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compost

 
(kŏm'pōst') pronunciation
n.
  1. A mixture of decaying organic matter, as from leaves and manure, used to improve soil structure and provide nutrients.
  2. A composition; a mixture.
tr.v., -post·ed, -post·ing, -posts.
  1. To fertilize with a mixture of decaying organic matter.
  2. To convert (vegetable matter) to compost.

[Middle English compote, from Old French, mixture, compost, from Latin compositum, mixture, from neuter past participle of compōnere, to put together. See component.]


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Mass of rotted organic matter made from decomposed plant material. It is used in agriculture and gardening generally to improve soil structure rather than as a fertilizer, because it is low in plant nutrients. When properly prepared, it is free of obnoxious odours. Composts commonly contain about 2% nitrogen, 0.5 – 1% phosphorus, and about 2% potassium. Lime and nitrogen fertilizers and manure may be added to speed decomposition. The nitrogen of compost becomes available slowly and in small amounts. Because of their low nutrient content, composts are applied in large amounts.

For more information on compost, visit Britannica.com.

Gale's How Products Are Made:

How is compost made?

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Compost is a finely divided, loose material consisting of decomposed organic matter. It is primarily used as a plant nutrient and soil conditioner to stimulate crop growth. Although many people associate compost production with small garden compost piles that are tended with a shovel, most compost is produced in large municipal, industrial, or agricultural facilities using mechanized equipment.

Background

The expression "older than dirt" certainly applies to compost. Nature has been producing compost for millions of years as part of the cycle of life and death on Earth. The first human use of animal manure, a raw form of compost, was in about 3,000B.C. in Egypt when it was spread directly on the fields as a fertilizer. Later, manure was mixed with dirty stable straw and other refuse and allowed to sit in piles until it was needed. Rain kept the piles wet and aided the decomposition process, producing a rich compost.

The Greeks and Romans knew the value of compost to boost crop production and even used the warmth of decomposing compost to produce summer vegetables in winter. Christian monasteries kept the art of composting alive in Europe after the fall of the Roman Empire, and by about 1200 compost was again being used by many farmers. Shakespeare mentions it in several of his plays written in the early 1600s.

In the United States, Presidents George Washington and Thomas Jefferson were prominent landowners during the late-1700s and early-1800s. When they were not involved with affairs of state, they both spent much of their time trying innovative farming practices, including experiments with various composting methods and materials. As years of successive crops depleted the nutrients in the soil on the East Coast, the practice of composting became widespread. This trend continued until the early 1900s when it was estimated that 90% of the fertilizer used in the United States came from compost.

That all changed in 1913, when a German company began producing synthetic nitrogen compounds, including fertilizers. These new chemical fertilizers could be produced less expensively than messy animal manure compost, and the farmyard compost pile quickly became a thing of the past. By 1950, it was estimated that only 1% of the fertilizer used in the United States was derived from compost.

One notable exception to this trend was the work started in 1942 by J.I. Rodale, a noted pioneer in the development of the organic method of farming. Rodale was one of the first to see the hazards of relying on synthetic fertilizers and the benefits of using compost derived from natural sources. Composting got a short-lived boost during the environmentally conscious era of the 1960s, but it wasn't until the 1980s when it became a big business. This surge wasn't the result of a renewed awareness of the positive aspects of compost, but rather a growing concern over the negative aspects of refuse. In short, in our efforts to get rid of our refuse, we were polluting our air, poisoning our rivers, and quite literally burying ourselves in it with our landfills.

In order to divert some of the municipal refuse away from landfills, several cities established recycling centers in the early 1970s where people could bring cans, bottles, and newspaper rather than throw them in the trash. This was followed by curbside recycling, where people could place these recyclable materials in separate containers for pickup in front of their houses. Finally, many cities added additional curbside containers for yard wastes to be composted. By 1992, almost 1,500 cities had yard waste composting facilities.

At the same time, tough new environmental laws mandated that industries could no longer simply dump their waste products onto the surrounding land or discharge them into nearby rivers. To meet these laws, many industries began their own recycling and composting programs. Environmental concerns also affected farmers, who were being blamed for the negative health effects that chemical fertilizers and pesticides had on humans and wildlife. As a result, many farmers decided to cut back or eliminate chemicals in favor of using compost.

Today, most compost is processed in large facilities designed to handle a specific type of raw material. Agricultural compost is usually produced and used on the same farm that generated the raw materials. Industrial compost may be bagged and sold to individual buyers, or the raw materials may be sold in bulk to other composting facilities. Municipal yard waste compost is usually produced in facilities operated by the city or the refuse collection company and is sold to local landscaping companies and garden centers.

Raw Materials

Technically, compost may be made from any organic material. That is, it may be made from any part of an organism, plant or animal, that contains carbon. Compost also requires a source of nitrogen, oxygen, and water, plus small amounts of a variety of elements usually found in organic material, including phosphorus, copper, potassium, calcium, and others.

In order for the organic materials to combine with the other materials and decompose into compost, several living organisms and microorganisms are needed. These include sowbugs, which help digest the materials and transport bacteria; earthworms, which aerate the materials with their tunnels; a variety of fungi, which help digest decay-resistant cellulose; mold-like bacteria called actinomycetes, which attack raw plant tissues; and many others.

