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https://en.wikipedia.org/wiki/Reuse_of_human_excreta

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Reuse of human excreta

人類排泄物的再利用

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海地收穫用人類排泄物製成的堆肥種植的辣椒

人類排泄物的再利用 是指在採用針對預期再利用應用應用客製化的適當處理步驟和風險管理方法後，對經過處理的人類排泄物進行安全、有益的利用。經處理的排泄物的有益用途可集中於利用經處理的排泄物中所含的植物可利用的養分（主要是氮、磷和鉀）。它們還可以利用排泄物中含有的有機物和能量。在較小程度上，排泄物中的水分也可能被再利用，儘管這更廣為人知的是從城市廢水中回收水。養分含量的預期再利用應用可能包括：農業或園藝活動中的土壤改良劑或肥料。其他再利用應用更著重於排泄物的有機物含量，包括用作燃料源或沼氣形式的能源。

有大量且不斷增加的處理方案可以使排泄物安全且易於管理，以實現預期的再利用。[1]選項包括尿液分流和糞便脫水（尿液分流旱廁）、堆肥（堆肥廁所或外部堆肥）、污水污泥處理技術和一系列糞便污泥處理流程。它們都實現了不同程度的病原體去除和水含量降低，以便於處理。值得關注的病原體是腸道細菌、病毒、原生動物和糞便中的寄生蟲。[2]其他需要考慮的健康風險和環境污染方麵包括微污染物、藥物殘留物和硝酸鹽在環境中的擴散，這可能會導致地下水污染，這可能會影響飲用水品質標準。

有幾種“人類排泄物衍生肥料”，其性質和施肥特性各不相同，例如：尿液、乾糞便、堆肥糞便、糞便污泥、污水、污水污泥。

幾個世紀以來，人類排泄物或生活廢水（污水）中所含的營養物質和有機物一直被用於農業。然而，這種做法在發展中國家往往以不受監管和不安全的方式進行。世界衛生組織 2006 年的指導方針建立了一個框架，描述如何透過遵循「多重屏障方法」安全地進行這種再利用。[3]

術語

人類排泄物、糞便污泥和廢水通常被稱為廢棄物。[4]衛生處理系統的最終輸出可稱為「再利用產品」或「其他輸出」。[4]這些再利用產品是一般肥料、土壤改良劑、生物質、水或能源。

人類排泄物的再利用關注的是人類排泄物的營養成分和有機物含量，而再生水則關注的是水份含量。

另一個術語是“人類排泄物的利用”而不是“再利用”，嚴格來說，這是人類排泄物的“第一次”“使用”，而不是第二次使用。[3]

技術和方法

 
A sewage farm in Hampshire, England

The resources available in wastewater and human excreta include water, plant nutrients, organic matter and energy content. Sanitation systems that are designed for safe and effective recovery of resources can play an important role in a community's overall resource management.

Recovering the resources embedded in excreta and wastewater (like nutrients, water and energy) contributes to achieving Sustainable Development Goal 6 and other sustainable development goals.[5]

It can be efficient to combine wastewater and human excreta with other organic waste such as manure, and food and crop waste for the purposes of resource recovery.[6]

處理選項

There is a large and growing number of treatment options to make excreta safe and manageable for the intended reuse option.[1] Various technologies and practices, ranging in scale from a single rural household to a city, can be used to capture potentially valuable resources and make them available for safe, productive uses that support human well-being and broader sustainability. Some treatment options are listed below but there are many more:[1]

A guide by the Swedish University of Agricultural Sciences provides a list of treatment technologies for sanitation resource recovery: Vermicomposting and vermifiltration, black soldier fly composting, algae cultivation, microbial fuel cell, nitrification and distillation of urine, struvite precipitation, incineration, carbonization, solar drying, membranes, filters, alkaline dehydration of urine,[7][8] ammonia sanitization/urea treatment, and lime sanitization.[4] Further research involves UV advanced oxidation processes in order to degrade organic pollutants present in the urine before reuse [9] or the dehydration of urine by using acids.[10]

重複利用選項

The most common reuse of excreta is as fertilizer and soil conditioner in agriculture. This is also called a "closing the loop" approach for sanitation with agriculture. It is a central aspect of the ecological sanitation approach.

Reuse options depend on the form of the excreta that is being reused: it can be either excreta on its own or mixed with some water (fecal sludge)[11] or mixed with much water (domestic wastewater or sewage).

