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An in-depth exploration of composting, including the natural decomposition process, the role of invertebrates and microorganisms, and the three main composting processes: biological, chemical, and physical. The text also covers the five stages of composting practices and various techniques such as windrow, aerated, static pile, in-vessel composting, and anaerobic processing. Additionally, the benefits of composting and biogasification are discussed.
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Composting is the transformation of organic material (e.g., plant matter) through decomposition into a soil-like material called compost. Invertebrates (e.g., insects and earthworms) and microorganisms (e.g., bacteria and fungi) help in transforming the material into compost. Composting is a natural form of recycling, which continually occurs in nature. Decomposition occurs naturally wherever plants grow. Creating ideal conditions can encourage this natural decomposition. The microorganisms and invertebrates fundamental to the composting process require oxygen and water to successfully decompose the material. The end products of the process are soil-enriching compost, carbon dioxide, water and heat. For example, composting of organic wastes such as vegetable wastes produce an organic manure, which is good for garden plants.
There are 3 processes of composting, viz., biological, chemical and physical. In biological processes, microorganisms such as bacteria, fungi and actinomycetes break down the organic matter present in the waste. As microorganisms begin to decompose the organic material, the carbon in it is converted to by-products like carbon dioxide and water and a humic end product called compost. Inoculum is added in case of a lack of microbial organisms. If all conditions are ideal for a given microbial population to perform at its maximum potential, composting will occur rapidly. The chemical environment is largely determined by the composition of material to be composted. Several factors determine the chemical environment for composting: carbon energy source, the correct amount of water, adequate oxygen, appropriate pH and the absence of toxic constituents that could inhibit microbial activity. A physical environment is essential for the composting process to proceed efficiently. This includes factors such as temperature, particle size, mixing and pile size. Smaller particle size is preferred, as it has more surface per unit weight, and therefore, facilitates more microbial activity, which leads to rapid decomposition. The optimum temperature range is between 32^0 C and 60^0 C. Temperature above 65^0 C is not
ideal for composting. Mixing is done to distribute moisture and air evenly and promote the breakdown of compost clumps.
There are 5 basic stages involved in all composting practices, namely, preparation, digestion, curing, screening and finishing and storage or disposal. Preparation consists of sorting the recyclables, removal of non-combustibles, shredding, pulping, grinding and the addition of water sludge. There are 5 techniques of digestion, viz., windrow, aerated, static pile, in-vessel composting and anaerobic processing. These techniques vary in the method of air supply, temperature control, mixing/turning of the material, time required for composting and capital and operating costs. The amount of curing necessary at the initial stabilisation depends on the proposed use of the composted material. If the compost is to be pelletised and/or bagged, it must be completely stable before being finished. The amount of finishing required is also dependent on the final marketing of the compost. Regrinding and rescreening is done, so as to make the compost uniform in size. The efficiency of the composting process, i.e., the success or failure of the operation, depends on the method of disposal. Even where a good compost market exists, provisions must still be made for storage because the use of composting is seasonal, with greatest demand during the spring and fall.
In the anaerobic composting process, facultative bacteria break down the organic materials in the absence of oxygen and produce methane and carbon dioxide. Single-stage digesters contain the entire process in one airtight container. The feedstock is first shredded, and before being placed in the container, water and possible nutrients are added to the previously shredded material. The single-stage digester may contain agitation equipment, which continuously stirs the liquefied material. As digestion progresses, a mixture of methane and carbon dioxide is produced. These gases are continuously removed from both first- and second- stage digesters and are either combusted on-site or directed to off-site gas consumers. A stabilised residue remains, when the digestion process is completed, which can be removed either by mechanical equipment or pumped out as a liquid. The digested residue may require further curing by windrow or static pile composting.