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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2.5.4 Deamox<br />
Deamox (denitrify<strong>in</strong>g ammonium oxidation) comb<strong>in</strong>es the <strong>anammox</strong> <strong>process</strong> with<br />
autotrophic denitrification utilis<strong>in</strong>g sulphide as an electron donor for <strong>production</strong> of<br />
nitrite from nitrate. The Deamox reactor can therefore be used <strong>in</strong> the treatment <strong>process</strong><br />
of wastewaters conta<strong>in</strong><strong>in</strong>g organic bound nitrogen and SO4 2− (Kalyuzhnyi et al., 2006).<br />
The organic nitrogen content <strong>in</strong> these wastewaters firstly has to be anaerobic<br />
m<strong>in</strong>eralised before nitrification can proceed. If the Deamox <strong>process</strong> is utilised not all<br />
effluent water from the anaerobic m<strong>in</strong>eralisation reactor has to be nitrified, it can<br />
<strong>in</strong>stead be partially fed to the Deamox reactor. Anammox activity is stimulated by the<br />
denitrify<strong>in</strong>g conditions <strong>in</strong> the Deamox reactor and s<strong>in</strong>ce nitrite concentrations are kept<br />
low the <strong>process</strong> is not thought to produce unwanted emissions of NOx-gases (Kalyuzhnyi<br />
et al., 2006). S<strong>in</strong>ce sulphide rich waters are not common <strong>in</strong> municipal wastewater<br />
treatment the Deamox <strong>process</strong> has been further developed utilis<strong>in</strong>g volatile fatty acids<br />
as a more widespread electron donor for the partial denitrification (Kalyuzhnyi et al.,<br />
2008).<br />
2.5 <strong>N2O</strong> emissions from wastewater treatment<br />
It has been known for decades that <strong>N2O</strong> is produced both as an <strong>in</strong>termediate and end<br />
product <strong>in</strong> the metabolism of microorganisms perform<strong>in</strong>g nitrification and<br />
denitrification <strong>process</strong>es (Hooper, 1968, Poth and Focht, 1986, Firestone et al., 1979).<br />
Until recently, <strong>anammox</strong> activity has not been believed to produce any <strong>N2O</strong>, however<br />
Kartal et al., (2007) have shown that <strong>anammox</strong> bacteria produces small amounts of <strong>N2O</strong><br />
as a result of detoxification of NO which is an <strong>in</strong>termediate <strong>in</strong> the <strong>anammox</strong> <strong>process</strong>.<br />
Variable temperature and load<strong>in</strong>g rates of <strong>in</strong>organic nitrogen compounds, low pH,<br />
alternat<strong>in</strong>g aerobic and anaerobic conditions together with growth rate and microbial<br />
composition are parameters that have great <strong>in</strong>fluence on <strong>N2O</strong> emissions from a<br />
wastewater treatment plant (Kampschreur et al., 2008 b). <strong>N2O</strong> <strong>production</strong> as a<br />
consequence of these environmental conditions dur<strong>in</strong>g nitrification and denitrification<br />
will be described <strong>in</strong> the chapter 2.5.1-2.5.2.The possibility of chemical <strong>N2O</strong> <strong>production</strong> <strong>in</strong><br />
wastewater treatment is shortly described <strong>in</strong> 2.4.3. Table 2 gives molecular weight of<br />
<strong>N2O</strong> and the water solubility both <strong>in</strong> mol/l and g/l.<br />
Table 2. Physical properties of N 2O<br />
Property:<br />
Unit:<br />
Molecular weight 44.0 g/mol<br />
Water solubility (0 sal<strong>in</strong>ity at 20 ̊C)<br />
27.05∙10 − 3 mol/l<br />
1.19 g/l<br />
18