environmental impact statement kilmainhamwood compost facility ...
environmental impact statement kilmainhamwood compost facility ...
environmental impact statement kilmainhamwood compost facility ...
Create successful ePaper yourself
Turn your PDF publications into a flip-book with our unique Google optimized e-Paper software.
5361- Kilmainhamwood Compost Facility Extension- EIS<br />
Table 2.1 Water Management Plan<br />
Facility Area Water Use m 3 per Day Water Source<br />
Composting Building<br />
Facility Administration<br />
Building<br />
Washing<br />
Requirements<br />
Washing<br />
Requirements and<br />
Potable Water<br />
27<br />
0.6<br />
0.3<br />
Rainwater<br />
Storage Tank<br />
On Site<br />
Borehole (BH3)<br />
The capacity of the rainwater storage tank is 36m 3 . Given that:<br />
� The rainwater storage tank can provide wash water requirements for a dry weather period of 60<br />
days; and<br />
� 4.5mm of rainfall will replenish the tank on the basis of a total roofed area of 7961m 2 ;<br />
It is reasonable to assume that all water usage for washing requirements within the <strong>compost</strong>ing building<br />
can be provided by collection of rainfall.<br />
An onsite water treatment plant is proposed at the point of entry to the <strong>facility</strong> administration building to<br />
treat the borehole (BH3) supply to drinking water standards. It is proposed to provide a package plant in<br />
the Tea Station providing chlorination and filtration.<br />
Surplus roof rainwater will overflow from the rainwater storage tank to the roof water sewer and will<br />
combine with the yard water sewer (downstream of the oil interceptor). The green field runoff rate to the<br />
existing drainage ditch will be controlled by a hydrobrake. An overflow, downstream of the oil<br />
interceptor, will discharge into a proposed attenuation area as shown on Drawing No. 5361-2402.<br />
2.5.7 Odour Abatement System<br />
The odour abatement system currently in operation at the Kilmainhamwood Compost <strong>facility</strong> involves<br />
biofiltration.<br />
Biofilter Principle<br />
For inspection purposes only.<br />
Consent of copyright owner required for any other use.<br />
It is widely accepted that the wide range of micro-organisms found in soils can oxidise many<br />
compounds, including both volatile organic compounds and other odourous compounds. Prepared beds<br />
have therefore been used for odour control for about 40 years. With adequate construction and<br />
maintenance of biofilter beds, they can be very effective for odour abatement. Mixtures of porous, well<br />
structured material with some <strong>compost</strong> are typically used and the bed is kept open by turning the top<br />
layer two or three times per year. Adequate bottom drainage is essential, as is the <strong>facility</strong> to keep the<br />
bed moist in dry weather.<br />
The residence time in a biofilter depends largely on the substrate. For most odorous air or gases, a<br />
residence time of approximately 28 seconds is required. The typical height of biofilter beds is 1 to 2<br />
metres, so that a linear flow rate of approximately 130 m3 (h) (m2) is provided. Greater bed heights will<br />
EPA Export 01-06-2010:03:55:51