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Policy Uncertainty Reduces Green Innovation: Wang, Wurgler & Zhang (2026)

Distilled by claude-sonnet-4-6 · extracted Jun 24, 2026, verified Jun 24, 2026

JEL (IAR-assigned): G18, G31, Q55 · assigned from the abstract, not the journal

Full structured metadata (methods, scope, relatesTo, topics, datasets): raw Markdown (.md)

paper-summaryclimate-financegreen-innovationpolicy-uncertaintyenvironmental-economicschinapanel-regressionfama-macbethpeer-reviewedunreplicateddata:csmardata:cnrdsdata:winddata:cma-weather

What this is. The paper’s core results, the simple mean-variance model of investment under uncertain subsidies, and the two-stage IV design that instruments policy uncertainty with weather volatility: enough to understand what was found and how, without reading all 14 pages. To replicate or extend, read the full source at the original.

The paper documents that policy uncertainty about environmental subsidies suppresses the green R&D that those subsidies are designed to stimulate. The setting is China, where provincial and local governments allocate environmental subsidies partly on the basis of Air Quality Index (AQI) readings, and weather (wind and rain) drives AQI in predictable but noisy ways. Weather variability over a rolling six-year window therefore generates exogenous variation in how predictable a city’s subsidy allocation will be, forming an instrument for policy uncertainty. A one-standard-deviation increase in weather variability reduces city-level green R&D by 0.132 standard deviations (IV estimate, Table 4 Model 5, p. 9). Effects are stronger for green-tech firms, subsidy-reliant firms, and firms under financial pressure. Placebo tests on non-green R&D and capital expenditure show no significant effect, consistent with the channel being specific to subsidized green activities. The paper extends Gulen and Ion (2016) by identifying a behavioral source of policy uncertainty: policymakers respond to salient recent pollution readings, which are themselves influenced by transient weather, creating a recency-bias channel that Bernanke (1983) and Dixit and Pindyck (1994) frameworks predict will deter investment.

Magnitudes and significance are as reported; \*/\*\*/\*\*\* = 10%/5%/1%. Locators point into the source PDF.

#ResultLocatorMagnitude
R1Policy uncertainty (IV) reduces city-level green R&DTable 4 Model 5, p. 8PU coefficient = -2.23*** (t = -2.64); one-SD weather variability reduces green R&D by 0.132 SD; OLS comparison: -0.29** (Table 4 Model 1)
R2Higher average subsidies stimulate green R&DTable 4 Model 5, p. 8Avg Green Subsidy = 0.34*** (t = 2.76); one-SD subsidy increase raises green R&D by 0.158 SD
R3Policy uncertainty reduces green R&D employmentTable 8 Model 1, p. 12PU coefficient = -1.07*** (t = -3.41); one-SD weather variability reduces employment by 0.153 SD
R4Green-tech firms are more sensitive to policy uncertaintyTable 6 Model 2, pp. 10-11PU × Green Tech = -0.58*** (t = -7.47), adding to average-firm effect of -0.40*** (Table 6 Model 1, t = -2.72)
R5Subsidy-reliant firms are more sensitive to policy uncertaintyTable 6 Model 5, p. 11PU × Subsidy Reliant = -0.62*** (t = -7.77)
R6Policy uncertainty does not affect non-green R&D or capital expenditure (placebo)Table 5 Models 6-8, p. 10Non-green R&D: PU = 0.83 (t = 1.48, n.s.); capex: PU = -0.00 (t = -0.44, n.s.); real estate capex: PU = 0.03 (t = 0.32, n.s.)

Overall (paper’s conclusion). Policy uncertainty about environmental subsidies has real effects on green innovation: it reduces both the R&D investment and the technical employment that subsidies are intended to promote. Effects concentrate on the firms theory predicts should be most sensitive (green-tech, subsidy-reliant, financially pressured), and placebos confirm the result is not a general investment or uncertainty shock but is specific to the green component tied to the subsidized activities.

