Here is an essays on ‘Composting’ for class 9, 10, 11 and 12. Find paragraphs, long and short essays on ‘Composting’ especially written for school and college students.
Essay on Composting
Essay # 1. Meaning of Composting:
Composting is the purposeful biodegradation of organic matter, such as yard and food waste. The decomposition is performed by microorganisms, mostly bacteria, but also yeasts and fungi. In low temperature phases a number of macro-organisms, such as springtails, ants, nematodes, isopods and earthworms also contribute to the process, as well as soldier fly, fruit flies and fungus gnats. There are a wide range of organisms in the decomposer community.
i. A biodegradable material is capable of being completely broken down under the action of microorganisms into carbon dioxide, water and biomass. It may take a very long time for some material to biodegrade depending on its environment (e.g., wood in an arid area versus paper in water), but it ultimately breaks down completely. Many contaminating materials not dealt with in common composting are in fact “biodegradable”, and may be dealt with via bioremediation, or other special composting approaches.
ii. A compostable material biodegrades substantially under specific composting conditions. It is metabolized by the microorganisms, being incorporated into the organisms or converted into humus. The size of the material is a factor in determining compostability, and mechanical particle size reduction can speed the process. Large pieces of hardwood may not be compostable under a specific set of composting conditions, whereas sawdust of the same type of wood may be. Some biodegradable materials are only compostable under very specific conditions, usually with an industrial process.
Essay # 2. Importance of Composting:
Composting upcycles organic kitchen and yard waste and manures into an extremely useful humus like, soil end product, permitting the return of vital organic matter, nutrients, and particularly bacteria, that are vital to plant nutrition to the soil. Managed aerobic composting arranges environmental conditions so they are optimal for the natural processes to take place.
There is a popular expression:
“Compost happens”, but it is helpful to engineer the best possible circumstances for large amounts of organic waste to decompose quickly and efficiently, with the greatest conservation of useful nutrients and mass. Uncontrolled composting is when compost “happens”, and although that may be functional in some circumstances, as with forest floor detritus, a neglected heap of kitchen and yard wastes will more likely result in “smells happen”, or “rodents happen” long before useful compost does.
Long used in subsistence farming and home gardening for creating garden ready soil, composting is becoming increasingly important and better understood as a tool for reducing municipal solid waste, and reducing the amount of green waste going into landfills. The decomposition of organic material sent to landfills is a principal cause of methane, an important greenhouse gas, making reduction of organic waste being landfilled a key element in the fight against climate change.
In suburban and rural areas, much of the organic waste could be removed from the waste stream by promoting home composting, where consumers compost their yard waste and kitchen scraps on their own land, regardless of whether the material is ever actively re-used as “soil”. In urban areas with dwellings predominantly lacking individual yard space, there are indoor small scale composting alternatives, such as vermicomposting and bokashi composting.
Composting organisms require four equally important things to work effectively:
i. Carbon (“C” or carbohydrates), for energy – the microbial oxidation of carbon produces the heat.
— High carbon materials tend to be brown and dry.
ii. Nitrogen (“N” or protein), to grow and reproduce more organisms to oxidize the carbon.
— High nitrogen materials tend to be green (or colorful, like fruits and vegetables) and wet.
iii. Oxygen, for oxidizing the carbon, the decomposition process.
iv. Water, in the right amounts to maintain activity without causing anaerobic conditions.
Certain ratios of these elements will provide beneficial bacteria with the nutrients to work at a rate that will heat up the pile. In that process much water will be released as vapor (“steam”), and the oxygen will be quickly depleted, explaining the need to actively manage the pile. The hotter the pile gets, the more often added air and water is necessary; the air/water balance is critical to maintaining high temperatures until the materials are broken down. At the same time, too much air or water also slows the process, as does too much C (or too little N).
The most efficient composting occurs with a C:N mix of about 30 to 1. All organics have both carbon and nitrogen, but amounts vary widely, with characteristics noted above (dry/wet, brown/’ green). Fresh grass clippings have an average ratio of about 15 to 1 and dry autumn leaves about 50 to 1 depending on species.
Mixing equal parts by volume approximates the ideal C:N range. Few individual situations will provide the ideal mix of materials at any point in time in this respect, home composting is like horseshoes, perfect is great, but close still works. Observation of amounts, and consideration of different materials as a pile is built over time, can quickly achieve a workable technique for the individual situation.
