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

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It should be noted that bioaerosols from the composting process contain the same<br />

micro-organisms as ones to which citizens are routinely exposed. They are present<br />

naturally and are essential to the recycling <strong>of</strong> nutrients in our gardens, parks and<br />

countryside.<br />

We have not been able to incorporate the impacts <strong>of</strong> bioaerosol emissions into our<br />

model as no dose-response functions have yet been developed to quantify the<br />

impacts associated with this type <strong>of</strong> pollutant. However the preceding discussion<br />

suggests the environmental and health impacts <strong>of</strong> these emissions should be<br />

minimised with the adoption <strong>of</strong> appropriate operational management techniques.<br />

63.8.4 Benefits Associated with the Use <strong>of</strong> Compost<br />

The use <strong>of</strong> compost is associated with monetised benefits, extending beyond the<br />

realm <strong>of</strong> air pollution to include, amongst others, reductions in water pollution and<br />

improvements to soil quality.<br />

We include within our model the slow release <strong>of</strong> CO2 from the soil after the compost is<br />

added. After 50 years, approximately 13% <strong>of</strong> the initial carbon contained within the<br />

compost remains in the soil.<br />

65% <strong>of</strong> the compost produced is assumed to be used in agriculture. Our model<br />

considers the following benefits associated with the use <strong>of</strong> compost in this way: 1269<br />

1023<br />

� The displacement <strong>of</strong> alternative nutrient sources otherwise applied through<br />

the use <strong>of</strong> synthetic fertiliser, including the avoided external costs <strong>of</strong> fertiliser<br />

manufacture and the avoided energy use associated with this;<br />

� The greenhouse gases avoided from nitrogenous fertiliser applications (i.e.<br />

N2O emissions) and the external costs associated with this;<br />

� Avoided external costs from a reduction in the leaching <strong>of</strong> nitrate (from<br />

nitrogenous fertilisers) into groundwater;<br />

� Avoided external costs associated with process wastewater and<br />

phosphogypsum disposal during the manufacture <strong>of</strong> phosphate fertiliser;<br />

� Avoided energy requirement associated with the mining <strong>of</strong> phosphate rock for<br />

phosphate fertiliser, and the avoided external costs associated with this;<br />

� Avoided external costs through a reduction in the use <strong>of</strong> pesticides; and<br />

� Avoided external costs through a reduction in the use <strong>of</strong> water.<br />

The remaining 35% <strong>of</strong> the compost is assumed to displace the use <strong>of</strong> peat in<br />

horticulture and hobby gardening applications. Here the avoided impacts are the slow<br />

release <strong>of</strong> CO2 from the aerobic degradation <strong>of</strong> peat after its removal from the peat-<br />

1269 For a detailed description <strong>of</strong> the methodology used to calculate these estimates see: Eunomia (2007)<br />

Managing Biowastes from Households in the UK: Applying Life-cycle Thinking in the Framework <strong>of</strong> Cost-benefit<br />

Analysis, Appendices to the Main Report, Report for WRAP, May 2007<br />

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

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