Use of Dehydrated Faeces

Compiled by:
Gina Itchon (Xavier University), Niels Sacher (Xavier University)
Adapted from:
TILLEY, E.; LUETHI, C.; MOREL, A.; ZURBRUEGG, C.; SCHERTENLEIB, R. (2008)
JOENSSON, H.; RICHERT, A.; VINNERAAS, B.; SALOMON, E. (2004)

Executive Summary

When faeces are stored in the absence of moisture (i.e. urine, anal cleansing water and water) and dehydrating agents like ash, lime or sawdust are added after each defecation they dehydrate over time into a crumbly, white-beige, coarse, flaky material or powder. Dehydration means that the moisture naturally present in the faeces evaporates and/or is absorbed by added drying agents. Dried faecal material acts as a good soil conditioner due to its high organic matter content and is a good phosphorus and potassium fertilizer, which also contributes considerable amounts of nitrogen.

In Out

Faeces

Compost / Biosolids, Food Products

Dehydration Process

In a dehydration toilet, the excreta inside the processing vault are dried with the help of sun, natural evaporation and ventilation. Dehydration is different from composting because the organic material present is not degraded or transformed (e.g. shells and carcasses of worms and insects will remain in the dried faeces); only the moisture is removed. After dehydration, faeces will reduce in volume by about 75%.

 TILLEY, E. (2008)

Using dried faeces from a UDDT toilet. Source: TILLEY et al. (2008)

The primary motivation for dehydrating the faeces is that dried faeces are a hostile environment for pathogens and help to reduce the amount of pathogens in the faeces significantly over time. The degree of pathogen inactivation will depend on the temperature, the pH and storage time. The addition of calcium carbonates, contained in lime or wood ashes helps to raise the pH, and thus accelerate the process of pathogen inactivation. However, dry faeces may still contain pathogens. Oocysts for examples are spores that can survive extreme environmental conditions and re-grow under favourable conditions.

It is generally accepted that faeces should be stored between 12 to 24 months, although pathogens may still exist after this time. Faeces that are dried and stored between 2 and 20°C should be stored for between 18 up to 24 months before they can be used at the household or regional level without any health concern. At higher temperatures (i.e. greater than 20°C storage) 12 months is accepted to be sufficient for the inactivation of Ascaris eggs (a type of intestinal parasitic worm). A shorter storage time of six month only, is required if the faeces are stored with a pH above 9. However, a secondary treatment (composting, vermi-composting) of dehydrated faeces should always be considered (if possible) as an additional barrier to inactivate pathogens (and here most importantly Ascaris).

 

 Xavier University

Dehydrated faeces as the product of a UDDT. Source: XAVIER UNIVERSITY (2009)

The World Health Organization (WHO) has published guidelines for the safe use of wastewater, excreta and greywater in agriculture (see further readings); these should be consulted before using dried faeces. When the faeces are completely dry, they will emerge as a crumbly, powdery substance. This material is rich in carbon and nutrients and fibrous material. If the drying is fast and a low moisture level is achieved, the losses of both organic matter and Nitrogen are small. Compared to composting, dry storage of the faeces recycles more organic matter and Nitrogen to the soil, but the organic matter is less stable. Dried faecal matter is a complete phosphorus and potassium fertiliser, which also contributes considerable amounts of nitrogen (JOENSSON et al. 2004).

While the total amount of nutrients excreted with faeces is lower than with urine, the concentration of nutrients, and especially P and K, is high in faeces. P is particularly valuable for the plant in its early development and important for good root development. In addition to supplying macro- and micronutrients, faeces contain organic matter, which increases the water-holding and ion-buffering capacity of the soil, serves as food for the microorganisms and is important for improving soil structure.

As the breakdown of organic material in dehydrating conditions is slow, toilet paper or similar objects placed in the chamber will not disintegrate quickly. Toilet paper can therefore either be handled separately, or be composted in a secondary treatment process.

Application

Dehydrated faeces can be mixed into soil, buried or composted at home or in a community based composting site depending on acceptance. Nutrients will be available to plants directly or after further decomposition of the dehydrated material. The addition of wood ashes not only enhances the inactivation process of pathogens due to the rise of pH, but can also increase the potassium (K) content of the final product.

The application rate of faeces can be based on local recommendations for the use of phosphorus-based fertilisers and analysis of the phosphorus content of the faecal product. This gives a rather low application rate, and the improvement of the crop due to the added organic matter is hard to distinguish. As the dry faeces can also considerably improve the soil structure and water-holding capacities, they are often applied at much higher rates. If organic matter (wood chips) or ashes are added to the faeces during collection and processing, these will improve the buffering capacity and the pH of the soil, which is especially important on soils with low pH (ECOSANRES 2008).

The average person produces around 50 L of faeces each year. This amount of faeces will fertilise 1.5 to 3.0 m2 of crop if the application is made according to organic content. If application is instead based on phosphorus content, it will be enough to fertilise 200-300 m2 (ECOSANRES 2008).

Because faeces contain large amounts of P, which is important for the development of young plants and roots, faeces should be applied prior to sowing or planting. Faeces must be applied at a depth where the soil stays moist, because the P only becomes available to the plants when it dissolves into the soil liquid, and the water-holding and buffering capacity of the organic matter are fully utilised only in moist conditions. Thus, applied faeces should be incorporated into the soil and covered. However, faeces should not be applied at depths exceeding the rooting depth.

Handling & Health Risk

The handling and use of dried faeces may not be acceptable to some. However, because the dried faeces should be dry, crumbly, and odour free, the use of dehydrated faeces may be more acceptable than that of manure or sludge.

Dehydrated faeces can still contain pathogens and therefore, a number of barriers to minimise the risk of disease transmission on the way from dehydration to crop production and harvesting should be considered. Such barriers could be a secondary treatment (e.g. composting, vermi-composting).