The paper develops a stylized mean-variance model to derive qualitative predictions about how subsidy uncertainty affects green investment relative to traditional investment (Section 2.2, p. 4). A firm raises capital to invest in two technologies at the start of a period. The first, GG, is an environmental technology receiving an uncertain government subsidy SN(Sˉ,σS2)S \sim N(\bar{S}, \sigma_S^2). The total per-dollar payoff from GG is RˉG+Sˉ\bar{R}_G + \bar{S} with variance σG2+σS2\sigma_G^2 + \sigma_S^2. The second, XX, is a traditional technology with per-dollar payoff RˉXN(RˉX,σX2)\bar{R}_X \sim N(\bar{R}_X, \sigma_X^2). Both investments are subject to a gross financing cost CC. The firm maximizes mean-variance utility (equation 1, p. 4):

maxG,X  G(RˉG+SˉC)γ2G2(σG2+σS2)+X(RˉXC)γ2X2σX2(1)\max_{G,X} \; G(\bar{R}_G + \bar{S} - C) - \frac{\gamma}{2}G^2(\sigma_G^2 + \sigma_S^2) + X(\bar{R}_X - C) - \frac{\gamma}{2}X^2\sigma_X^2 \tag{1}

where γ\gamma is risk aversion, which stands in for irreversibility, adjustment costs, or managerial risk aversion in the spirit of Bernanke (1983), Dixit and Pindyck (1994), and Julio and Yook (2012). The first-order conditions yield optimal investments (equation 2, p. 4):

G=RˉG+SˉCγ(σG2+σS2),X=RˉXCγσX2(2)G^* = \frac{\bar{R}_G + \bar{S} - C}{\gamma(\sigma_G^2 + \sigma_S^2)}, \qquad X^* = \frac{\bar{R}_X - C}{\gamma\sigma_X^2} \tag{2}

The ratio of green to traditional investment is (equation 3, p. 4):

GX=RˉG+SˉCRˉXC×σX2σG2+σS2(3)\frac{G^*}{X^*} = \frac{\bar{R}_G + \bar{S} - C}{\bar{R}_X - C} \times \frac{\sigma_X^2}{\sigma_G^2 + \sigma_S^2} \tag{3}

The model yields three comparative statics that the paper tests empirically:

  1. Higher subsidy policy uncertainty σS2\sigma_S^2 reduces both the level GG^* and the share G/XG^*/X^*.
  2. Higher average subsidies Sˉ\bar{S} increase the level and share of green R&D.
  3. Higher financing cost CC (a proxy for financial pressure or over-indebtedness) increases the sensitivity of G/XG^*/X^* to σS2\sigma_S^2, predicting that financially constrained firms are more affected by policy uncertainty.

This is not a structural model; it is a stylized device for generating falsifiable comparative statics. The paper also discusses irreversibility and adjustment-cost channels and a recency-bias channel, in which policymakers over-weight recent salient pollution conditions and under-account for transient weather, creating avoidable policy noise.

Identification logic. The empirical chain is: weather volatility drives AQI volatility, which drives subsidy volatility, which creates policy uncertainty that depresses green R&D. The exclusion restriction is that weather volatility affects green R&D only through this subsidy-uncertainty channel, not through other routes such as direct productivity effects of air quality on R&D effort. Placebos against non-green R&D and capex (R6) support this restriction.

Step 1: Subsidies depend on AQI. To show that green subsidy allocations respond to observed pollution, the paper estimates a Fama and MacBeth (1973) cross-sectional regression of city-level green subsidy on lagged AQI (equation 4, p. 6):

Green Subsidyjt=a0+a1×AQIj,t1+A×Xj,t1+εjt(4)\text{Green Subsidy}_{jt} = a_0 + a_1 \times AQI_{j,t-1} + A \times X_{j,t-1} + \varepsilon_{jt} \tag{4}

where Green Subsidyjt\text{Green Subsidy}_{jt} is the log RMB of total environmental subsidies in city jj in year tt, AQIj,t1AQI_{j,t-1} is the lagged average AQI, and Xj,t1X_{j,t-1} contains city and firm-level controls. Coefficients are averaged across cross-sections with standard errors robust to cross-sectional correlation. A one-SD higher AQI is associated with a 0.17 SD higher subsidy the following year (Table 2 Model 2, coefficient = 0.05***, t = 4.88, p. 6).