The most common raw materials used to make compost are yard wastes such as grass clippings, leaves, weeds, and small prunings from shrubs and trees. Most home garden compost piles and municipal compost facilities use yard wastes exclusively because of the large volume of materials available.

Industrial compost facilities tend to use waste materials generated within a particular plant or region. For example, sugar beet pulp is mixed with other materials to make compost in an area where sugar refineries operate. Spent hops and grain from breweries also make excellent compost materials. Other materials include sawdust and wood chips from lumber mills, fish waste from canneries, and dried blood and pulverized animal bones from slaughterhouses.

Agricultural compost facilities use materials readily available on nearby farms. These include animal manure, used stable straw, spoiled fruits and vegetables, field refuse, vineyard and orchard prunings, rotted hay, and other agricultural waste products.

Some of the more unusual raw materials used to make compost include seaweed, chicken feathers, peanut shells, and hair clippings.

The Manufacturing
Process

The production of compost is both a mechanical and a biological process. The raw materials must first be separated, collected, and shredded by mechanical means before the biological decomposition process can begin. In some cases, the decomposition process itself is aided by mechanical agitation or aeration of the materials. After decomposition, the finished compost is mechanically screened and bagged for distribution.

There are several methods for producing compost on a large scale. The methane digester method places the raw materials in a large, sealed container to exclude oxygen. The resulting oxygen-starved decomposition not only produces compost, but also methane gas, which can be used for cooking or heating. The aerated pile method places the raw materials in piles or trenches containing perforated pipes that circulate air. The resulting oxygen-rich decomposition produces a great amount of heat, which kills most harmful bacteria. The windrow method places the raw materials in long piles, called windrows, where they are allowed to decompose naturally over a period of several weeks or months. It is the least expensive method of all. Here is a typical sequence of operations used to convert municipal yard wastes into compost using the windrow method.

Separating

  • Yard wastes are deposited in separate containers by homeowners, and the containers are placed at the curb for pickup on the regular refuse collection day. Homeowners are instructed that only certain yard wastes are acceptable for collection. These include grass clippings, leaves, weeds, and small prunings from shrubs and trees. Short pieces of tree limbs up to about 6 in (15 cm) in diameter are also acceptable. Homeowners are also instructed that certain other yard wastes are not acceptable. These include rocks, sod, animal excrement, and excessive amounts of dirt. Palm fronds are prohibited because the frond spikes do not decompose and carry a poison. Food scraps, fruits, and vegetables are also prohibited because they can attract rodents, carry unwanted seeds, and contribute to odors.
  • The yard wastes are collected by separate refuse trucks and are transported to the processing center where they are dumped in piles. The piles are visually inspected, and any oversized or unacceptable materials are manually removed.

Grinding

  • A large, wheeled machine called a front loader picks up material from the piles and dumps it into a tub grinder. The tub grinder has a stationary vertical cylindrical outer shell with a rotating cylindrical inner shell. As the material passes between the two shells, it is ground into smaller pieces and thoroughly mixed. The ground material falls out the bottom and through a screen where the larger pieces are screened out. The remaining material is transported by a conveyor belt to a holding pile.
  • The larger pieces are sold to landscaping companies for use as mulch or ground-cover without further processing. The rest is loaded into large dump trucks and transported to the composting area where it is dumped in long rows, called windrows. Each row is about 6-10 ft (2-3 m) high and several hundred feet (m) long with a triangular cross section. A flat space about 10 ft (3 m) wide is left between each row to allow vehicles to move along the length.

Composting

  • The composting area may cover several acres (hectares). After a windrow is laid in place, the material is dampened by a tank truck that moves along the row spraying water. The water aids in the composting process and helps minimize wind-blown dust.
  • Every few weeks, a special machine straddles each windrow and moves along its length to turn and agitate the material. This breaks down the material into even smaller pieces and exposes it to oxygen, which aids in the decomposition process. After the windrow is turned, it is sprayed with water again. This process continues for two or three months. In hot, dry weather, the windrows may have to be watered more often. During decomposition, the internal temperature of the pile may reach 130° F (54° C), which helps kill many of the weed seeds that might be present.

Curing

  • The raw compost is scooped up with a front loader and moved to a large conical pile where it is allowed to finish the decomposition process over a period of several weeks. This process is called curing and it allows the carbon and nitrogen in the compost to adjust to their final levels.

Screening

  • After the compost has cured, it is scooped up with a front loader and dumped into the hopper of a rotary screen. This device consists of a large cylindrical screen rotating on an axis that is slightly inclined above the horizontal. The openings in the screen are about 0.5 in (1 cm) in diameter. The compost is fed into the raised end of the rotating screen from the hopper by a conveyor belt. As the compost tumbles its way down the length of the rotating screen, the smaller material falls through the screen and is moved to a storage pile by a conveyor belt. The larger material that cannot pass through the screen falls out the lower end of the cylinder and is either returned to the compost piles for further decomposition or is sold as wood chips.

