Original question.
How would you examine a sample of water for (1) Lead, (2) Nitrates, (3) Organic matter ? Under what circumstances is water liable to contain each of these ?
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]

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