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5361- Kilmainhamwood Compost Facility Extension- EIS<br />

Odour Dispersion Modelling Results for Scenarios 1 and 2<br />

AERMOD Prime (USEPA ver. 07026) was used to determine the overall odour <strong>impact</strong> of the existing<br />

and proposed Kilmainhamwood Composting Facility design. Impacts from emission points are<br />

assessed in accordance with the <strong>impact</strong> criterion contained in Section 9.2.3.6 and 9.2.3.7. Two distinct<br />

scenarios were assessed:<br />

The output data was analysed to calculate the following:<br />

Ref Scenario 1:<br />

• Predicted odour emission contribution of overall existing <strong>compost</strong>ing <strong>facility</strong> design operation to<br />

surrounding population (see Table 9.6), to odour plume dispersal at the 98 th percentile for a<br />

ground level concentration of less than or equal to 1.50 OuE m -3 (see Figure 9.3).<br />

• Predicted odour emission contribution of overall existing <strong>compost</strong>ing <strong>facility</strong> design operation to<br />

surrounding population (see Table 9.6), to odour plume dispersal at the 99.5 th percentile for a<br />

ground level concentration of less than or equal to 6.0 OuE m -3 (see Figure 9.4).<br />

Ref: Scenario 2:<br />

• Predicted odour emission contribution of overall proposed <strong>compost</strong>ing <strong>facility</strong> design operation<br />

to surrounding population (see Table 9.7), to odour plume dispersal at the 98th percentile for a<br />

ground level concentration of less than or equal to 1.50 OuE m-3 (see Figure 9.5).<br />

• Predicted odour emission contribution of overall proposed <strong>compost</strong>ing <strong>facility</strong> design operation<br />

to surrounding population (see Table 9.7), to odour plume dispersal at the 99.5th percentile for<br />

a ground level concentration of less than or equal to 3.0 OuE m-3 (see Figure 9.6).<br />

• Comparison between predicted odour <strong>impact</strong> for existing and proposed <strong>facility</strong> design for the<br />

98th percentile of hourly averages (see Figure 9.7).<br />

• Comparison between predicted odour <strong>impact</strong> for existing and proposed <strong>facility</strong> design for the<br />

99.5th percentile of hourly averages (see Figure 9.8).<br />

For inspection purposes only.<br />

Consent of copyright owner required for any other use.<br />

These computations give the odour concentration at each Cartesian grid receptor location that is<br />

predicted to be exceeded for 0.5% (44 hours) and 2% (175 hours) of five years of hourly sequential<br />

meteorological data.<br />

This will allow for the predictive analysis of any potential <strong>impact</strong> on the neighbouring sensitive locations<br />

while the <strong>compost</strong>ing <strong>facility</strong> is in operation. It will also allow the operators of the <strong>facility</strong> to assess the<br />

effectiveness of their odour abatement/minimisation strategies. The intensity of the odour from the two<br />

or more sources of the <strong>facility</strong> operation within the <strong>compost</strong>ing <strong>facility</strong> will depend on the strength of the<br />

initial odour threshold concentration from the sources and the distance downwind at which the<br />

prediction and/or measurement is being made. Where the odour emission plumes from a number of<br />

sources combine downwind, then the predicted odour concentrations may be higher than that resulting<br />

from an individual emission source. It is important to note that various odour sources have different<br />

odour characters. This is important when assessing those odour sources to minimise and/or abate.<br />

Although an odour source may have a high odour emission rate, the corresponding odour intensity<br />

(strength) may be low and therefore is easily diluted.<br />

133<br />

EPA Export 01-06-2010:03:55:58

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