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The Single Pit is one of the most widely used sanitation technologies. Excreta, along with anal cleansing materials (water or solids) are deposited into a pit. Lining the pit prevents it from collapsing and provides support to the superstructure.

As the Single Pit fills, two processes limit the rate of accumulation: leaching and degradation. Urine and anal cleansing water percolate into the soil through the bottom of the pit and wall while microbial action degrades part of the organic fraction.

On average, solids accumulate at a rate of 40 to 60L per person/year and up to 90L per person/year if dry cleansing materials such as leaves, newspapers, and toilet paper are used. The volume of the pit should be designed to contain at least 1,000L. Ideally the pit should be designed to be at least 3m deep and 1 m in diameter. If the pit diameter exceeds 1.5m there is an increased risk of collapse. Depending on how deep they are dug, some pits may last up to 20 years without emptying. If the pit is to be reused it should be lined. Pit lining materials can include brick, rot-resistant timber, concrete, stones, or mortar plastered onto the soil. If the soil is stable (i.e. no presence of sand or gravel deposits or loose organic materials), the whole pit need not be lined. The bottom of the pit should remain unlined to allow the infiltration of liquids out of the pit.

As the effluent leaches from the Single Pit and migrates through the unsaturated soil matrix, faecal organisms are removed. The degree of faecal organism removal varies with soil type, distance travelled, moisture and other environmental factors and thus, it is difficult to estimate the necessary distance between a pit and a water source. A distance of 30m between the pit and a water source is recommended to limit exposure to chemical and biological contamination.

When it is impossible or difficult to dig a deep pit, the depth of the pit can be extending by building the pit upwards with the use of concrete rings or blocks. This adaptation is sometimes referred to as a cesspit. It is a raised shaft on top of a shallow pit with an open bottom that allows for the collection of faecal sludge and the leaching of effluent. This design however, is prone to improper emptying since it may be easier to break or remove the concrete rings and allow the faecal sludge to flow out rather than have it emptied and disposed of properly.

Another variation is the unlined shallow pit that may be appropriate for areas where digging is difficult. When the shallow pit is full, it can be covered with leaves and soil and a small tree can be planted. This concept is called the Arborloo and is a successful way of avoiding costly emptying, while containing excreta, and reforesting an area. The Arborloo is discussed in more detail on the Fill and Cover - Arborloo section.

Advantages Disadvantages
- Can be built and repaired with locally available materials.
- Does not require a constant source of water.
- Can be used immediately after construction.
- Low (but variable) capital costs depending on materials.
-Flies and odours are normally noticeable.
- Sludge requires secondary treatment and/or appropriate discharge.
- Costs to empty may be significant compared to capital costs.
- Low reduction in BOD and pathogens.

Adequacy[edit | edit source]

Treatment processes in the Single Pit (aerobic, anaerobic, dehydration, composting or otherwise) are limited and therefore, pathogen reduction and organic degradation is not significant. However, since the excreta are contained, pathogen transmission to the user is limited. Single Pits are appropriate for rural and peri-urban areas; Single Pits in urban or dense areas are often difficult to empty and/or have sufficient space for infiltration. Single Pits are especially appropriate when water is scarce and where there is a low groundwater table. They are not suited for rocky or compacted soils (that are difficult to dig) or for areas that flood frequently.

Health Aspects/Acceptance[edit | edit source]

A simple Single Pit is an improvement to open defecation; however, it still poses health risks:

  • Leachate can contaminate groundwater;
  • Stagnant water in pits may promote insect breeding;
  • Pits are susceptible to failure/overflowing during floods.

Single Pits should be constructed at an appropriate distance from homes to minimize fly and odour nuisances and to ensure convenience and safe travel.

Upgrading[edit | edit source]

A Ventilated Improved Pit (VIP) is slightly more expensive but greatly reduces the nuisance of flies and odours, while increasing comfort and usability. For more information on the VIP please refer to the Single Pit VIP page. When two pits are dug side-by-side, one can be used while the contents of the other pit are allowed to mature for safer emptying. For more information on dual pit technologies refer to Double Pit VIP and Twin Pits for Pour Flush pages.

Maintenance[edit | edit source]

There is no daily maintenance associated with a simple Single Pit. However, when the pit is full it can be a) pumped out and reused or b) the superstructure and squatting plate can be moved to a new pit and the previous pit covered and decommissioned.

References[edit | edit source]

  • Brandberg, B. (1997). Latrine Building. A Handbook for Implementation of the Sanplat System. Intermediate Technology Publications, London. (A good summary of common construction problems and how to avoid mistakes.)
  • Franceys, R., Pickford, J. and Reed, R. (1992). A guide to the development of on-site sanitation. WHO, Geneva. (For information on accumulation rates, infiltration rates, general construction and example design calculations.)
  • Lewis, JW., et al. (1982). The Risk of Groundwater Pollution by on-site Sanitation in Developing Countries. International Reference Centre for Waste Disposal, Dübendorf, Switzerland. (Detailed study regarding the transport and die-off of microorganisms and implications for locating technologies.)
  • Morgan, P. (2007). Toilets That Make Compost: Low-cost, sanitary toilets that produce valuable compost for crops in an African context. Stockholm Environment Institute, Sweden. (Describes how to build a support ring/foundation.)
  • Pickford, J. (1995). Low Cost Sanitation. A Survey of Practical Experience. Intermediate Technology Publications, London. (Information on how to calculate pit size and technology life.)

Acknowledgements[edit | edit source]

Tilley, E. et al. (2008). Compendium of Sanitation Systems and Technologies, published by Sandec, the Department of Water and Sanitation in Developing Countries of Eawag, the Swiss Federal Institute of Aquatic Science and Technology, Dübendorf, Switzerland.

The publication is available in English, French, and will be made available in Spanish. Available in the IRC Digital Library

See also[edit | edit source]

Composting toilets

Composting Latrines

Safety and risks[edit | edit source]

Clearly there is some dispute in terms as as Stenström et al[1] describe a large pit which may lined and used for 5-30 years and a composting toilet as a smaller container whereby material is stored for 6-12 months. The former is considered to be a low frequency medium (due to potential groundwater contamination) risk intervention, whereas the smaller composting toilet pit latrine is considered to be low frequency low risk as the material is contained and cannot leak. However, both may well need to be irregularly emptied in some way.

For more discussion on this, see Infection risk from Ecosan

FA info icon.svg Angle down icon.svg Page data
Keywords sanitation, health, toilet, single pit latrine, latrine
SDG SDG03 Good health and well-being, SDG06 Clean water and sanitation, SDG11 Sustainable cities and communities
Authors Joe Turner
License CC-BY-SA-3.0
Organizations Akvo
Ported from https://akvo.org/ (original)
Language English (en)
Related 0 subpages, 10 pages link here
Impact 972 page views
Created February 11, 2013 by Joe Turner
Modified February 28, 2024 by Felipe Schenone
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