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[[File:Compostingtoilet.jpg|thumb|Public composting toilet facility on E6 highway in Sweden]]
[[File:Compostingtoilet.jpg|thumb|Public composting toilet facility on E6 highway in Sweden]]


A '''composting toilet''' is a [[dry toilet]] that uses a predominantly aerobic processing system that treats [[Excretion|excreta]], typically with no water or small volumes of flush water, via [[composting]] or managed aerobic [[decomposition]].<ref>[http://www.epa.gov/owm/mtb/comp.pdf US EPA "Fact Sheet: Composting Toilets"]</ref> Composting toilets may be used as an alternative to [[flush toilet]]s in situations where there is no suitable water supply or waste treatment facility available, or to capture nutrients in human excreta as [[humanure]]. They are in use in many of the roadside facilities and national parks in for example Sweden, USA, United Kingdom and Australia.
A '''composting toilet''' is a [[dry toilet]] that uses a predominantly aerobic processing system that treats [[human waste|human excreta]], typically with no water or small volumes of flush water, via [[composting]] or managed aerobic [[decomposition]].<ref>[http://www.epa.gov/owm/mtb/comp.pdf US EPA "Fact Sheet: Composting Toilets"]</ref> Composting toilets may be used as an alternative to [[flush toilet]]s in situations where there is no suitable water supply or sewer system and [[sewage treatment plant]] available, or to capture nutrients in human excreta as [[humanure]]. They are in use in many of the roadside facilities and national parks in for example Sweden, USA, United Kingdom and Australia.


The human excrement is normally mixed with [[sawdust]], [[Coir|coconut coir]] or [[peat moss]] to support aerobic processing, absorb liquids, and to mitigate odor. The decomposition process is generally faster than the anaerobic decomposition used in wet [[sewage treatment]] systems such as [[septic tank]]s.
The human excrement is normally mixed with [[sawdust]], [[Coir|coconut coir]] or [[peat moss]] to support aerobic processing, absorb liquids, and to mitigate odor. The decomposition process is generally faster than the anaerobic decomposition used in wet [[sewage treatment]] systems such as [[septic tank]]s.


== Terminology ==
== Terminology ==
Composting toilets should not be confused with the [[pit latrine]], [[arborloo]] or [[tree bog]], all of which are forms of less controlled decomposition, and may not protect [[groundwater]] from nutrient or pathogen contamination or provide optimal nutrient recycling. They should also not be confused with [[Urine-diverting dry toilet|urine-diverting dry toilets]] (UDDTs) where pathogen removal is achieved through dehydration and the faeces collection vault is therefore kept as dry as possible (whereas in a composting toilet a certain degree of moisture is aimed for in the composting chamber).

Composting toilets are usually set up without [[urine diversion]] but can also include urine diversion. Offering a [[waterless urinal]] in addition to the composting toilet can help keep excess amounts of urine out of the composting chamber.
Composting toilets are usually set up without [[urine diversion]] but can also include urine diversion. Offering a [[waterless urinal]] in addition to the composting toilet can help keep excess amounts of urine out of the composting chamber.


Composting toilets can be used to implement an [[ecological sanitation]] (ecosan) approach for [[resource recovery]], however it would be wrong to call a composting toilet an "ecosan toilet" as ecosan is an approach and not a specific technology.
Composting toilets use aerobic decomposition and should therefore not be confused with [[Urine-diverting dry toilet|urine-diverting dry toilets]] (UDDTs) where sanitation is achieved through dehydration.

The [[ecosan]] concept which is sometimes referred to either one of those systems does not necessarily apply because certain criteria must be met.

Composting toilets should not be confused with the [[pit latrine]], [[arborloo]] or [[tree bog]], all of which are forms of less controlled decomposition, and may not protect ground water from nutrient or pathogen contamination or provide optimal nutrient recycling.


