Shared-blank covariance in carbon recovery
ID: shared-blank-covariance-in-carbon-recovery
Shared-blank covariance in carbon recovery is the statistical dependence between net-carbon results that subtract the same estimated background. Independent specimen measurements can become correlated through that common subtraction. The covariance matters when averaging results, comparing specimens or deciding how much effort to allocate to blank measurements.
Let Qi=Ti−B, with independent specimen totals Ti and a shared blank estimate independent of those totals. ThenHere uB is the standard uncertainty of the blank estimate. The added matrix term represents one shared random quantity, not a separate new blank error for each specimen. Common-reference covariance is explicitly retained in the GUM.[ref]
cov(Qi,Qj)=uB2(i=j),ΣQ=diag(uTi2)+uB211T.
For a weighted mean with ∑iwi=1,The specimen terms can decrease through averaging, but the shared blank term remains. With independent unequal specimen uncertainties, the minimum-variance weights remain proportional to 1/uTi2 under this particular common-additive model; the common term does not depend on the normalized weights.
Var(∑iwiQi)=∑iwi2uTi2+uB2.
A contrast behaves differently: Qi−Qj=Ti−Tj, so the same blank cancels exactly. This cancellation requires the identical additive correction on the same carbon basis. Different blank batches, collection durations or conversion factors need not cancel. Dividing each result by a different uncertain initial carbon inventory adds another measurement layer.
An original planning example chooses nT specimen-total measurements and nB independent blank measurements, with fixed total count N=nT+nB. If individual standard deviations are σT,σB, the net mean has varianceA continuous minimum at equal cost satisfies nT/nB=σT/σB. With stipulated N=12, σT=1 mg and σB=2 mg, four specimen measurements and eight blanks give variance 0.75mg2. Ten specimen measurements and two blanks give 2.1mg2. More specimen readings alone can therefore be a poor allocation. Blank-allocation design for carbon recovery also needs actual preparation costs and biological independence.
nTσT2+nBσB2.
The OECD carbon-dioxide evolution test measures gas production relative to inoculum blanks, but notes that endogenous activity with a test chemical may differ from the control.[ref]
Test No. 301: Ready Biodegradability by OECD. 1992 guideline, General principle §4; method 301 B §§1–3
Replication estimates random variation under the chosen background model. It cannot establish that the treated system's background is exactly additive. Preserve the experimental blank lineage and distinguish sampling uncertainty from a possible change in the background process. New to topics? Read the docs here!