Distributing

  • Much of the finished compost is loaded into large dump trucks and sold in bulk to landscaping companies, municipalities, nurseries, and other commercial customers. Some of it is sealed in 40 lb (18 kg) plastic bags for retail sale to homeowners. Using the windrow method, a typical suburban yard waste processing facility can produce as much as 100,000 tons (91,000 metric tons) of compost a year.

Quality Control

Composting companies regularly have their finished compost tested to ensure it is free of harmful materials and contains the proper amounts of plant nutrients. The tests measure the size of the particles, moisture level, mineral content, carbon-to-nitrogen ratio, acidity, nutrient content, weed seed germination rate, and many other factors. For example, waste particles should be between 0.5-2 in (1.2-5 cm) in diameter in order to encourage the flow of oxygen within the compost. Likewise, the level of moisture should be above 40% to facilitate the compost process. Moisture levels that dip below 40% slow the process and present the risk of spontaneous combustion. Also, the ideal ratio of carbon to nitrogen should average 30 parts carbon to one part nitrogen by weight. The ideal balance maintains a healthy microbial population that speeds decomposition and minimizes odor.

Harmful Materials

Compost made from yard wastes, such as leaves and grass clippings, rarely contains any harmful materials. Problems can occur, however, when compost is made from partially sorted municipal refuse, certain industrial wastes, or sewage sludge. In those cases, unacceptable levels of toxic metals, chemicals, or harmful bacteria may be present.

To protect the public, the federal Environmental Protection Agency (EPA) sets acceptable levels for thousands of materials that might be present in compost. Each state may have its own standards as well. For municipal refuse, source separation—that is, having homeowners sort their yard wastes into separate containers rather than throw them away with the rest of their trash—is felt to be one of the most effective way to produce clean, safe compost.

The Future

By separating home yard wastes and turning them into compost, it is estimated that municipalities can reduce the amount of trash going to landfills by about 20%. While that is a significant reduction, it is expected that even more trash will have to be diverted from landfills in the future. Materials such as soiled food packaging, disposable diaper padding, food scraps, natural fiber rags, pieces of wood, and other organic materials could all be composted. To do this, municipalities may have to establish municipal solid waste (MSW) treatment facilities to separate the compostible materials from the harmful materials, such as discarded batteries, motor oil, asbestos, and many household chemicals.

Eventually composting may also provide a means for handling and neutralizing even the harmful materials. For example, at several older military ammunition factories and storage facilities the surrounding soil is contaminated with the explosive material trinitrotoluene, also known as TNT. Researchers are using a specially formulated compost mix of vegetable wastes and buffalo manure to neutralize the soil through a simple biological composting process that converts the explosive organic components of TNT into less harmful compounds.

Where to Learn More

Books

Christopher, Tom and Marty Asher. Compost This Book! Sierra Club Books, 1994.

Hansen, Beth, editor. Easy Compost. Brooklyn Botanic Gardens, Inc., 1997.

Martin, Deborah L. and Grace Gershuny, ed. The Rodale Book of Composting. Rodale Press, Inc., 1992.

Periodicals

Raloff, Janet. "Cleaning Up Compost: Municipal waste managers see hot prospects in rot" Science News (January 23, 1993): 56-58.

Other

The Compost Resource Page. http://www.oldgrowth.org/compost/ (June 7, 1999).

Composting Council. May 1999. http://www.compostingcouncil.org/ (June 7,1999).

[Article by: Chris Cavette]


A mixture usually consisting largely of decomposed organic material; used for fertilizing soil.


compost, substance composed mainly of partly decayed organic material that is applied to fertilize the soil and to increase its humus content; it is often used in vegetable farming, home gardens, flower beds, lawns, and greenhouses. Compost usually is made from plant materials (e.g., grass clippings, vegetable tops, garden weeds, hay, tree leaves, sawdust, and peat) together with manure and some soil; lime, superphosphates, and nitrogen fertilizers are often added with manure to reinforce the compost and hasten its decomposition.



Decomposed organic matter, often referred to as “brown gold,” that has the crumbly texture and feel of good garden soil. It is both a fertilizer and a soil conditioner. Materials suitable for a compost pile include leaves, grass clippings, dead plants, and vegetable kitchen wastes, as well as cow and horse manures. See also cold compost; hot compost.

Word Tutor:

compost

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pronunciation

IN BRIEF: n. - A mixture of decaying vegetation and manure v. - Convert to a pile of rotting vegetation.

Tutor's tip: "Composed" is the past tense of compose, "composite" is something made up of separate elements or pieces, "compost" is a mixture of vegetable materials decomposing to make fertilizer, while a "compote" is a dessert composed of several cooked fruits.

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Compost

Compost (play /ˈkɒmpɒst/ or /ˈkɒmpst/) is organic matter that has been decomposed and recycled as a fertilizer and soil amendment. Compost is a key ingredient in organic farming. At the simplest level, the process of composting simply requires making a heap of wetted organic matter (leaves, food waste) and waiting for the materials to break down into soil after a period of weeks or months. Modern, methodical composting is a multi-step, closely monitored process with measured inputs of water, air and carbon- and nitrogen-rich materials. The decomposition process is aided by shredding the plant matter, adding water and ensuring proper aeration by regularly turning the mixture. Worms and fungi further break up the material. Aerobic bacteria manage the chemical process by converting the inputs into heat, carbon dioxide and ammonium. The ammonium is further converted by bacteria into plant-nourishing nitrites and nitrates through the process of nitrification.

