||This article contains instructions, advice, or how-to content. (September 2014)|
Vermicompost is the product or process of composting using various worms, usually red wigglers, white worms, and other earthworms to create a heterogeneous mixture of decomposing vegetable or food waste, bedding materials, and vermicast. Vermicast, also called worm castings, worm humus or worm manure, is the end-product of the breakdown of organic matter by an earthworm. These castings have been shown to contain reduced levels of contaminants and a higher saturation of nutrients than do organic materials before vermicomposting.
- 1 Suitable species
- 2 Large scale
- 3 Small scale
- 4 Climate and temperature
- 5 Feedstock
- 6 Harvesting
- 7 Properties
- 8 Benefits
- 9 As fertilizer
- 10 Troubleshooting
- 11 See also
- 12 Notes
- 13 References
- 14 External links
One of the earthworm species most often used for composting is the Red Wiggler (Eisenia fetida or Eisenia andrei); Lumbricus rubellus (a.k.a. red earthworm or dilong (China)) is another breed of worm that can be used, but it does not adapt as well to the shallow compost bin as does Eisenia fetida. European nightcrawlers (Eisenia hortensis) may also be used. Users refer to European nightcrawlers by a variety of other names, including dendrobaenas, dendras, and Belgian nightcrawlers. African Nightcrawlers (Eudrilus eugeniae) are another set of popular composters. Lumbricus terrestris (a.k.a. Canadian nightcrawlers (US) or common earthworm (UK)) are not recommended, as they burrow deeper than most compost bins can accommodate.
These species commonly are found in organic-rich soils throughout Europe and North America and live in rotting vegetation, compost, and manure piles. They may be an invasive species in some areas. As they are shallow-dwelling and feed on decomposing plant matter in the soil, they adapt easily to living on food or plant waste in the confines of a worm bin.
Composting worms are available to order online, from nursery mail-order suppliers or angling shops where they are sold as bait. They can also be collected from compost and manure piles. These species are not the same worms that are found in ordinary soil or on pavement when the soil is flooded by water.
Large-scale vermicomposting is practiced in Canada, Italy, Japan, Malaysia, the Philippines, and the United States. The vermicompost may be used for farming, landscaping, to create compost tea, or for sale. Some of these operations produce worms for bait and/or home vermicomposting.
There are two main methods of large-scale vermiculture. Some systems use a windrow, which consists of bedding materials for the earthworms to live in and acts as a large bin; organic material is added to it. Although the windrow has no physical barriers to prevent worms from escaping, in theory they should not due to an abundance of organic matter for them to feed on. Often windrows are used on a concrete surface to prevent predators from gaining access to the worm population.
The second type of large-scale vermicomposting system is the raised bed or flow-through system. Here the worms are fed an inch of "worm chow" across the top of the bed, and an inch of castings are harvested from below by pulling a breaker bar across the large mesh screen which forms the base of the bed.
Because red worms are surface dwellers constantly moving towards the new food source, the flow-through system eliminates the need to separate worms from the castings before packaging. Flow-through systems are well suited to indoor facilities, making them the preferred choice for operations in colder climates.
For vermicomposting at home, a large variety of bins are commercially available, or a variety of adapted containers may be used. They may be made of old plastic containers, wood, Styrofoam, or metal containers. The design of a small bin usually depends on where an individual wishes to store the bin and how they wish to feed the worms.
Some materials are less desirable than others in worm bin construction. Metal containers often conduct heat too readily, are prone to rusting, and may release heavy metals into the vermicompost. Some cedars, Yellow cedar, and Redwood contain resinous oils that may harm worms, although Western Red Cedar has excellent longevity in composting conditions. Hemlock is another inexpensive and fairly rot-resistant wood species that may be used to build worm bins.
Bins need holes or mesh for aeration. Some people add a spout or holes in the bottom for excess liquid to drain into a tray for collection. Worm compost bins made from plastic are ideal, but require more drainage than wooden ones because they are non-absorbent. However, wooden bins will eventually decay and need to be replaced.
Small-scale vermicomposting is well-suited to turn kitchen waste into high-quality soil amendments, where space is limited. Worms can decompose organic matter without the additional human physical effort (turning the bin) that bin composting requires.
Composting worms which are detritivorous (eaters of trash), such as the red wiggler Eisenia fetidae, are epigeic (surface dwellers) together with symbiotic associated microbes are the ideal vectors for decomposing food waste. Common earthworms such as Lumbricus terrestris are anecic(deep burrowing) species and hence unsuitable for use in a closed system. Other soil species that contribute include insects, other worms and molds.
Climate and temperature
The most common worms used in composting systems, redworms (Eisenia foetida, Eisenia andrei, and Lumbricus rubellus) feed most rapidly at temperatures of 15–25 °C (59-77 °F). They can survive at 10 °C (50 °F). Temperatures above 30 °C (86 °F) may harm them. This temperature range means that indoor vermicomposting with redworms is possible in all but tropical climates. (Other worms like Perionyx excavatus are suitable for warmer climates.) If a worm bin is kept outside, it should be placed in a sheltered position away from direct sunlight and insulated against frost in winter.
