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Restricted Tradability of Harvesting Rights and Unequal Exposure to Binding Resource Limits:��-Evidence from a Multispecies Fishery in Japan

Takefumi Fujimoto

Specially Appointed Assistant Professor

University of Tsukuba

(Co-authors: Keita Abe, Ryutaro, Kamiyama, Yutaro Sakai)

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Topic: Rights-Based Management (RBM) in fishery

・RBM assigns private rights to harvest resources & emit pollutants

⇒ Private decisions by economic agents align with social benefits

⇒ Rebuild depleted stock & reduce emissions

Area: Individual Quotas (IQ) in Sea of Japan & East China Sea

⇒Large-/medium-scaled purse seiners introduced IQs for two species:

・Horse mackerel (HM; マアジ)

・Chub/blue mackerel (CM; サバ)

*Fishers can harvest HM & CM

under allocated quota limits

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Individual Quota (IQ) in fishery

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Two problems in this IQ scheme

(1) Allocated quotas are in shortage ONLY for one species (CM)

Tight quota limits for one species constrain catch of the other

(2) Quota transfers are allowed only without monetary transactions

Receiving quotas from others is difficult without monetary incentives

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Quota-Unconstrained species

(HM)

Quota-Constrained species

(CM)

caught together with CM

Violate IQ

tight quota limits

⇒Cannot catch HM any more

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Purpose to show:

Constraining effects of tight quota limits are different by:

(1) Whether fishing firms have multiple operational units (fleets)

⇒ Can reallocate quotas internally within firms

(2) Whether fishing firms can access alternative operating areas

⇒ Can avoid pressure from tight quota by operating outside IQ area

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(1) Internal quota reallocation within firm

(2) Access to alternative operating areas

Inside IQ area

Outside IQ area

(internal transfer)

(switch operation)

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Relevance for Environmental Economics

This study departs from the traditional view on the trading of harvesting/emission rights in RBM

Traditional view:

Tradability of rights involves trade-off: efficiency vs equity

⇒ Market trading of rights is often restricted to ensure equity

This study:

Restricting market trading of rights may strengthen inequality among harvesters

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  1. Conceptual Framework
  2. Background Information

3. Estimation Methodology

4. Analytical Results

5. Conclusion

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Conceptual Framework

Purpose:

To analyze how fisher’s heterogeneities

・multiple operational units within same firm

・access to alternative operating environments

affect profits when quota markets do not work

Assumptions:

・Static model within single fishing period

・No uncertainty

・Fisher is assumed to be a price taker

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Structure of joint harvesting in this study

School of HM moves below that of CM

・CM can be caught solely

・HM must be caught together with CM

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CM

HM

CM can be caught solely

Two species are caught

together when catching HM

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Conceptual Framework

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joint catch

target catch

non-target catch (bycatch, 混獲)

 

Tight quota limit

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Total catch≠Target catch

Total catch=Target catch

 

 

Target catch

Non-target catch

 

bycatch

 

Revenue

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Cost

 

 

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Revenue

Cost

Revenue (linear)

Cost (quadratic)

Profit

(negatively quadratic)

Profit (difference)

 

 

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Iso-profit curves

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Analogue of consumer theory:

“slope of indifference curve = price ratio”

 

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Slutsky-like decomposition: substitution effects

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Slutsky-like decomposition: substitution effects

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Slutsky-like decomposition: substitution effects

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Slutsky-like decomposition: income effects

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substitution effect

income effect

Total

ambiguous

 

 

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Internal quota transfer within same firm

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Internal quota reallocation within firm

(internal transfer)

 

 

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Internal quota transfer within same firm

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Internal quota reallocation within same firm

internal transfer

 

 

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Alternative operating environments

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opportunity costs

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Summary

Two hypotheses follow from conceptual framework

Hypothesis 1:

Constraining effects of binding quotas are greater for fishers with single operational unit than for fishers with multiple ones

Hypothesis 2:

Constraining effects of binding quotas are greater for fishers without access to alternative fishing grounds than those without

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  1. Conceptual Framework
  2. Background Information

3. Estimation Methodology

4. Analytical Results

5. Conclusion

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Study site

In 2023, large-/medium-scale purse seiners (大中型まき網) in Sea of Japan & East China Sea introduced IQs for two main species

・horse mackerel (HM; マアジ)

・chub/blue mackerel (CM; サバ)

In this purse seine fishery,

a fleet (船団) is a single operational unit:

