Understand the key terms, definitions, and methods of SaniChoice and learn how to use the different functionalities. You will also find two videos, a guided tour and the story of Amita, that supports sanitation planning in a growing small town in Nepal.
The SaniChoice Practitioner's guide provides a five-steps procedure to define the required case data and discuss results with stakeholders.The steps integrate into any structured decision making (SDM) framework such as CLUES, Sanitation21, or City Sanitation Planning.
Choose from five presentation, four exercises, and two example session plans to design your SaniChoice training and built up future users.
Contact Information
Eawag - Swiss Federal Institute of Aquatic Science and Technology
Dorothee Spuhler
Überlandstrasse 133
CH-8600 Dübendorf
Anal cleansing water is water used to cleanse oneself after defaecating and/or urinating. It is generated by those who use water, rather than dry material, for anal cleansing. The volume of water used per cleaning typically ranges from 0.5 L to 3 L.
Incineration ash can be divided into two main categories: incinerator bottom ash (IBA) and air pollution control residue, which is commonly referred to as fly ash. IBA forms at the bottom of an incinerator from heavy components that are neither combustible nor volatile. These residues contain large proportions of phosphorous and potassium, which can fertilise the soil for agricultural purposes if the sludge is not chemically contaminated. It can also be used in construction materials such as roads.
Biochar is a solid material obtained from pyrolysis, the thermochemical conversion of biomass in an oxygen-limited environment. Biochar derived from pyrolysis of sludge, faeces and/or organic waste may be applied to soils to improve soil properties and crop yields. Additionally, it acts as a carbon sink to reduce climate change impacts. Other applications include use as an adsorption material for filters, especially for water purification purposes, or as a feedstock for energy recovery. It is typically called “biochar” when it is used as a soil conditioner and “char” when it is used as a fuel.
Biogas is the common name for the mixture of gases released from anaerobic digestion. Biogas is comprised of methane (50 to 75%), carbon dioxide (25 to 50%) and varying quantities of nitrogen, hydrogen sulphide, water vapour and other components. Biogas can be collected and burned for fuel (like propane).
Blackwater is the mixture of urine, faeces and flushwater along with anal cleansing water (if water is used for cleansing) and/or dry cleansing materials. Blackwater contains the pathogens of faeces and the nutrients of urine that are diluted in the flushwater.
Briquettes are the product of a process developed by Sanivation in Naivasha, Kenia. Consisting of a mixture of dried, ground faecal matter and coal-dust, the briquettes are round and black. They burn longer than normal charcoal and produce less smoke.
Brownwater is the mixture of faeces and flushwater, and does not contain Urine. It is generated by Urine-Diverting Flush Toilets and, therefore, the volume depends on the volume of the flushwater used. The pathogen and nutrient load of faeces is not reduced, only diluted by the flushwater. Brownwater may also include anal cleansing water (if water is used for cleansing) and/or dry cleansing materials.
Compost is decomposed organic matter that results from a controlled aerobic degradation process. In this biological process, microorganisms (mainly bacteria and fungi) decompose the biodegradable waste components and produce this earth-like, odourless, brown/black material. Compost has excellent soil-conditioning properties and variable nutrient content. Because of leaching and volatilization, some of the nutrients may be lost, but the material is still rich in nutrients and organic matter. Generally, excreta or sludge should be composted long enough (2 to 4 months) under thermophilic conditions (55 to 60 °C) in order to be sanitized sufficiently for safe agricultural use. This temperature is not guaranteed in most composting chambers, but considerable pathogen reduction can normally be achieved.
Concentrated urine is a nutrient solution obtained by removing water from urine. Water removal is achieved through evaporation, distillation or reverse/forward osmosis of urine. The finished product is between 3 and 7% of the initial volume. In order to ensure that nitrogen is not lost in the process, nitrification or acidification of the urine is done prior to volume reduction. Depending on the pre-treatment
process, the majority of the nutrients are retained.
Dried Faeces is faeces that has been dehydrated until it has become a dry, crumbly material. Dehydration takes place by storing faeces in a dry environment with good ventilation, high temperatures and/or the presence of absorbent material. Very little degradation occurs during dehydration and this means that the dried faeces are still rich in organic matter. However, faeces reduce by around 75% in volume during dehydration and most pathogens die off. There is a small risk that some pathogenic organisms can be reactivated under the right conditions, particularly, in humid environments.
Dry urine is a nutrient-rich solid fertiliser produced by dehydrating and concentrating human urine in an alkaline substrate (pH > 10). Dry urine’s treatment technology, alkaline urine dehydration, can be implemented using different alkaline substrates, which will determine the composition and physicochemical properties of the dried product. The dried urine captures nearly all of the fertilising nutrients in urine.