Ingredients that are primarily carbon include:
(i) Dry, straw type material, such as cereal straws and corn stalks
(ii) Dry leaves (best shredded, as with a rotary mower, to prevent matting)
(iii) Wood, as coarse or fine (may compact) sawdust, or ground wood waste.
Paper and card board, both unprinted and printed are not recommended as both the inks and paper contain materials such as pigments, clays, binders, etc., that are not biodegradable. While these insoluble ingredients are not toxic, they will not readily break down as other biodegradable materials. In addition, paper will decompose very slowly interfering with the composting process.
Ingredients with relatively high nitrogen content include:
(i) Green plant material, like crop residues, new shoots, hay (especially alfalfa), grass clippings and weeds.
(ii) Manure from poultry, humans, pets, and herbivorous animals such as horses, cows and llamas.
(iii) Kitchen waste, fruit and vegetable cooked waste and trimmings, juicing-pulp residue, tea and coffee grounds, meat, bones, eggs.
For “back yard” composting, mixing the materials as they are added increases the rate of decomposition, as does reduced particle size (i.e., chopped, shredded), or materials can be added in alternating layers, about 15 centimetres (6 in) thick. Keeping a carbon “cache” handy to the pile for covering and mixing with fresh wet additions (lawn clippings, kitchen scraps) is simplest.
Special additions or activators are not necessary, although some sprinklings of good garden loam as a first pile is built will aid more rapid working by inoculating it with beneficial soil bacteria, and some of the material from the first finished batch can be used in the subsequent mixes.
Adding soil also provides grit to help earthworms digest, as well as providing particles for finished compost to aggregate with to create humus. Agricultural lime is not necessary the bacteria prefer a slightly acidic pH, and their processing invariably results in a near neutral product. Seaweed meal, rock dust or rock flour, and other trace element amendments are best added to the finished compost, or directly to the garden.
Essay # 3. Approaches to Composting:
1. Active (Aerobic):
An active compost heap, steaming on a cool morning. The heap is kept warm by the exothermic action of the bacteria as they decompose the organic matter.
Hot thermophilic composting is essential with some materials, such as meat and other animal products, dairy products, eggs, grease, cooking oil, manure of non-herbivores, and residuals from the treatment of wastewater, in order to kill pathogens; but these materials are not generally recommended in home composting because of the likelihood of creating odors and attracting rodents.
Human waste can be composted by industrial methods as well as composting toilets. When high temperatures are reached, the resulting compost can be safely used for agricultural or horticultural purposes, providing local health regulations are met. Humanure fertilizer (as opposed to night soil) is used throughout the developing world and is becoming more accepted as a garden amendment in the developed world.
Hot, aerobic composting is conducted at close to the ideal conditions noted above, allowing thermophilic bacteria to thrive. These aerobic bacteria break down material faster, producing less odor, fewer pathogens, and less greenhouse gas than cool, uncontrolled, or accidental anaerobic methods.
Commercial scale composting operations actively control the composting conditions (C:N ratio, moisture level and air), usually in a closed environment (in-vessel composting, tunnel composting or aerated static pile composting), where air is fan forced through the mass, and moisture added with sprayers, or conserved via the enclosure, with computer monitored probes detecting conditions.
In Thailand an aerated static pile system is in use by farmer groups at over 400 sites. The process needs only 30 days to finish without manual turning, with 10 metric tons of compost produced per month. A 38 centimetres (15 in) squirrelcage blower with 2.2 kilowatts (3.0 hp) motor is used to force air through 10 covered static piles of compost twice a day. The raw materials consist of agricultural wastes and animal manure in the ratio of 3:1 by volume.
High temperatures destroy insects, larvae, and weed seeds, but no compost will be totally sterilized by high temperatures alone. In a hot compost where the temperature exceeds 55 °C (131 °F) for several days, the ability of most organisms to survive is compromised, and there are temperature standards set by various regulating authorities for commercial products Nevertheless, many organisms in nature can survive extreme temperatures, including extremophiles such as Thermus thermophilus which play an important role in thermogenic composting, as well as pathogens such as Clostridium.