・a light vessel attracts fish

・a net vessel captures fish

・a transport vessel carries fish to port

⇒Quotas are allocated at the fleet level

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Sea of Japan &

East China Sea

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Allocation of initial IQs for two species

Management years for two species

・HM: January-December

・CM: July-June

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80% of TAC:

Allocated proportionally to

past catch amounts

All Total Allowable Catch (TAC) for each species

in Sea of Japan/East China Sea

20% of TAC:

Equally allocated over fishing fleets

Allocated to individual fishing fleets

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*TAC for CM was equally allocated as emergency measure from January 2023 up to formal start of its IQ (July 2023)

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Abundance of CM in Sea of Japan/East China Sea

Average bycatch rate of CM in peak harvest season of HM

CM is often caught together

when catching HM since 2023

⇒ CM became abundant after IQ

⇒ CM quotas became severely

limited relative to HM quotas

(To avoid confusion…)

CM: Quota-Constrained species

HM: other main species

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IQ was introduced

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Restricted catch of HM

・Monthly average catch of HM (2022/23/24)

�・Drop in peak season of HM

(April-May) after IQ (2023/24)

⇒Catch of HM was limited by

tight quota limits for CM

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peak season (HM)

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Two coping strategies for quota limits

  1. Fishers can transfer quotas within a management year

・Monetary transactions are NOT officially allowed in quota transfer

⇒ Quota transfers to other fishers yield no economic incentives

⇒ Fishing firms with multiple fleets avoid quota limits by reallocating quotas internally within firm

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Fishing firm with multiple fleets

(internal transfer)

Fishing firm with single fleet

*transferred quotas do not carry over to next year

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Patterns of internal quota transfer

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Two coping strategies for quota limits

(2) Access to alternative operating environments

・Some fleets are licensed to operate in Pacific Ocean

*IQ area: Sea of Japan & East China Sea

・sardine (マイワシ) is a main species

in Pacific Ocean

⇒ Access to Pacific Ocean can reduce

the dependence on IQ area

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Sea of Japan &

East China Sea

Pacific Ocean

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Proportion of fleets which operated in Pacific Ocean

Some fleets shifted operations to Pacific Ocean after IQ started

・Operating proportions in Pacific Ocean continue to fall until 2022

・Operating proportion rose suddenly in 2023 (after IQ started)

⇒These fleets tried to avoid pressure

from tight quota limits by operating

in Pacific Ocean

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IQ was introduced

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  1. Conceptual Framework
  2. Background Information

3. Estimation Methodology

4. Analytical Results

5. Conclusion

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Analytical dataset

Goal:

Constraining effects of tight quota limits are different by:

(1) Whether fishing firms have multiple fleets

(2) Whether fleets are licensed to operate in Pacific Ocean

Data:

Three types of panel data at fleet level during January 2023 – December 2024 (two years after IQ)

・Daily catches of all species

・Daily records of quota allocations & quota transfers

・Monthly revenues from all species & costs on heavy oil

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Estimation Methodology

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Estimation Methodology

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Estimation Methodology

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First IQ year

Average initial IQ

Sum of additional IQ

Frequency of additional IQ

HM

1417.7 tons (76%)

446.1 tons (24%)

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CM

2537.5 tons (70%)

1149 tons (30%)

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Mechanisms & Welfare Consequences

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Using same empirical framework, we further clarify mechanism & welfare consequences:

① Mechanism

② Main analysis

③ Welfare consequences

 

 

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  1. Conceptual Framework
  2. Background Information

3. Estimation Methodology

4. Analytical Results

5. Conclusion

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Estimation results: ① Fishing selectivity

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-0.01

(0.12)

-0.02

(0.02)

-0.00

(0.11)

0.00

(0.02)

0.49

0.32

(Standard errors in parenthesis; bootstrapped in 200 times)

(p-values in joint significance tests)

 

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Estimation results: ② HM catch

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-0.17***

(0.05)

-0.10***

(0.03)

0.07***

(0.02)

0.07***

(0.03)

0.00***

0.11

(Standard errors in parenthesis; bootstrapped in 200 times)

(p-values in joint significance tests)

 

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Estimation results: ③ Monthly profit

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Monthly profit

-$62,532*

(37,030)

-$23,620**

(12,028)

$27,149

(18,102)

$27,735*

(14,400)

0.09*

0.74

(Heteroskedasticity-robust standard errors in parenthesis)

