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An organic substance may also contain nitrogen, sulfur, phosphorus, halogens and, in some cases, metals or other elements. “Organic” does not mean “made of only carbon, hydrogen and oxygen”. Detection generally requires converting a covalently bound element into a species that an appropriate inorganic test can recognize.

A historically available general method is the sodium fusion test. Fusion converts suitable nitrogen-containing material into cyanide, sulfur into sulfide, and chlorine-, bromine- or iodine-containing material into the corresponding soluble halides. The cooled reaction material is worked up to an aqueous extract, with separate portions reserved for separate tests. The transformations are analytical conversion principles, not claims that every nitrogen or sulfur compound must give quantitative recovery under any fusion conditions. Blanks and a known positive material are essential when a negative result is to be interpreted.^[ref]

For nitrogen, a suitable cyanide-containing extract is treated with a fresh iron(II) reagent and then brought through the appropriate oxidation and acidification sequence to obtain Prussian blue. Formation of ferrocyanide is represented byThe eventual ferric ferrocyanide material provides the blue observation. It is not sufficient simply to add any iron salt and assume that a positive blue must appear. Another classical principle converts nitrogen in suitable organic materials into Ammonia by heating with alkaline reagents, then recognizes the ammonia in a receiver. That test has substrate-dependent limitations and is not a universal replacement for complete nitrogen analysis. A later specialized nitrogen-digestion protocol must not be silently attributed to 1865.

For sulfur, a sulfide-containing alkaline extract can give black lead sulfide with a suitably introduced lead reagent:The strongly acidic form of the reagent conditions changes the available sulfide, so conditions must be controlled. Oxidizing the material to sulfate and identifying a persistent barium sulfate precipitate supplies another principle, using sulfur-free reagents and excluding pre-existing sulfate contamination. If nitrogen and sulfur occur together, thiocyanate formation can alter a fusion test; failure of the expected cyanide reaction is not conclusive evidence that nitrogen is absent.

For chlorine, bromine and iodine, remove interfering cyanide and sulfide by an appropriate controlled treatment of a separate extract portion, then use silver nitrate under suitable nitric-acid conditions. The precipitates are ordinarily white silver chloride, cream silver bromide and yellow silver iodide. Their differing behaviour with aqueous Ammonia provides corroboration: chloride dissolves relatively readily, bromide requires stronger conditions, and iodide is resistant. Do not use hydrochloric acid to prepare the portion in which original chloride is being sought. Fluorine requires a different recognition method: soluble silver fluoride means this precipitation scheme does not provide an equivalent fluoride test.

For phosphorus, oxidize a suitable portion to phosphate, then apply a phosphate test such as yellow ammonium phosphomolybdate formation under the proper acidic conditions. Arsenic species and other interferences must be excluded when relevant. Mineral ash can reveal metal constituents through their specific precipitation or flame reactions, but oxidation during ashing can change their original chemical form. Absence of a visible ash does not prove absence of every metallic or otherwise volatile element.

A positive result identifies an element or an operationally generated ion; it does not establish which functional group contained it in the original molecule. Conversely, an incomplete conversion can give a false negative. This is why the three-element premise used in the preceding combustion calculation should be checked rather than accepted merely because a substance is described as organic.

Ordinary air contains water vapour, carbon dioxide, variable trace gases and suspended particles in addition to nitrogen and oxygen. Which traces are detected depends on location, sampling volume and test sensitivity. A negative small-sample test is not proof of complete absence.

Water vapour is shown by condensation on a sufficiently cold surface or by the colour change of a suitable dry indicator: white anhydrous copper(II) sulfate becomes blue on hydration. Passing a known air stream through a drying tube and observing a controlled mass increase gives a more quantitative principle, provided other absorbable vapours are excluded.

Carbon dioxide gives a calcium carbonate turbidity when a suitable air sample is passed into clear limewater:Large excess of carbon dioxide can redissolve the deposit as dissolved bicarbonate species, so excessive exposure can obscure the initial result. Absorption into an alkaline solution, followed by an appropriate carbonate test, concentrates the trace component.

