gary_henry_causal attribution for environmental program evaluation
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Gary T. HenryMacRae Professor of Public Policy
University of North Carolina at Chapel Hill
2008 Environmental EvaluatorsNetworking Forum
June 12, 2008
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Not just RCT vs. everythingelse
The Received Theory ofCausality has Changed Campbell & Stanley (1966);
Cook and Campbell (1979);Shadish, Cook and Campbell(2002)
Design-based logic of inquiryapproach
Objective: to establish that a
causal relationship exists andcan reasonably begeneralized
Method: Making alternativeexplanations implausible
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Units, individuals or plots of land, havealternative potential outcomes, for example,recycling/not recycling or deforested/forested,
respectively.
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Each unit has alternative outcomesEvaluation Question: Does an environmental
program alter the potential outcomes in thedesired direction for a unit?
For a particular unit, we would like to observethe outcome after the intervention occurredfor two conditions:1. If the unit was included in the intervention;
2. If the unit was not included in the intervention.The objective is an unbiased estimate of the
effect of the program
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Fortunately, someone (Donald Rubin) hasdone the math for us
(but unfortunately the fine print says we have to collectthe data)
The Objective: Unbiased estimate of theeffect of treatment
Possible assignments (X, treatment orcontrol)
Potential outcomes (Y)YiT= outcome for individual i after exposure to
treatment
YiC= outcome for individual i after exposure to control
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Unit PotentialOutcomewithoutProgram
PotentialOutcomewithoutProgram(YiC)
PotentialOutcomewithProgram
PotentialOutcomewithProgram(YiT)
Label
1 deforested 0 forested 1 Programsuccess
2 forested 1 forested 1 Nodifferenc
e3 deforested 0 deforested 0
Nodifferenc
e4 forested 1 deforested 0
Programfailure
These four units exhaust all of the logicalpossibilities
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( )Ti Cii Y Y
The fundamental problem with causal inference:It is impossible to observe the idealcomparison
All designs including RCTs are approximations of the idealCausal inference requires assumptions: RCTs require the fewestExtrapolation of treatment effects to target population requiresadditional assumptions
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Strata
Units inStudy
Population
Potential Outcomes Label
YT YC
1 40 1 0Programsuccess
2 20 1 1No
Difference
3 20 0 0No
difference
4 20 0 1Programfailure
Program produced 60 forested parcelsNo program produces 40 forested parcelsThe program effect was 20 forested parcels or a 1.5increase in forested parcels
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The average treatment effect (ATE)
( )
( ) ( )
( ) ( )
T C
T C
T C
E Y Y
E Y E Y
Y Y
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StrataPercentage
of StudyPopulation
Possible Outcomes
YT YC
ControlGroup
1 20 1 0
2 10 1 1
3 10 0 0
4 10 0 1
TreatmentG
roup
1 20 1 0
210 1 1
3 10 0 0
4 10 0 1
Independence =Equivalence of theStudy PopulationPercentages forEach Strata in
Control andTreatment
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StrataPercentage
of StudyPopulation
Possible Outcomes
YT YC
ControlGroup
1 20 ? 0
2 10 ? 1
3 10 ? 0
4 10 ? 1
TreatmentGroup
1 20 1 ?
2 10 1 ?
3 10 0 ?
4 10 0 ?
Independence =Equivalence of theStudy PopulationPercentages forEach Strata in
Control andTreatment
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To complete the ingredients needed forcausal attribution (unbiased effect sizeestimate) we need a switch to assign unitsto treatment and control
We need a switch that meets theindependence assumption: createsequivalent groups
The Switch (S)The switch assigns each individual to treatment (S =
1)or control (S = 0)( | 1) ( | 0)i i i i
E Y S E Y S
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Strata
Percentageof Study
Population
Potential Outcomes Observed outcomes
YT YC X YT YC
Contro
lGroup
1 20 1 0 0 * 0
2 10 1 1 0 * 1
3 10 0 0 0 * 0
4 10 0 1 0 * 1
TreatmentGroup
1 20 1 0 1 1 *
2 10 1 1 1 1 *
3 10 0 0 1 0 *
4 10 0 1 1 0 *
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1. Random assignment to treatment & controlIf independence produces equivalence, extraneous sources of variation
(aka influence of disturbing variables) are equally distributed acrosstreatment and control
