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International Review of Waste Management Policy - Department of ...

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Aeration and the C:N ratio are believed to have an important effect on the nitrogen<br />

conversion processes. Where composting processes have included manures,<br />

intensive aeration in connection with low C-content has been shown to give rise to<br />

nitrite accumulation in slurry (up to 33% <strong>of</strong> the total nitrogen content) and incomplete<br />

ammonium oxidation. Low ventilation rates and sufficient carbon supply support the<br />

formation <strong>of</strong> nitrous oxide during nitrification and denitrification processes.<br />

Gronauer et al suggest that around 12% <strong>of</strong> total nitrogen escapes from the material in<br />

the form <strong>of</strong> ammonia. 1260 This gave a figure <strong>of</strong> 0.53kg/tonne waste in raw gas, but<br />

0.0264kg per tonne waste when the air is passed through a bi<strong>of</strong>ilter. Gronauer et al<br />

also assumed that 0.15kg N2O per tonne waste would be emitted.<br />

One Swedish study assumed the nitrogen leakage to air was 7.5% <strong>of</strong> the nitrogen<br />

content <strong>of</strong> the feedstock. 1261 Of this leakage, it was assumed 89% was emitted as<br />

NH3, 9% as N2O and 2% N2. The study for the Danish EPA assumed that <strong>of</strong> the total<br />

amount <strong>of</strong> nitrogen lost as gaseous emission, 98 % was volatilised as NH3, 0.5 % as<br />

N2O and 1.5 % as N2 (the figures relate to raw gas as opposed to gas which has been<br />

scrubbed). 1262<br />

Our analysis assumes nitrogenous emissions from composting processes are as<br />

follows:<br />

1018<br />

� 10% <strong>of</strong> the total nitrogen content <strong>of</strong> the waste is released in some form. Of this<br />

10%, we further assume that:<br />

29/09/09<br />

• 88% is released as NH3;<br />

• 2% is released as N2 (this is not a problem for the environment); and<br />

• 10% is released as N2O.<br />

Whilst the NH3 is released untreated in windrow systems, in vessel systems typically<br />

make use <strong>of</strong> bi<strong>of</strong>ilters to convert much <strong>of</strong> this pollutant to N2O. This is discussed in<br />

the sections that follow.<br />

63.8.2 Climate Change Impacts <strong>of</strong> Composting Processes<br />

Table 63-24 outlines the key assumptions used to model the climate change impacts<br />

<strong>of</strong> composting processes, which were developed in a previous study for WRAP by<br />

1260 A. Gronauer, M. Helm, H. Schon (1997) Verhafen und Konzepte der Bioabfallkompostierung –<br />

Vergleich – Bewertung – Empfehlungen, Bayerische Landesanstalt fur Landtechnik der TU Munchen-<br />

Weihenstephan<br />

1261 Goran Finnvenden, Jessica Johansson, Per Lind and Asa Moberg (2000) Life Cycle Assessments <strong>of</strong><br />

Energy from Solid <strong>Waste</strong>, Forskningsgruppen for Miljostrategiska Studier, FMS 137, August 2000<br />

1262 B. Gunnarsdotter Beck-Friis (2001) Emissions <strong>of</strong> Ammonia, Nitrous Oxide and Methane during<br />

Composting <strong>of</strong> Organic Household <strong>Waste</strong>, Agraria 266, Doctoral Thesis, SLU, Sweden, sited in A. Baky<br />

and O. Eriksson (2003) Systems Analysis <strong>of</strong> Organic <strong>Waste</strong> <strong>Management</strong> in Denmark, Environmental<br />

Project No. 822, Copenhagen: Danish EPA

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