Ammonia and ammonium-bearing particles may be collected by an acid wash and examined after suitable neutralization or liberation of the Ammonia. Nessler's reagent supplies a sensitive colour test, with a blank to exclude contaminated reagents. Simple moist litmus is much less sensitive. Acidic gases and nitrogen oxides may instead be collected in appropriate wash solutions and examined with tests for the resulting anions; their identity cannot be inferred from acidity alone.

Near relevant sources, hydrogen sulfide can blacken moist lead acetate paper by forming lead sulfide. Ozone-sensitive starch–iodide paper can indicate an oxidizing trace constituent through liberation of iodine, but other oxidants can give the same response: the historical observation is not a specific proof of ozone. Dust and droplets can be collected on a filter or surface and examined by microscopy, with chemical tests applied to separated material as needed.

Modern analysis also recognizes argon and other noble gases, as well as many low-concentration pollutants, using instrumental separation and spectroscopy. Their modern recognition should not be silently included among discoveries available to an 1865 candidate. The useful answer pairs each proposed constituent with a collection method, a specific reaction or observation, and the limits of that test.

Examine separate, properly collected aliquots for lead, nitrate and organic matter, and interpret the results with the source and sampling conditions. These are three different analytical questions. No sample observations are supplied, so no actual contaminant concentration or positive finding can be assigned.

For lead, preserve a representative portion in clean apparatus, avoiding lead-containing fittings or contaminated reagents. Distinguish dissolved material from suspended or particulate material if that distinction is wanted; filtering at the outset otherwise changes what is being measured. Historically, a suitable concentration step followed by hydrogen sulfide gives dark lead sulfide:A separate confirmation uses potassium iodide to give yellow lead(II) iodide. Its characteristic recrystallization behaviour on heating and cooling a suitable aqueous preparation is useful supporting evidence. Dark sulfide alone is insufficient, because other metals give dark precipitates. Establish a reagent blank, compare with known material, and record the sensitivity; a negative visual test cannot exclude all low-level lead.

The principal circumstance is contact with lead-bearing pipes, cisterns, solder or other plumbing materials. Stagnation, acidity and water chemistry influence release; newly exposed metal and disturbed corrosion deposits can also matter. Low hardness does not by itself predict a universally safe or unsafe supply: pH, alkalinity, dissolved gases, protective films and the actual materials must be considered together. Current CDC guidance confirms the importance of corrosion of plumbing and of contact time and water chemistry.^[ref]

For nitrate, the historical brown-ring test uses fresh iron(II) sulfate and a carefully formed strongly acidic interface. Reduction of nitrate produces nitrogen monoxide, which forms the brown nitrosyl complex with excess iron reagent:The observable ring is associated with the resulting iron–nitrosyl species, not with free nitrate having a brown colour. Use nitrate-free reagents and, if necessary, a suitably concentrated sample. Nitrite can interfere and must be distinguished independently; adding nitric acid during an earlier preparation would invalidate this test for nitrate originally in the water. Strong acid and heating can disturb the ring, so the observation depends on the procedure as well as the constituents.

Nitrate may occur after oxidation of nitrogenous wastes in soil, from manure, sewage, cesspit leakage, fertilizer leaching or natural nitrogen cycling. It can persist after much readily oxidizable organic material has disappeared. Its presence alone therefore neither proves recent sewage entry nor identifies a particular source. Current EPA source-water guidance includes agricultural runoff, septic leakage, sewage and atmospheric inputs among nitrate sources.^[ref]

For organic matter, inspect colour, turbidity and sediment, and examine a suitable concentrate by microscopy. Evaporating a measured portion and examining the residue for charring or change on ignition supplies further evidence, but loss on heating is not specific: salts and retained water can also change. A controlled potassium permanganate consumption experiment compares a sample with a reagent blank under stated acidity, reaction time and temperature. It detects oxidizable material, which can include inorganic reducing substances, and may incompletely oxidize organic material. The amount consumed is consequently an operational observation, not a universal conversion into a mass of “sewage”.

Sources include decaying vegetation, peat and soil-derived material as well as animal wastes, sewage and some industrial discharges. Natural organic colour is not synonymous with sewage, and clear water may contain dissolved organic contaminants or microorganisms. A modern safety assessment therefore adds validated microbiological and chemical measurements appropriate to the source; these historical qualitative tests alone cannot establish potability.^[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.