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Political economy of the environment · Field lab

The Downwind Ledger

Drop a fire anywhere on the plain, then turn the wind and see who inherits the smoke. A district officer who breathes their own farmers' stubble has a reason to stop it; one whose smoke crosses a border does not. This is the incentive Dipoppa & Gulzar measured — here it is as a dial and a draggable match.

Built on Dipoppa, G. & Gulzar, S. “Bureaucrat incentives reduce crop burning and child mortality in South Asia.” Nature 634, 1125–1131 (2024).

Season preset
—
Predicted change in burning
−30% or moreno change+30% or more
Every 5 km² square asks the same question as the test fire: at this wind, does the officer here have a reason to enforce? Blue means yes — burning falls.
The half of a district this fire's smoke falls on
Modelled PM2.5 plume, all fires
Fire detections Population
India–Pakistan border State border
Does this officer have a reason to enforce?—
—
—

Who breathes this fire
Wind field
NW 315° smoke travels SE
Map layers
District
Incentive by wind angleall 360°

Distance from centre = share of this district's smoke that settles on its own people. The needle marks the current wind.

01The ledger

One row per district. Retained is the share of a district's own burning smoke that lands on its own population — the fraction of the externality its officer internalises. Click any row to inspect it on the map; click a column head to sort.

District Population Fires / mo Retained Leaves region Imported PM Δ fires PM2.5 Infant deaths

02What the paper found

Every number this app moves is anchored to a published estimate. These are the paper's, not the model's.

Headline estimates
−14.5%
Fires in the grid cells closest to an upwind district border, where burning pollutes the officer's own district (treatment effect −0.0113, P<0.000).
+15.1%
Fires closest to a downwind border, where the smoke leaves (differential effect +0.0231, P<0.000).
10–13%
Pooled fall in fires once wind shifts a cell from polluting a neighbour to polluting home — roughly 54–72 fires per district per year.
5×
How much larger both effects are at the India–Pakistan border: −56.2% upwind, +146.4% downwind.
−13%
Extra fall in fires after one farmer is criminally penalised — deterrence spills over to others, concentrated in the first three months.
30–36
Additional child deaths per 1,000 births from a one-log rise in in utero PM2.5 from burning (infant: 24–26).
Why wind is the experiment

The authors hold the farmer, the field and the officer fixed and let the wind move. The same 5 km² cell is “treated” in a month when the downwind half of its district is larger than the upwind half — smoke will mostly fall on the officer's own jurisdiction — and “control” when the wind turns and that smoke would blow next door.

Because a monsoon reversal is not chosen by any district officer, the parallel-trends assumption is far more credible than in a usual difference-in-differences. The event study in Fig. 2d shows a flat pre-trend and a drop bottoming out at −22.2% two months after the switch.

That is the whole argument: the same people, the same fields, a different set of lungs downwind — and 10–13% fewer fires. Institutions are not fixed; incentives are.

03Your assignment

Work through these with the controls above. Answers should cite specific districts and numbers from the ledger.

Questions
  1. One field, two borders. Set the wind to NW 315° (late October, the rice peak). Park the test fire in the middle of Sangrur and write down the verdict. Now drag it to within ~20 km of Sangrur's northwestern edge, then to within ~20 km of its southeastern edge. Record the predicted change at all three spots. Same farmer, same district, same officer — why does the recommendation move?
  2. The reversal. Leave the fire where it is and turn the dial to SE 135°. The verdict flips. Explain why this reversal is what lets the authors claim a causal effect rather than a correlation — and name one thing that, if true, would break the claim.
  3. Distance decay. Keeping the wind fixed, walk the fire from a border straight toward the middle of a district and watch the quintile label and the border effect. At what point does the officer stop caring where the smoke goes? Why does the paper let the effect fade to zero at q5 instead of holding it constant?
  4. The international case. Put the fire on the Pakistani side of the India–Pakistan line, a few kilometres from the border, with the wind blowing into India. Report the number. The paper measures −56% upwind and +146% downwind at this border versus ±15% elsewhere. What is it about a national border that makes an officer's indifference so much more extreme than a district border?
  5. When the two rules disagree. Find a spot where the cell is treated (the downwind half of its district is the larger one, so the level effect is −11.5%) but the nearest border is still downwind (so the border effect is positive). Which one wins? What does that tell you about how the paper's two specifications — eq. 2 and eq. 3 — relate to each other?
  6. Population is not the same as stake. Compare a fire near Lahore (11.1 m people, modest burning) with one in Sangrur (1.7 m, heavy burning). Does a large exposed population by itself give an officer a reason to act? Use the “who breathes this fire” bar to argue either way.
  7. Capacity. Drag bureaucratic capacity to 0×, then 1.5×, watching both the fire card and the regional panel. The paper's counterfactual — officers policing downwind areas as hard as upwind ones — is 1.8–2.7 fewer infant deaths per 1,000 births. Does this region reproduce that range? Where it does not, what is the model leaving out?
  8. What is missing. The paper's deterrence result (one criminal penalty → 9–13% fewer fires nearby for three months) is not in this simulation. Sketch how you would add it to the test fire, and say what the map would look like afterwards.
How this model works

Treatment. For every grid cell the app draws a 180° line through the cell perpendicular to the wind and clips the district polygon against it — exactly the authors' definition. If the downwind slice is the larger one, the cell is treated.

Response, in two parts. The level comes from the paper's pooled estimate: a treated cell burns 11.5% less, the midpoint of its 10–13% range. The pattern comes from the border gradient — each cell finds its nearest district border, asks whether that border is upwind or downwind, and takes the paper's coefficient ramped linearly across the five distance-to-border quintiles: −14.47% at the closest upwind quintile, +15.11% at the closest downwind one, fading to zero at the farthest. Cells whose nearest border is the international one use the far larger cross-national coefficients, which is why Lahore and Sheikhupura can burn more even while keeping much of their own smoke.

Exposure. Each burning cell emits a Gaussian plume downwind whose reach scales with wind speed, scored against every population node — plus a ring of receptors outside the frame, so smoke that leaves the region is counted as having gone somewhere rather than quietly disappearing. The result is a who-pollutes-whom matrix. Retained is its diagonal.

Mortality. Δln PM2.5 over a 45 µg/m³ background, multiplied by the paper's instrumental-variables estimates (25.0 infant and 30.8 child deaths per 1,000 births per log point). Read these as this month's exposure held across a whole pregnancy — an upper bound, not an annual figure.