Effluent is the general term for a liquid that leaves a technology, typically after blackwater or sludge has undergone solids separation or some other type of treatment. Effluent originates at either a collection and storage/treatment or a (semi-) centralized treatment technology. Depending on the type of treatment, the effluent may be completely sanitized or may require further treatment before it can be used or disposed of.
Excreta consists of urine and faeces that is not mixed with any flushwater. Excreta is small in volume but concentrated in both nutrients and pathogens. Depending on the quality of the faeces, it has a soft or runny consistency.
Faeces refers to (semi-solid) human excrement that is not mixed with urine or water. Depending on diet, each person produces approximately 50 L per year of faecal matter. Fresh faeces contain about 80% water. Of the total nutrients excreted, Faeces contain about 12% N, 39% P, 26% K and have 107 to 109 faecal coliforms in 100 mL.
Flushwater is the water discharged into the User Interface to transport human excreta and anal cleansing material and/or clean the user interface. Freshwater, stormwater, recycled greywater or any combination of the three can be used as a flushwater source. The volume of flushwater used depends on the toilet but generally ranges from 2 to 15 L per flush.
Freshwater is the water derived from a water source and is assumed to be uncontaminated.
Greywater is the water generated from washing food, clothes and dishware, as well as from bathing, but not from toilets. It may contain traces of excreta (e.g. from washing diapers) and, therefore, also pathogens. Greywater accounts for approximately 65% of the wastewater produced in households with flush toilets.
Excreta consists of urine and faeces that is not mixed with any flushwater. Excreta is small in volume but concentrated in both nutrients and pathogens. Depending on the quality of the faeces, it has a soft or runny consistency.
Organics refers to biodegradable plant material (organic waste) that must be added to some technologies for them to function properly (e.g. composting chambers). Organic degradable material can include but is not limited to, leaves, grass and market waste. Although other products in SaniChoice contain organic matter, the term organics refers to undigested plant material only.
Pellets are the product of the LaDePa (Latrine Dehydration and Pasteurization) machine and are brown and brittle. They are produced from faecal sludge and have a similar nutrient content to manure and compost, and similar calorific value to wood. As such they have suitable characteristics for reuse in agriculture and as a biofuel.
Pit humus is the term used to describe the nutrient-rich, hygienically improved, humic material that is generated in double pit technologies (double ventilated improved pit (VIP), fossa alterna, twin pits for pour flush) through dewatering and degradation. This earth-like product is also referred to as EcoHumus, a term conceived by Peter Morgan in Zimbabwe. The various natural decomposition processes taking place in alternating pits can be both aerobic and anaerobic in nature, depending on the technology and operating conditions. The main difference between pit humus and compost is that the degradation processes are passive and are not subjected to a controlled oxygen supply, C:N ratio, humidity and temperature. Therefore, the rate of pathogen reduction is generally slower and the quality of the product, including its nutrient and organic matter content, can vary considerably. Pit Humus can look very similar to compost and have good soil conditioning properties, although pathogens may still be present.
Sludge that was further processed in drying beds, SBRs, or biogas reactors.
Effluent that has undergone treatment for stabilisation and is expected to have better quality, than for example, septic tank effluent. Examples are aurin production, waste stabilization ponds (WSP) and horizontal subsurface flow constructed wetland (HSSFCW).
Sludge is a mixture of solids and liquids, containing mostly excreta and water, in combination with sand, grit, metals, trash and/or various chemical compounds. A distinction can be made between faecal sludge and wastewater sludge. Faecal sludge comes from onsite sanitation technologies, i.e. it has not been transported through a sewer. It can be raw or partially digested, a slurry or semisolid, and results from the collection and storage/treatment of excreta or blackwater, with or without greywater. For a more detailed characterization of faecal sludge refer to Strande et al., 2014. Wastewater sludge (also referred to as sewage sludge) is sludge that originates from sewer-based wastewater collection and (semi-) centralized treatment processes. The Sludge composition will determine the type of treatment that is required and the end-use possibilities.
Stabilized sludge is the sludge that has undergone some sort of treatment similar to processed sludge but is expected to be of better hygienic quality. Stabilized sludge is obtained e.g. in drying beds or from lactic acid fermentation.
Stabilized urine is the urine that was kept in a urine bank and has been hydrolysed naturally over time, i.e. the urea has been converted by enzymes into ammonia and bicarbonate. It has a pH of approximately 9. Most pathogens cannot survive at this pH. After 6 months of storage, the risk of pathogen transmission is considerably reduced. Stored urine, if stored according to the guidelines from the World Health Organisation is a type of stabilized urine.
Faeces that were collected in a faeces storage chamber to be collected and transported to a treatment facility.
Urine that was collected in a urine storage tank to be collected and transported to a treatment facility.
