Nitrous Oxide Emissions from Wastewater Treatment Plants. A Balancing Act
Eugenio Giraldo
Innovation and Environmental Stewardship
American Water, 1025 Laurel Oak Rd, Voorhees, NJ
Eugenio.giraldo@amwater.com
ABSTRACT
Acknowledgement of the role of nitrification on the emission of N
2
O from wastewater treatment
plants is generating a renewed interest in the subject. Actual emission factors for N
2
O in WWTP
seem to be higher than previously estimated. The impact of temperature, dissolved oxygen,
nitrites, nitrates, C/N, pH, ammonia, H
2
S is reviewed. It is argued that actual emissions from the
plant are result of interactions among nitrifiers, denitrifiers and the stripping effect of aeration.
Nitrifiers are mostly a source through the nitrifiers-denitrification pathway. Denitrifying bacteria
can act as a source or a sink. Denitrifiers play a significant role in reducing emissions in anoxic
tanks. Locations prone to nitrous oxide emission in treatment plants are proposed. The impact of
dynamic conditions in the plant is emphasized. Emission measurement protocols need to account
for the diurnal variability of N
2
O emissions in treatment plants due to changing influent and
operational conditions. Steady state evaluation in the laboratory can not capture the effects
observed in the field. Some trends observed in mixed cultures of bacteria in treatment plants can
be explained based on fundamental studies in pure cultures, others are not. Increased nitrous
oxide emissions at high dissolved oxygen concentration often seen in mixed cultures from
treatment plants are not directly inferred from the behaviour of nitrifiers or denitrifiers in pure
culture. The impact of potentially higher nitrous oxide emission factors on green-house-gas
emissions from the plant is quantified. If current trends are confirmed in full scale facilities the
wastewater sector would have a larger impact than previously estimated. Alternative strategies
for nitrous oxide control are reviewed. The need to remove nutrients from the water environment
might lead to a different type of pollution in the atmosphere; there is a need to balance and
minimize the overall effect.
Keywords nitrous oxide, wastewater, inventory, green house gas, nitrification, denitrification,
review
Introduction
Nitrous oxide (N
2
O) is a stable gas with an atmospheric life time of approximately 120 years that
can trap heat acting as a greenhouse gas. Due to these characteristics it is calculated that its
heat retention effect in the atmosphere is 310 times more potent than carbon dioxide on a per
molecule basis. Concentrations of nitrous oxide in the atmosphere continue to increase at a rate
of 0.25% per year (EPA, 2009). Nitrous oxide has both natural and human related sources. A
recent report from EPA establishes that nitrous oxide contributes to 5.2% of the total
anthropogenic emissions of greenhouse gases for the United States in 2006 (EPA, 2008).
Emissions of nitrous oxide within the wastewater treatment sector account for approximately one
third of the total direct emissions. The emissions of nitrous oxide attributed to wastewater
treatment are due to direct emissions at the treatment plant, and emissions due to discharge of
nitrogenous compounds to the environment, e.g. a river.
Nitrous oxide is produced during nitrification and denitrification processes that occur in treatment
plants and water bodies receiving treatment plant effluents. Early studies used to obtain emission
factor of nitrous oxide in wastewater treatment plants were focused on denitrification as the
principal source, however, it is now recognized that nitrification also plays a significant role in the
emissions at the plant. As a result there are very few studies measuring emissions in treatment
plants that account for the contribution of nitrifiers to the overall inventory of the plant. Recent
published information on the emission factors from nitrification processes suggest that actual
emissions from treatment plants are higher than originally estimated. In contrast with this, recent
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Nutrient Removal 2009
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