The necessary second stage of hot composting is maturation, a period allowing the dissipation of any phyto-toxins remaining from the process or contaminating ingredients (e.g., chemical residues), and achieving a state of nutrient stability (low C:N ratio) that will not have an impact on Nitrogen availability in the receiving soil.
For backyard composters, carbon and nitrogen ratios in various ingredients and the calculations required to get the ideal mixture can be intimidating, so rules of thumb exist for approximating it by ingredient types and condition. If the pile is built in a short period, and has a good mix of materials (C:N) and a coarse structure, with about 50% moisture (“like a squeezed out sponge”), the temperature should rise within days to as high as 60 °C (140 °F).
When the temperature begins to fall, more air is needed, usually added by turning the pile or using an agitating tool, and moisture may be needed at the same time. Turning or other aeration is usually needed about every 6-10 days to maintain the highest heat levels until the material is fairly uniformly broken down to unrecognizability, and temperatures no longer rebound. A pile that has been maintained at peak temperatures may be ready for maturing in as little as 30 days. Another 30-60 days maturing should suffice to allow passing the “germination test”.
To achieve thermophilic decomposition, a compost bin is best about 1 cubic metre (1.3 cu yd), or 1 metre (3 ft) wide, 1 metre (3 ft) tall, and as long as desired for windrow composting. This provides enough insulating mass to build up heat but also allows oxygen infiltration.
The center of the pile heats up the most, so regular turning/mixing is needed for insuring all material spends some time in the hottest area. When turning the pile results in no further temperature rise, the active aerobic phase is complete, and the mass may be turned out to a maturing pile. When the matured material has a dark brown crumbly appearance and the smell of rich damp earth, it is ready to use.
The natural sequence of the decomposition community involved will be:
(i) 0-15 °C (32-59 °F): Psychrophiles predominate, beginning the heating process as they multiply.
(ii) 15-40 °C (60-104 °F): Mesophiles take over, psychrophiles die off or are relegated to the borders.
(iii) 40-70 °C (105-160 °F): Thermophiles work at their peak, including consuming many other bacteria.
At the lower temperatures and around the borders, there will also be various fungal activity, as well as larger organisms, getting their share — a very dry, cooler pile may be attractive to ants, and gastropods may visit very wet piles. As the temperature returns to ambient at the end of the process, the sequence reverses, including new organisms that prefer the more degraded materials.
Added heat and pile insulation may be useful in the coldest weather, but is not ordinarily necessary, and is not desirable if it interferes with aeration or natural convective evaporation. Keeping the top dry and burying fresh additions in the center of a pile will be effective during winter conditions until heating resumes in spring.
2. Passive (Anaerobic):
Cool or ambient temperature composting, when the level of physical intervention is minimal, usually results in temperatures never reaching above 30 °C (86 °F). It is slower but effective, and is the more common type of composting in domestic gardening. Such composting systems may be in open or closed containers of wood or plastic, or in open exposed piles. Kitchen scraps are put in the garden compost bin and left untended.
This scrap bin can have a very high water content which reduces aeration, and may become odorous. To improve drainage and airflow, and reduce odor, carbon-rich materials, or ‘browns’, such as wood chips, shredded bark, leaves, or twigs may be added to mix and cover each wet addition, or holes made occasionally in the pile. The amount of attention may vary from none through occasional to “regular”.
Industrial Systems of Composting:
Industrial composting systems are increasingly being installed as a waste management alternative to landfills, along with other advanced waste processing systems. Mechanical sorting of mixed waste streams combined with anaerobic digestion or in-vessel composting, is called mechanical biological treatment, increasingly used in developed countries due to regulations controlling the amount of organic matter allowed in landfills. Treating biodegradable waste before it enters a landfill reduces global warming from fugitive methane; untreated waste breaks down anaerobically in a landfill, producing landfill gas that contains methane, a potent greenhouse gas.
Large scale composting systems are used by many urban centers around the world. Co-composting is a technique which combines solid waste with de-watered biosolids, although difficulties controlling inert and plastic contamination from Municipal solid waste makes this approach less attractive.