Stormwater is the general term for the rainfall-runoff collected from roofs, roads and other surfaces before flowing towards low-lying land. It is the portion of rainfall that does not infiltrate into the soil.
Struvite, sometimes also called magnesium ammonium phosphate hexahydrate (MAP), is a phosphate mineral that occurs naturally in sanitation systems. It is a common precipitate in, e.g. pipes and heat exchangers, and it can also be purposefully extracted from waste streams, for example, through the addition of magnesium to urine. Struvite precipitation can be applied to reduce phosphorus concentrations in effluents while at the same time generating a product that can be applied as a fertiliser or industrial raw material.
Transferred sludge is sludge that has been transported to a transfer station for intermittent storage before being further transported for treatment. For instance, in densely populated sites, emptying has to be done with a smaller volume vehicle due to limited vehicular access. Storing the sludge in a transfer station allows usage of a larger vehicle for transporting it to a treatment site that lies out of the town.
For offsite treatment facilities, sanitation products require prior conveyance. The differentiation between transported and not transported products is made to ensure a correct assembly of technologies by the sanitation system builder.
Urine is the liquid produced by the body to rid itself of urea and other waste products. In this context, the urine product refers to pure urine that is not mixed with faeces or water. Depending on diet, human urine collected from one person during one year (approx. 300 to 550 L) contains 2 to 4 kg of nitrogen. With the exception of some rare cases, urine is sterile when it leaves the body.
For technologies from functional group, the output product is the transported version of the input product with the strongest pollution.
For instance for a technology Z with input blackwater and greywater, the output will be transported blackwater.
Contact Information
Eawag - Swiss Federal Institute of Aquatic Science and Technology
Dorothee Spuhler
Überlandstrasse 133
CH-8600 Dübendorf
Arba Minch
Changunarayan
Cox's Bazar - Acute
Cox's Bazar - Stabilisation
Didactic Example
Katarniya
Quebrada Verde
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Arba Minch is located in the southern part of Ethiopia and, in 2017, had a population of 114’570 inhabitants. With an annual growth rate of 4.5%, it is one of the fastest growing cities of Ethiopia. The area of the city is large (56 km2), with a low average density (approx. 2000 inhabitants per km2). But most of the population is concentrated in the residential areas around the university. The Arba Minch town municipality (AMTM) is part of the Great Rift Valley and is bordered by the Abaya and Chamo lakes in the East as well as by a mountain escarpment in the West. The topography is very diverse and combines both steep and undulating terrain of the upper town area and flat areas in the valley. It is divided into four sub-cities, which have been restructured into eleven administrative “kebeles” (smallest administrative zone). In the 2012, around the town of Arba Minch, in the Arba Minch District, there were 164,529 people, of whom 82,265 were male and 82,264 were female. In this district, 53.9% practiced Protestantism, 29.3% practiced Ethiopian Orthodox Christianity, 12.6% practiced Traditional beliefs, and all other religious practices made up 4.1%.
The situation can be briefly summarized as followed, for more detailed information, please refer to the appropriateness criteria in the case settings:
The case study located in Arba Minch, Ethiopia, was conducted by a large team of researchers from six different research institutes. The report of the case study was published in the Volume 271 of the Journal of Environmental Management in 2020.
The situation can be briefly summarized as followed, for more detailed information, please refer to the appropriateness criteria in the case settings:
Cox's Bazar is a refugee settlement in Bangladesh counting approximately 14’509 inhabitants in 2020. The camp can be characterized as very dense, with many areas being regularly flooded during the monsoon season and travel therefore mostly possible by foot. The population residing in the camp is contains predominantly people with Muslim affiliation. It was assumed that the emergency is in its initial phases to simulate the acute phase of an emergency. During the acute phase of an emergency the number of people in the camp is expected to rise quickly and unexpectedly. The new arrivals require urgently access to sanitation solutions and therefore toilets need to be built rapidly. Many NGOs (including substantial funds) as well as the military of Bangladesh are present, however coordination between the different entities has not yet been properly organized. Supply chains have not yet been properly set up. Overall, it is a chaotic situation with high levels of need and vulnerability.
The situation can be briefly summarized as followed, for more detailed information, please refer to the appropriateness criteria in the case settings:
This case study was based on a project by Kukka Ilmanen and Akanksha Jain of their master’s degree in environmental engineering at the Institute of Civil, Environmental and Geomatic Engineering of the Swiss Federal Institute of Technology (ETH), Zurich, Switzerland.