Compost can be rich in nutrients. It is used in gardens, landscaping, horticulture, and agriculture. The compost itself is beneficial for the land in many ways, including as a soil conditioner, a fertilizer, addition of vital humus or humic acids, and as a natural pesticide for soil. In ecosystems, compost is useful for erosion control, land and stream reclamation, wetland construction, and as landfill cover (see compost uses). Organic ingredients intended for composting can alternatively be used to generate biogas through anaerobic digestion. Anaerobic digestion is fast overtaking composting in some parts of the world including central Europe as a primary means of downcycling waste organic matter.

Contents

History

A modern compost bin constructed from plastics

Composting as a recognized practice dates to at least the early Roman Empire since Pliny the Elder (AD 23-79). Traditionally, composting was to pile organic materials until the next planting season, at which time the materials would have decayed enough to be ready for use in the soil. The advantage of this method is that little working time or effort is required from the composter and it fits in naturally with agricultural practices in temperate climates. Disadvantages (from the modern perspective) are that space is used for a whole year, some nutrients might be leached due to exposure to rainfall, and disease producing organisms and insects may not be adequately controlled.

Composting was somewhat modernized beginning in the 1920s in Europe as a tool for organic farming.[1] The first industrial station for the transformation of urban organic materials into compost was set up in Wels/Austria in the year 1921.[2] The early personages most cited for propounding composting within farming are for the German-speaking world Rudolf Steiner, founder of a farming method called biodynamics, and Annie Francé-Harrar, who was appointed on behalf of the government in Mexico and supported the country 1950–1958 to set up a large humus organization in the fight against erosion and soil degradation. In the English-speaking world it was Sir Albert Howard who worked extensively in India on sustainable practices and Lady Eve Balfour who was a huge proponent of composting. Composting was imported to America by various followers of these early European movements in the form of persons such as J.I. Rodale (founder of Rodale Organic Gardening), E.E. Pfeiffer (who developed scientific practices in biodynamic farming), Paul Keene (founder of Walnut Acres in Pennsylvania), and Scott and Helen Nearing (who inspired the back-to-land movement of the 1960s). Coincidentally, some of these personages met briefly in India - all were quite influential in the U.S. from the 1960s into the 1980s.

There are many modern proponents of rapid composting that attempt to correct some of the perceived problems associated with traditional, slow composting. Many advocate that compost can be made in 2 to 3 weeks.[3] Many such short processes involve a few changes to traditional methods, including smaller, more homogenized pieces in the compost, controlling carbon to nitrogen (CN) ratio at 30 to 1 or less, and monitoring the moisture level more carefully. However, none of these parameters differ significantly from early writings of Howard and Balfour, suggesting that in fact modern composting has not made significant advances over the traditional methods that take a few months to work. For this reason and others, many modern scientists who deal with carbon transformations are sceptical that there is a "super-charged" way to get nature to make compost rapidly.[1] They also point to the fact that it is the structure of the natural molecules - such as carbohydrates, proteins, and cellulose - that really dictate the rate at which microbial-mediated transformations are possible.

Some cities such as Seattle and San Francisco require food and yard waste to be sorted for composting.[4][5]

Ingredients

Home compost barrel in the Escuela Barreales, Chile.

Composting organisms require four equally important things to work effectively:

  • Carbon — for energy; the microbial oxidation of carbon produces the heat, if included at suggested levels [2].
    • High carbon materials tend to be brown and dry.
  • Nitrogen — to grow and reproduce more organisms to oxidize the carbon.
    • High nitrogen materials tend to be green (or colorful, such as fruits and vegetables) and wet.[6]
  • Oxygen — for oxidizing the carbon, the decomposition process.
  • Water — in the right amounts to maintain activity without causing anaerobic conditions.
Materials in a compost pile.

Certain ratios of these materials 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 (135°-160° Fahrenheit) until the materials are broken down. At the same time, too much air or water also slows the process, as does too much carbon (or too little nitrogen).

The most efficient composting occurs with a carbon:nitrogen mix of about 30 to 1. Nearly all plant and animal materials have both carbon and nitrogen, but amounts vary widely, with characteristics noted above (dry/wet, brown/green).[7] 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. Observation of amounts, and consideration of different materials[8] as a pile is built over time, can quickly achieve a workable technique for the individual situation.

