SecondaryTreatment

Engineering

Nitrification

Biological oxidation of ammonia to nitrate. The critical process for meeting nitrogen discharge limits in secondary treatment.

Nitrification Biology

Nitrification is a two-step autotrophic process where ammonia-oxidizing bacteria (primarily Nitrosomonas) convert ammonium (NH₄⁺) to nitrite (NO₂⁻), and nitrite-oxidizing bacteria (primarily Nitrobacter) convert nitrite to nitrate (NO₃⁻).

Nitrifiers are slow-growing organisms with doubling times of 12–36 hours (compared to 2–6 hours for heterotrophic bacteria). This means nitrification is typically the rate-limiting biological process and dictates the minimum SRT required.

Treated effluent cascading over aeration weirs to reoxygenate water after biological nitrification at a wastewater treatment plant

Key Parameters

≥2.0mg/L

Dissolved Oxygen

Minimum for reliable nitrification

10–25days

SRT

Temperature-dependent; longer at <12°C

6.8–8.0

pH Range

Optimal for nitrifying bacteria

7.14mg/L alk

Alkalinity Consumed

Per mg NH₄-N oxidized

Temperature Dependency

Nitrification rate approximately halves for every 8–10°C drop in temperature. At 10°C, the required SRT may exceed 25–30 days. This is often the critical design condition for plants in temperate climates.

Engineering Note

Design nitrification capacity for the minimum expected wastewater temperature, not the annual average. A plant that nitrifies reliably at 15°C may fail completely at 10°C if the SRT is insufficient.

Inhibition

Nitrifying bacteria are sensitive to several inhibitory conditions:

Low pH (<6.5) — reduces nitrification rate significantly

Free ammonia (>10–150 mg/L at high pH) — inhibits Nitrobacter

Heavy metals — copper, zinc, nickel at low concentrations

Organic toxicants — industrial discharges, solvents, biocides

Low dissolved oxygen — nitrifiers outcompeted by heterotrophs at <1.0 mg/L

Nitrification Troubleshooting

ConditionPotential IssueWhat to Investigate
Effluent NH₄-N > 5 mg/LIncomplete nitrificationCheck SRT, DO profile, temperature, alkalinity
SRT < 10 days at 15°CNitrifier washout riskReduce WAS rate, verify SRT calculation
DO < 1.5 mg/L in aeration basinOxygen limitationIncrease blower output, check diffuser condition
pH < 6.8Alkalinity depletedMonitor alkalinity; consider lime or soda ash dosing
Nitrite accumulation > 1 mg/LPartial nitrificationCheck free ammonia, DO, Nitrobacter inhibition

Frequently Asked Questions

Nitrification is the two-step biological oxidation of ammonia. Ammonia-oxidising bacteria (such as Nitrosomonas) convert ammonium to nitrite, and nitrite-oxidising bacteria (such as Nitrobacter) convert nitrite to nitrate. It is the key process for meeting ammonia and nitrogen discharge limits.

Nitrifiers are slow-growing and highly temperature-sensitive. The nitrification rate approximately halves for every 8–10°C drop in temperature, so at around 10°C the required SRT can exceed 25–30 days. Plants in temperate climates are often designed for this winter condition; too short an SRT causes nitrifier washout.

A dissolved oxygen concentration of at least about 2.0 mg/L in the aeration basin is generally needed for reliable nitrification. Below roughly 1.0 mg/L, nitrifiers are outcompeted by faster-growing heterotrophic bacteria and ammonia removal deteriorates.

Nitrification consumes alkalinity — about 7.14 mg of alkalinity (as CaCO₃) per mg of ammonia-nitrogen oxidised. If alkalinity is depleted, pH falls below the optimal 6.8–8.0 range and nitrification slows. Monitoring alkalinity and, if needed, dosing lime or soda ash helps maintain stable performance.

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