N2O production in a single stage nitritation/anammox MBBR process
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 />
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