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The soluble silver–cyanide complex central to the two-cyanides-per-silver ratio in alkaline silver nitrate titration.

Volumetric analysis determines an amount of substance from the measured volume of a reagent of known strength that reacts with it in a known proportion. A measured aliquot is placed in a suitable vessel, the standard solution is delivered from a burette, and the volume required to reach the chosen titration endpoint is read. A pipette measures the aliquot; a volumetric flask prepares or dilutes the standard solution.

For a reaction $aA+bB⟶\text{products}$, if the concentration of the titrant $B$ is $c_B$ and the corrected volume delivered is $V_B$, thenWith volume in litres and concentration in moles per litre, the answer is an amount in moles. The corresponding mass is $m_A=M_A{n}_A$, using the appropriate molar mass. For an unknown solution of aliquot volume $V_A$,These are modern symbols for the same proportional reasoning that a nineteenth-century analyst could express with equivalent weights and a specified standard solution.

A suitable reaction is sufficiently rapid, complete and selective, with a recognisable endpoint. In an acid-base titration, an indicator can change colour near neutralization; other reactions use precipitation, redox or a colour intrinsic to a reagent. The observed titration endpoint must represent the required equivalence point closely enough. The reagent's nominal preparation alone is insufficient if its concentration changes in storage; standardisation of a solution, a reagent blank where needed, and correct reading of the meniscus control systematic error. A titration measures the intended analyte only insofar as interfering substances have been excluded or accounted for.

Confirm hydrogen cyanide by chemical tests on a suitable separated fraction, then estimate its amount with a defined quantitative assay. Here “hydrocyanic acid” means $\mathrm{HCN}$ in water, also historically called prussic acid. Smelling or tasting is not an analytical test: hydrogen cyanide is acutely poisonous, and its characteristic odour is not reliably perceived.^[ref]

A coloured or complex liquid can mask the tests or contain interfering ions. Historically, controlled distillation separated volatile hydrogen cyanide from many nonvolatile constituents; a receiving solution captures the analyte. In a modern analytical apparatus, the closed transfer system includes a condenser and an alkaline gas absorber. The receiver converts volatile hydrogen cyanide into less volatile cyanide:The measured fraction must be defined: free hydrogen cyanide in the original liquid is not automatically identical to “total cyanide” released from complexes by a more aggressive preparation. A blank, a known positive control and recovery checks help distinguish a negative sample from failed separation or reagent failure.^[ref]

For the historical iron test, make a separate test portion alkaline, introduce fresh iron(II) salt together with an iron(III) source, and finally acidify as specified by the historical procedure. Cyanide first forms ferrocyanide with iron(II); iron(III) then gives the characteristic Prussian blue precipitate. Idealized balances explaining the recognition chemistry areReal Prussian blue can be hydrated and nonstoichiometric; the second chemical equation is a useful idealization. The acid stage also removes obscuring iron hydroxide precipitates. These steps explain the old mixed iron-salt test, rather than assuming that cyanide simply reacts directly with any iron salt to give blue material.^[ref]

A second aliquot can be examined with silver nitrate. Silver cyanide is white, but whiteness alone is not specific because silver chloride and other precipitates can interfere:For a purified aliquot, precipitate the cyanide quantitatively with silver nitrate, separate the silver cyanide, wash it free of soluble salts, dry it to constant mass and weigh it. The precipitation conditions must avoid losses as volatile hydrogen cyanide and dissolution as dicyanoargentate; interfering precipitates must be excluded. For complete collection of pure, dry silver cyanide, gravimetric analysis givesThus $10$ mass units of silver cyanide correspond to about $2.02$ mass units of hydrogen cyanide. The 1867 pharmacopoeial check was $10$ grains of dry silver cyanide from $100$ grains of the diluted acid, corresponding approximately to its stated $2\%$ strength by mass.^[ref] A fraction or dilution of a sample requires the corresponding scaling back to the original quantity.

Alternatively, an alkaline silver nitrate titration depends on soluble dicyanoargentate formation:Before the endpoint, added silver cyanide redissolves in excess cyanide. In the classical version, the first persistent turbidity marks the end of this clear-solution stage. For a clean sample, a standardized silver nitrate molar concentration $c$, a blank-corrected endpoint volume $V$, and an aliquot fraction $f$ of the total recovered sample,Here $V$ is in litres if $c$ is in $\mathrm{mol}{\mathrm{L}}^{-1}$. Divide by the original sample mass for a mass fraction, or by its original volume for a mass concentration. No numerical sample amount is supplied, so no particular measured concentration can be inferred.

Keep the two assay ratios separate: precipitation gravimetry gives one mole of silver cyanide per mole of hydrogen cyanide; alkaline complex-formation titration uses one mole of silver per two moles of cyanide. A modern version of the latter uses a rhodanine indicator and a blank, as in EPA Method 9014; that indicator procedure is a modern comparison, not a detail assigned to 1867.^[ref]

The nineteenth-century phrase “impure air” mixed several different mechanisms. Irritant smoke and dust can damage the respiratory system; toxic gases can poison without causing an infection; crowded, poorly ventilated rooms can increase exposure to infectious material. The historical miasma theory treated foul emanations much more broadly as generators of disease. In particular, the smell of sewage does not itself establish the cause of typhoid fever, cholera or malaria.

For the first part, important real consequences include the following:

For the second part, ordinary outdoor air already contains nitrogen, oxygen, a small amount of carbon dioxide, and variable water vapour. Their presence alone is not evidence of pollution. In a smoky industrial town, soot, mineral dust, products of fuel combustion and sulfur dioxide would be particularly relevant. In occupied rooms, expired carbon dioxide, water vapour and suspended biological material increase unless removed. Decomposing wastes may contribute Ammonia, hydrogen sulfide and other volatile products. The actual mixture depends on sources, ventilation and weather.

For the third part, begin with a defined sampling site and time, record occupancy or industrial activity, and compare with a suitable reference. A volume of air, not simply an unrecorded sniff or a discoloured paper, is the basis of quantitative comparison. Methods available by 1867 include:

The chemical equations underlying two of these qualitative tests areHere the precipitates are barium carbonate and lead sulfide. For the baryta absorption method, in an ideal, fully captured sample with no interfering acid gases, the difference between blank and sample acid requirements satisfieswhere $c_{{\mathrm{H}}^{+}}$ is the amount concentration of titratable acid equivalents and the volumes refer to titration of the entire corresponding absorbent portions; any aliquot requires its scale factor. The factor two follows from the two acid equivalents neutralized per mole of barium hydroxide. This calculation assumes that the barium carbonate precipitate is excluded from the residual-base determination; dissolving it again with the titrant would invalidate the inference.

Odour, visible smoke and room stuffiness are useful prompts to investigate, but no single smell, carbon dioxide value, microscopic field or chemical colour test establishes that air is free of harmful impurities. Specify which material was measured and which uncertainty remains.

A solution whose concentration has been established for use as a measurement reference, for example in titration. It can be prepared from a primary standard or established by titrant standardization. The word “standard” does not imply one universal concentration.