Step 2: AQI depends on weather. The paper documents the physical link between weather and AQI using a city-season-level specification (equation 5, p. 7):

AQIjt,s=b0+b1×Wind Speedjt,s+b2×Rain Volumejt,s+B×Xjt+δj+δt+εjts(5)AQI_{jt,s} = b_0 + b_1 \times \text{Wind Speed}_{jt,s} + b_2 \times \text{Rain Volume}_{jt,s} + B \times X_{jt} + \delta_j + \delta_t + \varepsilon_{jts} \tag{5}

where AQIjt,sAQI_{jt,s} is the average daily AQI in city jj in season ss of year tt; city and year fixed effects are included; standard errors are clustered by city and year. Wind speed and rain volume are both negative and significant (Table 3, p. 7), confirming that weather disperses particulates and lowers AQI.

Step 3: Instrument construction. Policy uncertainty PUj,t5:tPU_{j,t-5:t} is defined as the standard deviation of the characteristics-adjusted residuals from equation (4) over a six-year rolling window ending at tt. The first stage regresses PUPU on six-year rolling standard deviations of windy days and rainy days (equation 6, p. 8):

PUj,t5:t=c0+c1×SD Windy Daysj,t6:t1+c2×SD Rainy Daysj,t6:t1+C×Xjt+δj+δt+εjt(6)PU_{j,t-5:t} = c_0 + c_1 \times \text{SD Windy Days}_{j,t-6:t-1} + c_2 \times \text{SD Rainy Days}_{j,t-6:t-1} + C \times X_{jt} + \delta_j + \delta_t + \varepsilon_{jt} \tag{6}

The fitted weather component alone forms the instrument (equation 7, p. 9):

PU^j,t5:t=c^1×SD Windy Daysj,t6:t1+c^2×SD Rainy Daysj,t6:t1(7)\hat{PU}_{j,t-5:t} = \hat{c}_1 \times \text{SD Windy Days}_{j,t-6:t-1} + \hat{c}_2 \times \text{SD Rainy Days}_{j,t-6:t-1} \tag{7}

First-stage estimates: c^1=0.01\hat{c}_1 = 0.01^{***} (t = 3.27), c^2=0.16\hat{c}_2 = 0.16^{***} (t = 3.71); first-stage F = 14.5 (Table 4 Model 2, p. 8). One-SD weather variability raises measured policy uncertainty by 0.228 SD. The estimation builds on instrumental-variables and panel-regression primitives.

City-level green R&D (R1, R2). The second stage regresses next-year city-level green R&D on instrumented policy uncertainty and average subsidy (equation 8, p. 9):

Green R&Dj,t+1=d0+d1×PU^j,t5:t+d2×Avg Subsidyj,t5:t+D×Xjt+δj+δt+ηj,t+1(8)\text{Green R\&D}_{j,t+1} = d_0 + d_1 \times \hat{PU}_{j,t-5:t} + d_2 \times \text{Avg Subsidy}_{j,t-5:t} + D \times X_{jt} + \delta_j + \delta_t + \eta_{j,t+1} \tag{8}

where Green R&Dj,t+1\text{Green R\&D}_{j,t+1} is log aggregate green R&D of city jj‘s listed firms, PU^\hat{PU} is the weather-instrumented policy uncertainty (equation 7), Avg Subsidyj,t5:t\text{Avg Subsidy}_{j,t-5:t} is the six-year moving average of the characteristics-adjusted subsidy, and XjtX_{jt} includes AQI and city and firm-level controls. City and year fixed effects; standard errors clustered by city and year. Headline estimates: d1=2.23d_1 = -2.23^{***} (t = -2.64) and d2=0.34d_2 = 0.34^{***} (t = 2.76), Table 4 Model 5.

The one-standard-deviation translation: (0.01×25.3+0.16×1.95)×(2.23)/9.54=0.132(0.01 \times 25.3 + 0.16 \times 1.95) \times (-2.23) / 9.54 = -0.132 SD in green R&D per SD in weather variability (footnote 18, p. 9).