But also simple other measures such as avoiding the emptying of the vaults on windy days to prevent the powder from blowing and being inhaled or incorporation during the dry season, can considerably decrease the hygienic risk.

Furthermore, it also makes sense to apply faeces on crops that grow above the ground (e.g. fruit trees or bushes). To heighten acceptance, it can also be used for non-food crops that need fertilisations (animal fodder, wood etc.).

Applicability

Dried faeces are not as well treated or as useful as a soil amendment as composted faeces. However, they contain significant amounts of phosphorus, important in the early stage of plant growth and are useful for replenishing poor soils and for boosting the carbon content and thus the water-holding properties of soil with a low-risk of pathogen transmission.

For hygiene reasons, faeces should be incorporated into the soil and covered by a soil upper layer. Also the fertilisation of vegetables eaten raw should be avoided.

The application of faeces is suited for tree plantations or the cultivation of cereals (e.g. wheat), potatoes, yam and other tuberous crops.

Advantages

  • Periodical incorporation can improve the structure and water-holding capacity of soil
  • Simple technique for all users
  • Low cost
  • Low risk of pathogen transmission (when fully dried and properly handled)
  • May encourage income generation (tree planting and fruit production)

Disadvantages

  • Labour intensive
  • Requires that faeces are kept strictly dry
  • Pathogens may exist in a dormant stage (oocysts) which may become infectious if moisture is added
  • Can only partly replace fertiliser (N,P,K)

References Library

TILLEY, E.; LUETHI, C.; MOREL, A.; ZURBRUEGG, C.; SCHERTENLEIB, R. (2008): Compendium of Sanitation Systems and Technologies. Duebendorf and Geneva: Swiss Federal Institute of Aquatic Science and Technology (EAWAG). URL [Accessed: 15.02.2010]. PDF

JOENSSON, H.; RICHERT, A.; VINNERAAS, B.; SALOMON, E. (2004): Guidelines on the Use of Urine and Faeces in Crop Production . Stockholm: EcoSanRes. URL [Accessed: 17.04.2012]. PDF

ECOSANRES (Editor) (2008): Guidelines on the Use of Urine and Faeces in Crop Production. Factsheet. (pdf presentation). Stockholm: Stockholm Environment Institute. PDF

XAVIER UNIVERSITY (Editor) (2009): Excreta Use in Agriculture, Lecture taken from the XU Ecosan Course. XAVIER UNIVERSITY . PDF

Further Readings Library

Reference icon

ECOSANRES (Editor) (2008): Guidelines on the Use of Urine and Faeces in Crop Production. Factsheet. (pdf presentation). Stockholm: Stockholm Environment Institute. PDF

A 2-page factsheet summarizing the EcoSanRes ‘Guidelines on the Use of Urine and Faeces in Crop Production’ publication with short information on urine as a fertilizer, application rates etc.


Reference icon

DAGERSKOG, L. ; SuSanA (Editor) (2009): Urine and Faeces as Fertilizers in the CREPA Network. pdf presentation. Ouagadougou: Sustainable Sanitation Alliance. PDF

Presentation on experiences with the use of urine (and faeces) in agriculture including research results, conducted taste tests and calculations on the fertiliser value.


Reference icon

JOENSSON, H.; RICHERT, A.; VINNERAAS, B.; SALOMON, E. (2004): Guidelines on the Use of Urine and Faeces in Crop Production . Stockholm: EcoSanRes. URL [Accessed: 17.04.2012]. PDF

These guidelines provide a thorough background on the use of urine (and faeces) for agricultural purposes. Aspects discussed are requirements for plant growth, nutrients in excreta, hygiene aspects, and recommendations for cultivation. It provides detailed guidance on the use of urine for purposes.


Reference icon

SCHOENNING, C.; STENSTROEM, T. A. (Editor) (2004): Guidelines for the Safe Use of Urine and Faeces in Ecological Sanitation Systems. Stockholm: Stockholm Environment Institute. PDF

These guidelines provide a thorough background on the safe use of urine and faeces for agricultural purposes. Aspects like the health risk associated we the use of human excreta in agriculture and how to limit them are discussed.


Reference icon

WINDBLAD, U.; SIMPSON-HERBERT, M. (2004): Ecological Sanitation - revised and enlarged edition. (pdf presentation). Sweden: Stockholm Environment Institute. URL [Accessed: 04.08.2010]. PDF

This book is one of the most fundamental and important books that defined the concept of ecological sanitation. The first version came out in 1998 - this version presents the findings of over ten years of research and development in ecological sanitation supported by SIDA (Swedish International Development Cooperation Agency).


Training Material Library

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JENSSEN, P.; HEEB, J.; GANAKAN, K.; CONRADIN, K. (2008): M4-7: Agricultural Aspects. In: HEEB, J.; JENSSEN, P.; GNANAKAN; CONRADIN, K. (2008): Ecosan Curriculum 2.3. Switzerland, India and Norway. URL [Accessed: 21.03.2011]. PDF

Lecture on agricultural aspects of ecosan comprising chapters on plant requirements, composition and plant availability of nutrients in human excreta as well as general application recommendations and safety measures.


Reference icon

XAVIER UNIVERSITY (Editor) (2009): Excreta Use in Agriculture, Lecture taken from the XU Ecosan Course. XAVIER UNIVERSITY . PDF

Short lecture on the reuse of urine and faeces in agriculture with a local Philippine focus.


Important Weblinks

http://www.akvo.org/wiki/index.php/Soak_Pit [Accessed: 06.05.2010]

The sanitation portal of Akvopedia offers state of the art information on several sanitation technologies including strategies and knowledge for using dehydrated faeces