The Science of Composting
While our ancestors realized that compost was helpful for growing plants and improving soil health, they did not know how or why it worked. Our knowledge about the science of composting comes from research conducted during the past 50 years – relatively recent compared to the 2000 plus years that humans have been composting.
Backyard composting speeds up the natural process of decomposition, providing optimum conditions so that organic matter can break down more quickly. As you dig, turn, layer and water your compost pile, you may feel as if you are doing the composting , but the bulk of the work is actually done by numerous types of decomposer organisms.
Microorganisms In A Compost Pile
Microorganisms such as bacteria, fungi, and actinomycetes account for most of the decomposition that takes place in a pile. They are considered chemical decomposers, because they change the chemistry of organic wastes. The larger decomposers, or macroorganisms, in a compost pile include mites, centipedes, sow bugs, snails, millipedes, springtails, spiders, slugs, beetles, ants, flies, nematodes, flatworms, rotifers, and earthworms. They are considered to be physical decomposers because they grind, bite, suck, tear, and chew materials into smaller pieces.
Of all these organisms, aerobic bacteria are the most important
decomposers. They are very abundant; there may be millions in a gram of soil
or decaying organic matter. You would need 25,000 of them laid end to end
on a ruler to make an inch. They are the most nutritionally diverse of all
organisms and can eat nearly anything. Bacteria utilize carbon as a source
of energy (to keep on eating) and nitrogen to build protein in their bodies
(so they can grow and reproduce). They obtain energy by oxidizing organic
material, especially the carbon fraction. This oxidation process heats up
the compost pile from ambient air temperature. If proper conditions are present,
the pile will heat up fairly rapidly (within days) due to bacteria consuming
readily decomposable materials.
While bacteria can eat a wide variety of organic compounds, they have difficulty escaping unfavorable environments due to their size and lack of complexity. Changes in oxygen, moisture, temperature, and acidity can make bacteria die or become inactive. Aerobic bacteria need oxygen levels greater than five percent. They are the preferred organisms, because they provide the most rapid and effective composting. They also excrete plant nutrients such as nitrogen, phosphorus, and magnesium. When oxygen levels fall below five percent, the aerobes die and decomposition slows by as much as 90 percent. Anaerobic microorganisms take over and, in the process, produce a lot of useless organic acids and amines (ammonia-like substances) which are smelly, contain unavailable nitrogen and, in some cases, are toxic to plants. In addition, anaerobes produce hydrogen sulfide (aroma-like rotten eggs), cadaverine, and putrescine (other sources of offensive odors).
There are different types of aerobic bacteria that work in composting piles. Their populations will vary according to the pile temperature. Psychrophilic bacteria work in the lowest temperature range. They are most active at 55° F and will work in the pile if the initial pile temperature is less than 70º F. They give off a small amount of heat in comparison to other types of bacteria. The heat they produce is enough however, to help build the pile temperature to the point where another set of bacteria, mesophilic bacteria, start to take over.
Mesophilic bacteria rapidly decompose organic matter, producing acids, carbon
dioxide and heat. Their working temperature range is generally between 70º to
100º F. When the pile temperature rises above 100º F, the mesophilic
bacteria begin to die off or move to the outer part of the heap. They are
replaced by heat-loving thermophilic bacteria.
Thermophilic bacteria thrive at temperatures ranging from 113º to 160º F. Thermophilic bacteria continue the decomposition process, raising the pile temperature 130º to 160º F, where it usually stabilizes. Unless a pile is constantly fed new materials and turned at strategic times, the high range temperatures typically last no more than three to five days. Thermophilic bacteria use up too much of the degradable materials to sustain their population for any length of time. As the thermophilic bacteria decline and the temperature of the pile gradually cools off, the mesophilic bacteria again become dominant. The mesophilic bacteria consume remaining organic material with the help of other organisms.
The drop in compost pile temperature is not a sign that composting is complete, but rather an indication that the compost pile is entering another phase of the composting process. While high temperatures (above 140º F) have the advantage of killing pathogenic organisms and weed seeds, it is unnecessary to achieve those temperatures unless there is a specific concern about killing disease organisms and seeds. (You can greatly reduce the possibility of pathogens in a pile by excluding pet waste, diseased plants, and manure from diseased animals.) Many decomposers are killed or become inactive when pile temperatures rise above 140º F. If the pile temperature exceeds 160º F, you may want to take action and cool the pile by turning it. A number of research projects have shown that soil amended with compost can help fight fungal infestations. If the compost pile temperature goes above 160º F, the composting material may become sterile and lose its disease fighting properties.