Firm-level heterogeneity (R4, R5). The city-level instrument enters a firm-level regression interacted with firm-type indicators (equation 9, p. 10):

Green R&Dic,j,t+1=e0+e1×PU^j,t5:t+e2×Firm Typeic,jt×PU^j,t1+e3×Avg Subsidyj,t5:t+E×Xic,jt+δi+δt+ηic,j,t+1(9)\text{Green R\&D}_{ic,j,t+1} = e_0 + e_1 \times \hat{PU}_{j,t-5:t} + e_2 \times \text{Firm Type}_{ic,jt} \times \hat{PU}_{j,t-1} + e_3 \times \text{Avg Subsidy}_{j,t-5:t} + E \times X_{ic,jt} + \delta_i + \delta_t + \eta_{ic,j,t+1} \tag{9}

with firm and year fixed effects; standard errors clustered by city and year. Firm type indicators include green tech (CSRC industry N77), metropolitan area, large size, state ownership, subsidy reliance (above-median ratio of environmental subsidy to total assets), cross-city registration, and industry affiliation (manufacturing, chemical, metal, public facility). The green-tech and subsidy-reliant interactions are the most significant (Table 6, pp. 10-11).

Green R&D employment (R3). Equation (8) replaces the dependent variable with log(1+total R&D and technical employees in city j)\log(1 + \text{total R\&D and technical employees in city } j). Result: PU = -1.07*** (t = -3.41), Table 8 Model 1.

Placebos (R6). Equation (8) with three alternative dependent variables: total R&D minus green R&D, city capital expenditure, and city capital expenditure of real estate firms (Table 5 Models 6-8). None shows a significant effect of PU^\hat{PU}, supporting the exclusion restriction.

Robustness. Table 5 reports eight robustness checks including: excluding city-years with zero green R&D, two-year average AQI, weather-adjusted AQI, subsidy starting from 2007, and a subsample from 2013 onward. The main result is stable across all variations (PU coefficients ranging from -2.22 to -5.14, all significant at 5% or better except in Model 6 which is a placebo). Baker, Bloom and Davis (2016) style policy uncertainty indices serve as a conceptual foil; the paper distinguishes its weather-based channel from those political and fiscal sources.

The estimation sample is 2009-2019, pre-Covid. City-year panel: 1,340 observations (up to 352 cities). Firm-year panel: 26,189 observations (3,168 firms).

DatasetRole in paperWiki page
CSMAR (China Stock Market & Accounting Research Database)Firm-level green R&D (from financial statement footnotes), environmental subsidy receipts, stock returnNo page yet
CNRDS (China Research Data Services)City-level GDP, GDP growth, consumption, population growth; firm characteristics digitized from China Statistical YearbookNo page yet
WIND Financial TerminalFirm-level turnover, ROA, leverage, size, cash holdings, capex, profit marginNo page yet
Ministry of Ecology and Environment (MEPC)Annual average AQI for major cities from the national monitoring networkNo page yet
China Meteorological Administration (CMA)Daily city-level wind speed (m/s) and rain volume (mm) used to construct Windy Days, Rainy Days, and their rolling standard deviationsNo page yet
EPSnetCity-level industrial Waste Gas Treatment expenditure; used to confirm the AQI-subsidy relationship independently (Table 2 Models 5-6)No page yet

Sample: weather and subsidy data back to 2003 (needed for six-year rolling windows); main regressions: 2009-2019 (pre-Covid). 352 Chinese cities; 3,168 listed firms; 1,340 city-year observations in primary city-level regressions; 26,189 firm-year observations in firm-level regressions.

Read the original if you are:

  • studying how uncertainty about government policies, not just their level, can undermine their intended effects on investment;
  • building a weather-based IV design for policy uncertainty in settings where subsidies are tied to observable environmental indicators;
  • interested in the institutional mechanics of Chinese environmental policy and AQI-linked subsidy allocation;
  • examining heterogeneous investment responses to policy uncertainty across firm types (green-tech, subsidy reliance, financial constraints);
  • researching the real-side effects of climate policy uncertainty for the growing green finance literature.

The online appendix (available at the DOI) contains additional institutional background, variable definitions, and further robustness checks.

Source: peer-reviewed, Journal of Financial Economics 175 (2026) 104189. This distillation was extracted by an LLM on 2026-06-24 and is not human-verified or independently reproduced. The paper is paywalled; only extract-only redistribution is permitted.

Wang, Mengyu, Jeffrey Wurgler, and Hong Zhang. “Policy uncertainty reduces green innovation.” Journal of Financial Economics 175 (2026) 104189. DOI: 10.1016/j.jfineco.2025.104189. © 2025 Published by Elsevier B.V.

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