environmental impact statement kilmainhamwood compost facility ...
environmental impact statement kilmainhamwood compost facility ... environmental impact statement kilmainhamwood compost facility ...
5361- Kilmainhamwood Compost Facility Extension- EIS microbial activity and hence oxygen consumption are highest. Each composting bay is approximately 5.75m wide and 11.57m long. The feedstock is piled to a height of approximately 3m within the bays. The composting process is a forced aeration temperature feedback system. The composting bays feature an automated forced aeration system. There is an aeration fan behind each composting bay to blow air up through the pile and control temperature. These fans are located in tunnels/corridors behind the composting bays. Air is blown from the underside of the static pile of composting material towards the exterior of the mixture. The system maintains a temperature ceiling of 60°C by means of the ondemand removal of heat by ventilation through temperature feedback control. This encourages a high decomposition rate as significantly higher temperatures inhibit and slow down decomposition by reducing microbial activity. In addition the interior of the composting facility building is a controlled environment, where an atmosphere of negative pressure is maintained. Temperature probes inserted into the composting mixture can generate a control signal used to adjust the air/oxygen supply and maintain a set point temperature. Temperature is the controlled variable and aeration rate is the manipulated variable during the process. Aeration fans linked to a pre-programmed control panel operate according to the temperature of the individual bays. Throughout all stages of the composting process, temperature is monitored by use of temperature probes. This helps to ensure that the bays are being adequately aerated. Moisture is checked by means of a "squeeze" test which is a non-quantitative method of estimating moisture. The high temperatures generated in all stages of the composting process, in combination with the measures taken during feedstock blending/mixing to include sufficient dry amendment to adjust the moisture content to within an optimal range, ensures that no leachate is produced by the process under normal conditions. Any leachate produced including leachate from incoming feedstock is contained and reintroduced in the blending/mixing stage of the process. For inspection purposes only. Consent of copyright owner required for any other use. After the initial phase of high rate composting, the material is moved by loading shovel to composting bays in the maturation area of the facility where the compost is matured by aerating the compost for another 10-12 days. Following this stage, the compost is processed through a trommel screen fitted with 12mm and 40mm screens. The minus 12mm fraction produced by the screening process is placed in a bulking tunnel which allows enough material to be bulked in order to fill the pasteurisation tunnel. This normally takes approximately 3 weeks. The material is then transferred in to an Animal By-product (ABP) treatment tunnel No.2 where the temperature of the material is maintained at 70 o C for a minimum of 1 hour, in line with the requirements of DAFF. Samples of compost product are subsequently taken from the ABP treatment tunnel and sent for testing (E. Coli and Salmonella) to a DAFF approved laboratory and compost is left in situ until analysis results are returned from the laboratory. This process from when material enters the ABP tunnel and receipt of final results may take up to 3 weeks. Following a successful outcome to laboratory testing, the compost product is removed from the ABP treatment tunnel for delivery to a customer. 23 EPA Export 01-06-2010:03:55:51
5361- Kilmainhamwood Compost Facility Extension- EIS The 12-40mm fraction (seed compost) produced by the screening process is moved to the beginning of the process where it is mixed with incoming feedstock to adjust the porosity, moisture content and C:N ratio of the blended mix. The plus 40mm fraction primarily comprises of plastic film and other large contaminants and is hence stored for dispatch from the facility to a licensed facility for recovery/disposal. It is proposed that approximately 8,280 tonnes per annum of finished product and approximately 1,625 tonnes per annum of residual waste will be generated by the extended and intensified Kilmainhamwood facility. Given that the process proposed for the additional feedstock is the same as the existing process, it is reasonable that the mass balance for the extended and intensified facility is based on the mass balance for the existing facility. Process losses are due to a combination of reductions in dry matter content and moisture content. The microbial activity in the process consumes carbon, as an energy source, and releases carbon dioxide and heat. The heat generated results in the evaporation of moisture within the feedstock. In summary, the process losses are represented in terms of carbon dioxide and water vapour emissions at the biofilter. Process losses in excess of 60% are typical of a well managed in-vessel composting process. A flow diagram of the process at Kilmainhamwood Compost is provided below. On the basis of the data compiled for the existing process, losses have been approximated for the treatment of 40,000 tonnes per annum and are included in the flow diagram below. For inspection purposes only. Consent of copyright owner required for any other use. 24 EPA Export 01-06-2010:03:55:51
