Glossary term

Free Ammonia

Un-ionized ammonia fraction of total ammonia nitrogen, controlled by pH and temperature and used to assess toxicity and biological inhibition.

Definition

metric

Free ammonia is the un-ionized NH3 fraction of total ammonia nitrogen, controlled mainly by pH and temperature.

In water and wastewater engineering, free ammonia is used to interpret aquatic toxicity, nitrification inhibition, sidestream treatment stability and ammonia speciation. It is not the same as total ammonia nitrogen or ammonium. For a given total ammonia nitrogen concentration, higher pH and higher temperature increase the un-ionized NH3 fraction. Interpretation depends on reporting basis, pH, temperature, salinity or ionic strength where relevant, sample location, biological process state and the decision being made.

Free ammonia is the un-ionized NH_3 fraction of total ammonia nitrogen. It is important because the same total ammonia result can have very different toxicity or biological inhibition risk depending on pH and temperature.

In wastewater treatment, free ammonia is used to interpret nitrification inhibition, sidestream deammonification stability and receiving-water toxicity. It should not be confused with total ammonia nitrogen, ammonium or ammonia reported on a different molecular basis.

Engineering Meaning

The ammonia-ammonium equilibrium can be written as:

NH_4^+ \rightleftharpoons NH_3 + H^+

A common engineering fraction for un-ionized ammonia is:

\displaystyle f_{NH3}=\frac{1}{1+10^{pK_a-pH}}

where f_{NH3} is the fraction of total ammonia present as NH_3 on the same nitrogen basis.

Temperature Effect

For freshwater screening, the ammonium dissociation constant can be approximated with absolute temperature:

\displaystyle pK_a\approx0.09018+\frac{2729.92}{T_K}

where:

T_K=T_C+273.15

At:

T_C=25^\circ\text{C}

the absolute temperature is:

T_K=298.15\ \text{K}

and:

\displaystyle pK_a=0.09018+\frac{2729.92}{298.15}=9.25

Warmer water generally lowers pK_a and increases the free-ammonia fraction at the same pH.

At:

T_C=15^\circ\text{C}

the absolute temperature is:

T_K=288.15\ \text{K}

and:

\displaystyle pK_a=0.09018+\frac{2729.92}{288.15}=9.56

At pH=8.0, the lower-temperature fraction is:

\displaystyle f_{NH3}=\frac{1}{1+10^{9.56-8.0}}=0.0268

For the same 30\ \text{mg/L as N} total ammonia nitrogen, free ammonia is about:

C_{FA}=30(0.0268)=0.804\ \text{mg/L as N}

This is roughly half the 25 C value in the worked example, showing why pH and temperature should be recorded with the ammonia result rather than added later from a different period.

Free Ammonia Concentration

If:

TAN=30\ \text{mg/L as N},\quad pH=8.0,\quad pK_a=9.25

then:

\displaystyle f_{NH3}=\frac{1}{1+10^{9.25-8.0}}=0.053

and:

C_{FA}=TAN f_{NH3}=30(0.053)=1.59\ \text{mg/L as N}

That value is the free ammonia concentration on an as-nitrogen basis. If a criterion or process limit is reported as NH_3 molecular mass, a basis conversion is required.

pH Sensitivity

At the same temperature and total ammonia concentration, lowering pH to:

pH=7.5

gives:

\displaystyle f_{NH3}=\frac{1}{1+10^{9.25-7.5}}=0.0175

so:

C_{FA}=30(0.0175)=0.525\ \text{mg/L as N}

This example shows why pH control can strongly change free ammonia even when total ammonia nitrogen is unchanged.

Process Use

In biological wastewater treatment, free ammonia can inhibit sensitive organisms or shift microbial selection. In sidestream deammonification, it can be useful or harmful depending on concentration, exposure time and which microbial group is being suppressed. A value that helps suppress nitrite-oxidizing bacteria may still harm ammonia oxidizers or anammox organisms if excessive.

For receiving waters, free ammonia is often more relevant to acute toxicity than total ammonia alone. The correct review must use the applicable criterion, pH, temperature and reporting basis.

The same calculated value can have different meanings in different locations. In an aeration basin, it may indicate nitrifier inhibition risk. In a sidestream reactor, it may be part of the control strategy. In an effluent or receiving water, it may be a compliance or aquatic-toxicity concern. The decision context should be stated before comparing the number with a threshold.

Interpretation Limits

Free ammonia is normally calculated from measured total ammonia nitrogen, pH and temperature. It is not a separate laboratory analyte in many routine wastewater datasets. The result inherits uncertainty from every input, especially pH when the sample is unstable or biologically active.

Salinity, ionic strength and activity corrections can matter in some waters. For ordinary wastewater screening, the simple freshwater relation is often useful, but design or compliance work may need the method specified by the permit, regulator, standard method or local monitoring program.

Validation Evidence

Useful evidence includes total ammonia nitrogen, pH, temperature, sample location, preservation, salinity or ionic strength where relevant, dissolved oxygen, alkalinity, nitrite, nitrate, biological process state, sidestream schedule, receiving-water condition and the limit or inhibition threshold being applied.

Validation should connect the calculated free ammonia value to the decision: toxicity review, nitrification inhibition, sidestream treatment control, process upset diagnosis, permit compliance or post-change release.

For process troubleshooting, validation should compare free ammonia with observed behavior: ammonia removal rate, nitrite or nitrate trend, oxygen uptake, pH movement, temperature change and recovery after operating adjustments. A calculated high value without matching process evidence should trigger a data-quality check before major operational changes.

Common Mistakes

Common mistakes include treating total ammonia nitrogen as free ammonia, ignoring pH, using temperature from a different sampling period, mixing as-N and as-NH3 units, applying a generic inhibition threshold without process context and calculating a precise value from uncertain pH or TAN data. A strong free-ammonia review states TAN basis, pH, temperature, formula, concentration basis, limit and validation evidence.

REF

See also