Basic Prerequisites: 04 · ESG Scores & the Carbon Premium.


1. Intuition & Practical Objective

Climate and ESG risk are mathematically ordinary - a weighted average, a cost identity, a quantile, a regression - and operationally treacherous. This page names the failure modes precisely so a risk manager knows which input to distrust and how the failure shows up in a number. The objective is not cynicism; it is the discipline of knowing that in this domain the dominant error term lives in the data definition, not in the estimator.

Three failure modes, in one line each:

  1. Data-quality failure (the technical meaning of greenwashing). A sustainability label that the underlying data cannot support at the stated boundary. It is not primarily a lie by a firm; it is the normal output of a measurement pipeline in which scope, rater, vintage and weights are all discretionary. Greenwashing is the name for the aggregate effect, and it is the same species as look-ahead bias and survivorship bias in quantitative research: an artefact of how the data were generated, invisible in the mathematics.
  2. Non-stationarity. Both the policy path and the market’s pricing of carbon change regime; a fitted carbon beta is a conditional moment, and its out-of-sample value can have the opposite sign.
  3. Scenario resolution limits. A finite scenario set cannot express a high confidence level: with scenarios of maximum weight , the quantile is identified only for (03 · §2.2).

The practical lesson is a change of reporting discipline: publish the boundary, the rater and vintage, the pass-through and the benchmark table alongside the number, because those four choices move the answer more than any modelling refinement.


2. Mathematical Ground Truth & Derivations

2.1 The four axes of freedom of a climate number

Any reported climate metric is a function of the boundary (which scopes), the rater/methodology (which indicators and weights), the vintage (as-of date of the data) and the economic parameters (pass-through, damage coefficient, benchmark table). The first three are definitional - they have no error bars, only alternatives; the fourth is a model. The measured swings in this folder:

AxisDefensible rangeSwing in the reported numberVerified (§)
Boundary (Scope 1+2 vs 1+2+3), same firm/yearboth standards-compliantintensity tCO2e per $1m = 13.5×01 §3
Boundary in temperature alignmentsame holdingsC beyond the C benchmark05 §3(B)
Rater (weights + indicator choice)three mainstream methodologiesmean rank correlation ; largest rank move places; top-5 overlap 04 §3(A), 05 §3(A)
Vintage (retroactive restatement)one historical revision of top-5 names changes05 §3(A)
Economic parameter (pass-through )$30/t shock: = hub §3
Economic parameter (damage )disclosure-dependentphysical loss is linear in - the parameter is the answer02 §3(B)
Scenario count 6 archetypes, confidence ceiling 03 §3

Read the last two rows against the first three: the model parameters are the ones practitioners argue about, while the definitional axes produce larger swings and are usually reported as settled facts. That inversion is the failure mode.

2.2 Label instability: rigorous statistics for a soft property

For a universe of names scored by raters and with ranks , define the rank-instability rate and the top- overlap:

Both are computed from ranks only, so they are invariant to the raters’ scales - the correct way to compare incommensurable scores. A restatement is a third rank vector (the same rater’s history after revision); the exposure to it is . Point-in-time rule: a backtest of any ESG signal must use the as-of-vintage score , not the as-of-today history ; otherwise the vendor’s revisions leak tomorrow’s information into yesterday’s portfolio (Purged CV & Backtest Hygiene).

2.3 Parameter drift

For a climate risk model with parameter vector (e.g. a carbon beta ), define the drift between an in-sample fit and an out-of-sample evaluation

A model used as a hedge ratio requires small. A model used as a risk measure only needs the correct sign - which is why the honest use of a carbon beta is scenario conditioning, not hedging (06 · §2).

2.4 Greenwashing as a data-quality failure, formally

Let a claim be a statement about the true sustainability attribute (e.g. true financed emissions). A pipeline produces an estimate . The greenwashing gap for a portfolio is a statement-level quantity,

i.e. the divergence between what the label asserts and what the same pipeline, honestly bounded, would support. Note the definition deliberately holds and fixed: the failure is not picking a wide boundary (that is legal and disclosed), it is asserting a claim at a boundary or vintage the pipeline does not support. This is why disclosure harmonisation - not more sophisticated mathematics - is the regulatory response (IOSCO’s ESG ratings and data-products work; the EU’s sustainable-finance disclosure framework), and why the divergence literature (Berg et al. 2022) frames the issue as one of data generation, not of statistical technique.