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5361- Kilmainhamwood Compost Facility Extension- EIS<br />
microbial activity and hence oxygen consumption are highest. Each <strong>compost</strong>ing bay is approximately<br />
5.75m wide and 11.57m long. The feedstock is piled to a height of approximately 3m within the bays.<br />
The <strong>compost</strong>ing process is a forced aeration temperature feedback system. The <strong>compost</strong>ing bays<br />
feature an automated forced aeration system. There is an aeration fan behind each <strong>compost</strong>ing bay to<br />
blow air up through the pile and control temperature. These fans are located in tunnels/corridors behind<br />
the <strong>compost</strong>ing bays. Air is blown from the underside of the static pile of <strong>compost</strong>ing material towards<br />
the exterior of the mixture. The system maintains a temperature ceiling of 60°C by means of the ondemand<br />
removal of heat by ventilation through temperature feedback control. This encourages a high<br />
decomposition rate as significantly higher temperatures inhibit and slow down decomposition by<br />
reducing microbial activity. In addition the interior of the <strong>compost</strong>ing <strong>facility</strong> building is a controlled<br />
environment, where an atmosphere of negative pressure is maintained.<br />
Temperature probes inserted into the <strong>compost</strong>ing mixture can generate a control signal used to adjust<br />
the air/oxygen supply and maintain a set point temperature. Temperature is the controlled variable and<br />
aeration rate is the manipulated variable during the process. Aeration fans linked to a pre-programmed<br />
control panel operate according to the temperature of the individual bays.<br />
Throughout all stages of the <strong>compost</strong>ing process, temperature is monitored by use of temperature<br />
probes. This helps to ensure that the bays are being adequately aerated. Moisture is checked by<br />
means of a "squeeze" test which is a non-quantitative method of estimating moisture.<br />
The high temperatures generated in all stages of the <strong>compost</strong>ing process, in combination with the<br />
measures taken during feedstock blending/mixing to include sufficient dry amendment to adjust the<br />
moisture content to within an optimal range, ensures that no leachate is produced by the process under<br />
normal conditions. Any leachate produced including leachate from incoming feedstock is contained and<br />
reintroduced in the blending/mixing stage of the process.<br />
For inspection purposes only.<br />
Consent of copyright owner required for any other use.<br />
After the initial phase of high rate <strong>compost</strong>ing, the material is moved by loading shovel to <strong>compost</strong>ing<br />
bays in the maturation area of the <strong>facility</strong> where the <strong>compost</strong> is matured by aerating the <strong>compost</strong> for<br />
another 10-12 days.<br />
Following this stage, the <strong>compost</strong> is processed through a trommel screen fitted with 12mm and 40mm<br />
screens. The minus 12mm fraction produced by the screening process is placed in a bulking tunnel<br />
which allows enough material to be bulked in order to fill the pasteurisation tunnel. This normally takes<br />
approximately 3 weeks. The material is then transferred in to an Animal By-product (ABP) treatment<br />
tunnel No.2 where the temperature of the material is maintained at 70 o C for a minimum of 1 hour, in line<br />
with the requirements of DAFF. Samples of <strong>compost</strong> product are subsequently taken from the ABP<br />
treatment tunnel and sent for testing (E. Coli and Salmonella) to a DAFF approved laboratory and<br />
<strong>compost</strong> is left in situ until analysis results are returned from the laboratory. This process from when<br />
material enters the ABP tunnel and receipt of final results may take up to 3 weeks. Following a<br />
successful outcome to laboratory testing, the <strong>compost</strong> product is removed from the ABP treatment<br />
tunnel for delivery to a customer.<br />
23<br />
EPA Export 01-06-2010:03:55:51