Urine

People excrete far more of certain water-soluble plant nutrients (nitrogen, phosphorus, potassium) in urine than in feces.[9] Human urine can be used directly as fertilizer or it can be put onto compost. Adding a healthy person's urine to compost usually will increase temperatures and therefore increase its ability to destroy pathogens and unwanted seeds. Urine from a person with no obvious symptoms of infection is generally much more sanitary than fresh feces. Unlike feces, urine doesn't attract disease-spreading flies (such as house flies or blow flies), and it doesn't contain the most hardy of pathogens, such as parasitic worm eggs. Urine usually does not stink for long, particularly when it is fresh, diluted, or put on sorbents.[citation needed]

Urine is primarily composed of water and urea. Although metabolites of urea are nitrogen fertilizers, it is easy to over-fertilize with urine, or to utilize urine containing pharmaceutical (or other) content, creating too much ammonia for plants to absorb, acidic conditions, or other phytotoxicity.[10]

Manure and bedding

On many farms, the basic composting ingredients are manure generated on the farm and bedding. Straw and sawdust are common bedding materials. Non-traditional bedding materials are also used, including newspaper and chopped cardboard. The amount of manure composted on a livestock farm is often determined by cleaning schedules, land availability, and weather conditions. Each type of manure has its own physical, chemical, and biological characteristics. Cattle and horse manures, when mixed with bedding, possess good qualities for composting. Swine manure, which is very wet and usually not mixed with bedding material, must be mixed with straw or similar raw materials. Poultry manure also must be blended with carbonaceous materials - those low in nitrogen preferred, such as sawdust or straw.[11]

Micro-organisms

With the proper mixture of water, oxygen, carbon, and nitrogen, micro-organisms are allowed to break down organic matter to produce compost.[12] The composting process is dependant on micro-organisms to break down organic matter into compost. There are many types of microorganisms found in active compost of which the most common are:[13]

  • Bacteria- The most numerous of all the micro organisms found in compost.
  • Actinomycetes- Necessary for breaking down paper products such as newspaper, bark, etc.
  • Fungi- Molds and yeast help break down materials that bacteria cannot, especially lignin in woody material.
  • Protozoa- Help consume bacteria, fungi and micro organic particulates.
  • Rotifers- Rotifers help control populations of bacteria and small protozoans.

In addition, earthworms not only ingest partly composted material, but also continually re-create aeration and drainage tunnels as they move through the compost.

A lack of a healthy micro-organism community is the main reason why composting processes are slow in landfills with environmental factors such as lack of oxygen, nutrients or water being the cause of the depleted biological community.[13]

Common items suitable for composting

These common items can likely be added to compost with no negative effect.

  • Paperboard or clean paper
  • Dried-out egg shells
  • Leaves, garden trimmings
  • Fruits and vegetables
  • Coffee and tea

Uses

Compost is generally recommended as an additive to soil, or other matrices such as coir and peat, as a tilth improver, supplying humus and nutrients. It provides a rich growing medium, or a porous, absorbent material that holds moisture and soluble minerals, providing the support and nutrients in which plants can flourish, although it is rarely used alone, being primarily mixed with soil, sand, grit, bark chips, vermiculite, perlite, or clay granules to produce loam. Compost can be tilled directly into the soil or growing medium to boost the level of organic matter and the overall fertility of the soil. Compost that is ready to be used as an additive is dark brown or even black with an earthy smell.[14]

Generally, direct seeding into a compost is not recommended due to the speed with which it may dry and the possible presence of phytotoxins that may inhibit germination,[15][16][17] and the possible tie up of nitrogen by incompletely decomposed lignin.[8] It is very common to see blends of 20–30% compost used for transplanting seedlings at cotyledon stage or later.

Destroying pathogens, seeds, or unwanted plants

Composting can destroy pathogens or unwanted seeds. Unwanted living plants (or weeds) can be discouraged by covering with mulch/compost.

The "microbial pesticides" in compost may include thermophiles and mesophiles, however certain composting detritivores such as black soldier fly larvae and redworms, also reduce many pathogens. Thermophilic (high-temperature) composting is well known to destroy many seeds and nearly all types of pathogens (exceptions may include prions).

The sanitizing qualities of (thermophilic) composting are desirable where there is a high likelihood of pathogens, such as with manure. Applications include humanure composting or the deep litter technique.

Types

In addition to the traditional compost pile, various approaches have been developed to handle different composting processes, ingredients, locations, and applications for the composted product.

Grub composting

Grub composting uses the black soldier fly larvae (BSFL) to quickly convert manure or kitchen waste into an animal feed for poultry, fish, pigs, lizards, turtles, and possibly dogs. In a grub bin, BSFL self-harvest when mature by crawling into a separate collection container. The harvested grubs are exceptionally nutritious and medicinal for poultry. This is probably the fastest composting technique. The composted residue can be used as a soil amendment or as food for worms (redworms).

BSFL often appear naturally in worm bins, composting toilets, or compost bins. Without much added cost, these devices could be designed to also harvest BSFL.

Bokashi composting

Inside a recently started bokashi bin. The aerated base is just visible through the food scraps and bokashi bran.

Bokashi composting uses an aerobic or anaerobic inoculation to produce the compost. Once a starter culture is made, it can be used to extend the culture indefinitely, like yogurt culture. Since the popular introduction of effective microorganisms (EM), bokashi is commonly made with only molasses, water, EM, and wheat bran.

In home composting applications, kitchen waste is placed into a container (often known as a bokashi bin or bokashi bucket) that can be sealed with an air-tight lid. These scraps are then inoculated with a bokashi EM mix. This usually takes the form of a carrier, such as rice hulls, wheat bran, or sawdust, that has been inoculated with composting micro-organisms. The EM are natural lactic acid bacteria, yeast, and phototrophic bacteria that act as a microbe community within the kitchen scraps, fermenting and accelerating breakdown of the organic matter. The user would place alternating layers of food scraps and Bokashi mix until the container is full. Liquid "compost tea" is drained once or twice a week and can be diluted 1:100 and added to plants as fertilizer, and is safe to pour down the sewer for disposal.[18] Once the container is full, it is left to ferment for one to two weeks in the container, and then buried under 6-8 inches of soil, in ground or in a non-reactive container. After another two weeks buried under soil, the food scraps should be broken down into rich humus.