Cox's Bazar is a refugee settlement in Bangladesh counting approximately 14’509 inhabitants in 2020. The camp can be characterized as very dense, with many areas being regularly flooded during the monsoon season and travel therefore mostly possible by foot. The population residing in the camp is contains predominantly people with Muslim affiliation. The camp has already existed for several decades and it cannot be assumed that the need for the camp will end soon. There is no longer an influx of people coming in and the camp is no longer in the acute phase of the emergency and in general, has characteristics belonging to the stabilization and recovery phases of an emergency. However, high levels of need and vulnerability remain critical. The WASH sector has identified huge gaps in faecal sludge management and disposal solutions. Due to a combination of factors, desludging of latrines built during the acute phase of the response has become an urgent priority and major gap. The crisis has created an imminent public health risk posed by the large number of poor-quality pit latrines, in many cases in the direct vicinity of shallow wells equipped with hand pumps. At present, 40 % of the pit latrines in the mega camp are estimated to be full. The government authorities, with support from the WASH sector, are putting greater emphasis on building toilets that are safe, emptiable and more sustainable.
The situation can be briefly summarized as followed, for more detailed information, please refer to the appropriateness criteria in the case settings:
This case study was based on a project by Kukka Ilmanen and Akanksha Jain of their master’s degree in environmental engineering at the Institute of Civil, Environmental and Geomatic Engineering of the Swiss Federal Institute of Technology (ETH), Zurich, Switzerland.
This is an didactic example developped for the practicioners guide. It is about the fictional town of Thirty Springs. The example is based on a case study in Ethiopia that took place between 2015 and 2019 in collaboration with the Arba Minch University and Town Municipality.
Katarniya is a very typical example of an emerging small town in the mid-western region of Nepal with a population of approximately 2’000 inhabitants. The city faces rapid and unplanned growth, so the population today is probably already far above 2000 inhabitants. Furthermore, it is characterized by a weak institutional setting and a lack of human and financial resources. Therefore, several sanitation related problems could occur as the population is growing rapidly. Basic sanitation elements such as toilet infrastructure are present, but full sanitation systems are mostly absent.
The situation can be briefly summarized as followed, for more detailed information, please refer to the appropriateness criteria in the case settings:
The case study was conducted by a team of researchers from the Swiss Federal Institute of Aquatic Science and Technology (Eawag), Dübendorf, Switzerland in cooperation with the Institute of Civil, Environmental and Geomatic Engineering of the Swiss Federal Institute of Technology (ETH), Zurich, Switzerland.The leading researcher of the Case Study was Dorothee Spuhler. The report of the case study was published in the Volume 145 of the journal "Water Research" in 2018.
The community of Quebrada Verde (QV) is located in the lower part of the Lurin River Basin in the Pachacámac District in Lima, Peru. QV is a semi-informal settlement with 800 inhabitants. It borders on the north and the west with highlands, and on the east and the south with the agricultural area and the Lurin River, one of the three main rivers in Lima. The settlement is equipped with a mix of urban, rural, and peri-urban infrastructures. The primary source of income for many settlers in the peri-urban areas of Lima is still agriculture which represents a significant percentage of economic activities. It receives inadequate drinking water and lacks a public sewer system. This leads to health risks. Parasites and diarrheal diseases are reported. An effort to provide safe sanitation service to such settlement through a container-based sanitation system has been shown by a social venture in Lima, x-runner. This system relies on a urine-diverting dry toilet (UDDT) with centralized emptying and treatment. However, these innovations are restricted by the absence of suitable regulations for their services that require different organization than centralized sewer systems. The provision of safe sanitation services for Lima’s informal settlements is a dilemma for both communities and regulators. Both parties are seeking a long-term solution, yet the implementation might not come soon. Alternative services, e.g., container-based sanitation or the condominial sewer, can be something to look forward to. Another technology that has long been used for treating wastewater is an activated sludge process. Activated sludge systems, such as conventional activated sludge and anaerobic-aerobic systems in sequencing batch reactors (SBR), have been implemented in Lima. The conventional activated sludge system is particularly applied at the wastewater treatment plant (PTAR) at PTAR Cieneguilla in the district of Cieneguilla in the Lurin Valley.
The situation can be briefly summarized as followed, for more detailed information, please refer to the appropriateness criteria in the case settings:
The case study was conducted by the researchers Ainul Firdatun Nisaa representing the Institute for Sanitary Engineering, Water Quality and Solid Waste Management, University of Stuttgart, Stuttgart, Germany as well as the Department of Environmental Engineering, Institut Teknologi Sepuluh Nopember, Surabaya, Indonesia; by Manuel Krauss representing the Institute for Sanitary Engineering, Water Quality and Solid Waste Management, University of Stuttgart, Stuttgart, Germany as well as the Research Institute for Water and Waste Management at the RWTH Aachen University (FiW), Aachen, Germany and by Dorothee Spuhler from the Swiss Federal Institute for Aquatic Science and Technology (EAWAG), Dübendorf, Switzerland. The report of the case study was published in the Number 9 of the Volume 13 of the journal "Water" in 2021.