Abstract: Sulfide in water is a critical indicator of pollution and anaerobic conditions. The methylene blue spectrophotometric method is the most widely used technique for its determination due to its sensitivity and reliability. This article provides a concise overview of the principle, standard procedure, key operational steps, and main factors influencing the accuracy of this method.
1. Introduction
Sulfide is commonly found in groundwater, industrial wastewater, and sediments. It is primarily produced by the reduction of sulfate by bacteria under anaerobic conditions or the decomposition of organic matter. Even at low concentrations, hydrogen sulfide (H?S) imparts a characteristic unpleasant odor and poses significant toxicity to aquatic life and humans . Therefore, accurate determination of sulfide is essential for environmental monitoring and water quality assessment.
2. Principle of the Method
The methylene blue spectrophotometric method is based on the reaction between sulfide and a color-forming reagent. Under acidic conditions and in the presence of N,N-dimethyl-p-phenylenediamine and ferric ammonium sulfate (or ferric chloride), hydrogen sulfide (H?S) generated from the sample reacts to form methylene blue, a stable blue-colored complex . The intensity of this blue color is proportional to the concentration of sulfide in the water sample and is measured spectrophotometrically at a wavelength of 665 nm.
3. Experimental Procedure
3.1 Sample Collection and Preservation
Due to the ease of oxidation and volatility of sulfide, proper sample handling is crucial. Samples should be collected with minimal aeration and preserved immediately by adding zinc acetate and sodium hydroxide to form a zinc sulfide (ZnS) precipitate. Samples are stored at 4°C in the dark and analyzed within 24 hours .
3.2 Sample Pretreatment (Separation)
To eliminate interferences from color, turbidity, or reducing substances, a pretreatment step is often necessary. The most common method is the acidification-purge-and-trap (or distillation) technique. The preserved sample is acidified (e.g., with phosphoric acid) to convert all sulfides to H?S gas. The H?S is then purged with an inert gas (like nitrogen, purity ≥99.999%) or steam and absorbed into a sodium hydroxide solution .
3.3 Color Development and Measurement
The absorbing solution containing the sulfide is transferred to a colorimetric tube. N,N-dimethyl-p-phenylenediamine solution and ferric ammonium sulfate solution are added sequentially. After a reaction time (typically 10-15 minutes), the solution is diluted to volume. The absorbance is measured at 665 nm against a reagent blank . The concentration is determined by comparing the absorbance to a calibration curve prepared from standard sulfide solutions.