It is necessary to monitor the temperatures of large-scale bin systems (which can have high heat-retentive properties), as the feedstocks used can compost, heating up the worm bins as they decay and killing the worms.
There are few food wastes that vermicomposting cannot compost, although meat waste and dairy products are likely to putrefy, and in outdoor bins can attract vermin. Green waste should be added in moderation to avoid heating the bin.
Small-scale or home systems
- Fruits and vegetables (not including citrus, other "high acid" foods, onions and garlic)
- Vegetable and fruit peels and ends
- Coffee grounds and filters
- Loose tea and whole bags (even those with high tannin levels)
- Grains such as bread, cracker and cereal (including moldy and stale, but not including anything oily, such as pizza crusts)
- Ground up eggshells (well rinsed)
- Leaves and plant clippings (not sprayed with pesticides and no evergreen)
Large-scale or commercial
Such vermicomposting systems need reliable sources of large quantities of food. Systems presently operating use:
- Dairy cow or pig manure
- Sewage sludge.
- Brewery waste
- Cotton mill waste
- Agricultural waste
- Food processing and grocery waste
- Cafeteria waste
- Grass clippings and wood chips
Vermicompost is ready for harvest when it contains few-to-no scraps of uneaten food or bedding. There are several methods of harvesting from small-scale systems: "dump and hand sort", "let the worms do the sorting", "alternate containers" and "divide and dump." These differ on the amount of time and labor involved and whether the vermicomposter wants to save as many worms as possible from being trapped in the harvested compost.
While harvesting, it's also a good idea to try to pick out as many eggs/cocoons as possible and return them to the bin. Eggs are small, lemon-shaped yellowish objects that can usually be seen pretty easily with the naked eye and picked out.
Vermicompost has been shown to be richer in many nutrients than compost produced by other composting methods. It has also outperformed a commercial plant medium with nutrients added, but levels of magnesium required adjustment, as did pH.
It is rich in microbial life which converts nutrients already present in the soil into plant-available forms.
- Improves soil aeration
- Enriches soil with micro-organisms (adding enzymes such as phosphatase and cellulase)
- Microbial activity in worm castings is 10 to 20 times higher than in the soil and organic matter that the worm ingests 
- Attracts deep-burrowing earthworms already present in the soil
- Improves water holding capacity
- Enhances germination, plant growth, and crop yield
- Improves root growth and structure
- Enriches soil with micro-organisms (adding plant hormones such as auxins and gibberellic acid)
- Biowastes conversion reduces waste flow to landfills
- Elimination of biowastes from the waste stream reduces contamination of other recyclables collected in a single bin (a common problem in communities practicing single-stream recycling)
- Creates low-skill jobs at local level
- Low capital investment and relatively simple technologies make vermicomposting practical for less-developed agricultural regions
- Helps to close the "metabolic gap" through recycling waste on-site
- Large systems often use temperature control and mechanized harvesting, however other equipment is relatively simple and does not wear out quickly
- Production reduces greenhouse gas emissions such as methane and nitric oxide (produced in landfills or incinerators when not composted or through methane harvest)
Vermicompost can be mixed directly into the soil, or steeped in water and made into a worm tea by mixing some vermicompost in water, bubbling in oxygen with a small air pump, and steeping for a number of hours or days.
The microbial activity of the compost is greater if it is aerated during this period. The resulting liquid is used as a fertilizer or sprayed on the plants.
The dark brown waste liquid, or leachate, that drains into the bottom of some vermicomposting systems as water-rich foods break down, is best applied back to the bin when added moisture is needed due to the possibility of phytotoxin content and organic acids that may be toxic to plants.
The pH, nutrient, and microbial content of these fertilizers varies upon the inputs fed to worms. Pulverized limestone, or calcium carbonate can be added to the system to raise the pH.
When closed, a well-maintained bin is odorless; when opened, it should have little smell if any smell is present, it is earthy. Worms require gaseous oxygen. Oxygen can be provided by airholes in the bin, occasional stirring of bin contents, and removal of some bin contents if they become too deep or too wet. If decomposition becomes anaerobic from excess wet feedstock added to the bin, or the layers of food waste have become too deep, the bin will begin to smell of ammonia.
If decomposition has become anaerobic, to restore healthy conditions and prevent the worms from dying, the smelly, excess waste water must be removed and the bin returned to a normal moisture level. To do this, first reduce addition of food scraps with a high moisture content and second, add fresh, dry bedding such as shredded newspaper to your bin, mixing it in well.
Pests such as rodents and flies are attracted by certain materials and odors, usually from large amounts of kitchen waste, particularly meat. Eliminating the use of meat or dairy product in a worm bin decreases the possibility of pests.