3. Computational Implementation - measuring the three failures

Panel (A) quantifies label instability and a retroactive restatement; (B) shows the scope boundary flipping a temperature classification; (C) shows a fitted carbon beta changing sign out of sample. Standard library only.

Panel (A). Two of the three rater pairs agree on only of the top five - the “leaders” list is a different list depending on who is asked, and and (which share underlying data) agree perfectly at . A single retroactive revision to two firms’ environmental pillar moves one name () in and out of the top five. That is the operational content of point-in-time discipline: the label a backtest “would have” assigned is not recoverable from today’s vendor file.

Panel (B). The identical portfolio is “below C” on a Scope 1+2 basis and beyond the worst benchmark on a Scope 1+2+3 basis. No holdings changed; only the boundary. The interpolation correctly refuses to extrapolate, and the reported temperature is nevertheless quoted to two decimals in most investor materials.

Panel (C). A carbon beta fitted at (, apparently strong) is () on an independent sample drawn from a no-premium regime - a drift of , with a sign flip. A carbon beta is a regime-conditional statistic; using it as a hedge ratio without a regime model is using yesterday’s map.


4. Failure Modes & First-Principles Breakdowns

  1. Greenwashing = data-quality failure, not an estimator failure. Definitional axes (boundary, rater, vintage) swing the number more than any modelling refinement (§2.1). Fix the disclosure - pin the boundary, the rater, the vintage and the weights - before touching the model. Cross-link: this is the same discipline as purged cross-validation and point-in-time features in Backtest Hygiene.
  2. Look-ahead bias from vendor restatements. ESG history is revised retroactively; a signal backtested on as-of-today history is not a backtest. Require point-in-time vintages and archive the as-of score with every signal.
  3. Aggregating raters to “fix” divergence. Because measurement divergence is and includes a correlated rater (halo) effect, a simple average of raters reduces but does not remove the bias - and it destroys the interpretability of the score. Report the rater and the dispersion.
  4. Confusing the preference premium with the risk premium. A greenium in expected returns (investor preferences) and a brown risk premium (transition-risk compensation) coexist; a strategy that assumes one only will be wrong about the other’s sign (04 · §2.3).
  5. Using a scenario count as a confidence level. The ceiling is a hard limit; a ” climate VaR” from six scenarios is the worst narrative relabelled (03 · §4.3).
  6. Double-counting transition and physical risk. They are anti-correlated by scenario design; summing independent stresses overstates the total (02 · §4.6).
  7. Reporting a point on a curve. Stranding (), physical damage () and pass-through () are all curves or ranges misreported as points. Publish the sensitivity, not just the central number.
  8. Governance: the number used for marketing is the number used for risk. If the same metric drives both a fund’s label and its limit, the incentive to choose the favourable boundary is structural. Separate the disclosure metric from the risk metric, and fix both in policy.

5. References

  • Berg, F., Kölbel, J.F. & Rigobon, R. - Aggregate Confusion: The Divergence of ESG Ratings, Review of Finance 26(6):1315–1344 (2022)
  • Berg, F., Fabisik, K. & Sautner, Z. - Rewriting History II: The (Un)Predictable Past of ESG Ratings (ECGI Finance Working Paper 708/2020)
  • IOSCO - Final Report on ESG Ratings and Data Products Providers (2021) and the Statement on Sustainability Disclosure
  • BCBS - *Climate-related Financial Risks
  • Bolton, P. & Kacperczyk, M. (2021) and Pástor, Ľ., Stambaugh, R.F. & Taylor, L.A. (2021, 2022)
  • Kupiec, P., Techniques for Verifying the Accuracy of Risk Measurement Models, J. Derivatives 3(2) (1995)
  • López de Prado, M., Advances in Financial Machine Learning (Wiley, 2018)

6. Connected Graph Bridges