While the various types of bacteria are at work, other microorganisms are also contributing to the degradation process. Actinomycetes, a higher-form bacteria similar to fungi and molds, are responsible for the pleasant earthy smell of compost. Grayish in appearance, actinomycetes work in the moderate heat zones of a compost pile. They decompose some of the more resistant materials in the pile such as lignin, cellulose, starches, and proteins. As they reduce materials, they liberate carbon, nitrogen, and ammonia, making nutrients available for higher plants. Actinomycetes occur in large clusters and become most evident during the later stages of decomposition.
Like bacteria and actinomycetes, fungi are also responsible for organic matter decay in a compost pile. Fungi are primitive plants that can be either single celled or many celled and filamentous. They lack a photosynthetic pigment. Their main contribution to a compost pile is to break down cellulose and lignin, after faster acting bacteria make inroads on them. They prefer cooler temperatures (70 to 75º F) and easily digested food sources. As a result, they also tend to take over during the final stage of composting.
Macroorganisms
As
mentioned earlier, larger organisms are involved in physically transforming
organic material into compost. They are active during the later stages of
composting – digging, chewing, sucking, digesting and mixing compostable
materials. In addition to mixing materials, they break it into smaller pieces,
and transform it into more digestible forms for microorganisms. Their excrement
is also digested by bacteria, causing more nutrients to be released.
Micro- and macroorganisms are part of a complex food chain. This food chain consists of organisms classified as either first-, second-, or third-level consumers. The categories are based on what they eat and who eats them. First level consumers become the food for second level consumers, which in turn, are eaten by third level consumers. Soil ecologist Dr. Daniel L. Dindal gives an example of how the food chain works in Ecology of Compost:
“Mites and springtails eat fungi. Tiny feather-winged beetles feed on fungal spores. Nematodes ingest bacteria. Protozoa and rotifers present in water films feed on bacteria and plant particles. Predaceous mites and pseudoscorpions prey upon nematodes, fly larvae, other mites and collembolans. Free-living flatworms ingest gastropods, earthworms, nematodes and rotifers. Third-level consumers such as centipedes, rove beetles, ground beetles, and ants prey on second-level consumers.”
The following is an overview of some of the larger macroorganisms you are likely to find in a compost pile.
Ants - Ants
feed on a variety of materials including fungi, seeds, sweets and other insects.
They help the composting process by bringing fungi and other organisms into
their nests. Ants can make compost richer in phosphorus and potassium by
moving minerals around as they work.
Millipedes – Millipedes
have wormlike segmented bodies, with each segment having two pairs of walking
legs (except the front few segments). Millipedes help break down plant material
by eating soft decaying vegetation. They will roll up in a ball when in danger.
Centipedes – Centipedes are flat, segmented worms with one pair of legs in each segment. They are third-level consumers that feed on soil invertebrates, especially insects and spiders.
Sow
bugs – Sow bugs have a flat and oval body with distinct
segments and ten pairs of legs. They are first-level consumers that feed
on rotting woody materials and other decaying vegetation. Pill bugs look
similar to sow bugs, but roll up in a ball when disturbed.
Springtails – Springtails
are small insects distinguished by their ability to jump
when
disturbed. They rarely exceed one-quarter inch in length and vary in color from
white to blue to black. Springtails are principally fungi feeders, although
they also eat molds and chew on decomposing plants.
Flies – Flies
are two-wing insects that feed on almost any kind of organic material. They
also act as airborne carriers of bacteria, depositing it wherever they land.
Although flies are not often a problem associated with compost piles, you
can control their numbers by keeping a layer of dry leaves or grass clippings
on top of the pile. Also, bury food scraps at least eight to twelve inches
deep into the pile. Thermophilic temperatures kill fly larvae. Mites help
to keep fly larvae reduced in numbers.
Beetles - Beetles
are insects with two pairs of wings. Types commonly found in compost piles
include the rove beetle, ground beetle, and feather-winged beetle.The
feather-winged beetle feeds on fungal spores. Immature grubs feed on decaying
vegetables. Adult rove and ground beetles prey on snails, slugs, and other
small animals.
