14.12.2012 Views

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

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

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

SHOW MORE
SHOW LESS

You also want an ePaper? Increase the reach of your titles

YUMPU automatically turns print PDFs into web optimized ePapers that Google loves.

Table 63-33: Emissions <strong>of</strong> Gas-fuelled and Diesel-fuelled Buses<br />

1030<br />

29/09/09<br />

Emissions Emissions g g / / km<br />

km<br />

NMHC NMHC<br />

NOx NOx<br />

PM PM<br />

Diesel 0.12 8.50 0.10<br />

Gas 0.03 4.60 0.01<br />

Source: N. Nylund, K. Erkkilä, M. Lappi, and M. Ikonen (2004) Transit Bus Emission Study: Comparison<br />

<strong>of</strong> Emissions from Diesel and Natural Gas Buses, VTT Processes, October 2004<br />

The data in Table 63-33 suggests the use <strong>of</strong> biogas to fuel vehicles should result in<br />

improvements to air quality, particularly with regard to the NOx emission.<br />

63.9.3 Compost Produced by AD Process<br />

The residues can either be dewatered, creating a solid and a liquid fraction, or used<br />

directly on land as a slurry, sometimes using flocculants in the process.<br />

Whilst there may be some arguments for direct spreading, not least that <strong>of</strong> cost, it is<br />

considered better practice to stabilise the solid residues (following dewatering<br />

depending upon the materials and the process) through an aerobic stage so as to<br />

produce a compost. One <strong>of</strong> the reasons for stabilising the solids from digestion is to<br />

reduce the potential for nitrogen to leach following application – the stabilisation<br />

process makes for an amendment with high organic matter content, but with reduced<br />

availability <strong>of</strong> nitrogen. The level <strong>of</strong> nutrients such as phosphorous is much lower than<br />

in, say, sludge based materials, making it possible to apply more organic material<br />

without creating problems <strong>of</strong> groundwater pollution / surface water run-<strong>of</strong>f.<br />

In this study, we have assumed that the digestion process is followed by an aerobic<br />

treatment phase, and that the early stages <strong>of</strong> the aerobic treatment employ a<br />

bi<strong>of</strong>ilter. This adds slightly to the costs <strong>of</strong> treatment, and some equipment suppliers<br />

prefer to make the slurry available without such a treatment step.<br />

Additional emissions <strong>of</strong> CO2 and NH3 are assumed to occur in the aerobic phase, and<br />

some additional CH4 is assumed to be emitted in the transition from the anaerobic to<br />

the aerobic phase. The use <strong>of</strong> the bi<strong>of</strong>ilter necessitates the use <strong>of</strong> some additional<br />

electricity.<br />

Emissions <strong>of</strong>fsets attributed to the use <strong>of</strong> the compost produced in this way are<br />

calculated using the same methodology described in Section 63.8.4.<br />

63.9.4 Summary – Damage Costs Associated with AD Processes<br />

Table 63-34 summarises the damage costs associated with treating source<br />

separated food waste in AD systems.

Hooray! Your file is uploaded and ready to be published.

Saved successfully!

Ooh no, something went wrong!