Compost tea

Compost tea is a liquid extract or a dissolved solution but not simply a suspension of compost. It is made by steeping compost in water for 3-7 days. It was discovered in Germany and became a practice to suppress foliar fungal diseases by nature of the bacterial competition, suppression, antibiosis on the leaf surface (phyllosphere). It has also been used as a fertilizer although lab tests show it is very weak in nutrients with less than 100ppm of available nitrogen and potassium. Other salts present in the tea solution are sodium, chlorides and sulfates.[19] The extract is applied as a spray to non-edible plant parts such as seedlings, or as a soil-drench (root dip), or as a surface spray to reduce incidence of harmful phytopathogenic fungi in the phyllosphere.[20]

Hügelkultur

The practice of making raised garden beds filled with rotting wood.[21][22] It is in effect creating a Nurse log, however, covered with dirt.

Benefits of hugelkultur garden beds include water retention and warming of soil.[23][24] Buried wood becomes like a sponge (material) as it decomposes, able to capture water and store it for later use by crops planted on top of the hugelkultur bed.[25][26]

The buried decomposing wood will also give off heat, as all compost does, for several years. These effects have been used by Sepp Holzer for one to allow fruit trees to survive at otherwise inhospitable temperatures and altitudes.[27]

"Humanure"

"Humanure" is a portmanteau neologism designating human excrement (feces and urine) that is recycled via composting for agricultural or other purposes. The term was popularized in a 1994 book by Joseph Jenkins[28] that advocates the use of this organic soil amendment.[29]

Humanure is not traditional sewage that has been processed by waste-treatment facilities, which may include waste from industrial and other sources; rather, it is the combination of feces and urine with paper and additional carbon material (such as sawdust). A humanure system, such as a composting toilet, does not require water or electricity, and when properly managed does not smell. Because the term "humanure" has no authoritative definition it is subject to misuse; news reporters occasionally fail to correctly distinguish between humanure and "sewer sludge" or "biosolids".[30]

By disposing of feces and urine through composting, the nutrients contained in them are returned to the soil. This aids in preventing soil degradation. Human fecal matter and urine have high percentages of nitrogen, phosphorus, potassium, carbon, and calcium. It is equal to many fertilizers and manures purchased in garden stores. Humanure aids in the conservation of fresh water by avoiding the usage of potable water required by the typical flush toilet. It further prevents the pollution of ground water by controlling the fecal matter decomposition before entering the system. When properly managed, there should be no ground contamination from leachate.

As a substitute for a flush water process, it reduces the energy consumption and, hence, greenhouse gas emissions associated with the transportation and processing of water and waste water.

Humanure may be deemed safe for humans to use on crops if handled in accordance with local health regulations, and composted properly. This means that thermophilic decomposition of the humanure must heat it sufficiently to destroy harmful pathogens, or enough time must have elapsed since fresh material was added that biological activity has killed any pathogens. To be safe for crops, a curing stage is often needed to allow a second mesophilic phase to reduce potential phytotoxins.

Humanure is different from night soil, which is raw human waste spread on crops. While aiding the return of nutrients in fecal matter to the soil, it can carry and spread a vast number of human pathogens. Humanure kills these pathogens both by the extreme heat of the composting and the extended amount of time (1 to 2 years) that it is allowed to decompose.

Vermicompost

Rotary screen harvested worm castings

Vermicompost is the product of composting utilizing various species of worms, usually red wigglers, white worms, and earthworms to create a heterogeneous mixture of decomposing vegetable or food waste (excluding meat, dairy, fats, or oils), bedding materials, and vermicast. Vermicast, also known as worm castings, worm humus or worm manure, is the end-product of the breakdown of organic matter by species of earthworm.[31] Vermicomposting is widely used in North America for on-site institutional processing of food waste, such as in hospitals and shopping malls[32]. This type of composting is sometimes suggested as a feasible indoor home composting method[33].

The earthworm species (or composting worms) most often used are red wigglers (Eisenia fetida) or Eisenia andrei), though European nightcrawlers (Eisenia hortensis) could also be used. Red wigglers are recommended by most vermiculture experts, as they have some of the best appetites and breed very quickly. Users refer to European nightcrawlers by a variety of other names, including dendrobaenas, dendras, and Belgian nightcrawlers.

