david butry thursday

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 Applying Program Evaluation Methods to Natural Resource Policy: Are Current Wildfire Mitigation Programs Effective? David T. Butry 1 , Subhrendu K. Pattanayak 2 , Erin O. Sills 3 , and D. Evan Mercer 4 1 Economist, NIST; 2 Fellow, RTI International and Research Associate Professor, North Carolina State University; 3 Associate Professor, North Carolina State University; 4 Research Economist, USDA Forest Service

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Page 1: David Butry Thursday

8/14/2019 David Butry Thursday

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Applying Program

Evaluation Methods toNatural Resource Policy: AreCurrent Wildfire Mitigation

Programs Effective?

David T. Butry1, Subhrendu K.

Pattanayak2, Erin O. Sills3, and D.Evan Mercer4

1Economist, NIST; 2Fellow, RTI International and Research Associate Professor,North Carolina State University; 3Associate Professor, North Carolina StateUniversity; 4Research Economist, USDA Forest Service

Page 2: David Butry Thursday

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 Talk Outline

• Introduction

– Wildfire in the US

• Program Evaluation Econometrics– Issues of Endogeneity

– Lack of natural resource applications

• Case Study: NE Florida– Rapid response and prescribed burning

– Propensity score matching model

• Conclusions and Discussion

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Wildfire

• Between 1994-2004, over $830million annually in wildfiresuppression (Federal)

• Over 1.4 million acres are prescribedburned per year (1995-2000 yearlyaverage) (Federal)

• Still wildfire burn more than 5.2million acres a year (1994-2004)

• Is wildfire management doingenough?

Page 4: David Butry Thursday

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Wildfire Economics

• Understanding tradeoffs

– Optimal amount of wildfire

– Optimal mix of wildfire mitigationstrategies

• Economic framework

– Minimize fire damage plus mitigation

cost

– Maximize fire damage averted givenmitigation cost

– Wildfire production function??

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Page 6: David Butry Thursday

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Wildfire Management

• Suppression– Rapid response

• Prescribed Fire

– Intentionally set, low intensity firesadministered under ideal weatherconditions by trained specialists

• Intended effect of management–  To limit fire spread and intensity

Page 7: David Butry Thursday

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Potential Endogeneity of Wildfire Management

• Fuels Management—selection

– Factors that influence wildfire behavior also

influence placement and intensity of fuelsmanagement

– Some of these factors may be unobserved

• Suppression—simultaneity (and selection)

– Fire fighting response and effort influenced bywildfire behavior,

– Wildfire behavior influenced by fire fighting

Page 8: David Butry Thursday

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Program EvaluationEconometrics

• Focuses on establishing causality forendogenous treatment

• Program evaluation isolates thecausal effect of a program/treatment

– Natural experiments

– Instrumental variables (IV) and control

functions

– Matching (e.g. with propensity scores, orPSM)

• Most commonly applied to social

Page 9: David Butry Thursday

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Program Evaluation & NaturalResource Applications

– Edmonds 2002 - IV and matching –community organizations on fuelwood

extraction in Nepal– Pattanayak 2004 – PSM - disturbance on

forest amenities

–Ferraro et al. 2005 – PSM – ESA onspecies recovery

– Somanathan et al. 2005 – PSM –decentralized management on forest

cover

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Program Evaluation EconometricMethods

• Instrumental Variables– Proxy endogenous program/treatment variable

with exogenous instrument(s)

• Control Functions

– Controls for endogeneity by modelingtreatment (selection) as a function of observable data

• Propensity Score Matching

– Matches treated observations with “like”untreated observations, identified byequivalent propensity scores

– Propensity score estimated as the probabilityof treatment using all variables that directly

influence treatment and treatment outcome

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Propensity Score Matching

• Estimate propensity score– Propensity score is the estimated probability of 

a wildfire receiving management

– Function of variables that directly affect

management and also directly affect wildfireproduction

• Match wildfires based on their propensityscore

– Matched wildfires have similar probability of being managed

– Thus, matched wildfires have no underlyingdifferences, except management status

