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Hydrogen Sulfide Review

Wastewater influent is commonly tested for sulfate (SO4-2) to asses its potential for odor formation and the treatability of sludge. Hydrogen sulfide results from the reduction of sulfate to hydrogen sulfide gas by bacteria under anaerobic conditions as shown in Equation 1.

Equation 1: Sulfate Reduction

h2s-1

Hydrogen sulfide is the most common (and most easily identified by the public) odorous gas found in sanitary sewers and wastewater treatment systems. This corrosive, toxic gas is soluble in wastewater and has a characteristic rotten-egg odor at low concentrations. H2S is colorless, flammable, and explosive. It paralyzes the respiratory system and lessens the sense of smell as it increases in concentration. The specific gravity of H2S is 1.19 so it concentrates down low though it can be at a higher elevation if the air is hot and humid. The effects of hydrogen sulfide at various concentrations is shown in Table 1.

Table 1: Effects of Hydrogen Sulfide

Concentration, mg/L

Effects/Standards

5

Easily detected odor

10

Permissible Exposure Limit (PEL), slight eye irritation

15

Short-term exposure limit

50

Ceiling limit, maximum concentration of exposure at any time during a work shift

100

Coughing, eye irritation, loss of sense of smell after 2 to 15 minutes

300—500

Dizziness, nausea, bronchitis, pulmonary edema; also immediately dangerous to life and health (IDLH) conditions exist at 300 mg/L

600—700

Rapid unconsciousness, cessation of respiration followed by death

1,000—2,000

Unconsciousness at once, death in a few minutes

40,000

Explosive range approximately 4 to 44% (40,000 to
440,000 mg/L)

The concentration of oxidized sulfur compounds in the influent to an anaerobic digester is important, as high concentrations can have a negative effect on anaerobic treatment. Sulfate-reducing bacteria compete with the methanogenic bacteria for COD and thus can decrease the amount of methane gas production so critical to a cogeneration project. While low concentrations of sulfide (less than 20 mg/L) are needed for optimal methanogenic activity, higher concentrations can be toxic as previously stated.

Because un-ionized H2S is considered more toxic than ionized sulfide, pH is important in determining H2S toxicity. The degree of H2S toxicity is also complicated by the type of anaerobic biomass present (granular versus dispersed), the particular methanogenic population, and the feed COD/SO4-2 ratio. With higher COD concentrations, more methane gas is produced to dilute the H2S and transfer more H2S to the gas phase.

Hydrogen sulfide exists in aqueous solution as either the hydrogen sulfide gas (H2S), the ion (HS‾), or the sulfide ion (S2-), depending on the pH of the solution. At a pH of approximately 9, more than 99% of the sulfide dissolved in wastewater occurs in the form of the non-odorous hydrosulfide ion (HS‾). Therefore, odorous amounts of hydrogen sulfide gas will not be released if a pH above 8 is maintained. Below this pH value, hydrogen sulfide gas is released from the wastewater. In anaerobic digesters the optimal pH is between 6.5 and 7.5, a range that allows the release of H2S of up to almost 70 percent as shown in Figure 1.

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Figure 1: Hydrogen Sulfide vs. pH

h2s

The Sulfur Cycle

The mechanisms by which sulfates are converted to hydrogen sulfide are shown graphically in Figure 2.

Figure 2: The Sulfur Cycle

sulfur_cycle_sm

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