== Appropriateness ==
== Appropriateness ==
Composting toilets can be suitable in areas with no suitable water supply or waste treatment facility. Furthermore they can be used for [[resource recovery]] by reusing sanitized faeces and urine in agriculture as fertilizer and soil conditioner.
Composting toilets can be suitable in areas with no suitable [[water supply]], [[sewer]] system and [[sewage treatment plant]]. Furthermore they can be used for [[resource recovery]] by reusing sanitized feces and urine in agriculture as fertilizer and soil conditioner.


In cold climates the composting chamber should be indoors so that the composting process is not inhibited due to low temperatures.
In cold climates the composting chamber should be indoors so that the composting process is not inhibited due to low temperatures.

Revision as of 17:37, 30 December 2014

Public composting toilet facility on E6 highway in Sweden

A composting toilet is a dry toilet that uses a predominantly aerobic processing system that treats human excreta, typically with no water or small volumes of flush water, via composting or managed aerobic decomposition.[1] Composting toilets may be used as an alternative to flush toilets in situations where there is no suitable water supply or sewer system and sewage treatment plant available, or to capture nutrients in human excreta as humanure. They are in use in many of the roadside facilities and national parks in for example Sweden, USA, United Kingdom and Australia.

The human excrement is normally mixed with sawdust, coconut coir or peat moss to support aerobic processing, absorb liquids, and to mitigate odor. The decomposition process is generally faster than the anaerobic decomposition used in wet sewage treatment systems such as septic tanks.

Terminology

Composting toilets should not be confused with the pit latrine, arborloo or tree bog, all of which are forms of less controlled decomposition, and may not protect groundwater from nutrient or pathogen contamination or provide optimal nutrient recycling. They should also not be confused with urine-diverting dry toilets (UDDTs) where pathogen removal is achieved through dehydration and the faeces collection vault is therefore kept as dry as possible (whereas in a composting toilet a certain degree of moisture is aimed for in the composting chamber).

Composting toilets are usually set up without urine diversion but can also include urine diversion. Offering a waterless urinal in addition to the composting toilet can help keep excess amounts of urine out of the composting chamber.

Composting toilets can be used to implement an ecological sanitation (ecosan) approach for resource recovery, however it would be wrong to call a composting toilet an "ecosan toilet" as ecosan is an approach and not a specific technology.

Appropriateness

Composting toilets can be suitable in areas with no suitable water supply, sewer system and sewage treatment plant. Furthermore they can be used for resource recovery by reusing sanitized feces and urine in agriculture as fertilizer and soil conditioner.

In cold climates the composting chamber should be indoors so that the composting process is not inhibited due to low temperatures.

Design considerations

A composting toilet usually consists of four main parts:[2]

  1. a reactor which is the storage or composting chamber
  2. a ventilation unit to provide air to ensure aerobic conditions and to allow carbon dioxide and water to evaporate
  3. a leachate collection system to drain excess liquid
  4. an access door for withdrawing the mature product

The composting chamber can be constructed below or above ground, indoors or outdoors with a separate superstructure. A drainage system should be installed to ensure the removal of leachate. Otherwise, too much moisture can cause anaerobic conditions and impede the degradation. Urine diversion can improve the compost quality since urine contains a large ammounts of ammonia that inhibits microbiological activity.[2]

Types

Several manufactured composting toilet models are on the market, and construct-it-yourself systems are also popular.[3]

  • This is the pedestal for a split-system composting toilet where collection/treatment chambers are located below the bathroom floor.
    This is the pedestal for a split-system composting toilet where collection/treatment chambers are located below the bathroom floor.
  • Inexpensive do-it-yourself compost toilet at Dial House, Essex, England, utilizing an old desk as the toilet unit.
    Inexpensive do-it-yourself compost toilet at Dial House, Essex, England, utilizing an old desk as the toilet unit.
  • Henry Moule's earth closet, patented in 1873. Example from around 1875. Rear chamber for dispensing cover material
    Henry Moule's earth closet, patented in 1873. Example from around 1875. Rear chamber for dispensing cover material
  • Composting toilet in wood
    Composting toilet in wood

Manufactured composting toilet systems

"Self-contained" composting toilets complete or begin the composting in a container within the receiving fixture. They are slightly larger than a flush toilet, but use roughly the same floor space. Some units use fans for aeration, and optionally, heating elements to maintain optimum temperatures to hasten the composting process and to evaporate urine and other moisture. Operators of composting toilets commonly add a small amount of absorbent carbon material (such as untreated sawdust, coconut coir, peat moss) after each use to create air pockets for better aerobic processing, to absorb liquid, and to create an odor barrier. This additive is sometimes referred to as "bulking agent." Some owner-operators use microbial "starter" cultures to ensure composting bacteria are in the process, although this is not critical.

