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If the biogas is cleaned <strong>of</strong> impurities it can be subsequently used as a vehicle fuel,<br />

displacing the use <strong>of</strong> diesel. Our assumptions for modelling this option assume the<br />

fuel to be used within a fleet <strong>of</strong> vehicles, re-fuelled from a central point, as is the<br />

practice in Scandinavia and France. Some modification to the vehicle will be required<br />

to allow it to run on gas as opposed to diesel. Assumptions used to model this option<br />

are summarised in Table 63-30.<br />

Table 63-30: Emissions from the Use <strong>of</strong> Biogas in a Vehicle<br />

Parameter Parameter<br />

Assumption<br />

Assumption<br />

Energy used during upgrade process 0.2 kWh / Nm 3 biogas<br />

Process losses for CH4 (from upgrade process) 2%<br />

Fuel consumption <strong>of</strong> CBG bus 23.4 MJ / km<br />

Emissions avoided by diesel production 13.63 g CO2 equ / MJ<br />

Emissions from diesel bus 1,226 g CO2 equ / km<br />

Sources: W. Urban (2008) Methods and costs <strong>of</strong> the generation <strong>of</strong> natural gas substitutes from<br />

biomass – presentation <strong>of</strong> results <strong>of</strong> latest field research, 17 th Annual Convention <strong>of</strong> Fachverband<br />

Biogas e.V, 15 th -17 th January 2008, Nuremberg; N. Nylund, K. Erkkilä, M. Lappi, and M. Ikonen (2004)<br />

Transit Bus Emission Study: Comparison <strong>of</strong> Emissions from Diesel and Natural Gas Buses, VTT<br />

Processes, October 2004; Bio-NETT (2008) Bio-methane in Lille: A Case Study<br />

63.9.2 Air Quality Impacts<br />

63.9.2.1 Combustion <strong>of</strong> the Biogas in a Gas Engine<br />

Where biogas is used to generate energy using a gas engine, emissions are<br />

associated with the combustion process. The most significant air quality impacts<br />

resulting from the combustion <strong>of</strong> biogas relate to emissions <strong>of</strong> SOx and NOx.<br />

SOx emissions are generally a matter for process management. To the extent that<br />

they stem from the H2S in raw gas, the emissions are related to the use <strong>of</strong>, for<br />

example, precipitation salts which seek to precipitate out the sulphur emitted from<br />

the degradation <strong>of</strong> proteins as iron sulphide.<br />

NOx emissions result from high temperature reactions occurring between<br />

atmospheric nitrogen, and trace elements such as NH3 and H2S contained within the<br />

biogas. 1272 These emissions can be significantly reduced using Selective Catalytic<br />

Reduction (SCR) techniques. Use <strong>of</strong> this technique was cited as the Best Available<br />

Technique (BAT) in the Reference Document for the <strong>Waste</strong> Treatment Industries for<br />

MBT systems using AD. However, although this equipment is widely used to reduce<br />

NOx emissions from waste incineration facilities across Europe, use <strong>of</strong> SCR within AD<br />

1272 V. Aschmann, R Kissel and A Gronauer (2008) Efficiency and Environmental Compatibility <strong>of</strong><br />

Biogas Fired Cogeneration Plants in Practical Service, 17 th Annual Convention <strong>of</strong> Fachverband Biogas<br />

e.V, 15 th -17 th January 2008, Nuremberg<br />

1027<br />

<strong>International</strong> <strong>Review</strong> <strong>of</strong> <strong>Waste</strong> <strong>Policy</strong>: Annexes

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