In April 2026, a 75-year-old wine-grape grower from California paid about $38,000 to walk into a forest in Gabon and shoot a yellow-backed duiker, a shy antelope that weighs less than a large dog and that almost no one outside a record book has heard of. He never got the antelope. A herd of five elephants, not the animals he had paid to pursue, reached him first.
The story moved quickly, and the version that moved was the obvious one: a wealthy man, an obscure little animal, a violent and ironic end. That reading is satisfying and almost entirely uninformative. The interesting question is not what the elephants did to Ernie Dosio. It is what his $38,000 were for. Not meat; a duiker yields a few kilograms. Not the animal as such; you can watch a yellow-backed duiker, alive, for the price of a park permit. What he was buying was the act, and more exactly the scarcity of the act: the right to have taken a species few people take, in a place few people go, at a cost few people can absorb.
Strip away the forest and the rifle and trophy hunting resolves into a market with an unusual product. The thing changing hands is not the carcass. It is a position. Once you read the product as position rather than protein, the price structure of the whole industry begins to make a different kind of sense, including the parts that look, from outside, like pathology.
Begin with price. If trophies were priced like meat or hide, the largest and most plentiful animals would cost the most per usable kilogram. They do not. Palazy and colleagues, in a 2012 analysis of trophy prices across 202 ungulate species, found that, holding body mass and location constant, rarer species command higher prices, with a rarity coefficient that is both positive and statistically significant. Scarcity carries a premium that has nothing to do with how much animal you take home. The same authors, a year earlier, had looked at ten trophy-hunted cat species and found something sharper: as a species was moved into a more threatened category, hunting effort rose rather than fell. Prescott and co-authors caught the signal again in 2012, with prices for African antelope climbing as a species’ conservation status worsened. The figures come with a caveat the literature states plainly, raised most directly by Sarasa in 2013, that many are advertised prices from outfitter catalogues rather than cleared transactions. But the pattern is too consistent, and too well matched by the public prices fetched at auction for permits to hunt single rare animals, such as the black-rhino permit a US club sold for $350,000 in 2014, to wave away. The market pays for rarity, and it pays more as the animal grows rarer.
That is odd behaviour for a consumer, until you ask what the purchase is meant to say. The most economical explanation on offer comes from evolutionary anthropology rather than economics. Darimont, Codding and Hawkes took the puzzle directly in 2017: people hunt animals they cannot eat, at great expense, and then display the proof. Hunger does not account for it, and neither does sport in any ordinary sense. What survives is signalling. The hunt is costly by design, and the cost is the message. The lead author put it in terms an economist would recognise at once, that it works like a luxury car, a visible demonstration that you can afford to burn resources others cannot, except that here the resource burned is an animal’s life. The trophy is not a souvenir. It is a receipt.
And like any market in receipts, this one has built the machinery to make them legible. The Safari Club International record book scores animals on dozens of standardised measurements and ranks the results, handing out medals and tiers with names like Inner Circle and the Africa Big Five at annual conventions. Two rival record books, one American and one African, keep competing ledgers. The detail that matters is not which animal scores highest but that scoring exists at all. A market does not maintain three parallel ranking systems for an object unless rank is the object. The animal is the input. The position in the book is the good.
Priced scarcity, a status motive, and a formal ranking infrastructure: together these are about as clean a description of a positional market as any consumer category provides. It is, in fact, a better-documented one than the market I have been circling throughout this series, because trophy prices and rankings are published while rhino horn trades in the dark. They are nonetheless the same market in different clothes.
The mechanism underneath both has a name in the ecology literature, the anthropogenic Allee effect: human valuation rises as a species grows scarce, so that price can climb faster than the animal vanishes, and rarity becomes self-reinforcing instead of self-correcting. Courchamp and colleagues, who named the effect in 2006, reached for the oldest example in economics, the gap between the price of water and the price of diamonds, and it was Palazy’s team that carried the same model straight into trophy hunting. A rhino’s horn and a record-book antelope are priced by the same logic. The authenticity problem travels with it. A captive-bred lion shot inside a fence sells for a fraction of a wild one, for the same reason a synthetic stone unsettles a diamond buyer and farmed horn unsettles a horn buyer: once the scarcity is manufactured, the signal it was meant to carry drains out of it. And both markets absorb the tools aimed at them. The shaming that followed Cecil the lion suppressed the public photograph without touching the private game that photograph advertised, the same pattern I traced in demand-reduction campaigns that end up marketing what they condemn. The only structural difference between the legal version and the illegal one is who collects the money: a state and its communities, or a syndicate.
That difference is not small, and it is the point at which the argument has to stop being tidy. Legal trophy hunting does fund conservation in places where little else would. Lindsey and colleagues put the hunting estate across sub-Saharan Africa at roughly 1.4 million square kilometres, more land than all the national parks combined, much of it too remote or too plain to draw a single photographic tourist. In Namibia, whose communal conservancy model is the strongest case anyone has assembled, hunting produced around N$292 million for those conservancies over the 11 years to 2024, well above what photographic tourism brought to the same land and close to two-thirds of the communities’ wildlife income, according to figures the country’s environment ministry reported to parliament in 2026. That is real money reaching real people who would otherwise have every reason to treat wildlife as vermin.