(p-values in joint significance tests)

 

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  1. Conceptual Framework
  2. Background Information

3. Estimation Methodology

4. Analytical Results

5. Conclusion

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Conclusion

・In this context, fishing selectively between HM & CM does not work

⇒ Fishers try to avoid pressure from tight quota limits through other operational options (if they have)

・Tight quota limits for one species (CM) reduce the catch of the other species (HM) & profits

・These negative effects are smaller if

① fleets belong to firms owning multiple fleets

⇒ internal quota reallocation within firm

② fleets are licensed to operate in Pacific Ocean

⇒ access to alternative operating areas

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Implications for environmental economics

Problem:

Market-based reallocation mechanisms are entirely excluded in the trading of harvesting rights

∵Monetary transactions are not officially allowed in quota transfer

⇒ Quota transfers from other harvesters cannot be expected

Harvesters must rely solely on their own operational options:

① internal quota reallocation mechanisms

② access to alternative operating environments

⇒Harvesters lacking these options are fully exposed to tight quota limits

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Traditionally, tradability of rights involves trade-off: efficiency vs equity

・In trading markets, harvesting rights shift from small to large harvesters

・Pollution concentrates in poor & minority regions

⇒ Market trading of rights is often restricted to ensure equity

But our findings suggest that a uniform ban on market trading may reinforce inequality among harvesters & polluters

Policymakers should carefully restrict the tradability of rights in markets

Ex) imposing caps on annual quota holdings (rather than outright restriction on market trading)

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Implications for environmental economics

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Different IQ management years for two species

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January 2023

July 2023

January 2024

July 2024

Management year for CM (Jan-Dec)

Management year for CM (July-June)

Peak season (HM)

April-May

End

IQ for CM is in shortage at the end

⇒Tight quota limits for CM discourages fishers from catching HM

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Usage rates of IQ

Histograms of usage rates of IQ for

  1. horse mackerel
  2. chub/blue mackerel (formal)

in 1st management year

(including additional IQ)

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Usage rates of IQ

Usage rates of IQ for chub/blue mackerel tend to be close to 100% in many fleets

⇒ IQ for chub/blue mackerel is very tight

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Usage rates of IQ

Usage rates of IQ for horse mackerel are below 70% in most fleets

⇒Large waste of IQ for horse mackerel

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Allocation of initial IQs for two species

IQ for horse mackerel (January-December)

・20% of TAC: equally allocated over fishing fleets

・80% of TAC: allocated proportionally to 3 years’ catch amounts

IQ for chub/blue mackerel (July-June)

・20% of TAC: equally allocated over fishing fleets

・80% of TAC: allocated proportionally to 5 years’ catch amounts

*Emergently, small IQs were uniformly allocated to each fleet during January 2023-June 2023 (ex 300 tons in East China Sea)

⇒ Starting periods of IQs for two species coincide overall (Jan 2023)

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Every year, TAC in East China Sea is allocated to JPSA

January 2022

July 2022

January 2023

July 2023

January 2024

July 2024

Horse mackerel

57,600 tons

Horse mackerel

56,700 tons

Mackerel

80,370 tons

Mackerel

82,385 tons

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In January 2023, JPSA voluntarily introduced IQ for horse mackerel & mackerel

⇒JPSA allocates TAC to its members as IQ

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TAC in East China Sea is allocated to JPSA every year

January 2022

July 2022

January 2023

July 2023

January 2024

July 2024

IQ was introduced in January 2023

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Surge in bycatch rate of chub/blue mackerel

Monthly average catch of chub/blue mackerel (2022/23/24)

Catch of chub/blue mackerel

in 2023 & 2024 (after IQ) is

higher than in 2022 (before IQ)

⇒ Resources of chub/blue

mackerel became abundant

when IQ was introduced

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Bycatch rate

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Shadow value of quota for CBM

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Topic: Rights-based management (RBM) in fishery

・Assign private rights to harvest resources & emit pollutants

・Market trading Harvesting/emission rights enhances social welfare

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Individual Quota (IQ) in fishery

Cap-and-Trade in greenhouse gas

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Topic: Rights-based management in fishery

・Assign private rights to harvest resources & emit pollutants

・Economic agents internalize social costs of harvesting/polluting

Market trading of harvesting/emission rights enhances social welfare

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Individual Quota (IQ) in fishery

Want more

Sufficient

Traded

Caught a lot

Got cash