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Environmental policy’s new role in the
Brazilian Amazon
Jan Börner (UniBonn/CIFOR)
Jorge Hargrave (IPEA)
Krisztina Kis-Katos (Freiburg University)
Konstantin König (ICRAF)
Monique Sacardo Ferreira (IPEA)
Background
• Deforestation rates
peaked in 2004
• Command-and-
Control policy
considered largely
ineffective
• Broad changes in
governance system in
2004/5 (PPCdAM)
• Since then reductions
by over two thirds
0
5000
10000
15000
20000
25000
30000
2004200520062007 2008200920102011
years
Deforestation(sq.km) 0
1000
2000
3000
4000
5000
6000
7000
8000
9000
Numberoffines
Background
• Shift from large to smaller scale deforestation:
result of enforcement strategy (Rosa et al.
2012) or structural change (Pacheco 2011)?
Rosa et al. 2011
Research questions
1. Districts with high fine intensity were focus of
many complementary measures (e.g.
embargoes, exclusion from credit, etc.). What
is the deterrence effect of an individual fine
(field-based enforcement)?
2. Does targeting field operations towards large-
scale deforestation induce „avoidance
behavior“, e.g., an increase in small-scale
deforestation?
2010 fine locations and 2010/11
change in deforestation
Empirical strategy
• Grid-based approach
– Measurement of all covariates at 20x20km resolution
– Measurement of fine (location) and deforestation at
<=10x10 km resolution
• Matching analysis
– Pooling of 2010 and 2011 observation periods
– Exclusion of non-treated neighbors of treated grid
cells to reduce neighborhood effects
– Stratification by fine type (all fines vs only
deforestation fines)
– Analysis for small versus large-scale (>20ha*)
deforestation
– Problems: clouds and imprecise fines
* Minimum detection of DETER monitoring system
Cloud and/or Deforestation?
2010
2011
PRODES-Deforestation PRODES-Clouds PRODES + DETER -
Deforestation
Imprecisely measured fines
0
20
40
60
80
0.0
0.5
1.0
1.5
precise 44%
Imprecise (56%)
Matching full set of covariates
emb
Forest2007
acc_def
Clouds
Clouds_lagged
prodes_lag
prod_splagt1
DISTANCIA
DISTANCIAsq
MUNimprecise
TI_percent
UC
Assenta
smallsh
sh_high_lag
agrsh
pastsh
tractor_w
Prec_ann
Share.owners
-1 -0.5 0 0.5 1
unmatched
matched MHD
matched INV
Standardized difference in means
Matching (change in
deforestation)
ATT AI SE / AI p Number of
treated cells
All fine types / all cells -2.98 2.18 / 0.171 2848
All fine types / excluding
neighbors
-4.39 2.21 / 0.047 2848
Only deforestation fines -8.21 4.33 / 0.058 614
Only deforestation fines
no clouds
-8.42 5.31 / 0.113 410
Only deforestation fines
no clouds >20ha patches
-10.59 4.72 / 0.024 410
Only deforestation fines
no clouds <20ha patches
2.17 2.21 / 0.328 410
Matching (share of deforestation
patches > 20ha)
ATT AI SE / AI p Number of
treated cells
All fine types / excluding
neighbors
0.02 0.01 / 0.051 2848
Only deforestation fines 0.01 0.02 / 0.493 614
Only deforestation fines
no clouds
0.01 0.02 / 0.518 410
Key findings
• Significant deterrence effects of fines issued in
field-based enforcement campaigns
• On average a single additional fine reduces
deforestation by 10-20% in the subsequent year
• Effects vary across states (different dynamics of
confounding factors)
• Only limited evidence for “avoidance behavior”
Caveats
• Clouds, imprecisely measured fines, and
unobserved state-level action remain not
fully controlled confounding factors
• Balance on past deforestation cannot be
fully achieved with full set of covariates
• Further robustness tests pending
Conclusions
• After major reductions, field-based enforcement still
exerts significant and sizeable negative effects on
deforestation at the local scale
• Reason may not be the fine itself, but the host of
economic implications that arise from having
received one (embargo, etc.)
