environmental impact statement kilmainhamwood compost facility ...
environmental impact statement kilmainhamwood compost facility ... environmental impact statement kilmainhamwood compost facility ...
5361- Kilmainhamwood Compost Facility Extension- EIS 9.2.2.5 Odourous Compound Formation in Composting Plants Material coming onto a site may already have developed a strong odour due to the nature of the material itself or to the way it has been stored. For example: Material Stored under Anaerobic Conditions: fresh organic material stored in plastic bags or insufficiently ventilated containers. The potential for odour increases if the organic material has high moisture content, has been kept in an anaerobic state for a number of days, and/or has been subjected to high temperature and direct sunlight. (e.g. grass clippings, fresh plant material, wet leaves, food waste, etc). Material that has a Low C:N Ratio: this can be a particular problem if the material also has a high moisture content. (e.g. sewage sludge or other high nitrogen sludge’s, fish processing or slaughterhouse residuals, food waste, etc). MANAGEMENT STRATEGIES: Feedstock with a low C:N ratio is often invaluable because of the nitrogen and moisture they provide to the composting recipe. Proactive management strategies can help to capitalize on the benefits moist low C:N ratio material offer while minimising the potential for offensive odour release, the following strategy will be considered at minimum: � Knowledge of delivery schedule or pattern: Knowing when a potentially odorous load is likely to arrive facilitates readiness to deal with the material immediately, minimising the likelihood for potential odours to escape off-site. � An implementable plan in place for dealing with materials likely to be offensive. Such a plan will include the following: o Incorporate the material quickly. Have a stock of porous, high-carbon material on hand, which can be mixed immediately with the incoming material. Examples, currently being used with success, include wood chips, wood shavings, or sawdust, dry leaves and straw. This helps to balance the C:N ratio, absorb the moisture in wet materials and add porosity so that the mixture can remain aerobic. o Handle loads of potentially offensive feedstock inside an enclosed work area ventilated by an odour control system. o If the material must be stored before blending/handling, add a blanket of saw dust or overs to cover the material to minimise potential odourous emissions. o Ensure the facility can process the organic material as soon as, or within a short time frame (24 hrs), it enters the facility. For inspection purposes only. Consent of copyright owner required for any other use. 117 EPA Export 01-06-2010:03:55:57
5361- Kilmainhamwood Compost Facility Extension- EIS OPTIMISING THE PROCESS: The following basic elements: 1. Check carbon to nitrogen ratio (C:N) when preparing the composting mix: Recipes with a C:N ratio of less than 25 are likely to lose nitrogen in the form of ammonia. A ratio of 25-40 is better, with 30 being considered ideal for most materials. 2. Check the moisture content of the composting recipe: While too little moisture will slow the composting process, too much moisture will cause anaerobic conditions—as all of the small spaces in the material will be filled with water and not enough space is available for the air required by aerobic micro organisms. Moisture content between 40 and 60% is considered a good air/moisture balance to support aerobic processes. 3. Above neutral pH recipe. Basic mixtures above pH 8.5 will release nitrogen as ammonia. 4. Porosity is important in formulating the composting mix: A mixture consisting of nothing but fine textured materials will likely become compacted as the composting process develops, preventing air from penetrating the pile. To maintain porosity when composting, include some coarser material (such as wood shavings or chips) so that air can continue to move freely through the material as it breaks down. This is particularly important in systems where the material will not be turned during active composting. 5. Ensure that material is aerated to maintain aerobic conditions. The continuous monitoring of interstitial oxygen within the composting mix will help ensure maintenance of appropriate oxygen levels within the material. 6. Appropriate pile size, which is not too deep: Air will not be able to infiltrate the compost pile homogenously. If the pile is too deep, this results in various maturation rates for the composting process. 9.2.3 Materials and Methods For inspection purposes only. Consent of copyright owner required for any other use. This section describes the materials and methods use for the odour measurement and dispersion modelling assessment of the existing and proposed facility operations. This section will also include the backbone odour management methodology to be used at Kilmainhamwood Composting Facility to ensure no odour impact. 9.2.3.1 Airflow Rate and Temperature Measurement Using a calibrated pitot manometer and L type pitot tube, and PT100 temperature probe, the volumetric airflow rate and temperature of the emission air stream that passes through the emission source was determined in accordance with EN13284-1:2002. This allowed for the determination of physical operational parameters such as temperature, airflow velocity and volumetric airflow rate. Ten measurements were carried out in a straight section of ducting for airflow rate. Temperature readings were logged continuously to a Testo 400 handheld data logger and downloaded using Com soft 118 EPA Export 01-06-2010:03:55:57
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5361- Kilmainhamwood Compost Facility Extension- EIS<br />
OPTIMISING THE PROCESS:<br />
The following basic elements:<br />
1. Check carbon to nitrogen ratio (C:N) when preparing the <strong>compost</strong>ing mix: Recipes with<br />
a C:N ratio of less than 25 are likely to lose nitrogen in the form of ammonia. A ratio of<br />
25-40 is better, with 30 being considered ideal for most materials.<br />
2. Check the moisture content of the <strong>compost</strong>ing recipe: While too little moisture will slow<br />
the <strong>compost</strong>ing process, too much moisture will cause anaerobic conditions—as all of<br />
the small spaces in the material will be filled with water and not enough space is<br />
available for the air required by aerobic micro organisms. Moisture content between 40<br />
and 60% is considered a good air/moisture balance to support aerobic processes.<br />
3. Above neutral pH recipe. Basic mixtures above pH 8.5 will release nitrogen as<br />
ammonia.<br />
4. Porosity is important in formulating the <strong>compost</strong>ing mix: A mixture consisting of nothing<br />
but fine textured materials will likely become compacted as the <strong>compost</strong>ing process<br />
develops, preventing air from penetrating the pile. To maintain porosity when<br />
<strong>compost</strong>ing, include some coarser material (such as wood shavings or chips) so that air<br />
can continue to move freely through the material as it breaks down. This is particularly<br />
important in systems where the material will not be turned during active <strong>compost</strong>ing.<br />
5. Ensure that material is aerated to maintain aerobic conditions. The continuous<br />
monitoring of interstitial oxygen within the <strong>compost</strong>ing mix will help ensure maintenance<br />
of appropriate oxygen levels within the material.<br />
6. Appropriate pile size, which is not too deep: Air will not be able to infiltrate the <strong>compost</strong><br />
pile homogenously. If the pile is too deep, this results in various maturation rates for the<br />
<strong>compost</strong>ing process.<br />
9.2.3 Materials and Methods<br />
For inspection purposes only.<br />
Consent of copyright owner required for any other use.<br />
This section describes the materials and methods use for the odour measurement and dispersion<br />
modelling assessment of the existing and proposed <strong>facility</strong> operations. This section will also include the<br />
backbone odour management methodology to be used at Kilmainhamwood Composting Facility to<br />
ensure no odour <strong>impact</strong>.<br />
9.2.3.1 Airflow Rate and Temperature Measurement<br />
Using a calibrated pitot manometer and L type pitot tube, and PT100 temperature probe, the volumetric<br />
airflow rate and temperature of the emission air stream that passes through the emission source was<br />
determined in accordance with EN13284-1:2002. This allowed for the determination of physical<br />
operational parameters such as temperature, airflow velocity and volumetric airflow rate. Ten<br />
measurements were carried out in a straight section of ducting for airflow rate. Temperature readings<br />
were logged continuously to a Testo 400 handheld data logger and downloaded using Com soft<br />
118<br />
EPA Export 01-06-2010:03:55:57