are differentiated by stock ownership, cost per unit effort and stock elasticity of harvest. We find that cost asymmetry improves the likelihood of forming a stable grand coalition as harvesting load can be assigned to each fishing zone according to a player’s relative cost level and the density of fish. A dynamic distribution increases the bargaining power of Norway because of her ability to control both the total stock and the stock shares in different zones, especially during the stock transition years. However, the bargaining power of Norway may disappear if her cost of harvesting exceeds that of the other players. This loss of bargaining power can take on two forms: first, a dynamic distribution may encourage a minor player to free ride because Norway, needing a coalition partner to improve her cost-effectiveness, would be less inclined to retaliate as retaliation hurts her ally as much as the free-rider; second, in a stable grand coalition, Norway is not guaranteed to receive an allocation of benefit shares in proportion to (not to say in excess of) her stock ownership. At the current stock condition, the strategy where Norway reduces stock abundance below the level where the stock becomes non-migratory is found attractive only if the discounting rate is sufficiently high.

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Notes

  1. Shares of the herring quotas allocated to Norway, EU, Faroes, Island and Russia are 61, 6, 5, 15, and 13 %, respectively.

  2. We allow fishermen to fish until the last fish of the fishable stock is taken. In Steinshamn’s model (2011), fishermen stop fishing when the first age class in the fishable stock becomes exhausted, even if other age classes are still present.

  3. The fishable stock abundance, \(N_{j,t}^{tot}\), is the total stock abundance summing over all age classes with positive selectivity, i.e., \(s_i>0\).

  4. This treatment is different from Steinshamn (2011) where he assumed \(\tau _{j,t}^e=\min _{i}(\tau _{i,j,t})\); i.e., the seasonal fishing length is determined by the age class that is exhausted first.

  5. This classic definition has been challenged for being ‘myopic’ (de Zeeuw 2008), because it assumes that the rest of the coalition stays intact after one player deviates. Solving far-sighted equilibrium requires a different set-up, e.g., in a repeated game. For our one-shot game, the classic definition of the stability still suits the best.

  6. We set \(c_1=2\), but its exact value is not important, the value is calibrated to a level under which fishing is generally profitable.

  7. The boundary where fishing ceases under this circumstance is not drawn in the figure.

  8. This would not be possible when \(c_2/c_1>1\), under which Norway becomes a dominant exploiter (see Example b in Table 2 for a proof).

  9. The total biomass during the transition years can sometimes go below \(B_{low}\), the low biomass threshold defined in Eq. 1.

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Correspondence to Xiaozi Liu.

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We would like to thank Mikko Heino, Stein Ivar Steinshamn, Rögnvaldur Hannesson, and Sturla F. Kvamsdal for their input and comments and Vivienne B. Knowles and Leslie Tse for language editing. We wish to thank all three anonymous referees for their constructive comments. Liu acknowledges the financial support from the Nordic network on ‘Climate impacts on fish, fishery industry and management in the Nordic seas’. Lindroos acknowledges funding from Academy of Finland AKVA programme’s project ‘Economics of Aquatic Foodwebs’.

Appendix

Appendix

See Tables 4, 5 and 6.

Table 4 Age-specific parameters
Table 5 Notational summary
Table 6 Age-unspecific parameters

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Liu, X., Lindroos, M. & Sandal, L. Sharing a Fish Stock When Distribution and Harvest Costs are Density Dependent. Environ Resource Econ 63, 665–686 (2016). https://doi.org/10.1007/s10640-014-9858-9

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