• Signs of “avoidance behavior”, i.e. small-scale
deforestation increasing in response to enforcement
that targets large-scale deforestation less
pronounced than suggested by previous analyses
• Average operational costs per fine are at about
R$4650 and thus probably still lower than the
environmental benefit of avoided deforestation
measured at carbon offset price values
THANK YOU

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Environmental policy’s new role in the Brazilian Amazon

  • 1. Environmental policy’s new role in the Brazilian Amazon Jan Börner (UniBonn/CIFOR) Jorge Hargrave (IPEA) Krisztina Kis-Katos (Freiburg University) Konstantin König (ICRAF) Monique Sacardo Ferreira (IPEA)
  • 2. Background • Deforestation rates peaked in 2004 • Command-and- Control policy considered largely ineffective • Broad changes in governance system in 2004/5 (PPCdAM) • Since then reductions by over two thirds 0 5000 10000 15000 20000 25000 30000 2004200520062007 2008200920102011 years Deforestation(sq.km) 0 1000 2000 3000 4000 5000 6000 7000 8000 9000 Numberoffines
  • 3. Background • Shift from large to smaller scale deforestation: result of enforcement strategy (Rosa et al. 2012) or structural change (Pacheco 2011)? Rosa et al. 2011
  • 4. Research questions 1. Districts with high fine intensity were focus of many complementary measures (e.g. embargoes, exclusion from credit, etc.). What is the deterrence effect of an individual fine (field-based enforcement)? 2. Does targeting field operations towards large- scale deforestation induce „avoidance behavior“, e.g., an increase in small-scale deforestation?
  • 5. 2010 fine locations and 2010/11 change in deforestation
  • 6. Empirical strategy • Grid-based approach – Measurement of all covariates at 20x20km resolution – Measurement of fine (location) and deforestation at <=10x10 km resolution • Matching analysis – Pooling of 2010 and 2011 observation periods – Exclusion of non-treated neighbors of treated grid cells to reduce neighborhood effects – Stratification by fine type (all fines vs only deforestation fines) – Analysis for small versus large-scale (>20ha*) deforestation – Problems: clouds and imprecise fines * Minimum detection of DETER monitoring system
  • 7. Cloud and/or Deforestation? 2010 2011 PRODES-Deforestation PRODES-Clouds PRODES + DETER - Deforestation
  • 9. Matching full set of covariates emb Forest2007 acc_def Clouds Clouds_lagged prodes_lag prod_splagt1 DISTANCIA DISTANCIAsq MUNimprecise TI_percent UC Assenta smallsh sh_high_lag agrsh pastsh tractor_w Prec_ann Share.owners -1 -0.5 0 0.5 1 unmatched matched MHD matched INV Standardized difference in means
  • 10. Matching (change in deforestation) ATT AI SE / AI p Number of treated cells All fine types / all cells -2.98 2.18 / 0.171 2848 All fine types / excluding neighbors -4.39 2.21 / 0.047 2848 Only deforestation fines -8.21 4.33 / 0.058 614 Only deforestation fines no clouds -8.42 5.31 / 0.113 410 Only deforestation fines no clouds >20ha patches -10.59 4.72 / 0.024 410 Only deforestation fines no clouds <20ha patches 2.17 2.21 / 0.328 410
  • 11. Matching (share of deforestation patches > 20ha) ATT AI SE / AI p Number of treated cells All fine types / excluding neighbors 0.02 0.01 / 0.051 2848 Only deforestation fines 0.01 0.02 / 0.493 614 Only deforestation fines no clouds 0.01 0.02 / 0.518 410
  • 12. Key findings • Significant deterrence effects of fines issued in field-based enforcement campaigns • On average a single additional fine reduces deforestation by 10-20% in the subsequent year • Effects vary across states (different dynamics of confounding factors) • Only limited evidence for “avoidance behavior”
  • 13. Caveats • Clouds, imprecisely measured fines, and unobserved state-level action remain not fully controlled confounding factors • Balance on past deforestation cannot be fully achieved with full set of covariates • Further robustness tests pending
  • 14. Conclusions • After major reductions, field-based enforcement still exerts significant and sizeable negative effects on deforestation at the local scale • Reason may not be the fine itself, but the host of economic implications that arise from having received one (embargo, etc.) • Signs of “avoidance behavior”, i.e. small-scale deforestation increasing in response to enforcement that targets large-scale deforestation less pronounced than suggested by previous analyses • Average operational costs per fine are at about R$4650 and thus probably still lower than the environmental benefit of avoided deforestation measured at carbon offset price values