The world’s largest MSW co-composter is the Edmonton Composting Facility in Edmonton, Alberta, Canada, which turns 220,000 tonnes of residential solid waste and 22,500 dry tonnes of biosolids per year into 80,000 tonnes of compost. The facility is 38,690 meters2 (416,500 ft2), equivalent to 41/2 Canadian football fields, and the operating structure is the largest stainless steel building in North America, the size of 14 NHL rinks.
Purpose:
A home garden can be primarily fertilized with compost.
Past practices of biodegradable waste disposal not only remove valuable nutrients from the local biocycle, but when buried in a landfill, the anaerobic decomposition that results contributes to ground water contamination and uncontrolled methane generation, increasing the occurrence of greenhouse gas emissions.
Organic waste contains valuable nutrients that can contribute to the soil health in the immediate area of their production if recycled. Brown waste such as paper, cardboard, and dry plant material like leaves, are “captured carbon”, and green waste such as fresh plant residues and fruit and vegetable scrap contain much of the nitrogen used to generate their growth, as well as other essential macro and micronutrients, such as boron, copper, or iodine, lacking in some locales, so otherwise replaced with purchased commercial amendments. It also factors for minimum ammonium losses during composting of the residues of trimming.
From the compost at home, it can help improve your soil, prevent plant disease, and reduce greenhouse gases. The compost can also help soften plant material, increase the water holding capacity of the plant, and convert the ammonia in the plant into protein.
Agriculture:
Compost is an important source of nutrients commonly used in modern agriculture. Through steaming, compost can be sanitized and prepared for further use.
Home composting is the small scale domestic application of the principles of sustainable, biodegradable waste management, i.e. composting. The general principles involved in composting apply to any scale, from “backyard” to industrial, but the techniques will vary for each with the size of the waste stream, the cost, amount of effort, and the organization required.
Industrial scale systems are invariably capital and/or labor intensive, but on the home or small farm scale, composting can be managed to require varying outlay of capital and labor. For the small urban household, an indoor Bokashi or worm bin may suffice, for a suburban property with a larger yard and a food garden, a bin system would be preferable, while in small farm settings, a seasonal window system might be called for.
Container composting is a common style of small scale composting, using any of a wide variety of plastic, wood, masonry, or wire screen containers. Vented or closed sided compost bins each have proponents for the effect on air circulation and heat loss or retention in the compost. The Indore method developed by Sir Albert Howard, as well as the Shewell Cooper method favour spaced slats, while the New Zealand Box method advocates the use of closed sides. Combinations of the two are also used.
A compost bin is the container used to make compost. Commercially these bins may be made of hard plastic, and is commonly cylindrical in shape, although a variety of shapes and sizes are available. The manufactured bins are commonly found in urban and suburban areas, and in some districts of North America and the U.K., local authorities subsidise the cost to encourage public waste stream reduction.
They also may be user made out of wood, or whatever salvaged, recycled materials are at hand, particularly in rural areas or where larger amounts of yard and garden waste are generated. In some areas, community bin sites are provided. Compost bins can be as simple as a square slatted wood enclosure or as sophisticated as a tumbler, which allows for the “pile” to be turned for aeration purposes.
Sheet composting is the process of placing the organic matter for the compost directly onto the soil as a mulch and letting it decay there, rather than in a heap or container. One or more layers of organic material are spread over the growing area, watered thoroughly, and left to decompose until planting time. The next season’s garden is usually planted without tilling the compost into the soil.
More layers of organic material are placed as the bottom layers decompose thoroughly. This method is occasionally called “lasagna gardening” because of the layered structure.
Proponents of this system argue that sheet composting causes fewer nutrients to be lost through leaching than heap methods, also that fresh organic matter rather than decayed, provides a slower release of minerals when applied. It is also said that, in the long term, sheet composting leads to higher nitrogen levels in the soil, as some may be lost by leaching or vaporisation in a traditional heap.
Field composting is a large-scale composting method used in no till farming. Commonly, this is achieved by growing a ‘green manure’ cover crop such as mustard, alfalfa, or buckwheat, which is cut, preferably before seed setting, and left on the field to decompose. The next crop is sown without tilling the previous crop into the field. To avoid temporary nitrogen depletion, leguminous green manure crops such as lupin, winter tares, field beans, or clover, which are able to fix their own nitrogen supply in root nodules may be used. The nitrogen is released as the plants decay.