Nature markets turn ecological complexity into financial instruments. Biodiversity units, carbon credits, natural capital accounts, ecosystem service payments — each one takes something that resists summary and renders it in terms a balance sheet can hold. The appeal is obvious. If nature can be measured, it can be priced. If it can be priced, money will flow toward it. And money, in this framing, is what was missing.

The trouble is not that measurement is useless. It is that what gets measured is chosen for convenience and credibility, not for completeness. Monitoring, reporting and verification — the MRV layer that gives nature markets their scientific authority — must produce numbers that are auditable, repeatable, and comparable across sites. That is a reasonable demand if you are designing a financial market. It is a much less reasonable demand if you are trying to understand what is happening in a landscape. Ecology does not organise itself around auditable units. The metrics that survive the journey into a trading framework are the ones that were tractable enough to standardise, which is not the same as the ones that matter most. Information leaks out at every stage of compression. What arrives at the other end — a biodiversity unit, a credit, a score — is a proxy, and the distance between the proxy and the thing it claims to represent is rarely examined once the market is running. This is proxy capture at the scale of an entire emerging industry. The number becomes the point. Whether the number tracks the ecology becomes someone else’s problem, or no one’s.

That would be enough to warrant caution. But there are two further effects that receive even less attention.

The first is economic. Nature markets introduce new financial dependencies into landscapes that were already fragile. A farm that enters a biodiversity net gain scheme or a carbon payment programme becomes reliant on the continued existence of that market, the continued flow of buyers, the continued political will to enforce the obligation. These are not stable conditions. Environmental markets are policy-dependent, politically contested, and structurally young. The Dasgupta Review made the case for valuing nature in economic terms, but valuation is not the same as market creation, and the stability assumptions built into market design may not hold in the places where the ecological work is being done. If a carbon market contracts or a BNG obligation is weakened, the farm that restructured around it does not simply revert. It has taken on new costs, new contracts, new operational patterns. The resilience of the landscape — financial, social, ecological — may have decreased, not increased, even while the metrics were green. This is the pattern described in overoptimisation: the system narrows around what is rewarded, shedding the unmeasured capacity that was keeping it stable.

The second effect is behavioural. Markets shape how people think about the thing being traded. Once nature is legible as a revenue stream, decisions about land use begin to run through a financial logic that was not there before. This is not automatically harmful, but it changes what counts as a good reason to do something. A farmer who maintained a hedgerow because it was part of how the farm worked now maintains it because it generates credits. The action is the same. The reasoning underneath it has shifted, and with it the relationship between the person and the land. When the incentive changes or disappears, the reasoning that would have sustained the action independently may no longer be there. We do not yet know how this plays out at scale, because the markets are too new. But the pattern is familiar from other domains where productive collapse eventually surfaced: the system performs well by its own measures while quietly losing the thing it was meant to protect.

None of this means nature markets are worthless. Some version of channelling private finance toward ecological recovery is probably necessary, given the scale of public funding constraints. The question is whether the current generation of instruments is being examined seriously enough — not just for scientific credibility, which is where most scrutiny falls, but for systemic side effects in the economies, behaviours, and ecologies they touch. At present, the market rewards people who can make the instruments work within the existing frame. It does not reward people who ask whether the frame is adequate. That asymmetry is itself a signal worth reading.

  • Proxy capture — Nature markets are a live example of Goodhart’s Law operating at industry scale: the metric becomes the target and the ecology drifts out of view.
  • Overoptimisation — The narrowing to what is measurable and tradeable mirrors the general pattern of shedding unmeasured capacity for short-term performance.
  • Productive collapse — The risk is not that nature markets fail visibly but that they succeed on their own terms while the underlying ecology and landscape resilience quietly degrade.
  • Observation and reasoning — The tension between site-level ecological observation and the standardised reasoning required by financial instruments runs through the whole MRV question.
  • Finite and infinite games — Nature markets use the language of infinite purpose (ecological recovery, biodiversity, natural capital) while operating with finite market logic underneath.