In warm weather, fruit and vinegar flies breed in the bins if fruit and vegetable waste is not thoroughly covered with bedding. This problem can be avoided by thoroughly covering the waste by at least 2 inches (5.1 cm) of bedding. Maintaining the correct pH (close to neutral) and water content of the bin (just enough water where squeezed bedding drips a couple of drops) can help avoid these pests as well.
Worms generally stay in the bin, but may try to leave the bin when first introduced, or often after a rainstorm when outside humidity is high. Maintaining adequate conditions in the worm bin and putting a light over the bin when first introducing worms should eliminate this problem.
Commercial vermicomposters test, and may amend their products to produce consistent quality and results. Because the small-scale and home systems use a varied mix of feedstocks, the nitrogen, potassium and phosphorus content of the resulting vermicompost will also be inconsistent. NPK testing may be helpful before the vermicompost or tea is applied to the garden.
The mucus produced creates a natural time-release fertilizer which cannot burn plants.
- "Paper on Invasive European Worms". Retrieved 2009-02-22.
- Ndegwa, P.M.; Thompson, S.A.; Das, K.C. (1998). "Effects of stocking density and feeding rate on vermicomposting of biosolids" (PDF). Bioresource Technology 71: 5–12. doi:10.1016/S0960-8524(99)00055-3.
- 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.
- "Composting with earthworms". Herron Farms Dawsonville Ga. Retrieved March 26, 2013.
- "Composting Worms for Hawaii" (PDF). Retrieved 2009-02-22.
- "Great Lakes Worm Watch". Retrieved 2009-02-22.
- "Vermicomposting: A Better Option for Organic Solid Waste Management" (PDF). Retrieved 2009-02-21.
- "Compost Tea". Retrieved 2009-02-22.
- "Raising Earthworms Successfully" (PDF). Retrieved 2009-03-04.
- [dead link]
- "The Worm Dictionary and Vermiculture Reference Center". Working Worms. Retrieved 3 October 2012.
- Trautmann, Nancy. "Invertebrates of the Compost Pile". Cornell Center for the Environment. Retrieved 2012-10-03.
- Appelhof, p. 3
- "Map of vermicomposters". Vermicomposters.com. Retrieved 2012-10-03.
- Appelhof, p. 41
- Selden, Piper; DuPonte, Michael; Sipes, Brent; Dinges, Kelly (August 2005). "Small-Scale Vermicomposting" (PDF). Home Garden (University of Hawai'i) 45. Retrieved 2012-10-03.
- Reinecke, SA; Reinecke, AJ (February 2007). "The impact of organophosphate pesticides in orchards on earthworms in the Western Cape, South Africa." (PDF). Ecotoxicology and Environmental Safety 66 (2): 244–51. doi:10.1016/j.ecoenv.2005.10.006. PMID 16318873.
- Latest Developments In Mid-To-Large-Scale Vermicomposting[dead link]
- [dead link]
- Lotzof, M. "Very Large Scale Vermiculture in Sludge Stabilisation". Vermitech Pty Limited. Retrieved 2012-10-03.
- Appelhof, pp. 79-86
- [dead link]
- Dickerson, George W. (June 2001). "Vermicomposting: Guide H-164" (PDF). New Mexico State University. Retrieved 2012-10-03.
- Sherman, Rhonda. "Earthworm Castings as Plant Growth Media". Department of Biological and Agricultural Engineering at NCSU. Retrieved 2012-10-03.
- Lazcano, Cristina; Gómez-Brandón, María; Domínguez, Jorge (July 2008). "Comparison of the effectiveness of composting and vermicomposting for the biological stabilization of cattle manure" (PDF). Chemosphere 72 (7): 1013–1019. doi:10.1016/j.chemosphere.2008.04.016.
- Nancarrow, Loren; Taylor, Janet Hogan (1998). The Worm Book: The Complete Guide to Gardening and Composting with Worms Ten Speed Press. p. 4. ISBN 978-0-89815-994-3.
- Logsdon, Gene (October 1994). "Worldwide progress in vermicomposting". BioCycle 35 (10): 63.
- Appelhof, p. 111
- See Wikipedia article on single-stream recycling.
- "Waste Management to tap landfill methane". MSNBC. June 27, 2007. Retrieved 2012-10-03.
- Appelhof, p. 113
- Appelhof, p. 92
- "Manual of On-Farm Vermicomposting and Vermiculture" (PDF). p. 8. Retrieved 2009-12-10.
- Compost Worm Escape[dead link]
- [dead link]
- Grant, Tim; Littlejohn, Gail (2004). Teaching Green, The Middle Years. Gabriola Island, B.C.: New Society Publishers. p. 121. ISBN 978-0-86571-501-1.
- "Compost or Worm Castings?". VermiDirt. Retrieved 2012-10-03.
- Appelhof, Mary (2007). Worms Eat My Garbage (2nd ed.). Kalamazoo, Mich.: Flowerfield Enterprises. ISBN 978-0-9778045-1-1.
- Learning materials related to Vermicompost at Wikiversity