But the same paragraph has to carry the other figures. In Cameroon, Mayaka found under 3% of trophy revenue reaching local communities, the rest taken by operators and the state. The headline industry numbers, the figures in the hundreds of millions, come largely from the industry itself, and a reanalysis by Economists at Large puts the true economic contribution lower by an order of magnitude in some countries. The counterfactuals are messy in both directions. Botswana’s 2014 hunting ban was followed by rising human-elephant conflict and collapsing community funds, which is much of why it was reversed in 2019; Kenya’s 1977 ban is routinely blamed for the country’s wildlife collapse, yet Ogutu and colleagues, working through four decades of census data, assign most of that decline to livestock and land conversion rather than to the ban. The honest summary is that hunting can finance conservation and often does not, and that whether it does is a question about governance, about who captures the rent, not a question about hunting in the abstract. The Western debate, run as a referendum on whether trophy hunting is good or evil, is aimed at the wrong variable.
There is a deeper problem still, one that neither side of that referendum tends to raise, because it follows not from a moral stance but from taking the positional reading seriously. If demand is built on rarity, then conservation that works is conservation that erodes its own funding. Suppose the money does exactly what its defenders claim. Populations recover, the species grows less scarce, and the rarity premium, the very thing that made the animal worth a luxury price, starts to fall. Revenue per hunt declines. The mechanism that paid for the recovery is weakened by the recovery. A trophy-hunting model that succeeds as conservation is, in the same motion, undermining itself as a market. This is not a paradox for its own sake; it is a claim you could test. Take the Namibian conservancy data and ask whether per-hunt revenue, adjusted for inflation and for the mix of species on offer, falls as wildlife densities rise. The same trap is folded into the rhino-horn market from the other end: any conservation success large enough to make rhinos common again would, by the identical logic, collapse the scarcity premium on which a legal-trade solution would lean. Both markets price the animal’s endangerment as a feature. Both are worth the most to the people inside them at the moment the animal is worth the least to everyone else.
All of this rests, for now, on evidence that can only carry us so far. The rarity premium is read off advertised prices; the status motive is inferred from record books and from what hunters say they would pay in surveys. Field prices tangle rarity together with body size, charisma, legality, and a dozen other things that move in lockstep, and no amount of patient regression fully separates them. To know whether the scarcity signal itself shifts willingness to pay, you have to hold the animal fixed and vary only the story told about it: that it is rare, that it is forbidden, that owning it confers status, or nothing at all. That is an experiment rather than a field survey, and it is the one I am building. The thread through this entire series has been that wildlife policy keeps failing because it misreads the story the market tells itself. The trophy makes that story unusually easy to read. It says, in a language of medals and measurements and five-figure invoices, that what is being bought is scarcity, and it leaves us with the most uncomfortable line in conservation economics: that for the people who pay, the animal is never more valuable than just before it is gone.
References
Courchamp, F., Angulo, E., Rivalan, P., Hall, R. J., Signoret, L., Bull, L., & Meinard, Y. (2006). Rarity value and species extinction: The anthropogenic Allee effect. PLoS Biology, 4(12), e415.
Darimont, C. T., Codding, B. F., & Hawkes, K. (2017). Why men trophy hunt. Biology Letters, 13(3), 20160909.
Economists at Large. (2013). The $200 million question: How much does trophy hunting really contribute to African communities? A report for the African Lion Coalition. Melbourne: Economists at Large.
Lindsey, P. A., Roulet, P. A., & Romañach, S. S. (2007). Economic and conservation significance of the trophy hunting industry in sub-Saharan Africa. Biological Conservation, 134(4), 455–469.
Mayaka, T. B., Hendricks, T., Wesseler, J., & Prins, H. H. T. (2005). Improving the benefits of wildlife harvesting in Northern Cameroon: A co-management perspective. Ecological Economics, 54(1), 67–80.
Ogutu, J. O., Piepho, H.-P., Said, M. Y., et al. (2016). Extreme wildlife declines and concurrent increase in livestock numbers in Kenya: What are the causes? PLoS ONE, 11(9), e0163249.
Palazy, L., Bonenfant, C., Gaillard, J.-M., & Courchamp, F. (2011). Cat dilemma: Too protected to escape trophy hunting? PLoS ONE, 6(7), e22424.
Palazy, L., Bonenfant, C., Gaillard, J.-M., & Courchamp, F. (2012). Rarity, trophy hunting and ungulates. Animal Conservation, 15(1), 4–11.
Prescott, G. W., Johnson, P. J., Loveridge, A. J., & Macdonald, D. W. (2012). Does change in IUCN status affect demand for African bovid trophies? Animal Conservation, 15(3), 248–252.
Sarasa, M. (2013). Trophy hunting, size, rarity and willingness to pay: Inter-specific analyses of trophy prices require reliable specific data. Animal Biodiversity and Conservation, 36(2), 165–175.