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N2O production in a single stage nitritation/anammox MBBR process

N2O production in a single stage nitritation/anammox MBBR process

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7. Future research<br />

Better understand<strong>in</strong>g off which mechanisms and organisms that are responsible for <strong>N2O</strong><br />

<strong>production</strong> <strong>in</strong> the nitrify<strong>in</strong>g/<strong>anammox</strong> <strong>MBBR</strong> system is needed. There is also a need for<br />

better accuracy <strong>in</strong> the measurements of emitted <strong>N2O</strong> from the <strong>process</strong>.<br />

• Measurement should be done where <strong>N2O</strong> is measured both <strong>in</strong> the water phase<br />

and <strong>in</strong> the off-gas simultaneously, this would both help to better understand<br />

when the <strong>N2O</strong> is produced <strong>in</strong> the system and it would give a much better accuracy<br />

of how much <strong>N2O</strong> that is produced and emitted by the <strong>MBBR</strong> system.<br />

• S<strong>in</strong>ce the biofilm creates a microenvironment with anoxic conditions which are<br />

believed to enhance the <strong>N2O</strong> <strong>production</strong> by AOB the importance of biofilm<br />

structure and thickness should be <strong>in</strong>vestigated.<br />

• Disturbances are believed to cause higher <strong>N2O</strong> <strong>production</strong> from the<br />

microorganisms. It should be exam<strong>in</strong>ed whether <strong>in</strong>termittent aeration could be<br />

considered a disturbance to the bacteria perform<strong>in</strong>g the nitrogen removal<br />

caus<strong>in</strong>g higher <strong>N2O</strong> emissions from the <strong>process</strong>.<br />

• To be able to operate the <strong>MBBR</strong> <strong>in</strong> a manner that gives as small amounts of<br />

emitted <strong>N2O</strong> as possible it is of great importance to understand which<br />

microorganisms with<strong>in</strong> the system that are responsible for the <strong>N2O</strong> emissions.<br />

Measurements of the <strong>N2O</strong> <strong>production</strong> dur<strong>in</strong>g batch tests with <strong>in</strong>hibitors should be<br />

performed to ga<strong>in</strong> this k<strong>in</strong>d of knowledge.<br />

• S<strong>in</strong>ce substrate concentrations (NH4 + , NO2 − and NO3 − ) are known to <strong>in</strong>fluence the<br />

amount of produced <strong>N2O</strong>, it would be <strong>in</strong>terest<strong>in</strong>g to evaluate their impact on<br />

emitted <strong>N2O</strong> <strong>in</strong> both batch tests and with operation at different <strong>in</strong>fluent <strong>in</strong>organic<br />

nitrogen concentrations. Perform<strong>in</strong>g the tests <strong>in</strong> this manner could give answers<br />

to whether it is the <strong>in</strong>creased nitrogen concentrations /disturbance that causes<br />

the <strong>in</strong>crease <strong>in</strong> <strong>N2O</strong> <strong>production</strong> or the actual higher substrate concentration.<br />

• As volume to surface ratios are of importance to emitted <strong>N2O</strong> from a wastewater<br />

treatment <strong>process</strong> and s<strong>in</strong>ce there are further differences between full scale and<br />

laboratory systems the emitted <strong>N2O</strong> from full scale systems should be<br />

determ<strong>in</strong>ed.<br />

• Measurement from a <strong>process</strong> operated with real wastewater is needed for<br />

determ<strong>in</strong>ation of <strong>N2O</strong> emissions dur<strong>in</strong>g real conditions.<br />

• Exam<strong>in</strong>e the <strong>in</strong>fluence of aeration rate on <strong>N2O</strong> emission by cont<strong>in</strong>uous aeration<br />

with pure oxygen, (a much lower aeration rate can ma<strong>in</strong>ta<strong>in</strong> a sufficient oxygen<br />

concentration <strong>in</strong> the reactor if pure oxygen is used.)<br />

53

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