Abstract
Hydrogen sulfide in water stabilized with or absorbed from air in an alkaline mixture of zinc acetate and EDTA was treated with 4-N,N-diethylaminoaniline and iron(III) in sulfuric acid medium and the absorbance of ethylene blue was measured at 670 nm after 5 min. The molar absorptivity was found to be 9.42 × 105 l mol−1 cm−1. The ethylene blue dye could be preconcentrated by solid-phase extraction on a CN sorbent and eluted by potassium bromide solution in water–methanol leading to an enrichment factor of at least 50. Coloured samples were subjected to clean-up by using Lichrolut EN and the colourless eluate was treated for colour development. Rectilinear calibration graphs were obtained over the range 10–800 μg l−1 sulfide (r = 0.9997) without solid-phase extraction, and 1–100 μg l−1 sulfide (r = 0.9989) after solid-phase extraction of the dye. The limits of detection were 5 μg l−1 and 0.2 μg l−1 sulfide without and after solid-phase extraction, respectively. The interference of up to 100 mg l−1 thiols, 50 mg l−1 sulfite and 10 mg l−1 thiosulfate could be avoided by their masking with N-ethylmaleimide. Up to 10 mg l−1 fluoride and 100 mg l−1 thiocyanate did not cause any interference. Interference of up to 100 mg l−1 fluoride was avoided by masking with zirconyl nitrate. The method has been validated by analysing spiked river water samples, when the average recovery was 99% (range 96–104%) with an RSD of 3% (range 2–4%). Sulfide has been detected in many river waters at low μg l−1 levels.
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