"Remote," "central," or "underfloor" units collect excreta via a toilet stool, either waterless or micro-flush, from which it drains to a composter. "Vacuum-flush systems" can flush horizontally or upward with a small amount of water to the composter; "micro-flush toilets" use about 500 millilitres (17 US fl oz) per use. These units feature a chamber below the toilet stool (such as in a basement or outside) where composting takes place and are suitable for high-volume and year-round applications as well as to serve multiple toilet stools.

"Desiccating toilets" dry the excreta to destroy pathogens, though one study suggested that subsequent contact with moisture can cause rehydration of pathogens.[4]

Self built unit

Site-built or self-built composting toilet designs vary, ranging from roll-away containers fitted with aerators to large concrete sloped-bottom tanks.

Treatment of excreta

Finished compost from a composting toilet in Kiel-Hassee, Germany

There are four main factors that affect the decomposition process:[2]

  1. Oxygen: There has to be enough oxygen to ensure aerobic composting
  2. Moisture: Proper moisture content of 45 to 70 percent
  3. Internal heap temperature: ideally between 40 to 50 °C (achieved through proper chamber dimensioning)
  4. Carbon-to-nitrogen ratio (C:N): ideally 25:1

Rapid aerobic composting will be thermophilic decomposition in which bacteria that thrive at high temperatures (40-60 °C or 104-140 °F) oxidize (break down) the waste into its components, some of which are consumed in the process, reducing volume, and eliminating potential pathogens.

A urine-diverting-dehydration toilet. 1:Humus compartment, 2:Ventilation pipe, 3:Toilet seat, 4:Urinal, 5:Urine collection and dehydration, A:Second floor, B:First floor, C:Ground floor

Drainage of excess liquid or leachate via a separate drain at the bottom of the composter is featured in some manufactured units, as the aerobic composting process requires moisture levels to be controlled (ideally 50±10%): too dry, and the mass decomposes slowly or not at all; too wet and anaerobic organisms thrive, creating undesirable odors (cf. Anaerobic digestion). This separated liquid may be diverted to a blackwater system or collected for other uses. Some units include a urine-separator or urine-diverting system.

Urine can contain up to 90 percent of the nitrogen, up to 50 percent of the phosphorus, and up to 70 percent of the potassium present in human excreta.[5] In healthy individuals it is usually pathogen free, although undiluted it may contain inorganic salts and organic compounds at levels toxic to plants.[6]

The other requirement critical for microbial action, as well as drying, is air. Commercial systems provide methods of ventilation that move air from the room, through the waste container, and out a vertical pipe, venting above the enclosure roof. This air movement (via convection or fan forced) will vent carbon dioxide and odors.

Some units require manual methods for periodic aeration of the solid mass such as rotating a drum inside the unit or working an "aerator rake" through the mass. Composting toilet brands have different provisions for emptying the "finished product", and supply a range of capacities based on volume of use. Frequency of emptying will depend on the speed of the decomposition process and capacity, from a few months (active hot composting) to years (passive, cold composting). With a properly sized and managed unit, a very small volume (about 10% of inputs) of a humus-like material results, which can be suitable as soil amendment for agriculture, depending on local public health regulations.

Composting toilets greatly reduce the volume of excreta on site through psychrophilic, thermophilic or mesophilic composting and yield a soil amendment that can be used in horticultural or agricultural applications as local regulations allow. In combination with a constructed wetland these even require only the half area.[7]

History

Henry Moule's earth closet design, circa 1909.

