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environmental impact statement kilmainhamwood compost facility ...

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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

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