Containing water-soluble nutrients, vermicompost is a nutrient-rich organic fertilizer and soil conditioner in a form that is relatively easy for plants to absorb.[34] Worm castings are sometimes used as an organic fertilizer. Because the earthworms grind and uniformly mix minerals in simple forms, plants need only minimal effort to obtain them. The worms' digestive systems also add beneficial microbes to help create a "living" soil environment for plants.[citation needed]

Vermicompost tea has been shown to cause a 173.5% increase in plant growth by mass over plants grown without castings. These results were seen with only 10% addition of castings to produce these results.[35]

Alternative to land-filling

As concern about landfill space increases, worldwide interest in recycling by means of composting is growing, since composting is a process for converting decomposable organic materials into useful stable products.[36] Industrial scale composting in the form of in-vessel composting, aerated static pile composting, and anaerobic digestion takes place in most Western countries now, and in many areas is mandated by law. There are process and product guidelines in Europe that date to the early 1980s (Germany, the Netherlands, Switzerland) and only more recently in the UK and the US. In both these countries, private trade associations within the industry have established loose standards, some say as a stop-gap measure to discourage independent government agencies from establishing tougher consumer-friendly standards.[37][38] The USA is the only Western country that does not distinguish sludge-source compost from green-composts, and by default in the USA 50% of states expect composts to comply in some manner with the federal EPA 503 rule promulgated in 1984 for sludge products.[39] Compost is regulated in Canada and Australia as well.

Industrial systems

A large compost pile that is steaming with the heat generated by thermophilic microorganisms.

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, and are increasingly being 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.

Vermicomposting is used for medium-scale on-site institutional composting, such as for food waste from universities and shopping malls: selected either as an more environmental choice, or to reduce the cost of commercial waste removal[40].

Large-scale composting systems are used by many urban areas around the world. Co-composting is a technique that combines solid waste with de-watered biosolids, although difficulties controlling inert and plastics 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 4½ Canadian football fields, and the operating structure is the largest stainless steel building in North America, the size of 14 NHL rinks.[41] In 2006, the State of Qatar awarded Keppel Seghers Singapore, a subsidiary of Keppel Corporation to begin construction on a 275,000 tonne/year Anaerobic Digestion and Composting Plant licensed by Kompogas Switzerland. This plant, with 15 independent anaerobic digestors will be the world's largest composting facility once fully operational in early 2011 and forms part of the Qatar Domestic Solid Waste Management Center, the largest integrated waste management complex in the Middle East.[42]

See also

References

  1. ^ Heckman, J. 2006. A history of organic farming: transitions from Sir Albert Howard’s War in the Soil to USDA National Organic Program. Renew. Agric. Food Syst. 21:143–150.
  2. ^ Welser Anzeiger vom 05. Januar 1921, 67. Jahrgang, Nr. 2, S. 4
  3. ^ The Rapid Compost Method by Robert Raabe, Professor of Plant Pathology, Berkeley
  4. ^ "San Francisco Signs Mandatory Recycling & Composting Laws". http://www.inhabitat.com/2009/06/24/san-francisco-mandates-recycling-composting/. Retrieved 19 September 2010. 
  5. ^ Tyler, Aubin (21 March 2010). "The case for mandatory composting". The Boston Globe. http://www.boston.com/bostonglobe/magazine/articles/2010/03/21/the_case_for_mandatory_composting/. Retrieved 19 September 2010. 
  6. ^ Materials for composting - University of Illinois extension, retrieval date: 3/12/2009
  7. ^ Klickitat County WA, USA Compost Mix Calculator
  8. ^ a b Effect of lignin content on bio-availability
  9. ^ Stockholm Environment Institute - EcoSanRes - Guidelines on the Use of Urine and Feces in Crop Production
  10. ^ Pharmaceutical residures in urine and potential risks related to use as fertilzer in agriculture, Martina Winker, Doctoral dissertation, 2009
  11. ^ Dougherty, Mark. (1999). Field Guide to On-Farm Composting. Ithaca, New York: Natural Resource, Agriculture, and Engineering Service.
  12. ^ "Compost Made Simple". Greenmi.net. http://greenmi.net/compost-made-simple/. Retrieved 21 October 2010. 
  13. ^ a b "Composting - Compost Microorganisms". Cornell University. http://compost.css.cornell.edu/microorg.html. Retrieved 6 October 2010. 
  14. ^ Healthy Soils, Healthy Landscapes
  15. ^ Morel, P. and Guillemain, G. 2004. Assessment of the possible phytotoxicity of a substrate using an easy and representative biotest. Acta Horticulture 644:417–423
  16. ^ Itävaara et al. Compost maturity - problems associated with testing. in Proceedings of Composting. Innsbruck Austria 18-21.10.2000
  17. ^ Phytotoxicity and maturation
  18. ^ "Bokashi Composting Australia". http://www.bokashi.com.au/How-Bokashi-works.htm. 
  19. ^ Zhang, W., Han, D. Y., Dick, W. A., Davis, K. R., and Hoitink, H. A. J. 1998. Compost and compost water extract-induced systemic acquired resistance in cucumber and Arabidopsis. Phytopathology 88:450-455.
  20. ^ Tränkner, A. 1992. Use of agricultural and municipal organic wastes to develop suppression to plant pathogens. in: Biological Control of Plant Diseases. E. C. Tjamos, G. C. Papavizas, and R. J. Cook, eds. Plenum Press, New York.
  21. ^ http://www.richsoil.com/hugelkultur/
  22. ^ http://permaculture.org.au/2010/08/03/the-art-and-science-of-making-a-hugelkultur-bed-transforming-woody-debris-into-a-garden-resource/
  23. ^ http://www.richsoil.com/hugelkultur/
  24. ^ http://permaculture.org.au/2012/01/04/hugelkultur-composting-whole-trees-with-ease/#more-6825
  25. ^ http://www.richsoil.com/hugelkultur/
  26. ^ Hemenway, Toby (2009). Gaia's Garden: A Guide to Home-Scale Permaculture. Chelsea Green Publishing. pp. 84-85. ISBN 9781603580298.
  27. ^ http://permaculture.org.au/2010/08/03/the-art-and-science-of-making-a-hugelkultur-bed-transforming-woody-debris-into-a-garden-resource/
  28. ^ Joseph Jenkins
  29. ^ Jenkins, J.C. (2005). The Humanure Handbook: A Guide to Composting Human Manure. Grove City, PA: Joseph Jenkins, Inc.; 3rd edition. pp. 255. ISBN 978-0-9644258-3-5. http://www.humanurehandbook.com. Retrieved April 2011. 
  30. ^ Courtney Symons (13 October 2011). "'Humanure' dumping sickens homeowner". YourOttawaRegion. Metroland Media Group Ltd.. http://www.yourottawaregion.com/feature/article/1224782--humanure-dumping-sickens-homeowner. Retrieved 16 October 2011. 
  31. ^ "Paper on Invasive European Worms". http://southwoodsforestgardens.blogspot.com/2009/01/paper-on-invasive-european-worms.html. Retrieved 2009-02-22. 
  32. ^ "Latest Developments in Mid- to Large-scale Vermicomposting". http://www.jgpress.com/BCArticles/2000/110051.html. Retrieved 2012-01-31. 
  33. ^ "Vermicomposting: Indoor Composting with Earthworms". http://www.mass.gov/dep/recycle/reduce/vermi.htm. Retrieved 201-06-26. 
  34. ^ Coyne, Kelly and Erik Knutzen. The Urban Homestead: Your Guide to Self-Sufficient Living in the Heart of the City. Port Townsend: Process Self Reliance Series, 2008.
  35. ^ Web article on worm castings effects on plant growth
  36. ^ A Brief History of Solid Waste Management
  37. ^ British Standards Institute Specifications FAQ
  38. ^ http://www.compostingcouncil.org/
  39. ^ U.S. Government Printing Office. 1998. Electronic Code of Federal Regulations. Title 40, part 503. Standards for the use or disposal of sewage sludge. Available at: http://ecfr.gpoaccess.gov/cgi/t/text/text-idx?c ecfr&tpl /ecfrbrowse/Title40/40cfr503 main 02.tpl. Retrieved 30 March 2009.
  40. ^ "Latest Developments in Mid- to Large-scale Vermicomposting". http://www.jgpress.com/BCArticles/2000/110051.html. Retrieved 2012-01-31. 
  41. ^ Edmonton composting facility
  42. ^ Keppel Seghers developing the first integrated waste management facility in the Middle East