• The difference between matched wildfires

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ase u y— . o ns ver a erManagement District (SJRWMD),

FloridaSJRWMD 1996-2001

Wildfire7490 ignitions

502,754 acres burned

Prescribed Fire73,099 for hazard reduction

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Estimation Objectives

• Quantify the effectiveness of management(treatment) on wildfire behavior (outcome)

 Treatment– Rapid Suppression Response

 A rapid response is when fire report time to fire crewarrival is an hour or less

– Prescribed Fire

If the landscape had been treated with prescribed firewithin the last three years prior to the wildfire

Outcome– Wildfire behavior

Measured as intensity-weighted acres burned 

• Compare OLS estimates to propensity scorematching methods

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Data Sources

• FL Dept. of Forestry

– Wildfire

– Management

• NOAA & NCDC

– Climate and Weather

• Census TIGER/Line & NLCD– Landscape Characteristics

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DataWildfire Management (XManagement): rapid suppression response

indicator, previous prescribed fire indicator.

Fire Characteristics (XFire Characteristics): ignition cause, fire year, fire

month, use fire indicator, and report time.

Climate and Weather (XClimate and Weather): measures of the Niño3 sea-surface Pacific ocean temperature, Keetch-Byram Drought Index,humidity, spread index, wind speed, and wind direction indicators.

Landscape Characteristics (XLandscape): forest density, proportion of 

landscape in upland forest, vegetation build-up, elevation, slope, fueltype indicators, latitude, longitude, wildfire history, fire districtindicator, and county indicators.

Socioeconomic Factors (ZSocioeconomic): population, percent of 

landscape in residential, distance to nearest school, hospital, and firedepartment, and population living in a nursing home.

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Ordinary Least SquareModel

),,,,,()ln( OLSyFireHistor LandscapeWeather andClimatesticsCharacteriFireManagement εXXXXXw w f  =

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Propensity Score Estimators

( ) psm

 s

 psm

 s f   εXXXs ,,, LandscapeWeather andClimatesticsCharacteriFire=

 psm

 p

 p psm

 p f   εZZZXp ,,,, Weather ManagementmicSocioeconoLandscape=

Rapid Suppression Response Estimator (probit model)

Prescribed Fire Estimator (probit model)

A kernel matching was used to weight the best potential matches

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Results—Ordinary LeastSquares

• Model highly significant

• R2 = 0.13

• N=7490, K=81• Suppression parameter significant

(5% level) and negative

• Prescribed fire parameterinsignificant (5% level)

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Results—Propensity ScoreMatching

• Both propensity score estimatormodels are highly significant

• “Good matches” exist

• Conditional mean impact negativefor both suppression and prescribedfire

• Standard errors generated frombootstrapping the PSM kernelestimator shows significance at 1-5%

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Management on Wildfire Intensity-Acres (kW-acres/meters)

*insignificant 

-81367286PSM-26546520OLS*

-80366286Means

Prescribed Fire

-175500325PSM

-210546337OLS

-401723322Means

Suppression

TreatmentEffect

Control

Treated

WildfireManagement

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Summary of Results

• Wildfire management has asignificant impact on wildfirebehavior

– Rapid suppression response yields a35% reduction in wildfire intensity-acres

– Prescribed fire yields a 22% reduction in

wildfire intensity-acres•For prescribe fire, OLS does not find

statistical relationship impact

• OLS overestimates the effectivenessof su ression com ared to PSM

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Discussion

• Estimated results suggest hugebenefits

– 1998 one of the worst fire years inSJRWMD

– Damage approximately $325 million

– Estimated reduction in wildfire intensity-

acres suggests $140 million in damageswere avoided

• OLS estimates would overvalue

wildfire management’s effectiveness