Simplifies analysis
2. Matched sampling3. Matched sampling using propensity scores
Propensity scores are each individuals probability of being assigned totreatment
Matches based on finding individual in control similar to each individual intreatment based on propensity scores
4. Cutoff on assignment variable assigns individuals totreatment and control (regression discontinuity)If model correctly specified, produces unbiased estimate of average
treatment effect5. Instrumental variable6. Fixed effects (within individual estimates for panel data)Or using regression to adjust estimates
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Several important studies about differences in effect sizesbetween experimental and observational studies
Lipsey and Wilson (1992)Weisburd, Lum & Petrosino (2001)Glazerman, Levy & Myer (2003) matched sample labor
force interventions; assumed randomized experimentunbiased
5. Matching works well (better w/ one-on-one matchingextensive covariates;
6. Regression works well (better with specification tests,numerous controls, especially pretests);
7. Large sample studies less biased8. Controls selected from similar sitesLarge consensus that regression discontinuity is second
best switch after randomized control trials (van derKlaauw 2003; Trochim, Cappelleri, Reichhardt 1991)
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LEANAME ADM
Students
Proficient
Teacher
Retention
eac er%
greater
than 5
years
%
Above
Poverty Combined RankWELDON CITY 1,078 51.10 81.72 55.56 73.18 261.56 116 YVANCE COUNTY 8,157 62.70 78.96 58.53 74.06 274.25 115 YHERTFORD COUNTY 3,606 61.30 81.25 65.17 70.78 278.50 114 YHOKE COUNTY 6,593 66.40 72.41 62.47 77.75 279.03 113 YWARREN COUNTY 3,110 67.30 82.79 62.56 70.07 282.72 112 YLEXINGTON CITY 3,162 64.30 86.75 54.88 76.92 282.85 111 Y
NORTHAMPTON COUNTY 3,254 63.80 83.22 67.58 70.52 285.12 110 YHALIFAX COUNTY 5,428 67.10 90.43 62.56 66.19 286.28 109 YTHOMASVILLE CITY 2,666 64.10 78.86 63.27 81.10 287.33 108 YWASHINGTON COUNTY 2,155 57.40 88.36 71.20 73.13 290.09 107 YEDGECOMBE COUNTY 7,591 66.40 81.67 66.98 76.89 291.94 106 YFRANKLIN COUNTY 7,877 72.80 78.47 59.45 81.99 292.71 105 YMONTGOMERY COUNTY 4,502 68.20 81.95 64.26 78.65 293.06 104 YROBESON COUNTY 24,134 67.80 86.03 68.04 74.01 295.88 103 YHYDE COUNTY 670 73.50 85.53 69.01 69.22 297.26 102 YELIZABETH CITY/PASQUOTA 5,902 71.90 81.43 70.55 75.52 299.40 101 YKANNAPOLIS CITY 4,673 72.10 87.43 56.10 83.90 299.53 100
DURHAM COUNTY 30,810 71.20 81.24 64.72 82.70 299.86 99TYRRELL COUNTY 644 82.80 75.44 73.13 68.52 299.89 98BERTIE COUNTY 3,404 65.50 92.31 70.52 71.99 300.32 97DUPLIN COUNTY 8,802 75.60 79.62 67.97 78.25 301.44 96HARNETT COUNTY 16,917 75.50 81.66 63.17 81.22 301.55 95ANSON COUNTY 4,403 63.50 89.86 71.61 78.02 302.99 94GREENE COUNTY 3,222 72.30 86.70 64.84 79.93 303.77 93LENOIR COUNTY 10,211 77.70 79.87 70.21 76.25 304.03 92CHARLOTTE/MECKLENBURG 117,773 75.60 83.27 59.17 86.58 304.62 91
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p-value Coefficient Std. Err
Intercept 0.000 -0.097667 (0.021596 )
Asian mean 0.466 -0.001846 (0.002530 )
Black mean 0.067 0.000669 (0.000365 )Hispanic mean 0.266 0.001985 (0.001781 )
Multiracial mean 0.039 0.008692 (0.004204 )
American Indian mean 0.168 -0.001173 (0.000849 )
Free lunch mean 0.070 -0.001265 (0.000698 )
Reduced lunch mean 0.569 0.000825 (0.001450 )
School size 0.236 0.000016 (0.000014 )
DSSF Dummy 0.000 0.164639 (0.036082 )
Year 2006 0.001 -0.037745 (0.010466 )
Combined 0.000 0.471141 (0.123720 )
Combined Squared 0.020 0.524394 (0.224090 )
Combined Cubed 0.001 -2.669102 (0.731942 )
Regular classroom instruction ---- ---- ----
(Net Effects Model) -All Students
1. Estimates with individual level controls
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StrataPercentage
of TargetPopulation
Potential Outcomes Observed outcomes
YT YC X YT YC
ControlGroup
1 10 1 0 0 * 0
2 5 1 1 0 * 1
3 5 0 0 0 * 0
4 5 0 1 0 * 1
TreatmentGroup
1 10 1 0 1 1 *
2 5 1 1 1 1 *
3 5 0 0 1 0 *
4 5 0 1 1 0 *
UnobservedSample
1 20 1 0 * * *
2 10 1 1 * * *
3 10 0 0 * * *
4 10 0 1 * * *
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1. What kind of evidence isneeded to influenceenvironmental policy andprogram decisions?
2. Is there a program on thehorizon for which it wouldbe helpful to have this
information? likely to have large benefits? highly controversial?
Can you find the resourcesto invest in obtainingtrustworthy informationabout program effects?
Consider the extrapolationproblem how to estimateeffects on target populationbased on study population.