Further reading

  • Roger Tim Haug, Practical Handbook of Compost Engineering [Hardcover]. Lewis Publishers.
  • Insam, H; Riddech, N; Klammer, S (Eds.): Microbiology of Composting,Springer Verlag, Berlin New York 2002, ISBN 978-3-540-67568-6
  • Hogg, D., J. Barth, E. Favoino, M. Centemero, V. Caimi, F. Amlinger, W. Devliegher, W. Brinton., S. Antler. 2002. Comparison of compost standards within the EU, North America, and Australasia. Waste and Resources Action Programme Committee (UK)

External links

Organisations

Translations:

Compost

Top

Dansk (Danish)
n. - kompost, blanding
v. tr. - kompostere, gøde med kompost

Nederlands (Dutch)
compost, mengsel, met compost bedekken, composteren

Français (French)
n. - compost, terreau
v. tr. - composter

Deutsch (German)
n. - Kompost
v. - kompostieren

Ελληνική (Greek)
n. - κοπρόχωμα (κν. φουσκί), μίγμα, σύμφυρμα
v. - κοπρίζω, λιπαίνω

Italiano (Italian)
concimare, concime

Português (Portuguese)
n. - adubo composto (m)
v. - adubar

Русский (Russian)
удобрять компостом, компост

Español (Spanish)
n. - abono vegetal, abono compuesto
v. tr. - abonar, convertir en abono

Svenska (Swedish)
n. - kompost
v. - kompostera, gödsla m kompost

中文(简体)(Chinese (Simplified))
混合物, 堆肥, 施堆肥

中文(繁體)(Chinese (Traditional))
n. - 混合物, 堆肥
v. tr. - 施堆肥

한국어 (Korean)
n. - 혼합물, 배양토, 퇴비
v. tr. - 퇴비를 주다, 회반죽을 바르다

日本語 (Japanese)
n. - 堆肥
v. - 堆肥を施す, 堆肥にする

العربيه (Arabic)
‏(الاسم) مواد نباتيه متحلله لتسميد الأرض, سماد عضوي (فعل) سمد الأرض بهذه المواد‏

עברית (Hebrew)
n. - ‮זבל אורגני, זבל, קומפוסט, קרקע שדושנה בקומפוסט, הפך לקומפוסט‬
v. tr. - ‮זיבל בקומפוסט, הפך לקומפוסט‬


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