Snails
and slugs - Snails and slugs are mollusks that travel in
a creeping movement. Snails have a spiral shell with a distinct head and
retractable foot. Slugs do not have a shell and are somewhat bullet shaped
with antennae on their front section. They feed primarily on living plant
material, but they will also attack plant debris. Look for them in finished
compost before using it, as they could do damage to your garden if they
move in.
Spiders - Spiders
are eight-legged creatures and third-level consumers that feed on insects
and small invertebrates. They can be very helpful for controlling garden
pests.
Earthworms - Earthworms
are the most important of the large physical decomposers in a compost pile.
Earthworms ingest organic matter and digest it with the help of tiny stones
in their gizzards. Their intestinal juices are rich in hormones, enzymes,
and other
fermenting substances that continue the breakdown process. The
worms leave dark, fertile castings behind. A worm can produce its weight
in castings each day. These castings are rich in plant nutrients such as
nitrogen, calcium, magnesium, and phosphorus that might otherwise be unavailable
to plants. Earthworms thrive on compost and contribute greatly to its quality.
The presence of earthworms in either compost or soil is evidence of good
microbial activity.
Key Factors Affecting The Composting Process
There are certain key environmental factors which affect the speed of composting. The organisms that make compost need food (carbon and nitrogen), air, and water. When provided with a favorable balance, they will produce compost quickly. Other organism factors affecting the speed of composting include surface area/particle size, volume, and temperature.
Food Factor
Organic material provides food for organisms in the form of carbon and nitrogen.
As described earlier, bacteria use carbon for energy and protein to grow
and reproduce. Carbon and nitrogen levels vary with each organic material.
Carbon-rich materials tend to be dry and brown such as leaves, straw, and
wood chips. Nitrogen materials tend to be wet and green such as fresh grass
clippings and food waste. A tip for estimating an organic material’s
carbon/nitrogen content is to remember that fresh, juicy materials are usually
higher in nitrogen and will decompose more quickly than older, drier, and
woodier tissues that are high in carbon.
A C:N ratio ranging between 25:1 and 30:1 is the optimum combination for rapid decomposition. If ratio is more than 30:1 carbon, heat production drops and decomposition slows. You may have noticed that a pile of leaves or wood chips will sit for a year or more without much apparent decay. When there is too much nitrogen, your pile will likely release the excess as smelly ammonia gas. Too much nitrogen can also cause a rise in the pH level which is toxic to some microorganisms.
The C:N ratio does not need to be exact. Values in Table 1 are calculated on a dry-weight basis. It is difficult to determine an exact C:N ratio without knowing the moisture content of the materials being used. Blending materials to achieve a satisfactory C:N ratio is part of the art of composting. A simple rule of thumb is to develop a volume-based recipe using from one-fourth to one-half high-nitrogen materials.
Table 1 provides estimates of the C:N ratio for selected composting materials.
TABLE 1. Carbon:Nitrogen Ratios
MATERIAL |
C:N RATIO |
Corn stalks |
50-100:1 |
Fruit waste |
35:1 |
Grass clippings |
12-25:1 |
Hay, green |
25:1 |
Leaves, ash, black elder and elm |
21-28:1 |
Leaves, pine |
60-100:1 |
Leaves, other |
30-80:1 |
Manure, horse and cow |
20-25:1 |
Paper |
170-200:1 |
Sawdust |
200-500:1 |
Seaweed |
19:1 |
Straw |
40-100:2 |
Vegetable waste |
12-25:1 |
Weeds |
25:1 |
Wood chips |
500-700:1 |
Air Factor
Proper aeration is a key environmental factor. Many microorganisms, including aerobic bacteria, need oxygen. They need oxygen to produce energy, grow quickly, and consume more materials. Aeration involves the replacement of oxygen deficient air in a compost pile with fresh air containing oxygen. Natural aeration occurs when air warmed by the composting process rises through the pile, bringing in fresh air from the surroundings. Aeration can also be affected by wind, moisture content, and porosity (spaces between particles in the compost pile). Composting reduces the pile’s porosity and decreases air circulation. Porosity can be negatively affected if large quantities of finely sized materials such as pine needles, grass clippings, or sawdust are used. In addition, air circulation can be impeded if materials become water saturated.
Air movement in the pile can be improved with a few simple techniques. The
easiest way to aerate a pile is to regularly turn it with a pitchfork or
shovel. Turning will fluff up the pile and increase its porosity. Another
option is to add coarse materials such as leaves, straw, or corn stalks.