Before the flush toilet became universally accepted in the late 19th century, there were inventors, scientists, and public health officials who supported the use of dry earth closets, or composting toilets. These were invented by the English clergyman Henry Moule, who dedicated his life to improving public sanitation after witnessing the horrors of the cholera epidemics of 1849 and 1854. Impressed by the insalubrity of the houses, especially during the Great Stink in the summer of 1858, he invented what he called the 'dry earth system'.

In partnership with James Bannehr, he took out a patent for the process (No. 1316, dated 28 May 1860). Among his works bearing on the subject were: "The Advantages of the Dry Earth System", 1868; "The Impossibility overcome: or the Inoffensive, Safe, and Economical Disposal of the Refuse of Towns and Villages", 1870; "The Dry Earth System", 1871; "Town Refuse, the Remedy for Local Taxation", 1872, and "National Health and Wealth promoted by the general adoption of the Dry Earth System", 1873.

His system was adopted in private houses, in rural districts, in military camps, in many hospitals, and extensively in the British Raj. Ultimately, however, it failed to gain the same public support and attention as the water closet, although the design remains today in some parts of the world.

Society and culture

Regulation

United States of America

There are no universally accepted performance standards for composting toilets in the United States, although seven jurisdictions in North America[8] rely on testing of manufactured systems to American National Standard/NSF International Standard ANSI/NSF 41-1998: Non-Liquid Saturated Treatment Systems.[9] An updated version of ANSI/NSF Standard 41 was published in 2011.[10][note 1] Systems might also be listed with CSA, cETL-US, and other standards programs.

Examples

Germany

The ecological settlement in Allermöhe, Hamburg, is a reference project with a history reaching back to 1982. The settlement consits of 36 single-family houses with approximately 140 inhabitants and uses composting toilets besides rainwater harvesting and constructed wetlands. The waterless toilet system saves about 40 litres of water per capita per day compared to a conventional flush toilet (10 liter per flush) which adds up to 2,044 m³ water savings per year for the whole settlement.[11]

Notes

  1. ^ A listing of the most current NSF/ANSI standards can be found in PDF format at NSF International's Standards subdomain.

References

  1. ^ US EPA "Fact Sheet: Composting Toilets"
  2. ^ a b c Tilley, E., Ulrich, L., Lüthi, C., Reymond, Ph., Zurbrügg, C. Compendium of Sanitation Systems and Technologies - (2nd Revised Edition). Swiss Federal Institute of Aquatic Science and Technology (Eawag), Duebendorf, Switzerland. ISBN 978-3-906484-57-0.{{cite book}}: CS1 maint: multiple names: authors list (link) Cite error: The named reference ":0" was defined multiple times with different content (see the help page).
  3. ^ National Small Flows Clearinghouse, West Virginia University, Composting toilet technology
  4. ^ Austin, Aussie (October 2000). "Health implications of reusing dehydrated faecal matter" (PDF). Deutsche Gesellschaft für Technische Zusammenarbeit. Retrieved 2009-06-05. {{cite web}}: Cite has empty unknown parameter: |coauthors= (help)
  5. ^ J.O. Drangert, Urine separation systems
  6. ^ Liquid Gold: The Lore & Logic of Using Urine to Grow Plants, 2004
  7. ^ Waterreport: Composting toilets and constructed wetlands
  8. ^ Oregon Onsite Advisory Committee "Final Report of Recommended Changes to Rules Governing Onsite Systems", OR DEQ, February 8, 2010, accessed May 8, 2011.
  9. ^ EPA on ANSI/NSF standard
  10. ^ "PUBLICATIONS - Standards and Criteria - March 21, 2013" (PDF). NSF International. p. 4. Retrieved 24 March 2013. Wastewater Treatment Units … NSF/ANSI 41 – 2011: Non-liquid saturated treatment systems (composting toilets)
  11. ^ Rauschning, G., Berger, W., Ebeling, B., Schöpe, A. (2009). Ecological settlement in Allermöhe Hamburg, Germany - Case study of sustainable sanitation projects. Sustainable Sanitation Alliance (SuSanA)

External links