Under the proposed exposure-only model, suppose a unit of infectious exposure has the same probability of producing an ascertained onset in either cohort. Conditional on the total of onsets, the allocation is a binomial distribution with younger-cohort probability
Thus the expected cohort counts are and , respectively, whereas the observed allocation is reversed. The Pearson chi-squared goodness-of-fit test gives
With one degree of freedom its approximate p-value is ; the exact upper binomial distribution tail is approximately . These are exceptionally incompatible with proportional allocation. Equivalently, the observed onset count per exposure unit is four times larger in the younger cohort:
Under the stated common-risk exposure model, the observed counts are not consistent with the early exposure period as their sole explanation. This does not identify the source of the discrepancy, or prove a particular later exposure caused it. The inference also requires comparable ascertainment and a common fraction of exposure-derived cases manifesting by the observation date. Age-independent incubation periods alone do not guarantee that fraction when the two cohorts' exposure profiles within the decade differ; decade totals omit that timing information. The reasoning concerns the hypothetical historical BSE/vCJD model, not an estimate of current disease risk.
Two distinct issues are:
Thus the comparison must account for uncertainty in both its exposure denominator and its observed-disease numerator; a very small sampling p-value does not remove those model uncertainties.
Using the upper stated scrapie-test-positive fraction, its value among slaughtered sheep is . The stipulated conditional BSE positivity then gives marginal test-positive probability
because the other stratum contributes zero. If the sample consists of independently tested, representative animals, the count has a binomial distribution with parameters . Therefore
The two results are
The Poisson distribution approximation uses mean counts and , respectively. If fewer than 2000 animals belong to the test-positive stratum, these probabilities of finding nothing are higher; the calculation at 2000 is not a guaranteed detection probability.
There is also a sampling-design distinction. If exactly positive animals in a fixed annual population of are known and the sample is without replacement, use the hypergeometric distribution instead:
The given expected prevalence does not assert an exactly fixed , so the independent prevalence model is the natural interpretation of the requested calculation.
Surveillance should be calibrated to the prevalence of concern, , rather than only to the higher rate used in the preceding calculation. With representative independent tests,
Thus 50,000 tests give only about 22% detection probability at the concerning rate; a negative survey is quite likely, with probability about . It costs million. Even tests, costing million, give about detection probability at .
For a target detection probability, solve
The cost is about million. The zero-event binomial upper confidence bound gives the same perspective: after zero positives in tests, the one-sided upper bound is
roughly one in , well above the concerning rate. A 50,000-animal survey is insufficient to rule out that prevalence with high confidence. A practical design should specify its desired detection probability, diagnostic sensitivity, representativeness and dependence between sampled animals. Targeting the higher-risk scrapie-positive stratum may improve efficiency if testing that stratum is feasible and its contribution to the slaughter population is estimated; its result then needs the appropriate population weighting. A cost alone does not establish adequate surveillance.

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