Other options include using a compost aeration tool (available from garden
supply companies) or a ventilator stack. Stacks can be made out of perforated
plastic pipes, chicken wire wrapped in a circle, or bundles of twigs. Ventilator
stacks may be useful for large piles and should stick out the top or sides.
Moisture Factor
Decomposer organisms need water to live. Microbial activity occurs most rapidly in thin water films on the surface of organic materials. Microorganisms can only utilize organic molecules that are dissolved in water. The optimum moisture content for a compost pile should range from 40 to 60 percent. If there is less than 40 percent moisture, bacteria slow down and may become dormant. If there is more than 60 percent, water will force air out of pile pore spaces, suffocating the aerobic bacteria. Anaerobic bacteria will take over, resulting in unpleasant odors.
The ideal percentage of moisture will depend on the organic material’s
structure. Straw and corn stalks will need more moisture than leaves, while
food waste or grass clippings are not likely to need additional moisture.
Since it is difficult to measure moisture, a general rule of thumb is to
wet and mix materials so they are about as moist as a wrung-out sponge. Material
should feel damp to the touch, with just a drop or two of liquid expelled
when squeezed in your hand.
If a compost pile is too dry, it should be watered as the pile is being turned or with a trickling hose. Certain materials such as dead leaves, hay, straw, and sawdust should be gradually moistened until they glisten. These types of materials have a tendency to shed water or adsorb it only on the surface. If a pile is saturated with water, turn it so that materials are restacked. It may also help to add dry, carbon rich material.
Temperature Factor
Temperature is another important factor in the composting process and is related to proper air and moisture levels. As the microorganisms work to decompose the compost, they give off heat which in turn increases pile temperatures. Temperatures between 90º and 140ºF indicate rapid decomposition. Lower temperatures signal a slowing in the composting process. High temperatures greater than 140º F reduce the activity of most organisms.
Outside air temperatures can impact the decomposition process. Warmer outside temperatures in late spring, summer, and early fall stimulate bacteria and speed up decomposition. Low winter temperatures will slow or temporarily stop the composting process. As air temperatures warm up in the spring, microbial activity will resume. During winter months, compost piles can be covered with a tarp to help retain heat longer, but it is not necessary.
Novice composters and people interested in making fast compost may want to track temperatures. The most accurate readings will come from a compost thermometer or temperature probe. Compost thermometers are available from many garden supply companies.
Another method for monitoring temperature is to stick your fist into the pile. You can also place a metal pipe or iron bar in the middle of the pile, periodically pulling it out and feeling it. If the bar or the interior of the pile feels uncomfortably warm or hot during the first few weeks of composting, you’ll know everything is fine. If the temperature inside the pile is the same as the outside, that is an indication that the composting process is slow. You can increase activity by adding nitrogen rich material and turning the pile.
Particle Size Factor
Particle size affects the rate of organic matter breakdown. The more “surface area” available, the easier it is for microorganisms to work, because activity occurs at the interface of particle surfaces and air. Microorganisms are able to digest more, generate more heat, and multiply faster with smaller pieces of material. Although it is not required, reducing materials into smaller pieces will definitely speed decomposition. Organic materials can be chopped, shredded, split, bruised, or punctured to increase their surface area. Don’t “powder” materials, because they will compact and impede air movement in the pile.
For many yard trimmings, cutting materials with a knife, pruning shear,
or machete is adequate. An easy way to shred leaves is to mow them before
raking. You can collect them at the same time if your mower has a bag attachment.
Another option is to use a lawn trimmer to shred leaves in a garbage can. Several different models of shredders and chippers are available for sale or rental to use in shredding woody materials and leaves. It is a good idea to wear safety goggles when doing any type of shredding or chopping activity. Hands should be kept out of the machine while it is in operation.
Kitchen scraps can be chopped up with a knife. Some ambitious people use meat grinders and blenders to make “garbage soup” from their food scraps and water. They pour the mixture into their heaps.
Volume Factor
Volume is a factor in retaining compost pile heat. In order to become self insulating and retain heat, piles made in the Midwest should ideally be about one cubic yard. The one cubic yard size retains heat and moisture, but is not too large that the material will become unwieldy for turning. Homes located on lakes or in windy areas may want to consider slightly larger piles measuring 4 feet x 4 feet x 4 feet. Smaller compost piles will still decompose material, but they may not heat up as well, and decomposition is likely to take longer.