The most common types of excreta reuse include:[6]

  • Fertilizer and irrigation water in agriculture, and horticulture: for example using recovered and treated water for irrigation; using composted excreta (and other organic waste) or appropriately treated biosolids as fertilizer and soil conditioner; using treated source-separated urine as fertilizer.
  • Energy: for example digesting feces and other organic waste to produce biogas; or producing combustible fuels.
  • Other: other emerging excreta reuse options include producing protein feeds for livestock using black soldier fly larvae, recovering organic matter for use as building materials or in paper production.

Resource recovery from fecal sludge can take many forms, including as a fuel, soil amendment, building material, protein, animal fodder, and water for irrigation.[11]

Reuse products that can be recovered from sanitation systems include: Stored urine, concentrated urine, sanitized blackwater, digestate, nutrient solutions, dry urine, struvite, dried feces, pit humus, dewatered sludge, compost, ash from sludge, biochar, nutrient-enriched filter material, algae, macrophytes, black soldier fly larvae, worms, irrigation water, aquaculture, and biogas.[4]

作為肥料

與其他肥料的比較

更多信息：肥料和有機肥料

There is an untapped fertilizer resource in human excreta. In Africa, for example, the theoretical quantities of nutrients that can be recovered from human excreta are comparable with all current fertilizer use on the continent.[6]:16 Therefore, reuse can support increased food production and also provide an alternative to chemical fertilizers, which is often unaffordable to small-holder farmers. However, nutritional value of human excreta largely depends on dietary input.[2]

Mineral fertilizers are made from mining activities and can contain heavy metals. Phosphate ores contain heavy metals such as cadmium and uranium, which can reach the food chain via mineral phosphate fertilizer.[12] This does not apply to excreta-based fertilizers (unless the human's food was contaminated beyond safe limits to start with), which is an advantage.

Fertilizing elements of organic fertilizers are mostly bound in carbonaceous reduced compounds. If these are already partially oxidized as in the compost, the fertilizing minerals are adsorbed on the degradation products (humic acids) etc. Thus, they exhibit a slow-release effect and are usually less rapidly leached compared to mineral fertilizers.[13][14]

尿

Urine contains large quantities of nitrogen (mostly as urea), as well as reasonable quantities of dissolved potassium.[15] The nutrient concentrations in urine vary with diet.[16] In particular, the nitrogen content in urine is related to quantity of protein in the diet: A high protein diet results in high urea levels in urine. The nitrogen content in urine is proportional to the total food protein in the person's diet, and the phosphorus content is proportional to the sum of total food protein and vegetal food protein.[17]:5 Urine's eight main ionic species (> 0.1 meq L−1) are cations Na, K, NH4, Ca, and the anions, Cl, SO4, PO4, and HCO3.[18] Urine typically contains 70% of the nitrogen and more than half the potassium found in sewage, while making up less than 1% of the overall volume.[15] The amount of urine produced by an adult is around 0.8 to 1.5 L per day.[3]

Applying urine as fertilizer has been called "closing the cycle of agricultural nutrient flows" or ecological sanitation or ecosan. Urine fertilizer is usually applied diluted with water because undiluted urine can chemically burn the leaves or roots of some plants, causing plant injury,[19] particularly if the soil moisture content is low. The dilution also helps to reduce odor development following application. When diluted with water (at a 1:5 ratio for container-grown annual crops with fresh growing medium each season or a 1:8 ratio for more general use), it can be applied directly to soil as a fertilizer.[20][21] The fertilization effect of urine has been found to be comparable to that of commercial nitrogen fertilizers.[22][23] Urine may contain pharmaceutical residues (environmental persistent pharmaceutical pollutants).[24] Concentrations of heavy metals such as lead, mercury, and cadmium, commonly found in sewage sludge, are much lower in urine.[25]

Typical design values for nutrients excreted with urine are: 4 kg nitrogen per person per year, 0.36 kg phosphorus per person per year and 1.0 kg potassium per person per year.[17]:5 Based on the quantity of 1.5 L urine per day (or 550 L per year), the concentration values of macronutrients as follows: 7.3 g/L N; .67 g/L P; 1.8 g/L K.[17]:5[26]:11 These are design values but the actual values vary with diet.[15][a] Urine's nutrient content, when expressed with the international fertilizer convention of N:P2O5:K2O, is approximately 7:1.5:2.2.[26][b] Since urine is rather diluted as a fertilizer compared to dry manufactured nitrogen fertilizers such as diammonium phosphate, the relative transport costs for urine are high as a lot of water needs to be transported.[26]

The general limitations to using urine as fertilizer depend mainly on the potential for buildup of excess nitrogen (due to the high ratio of that macronutrient),[20] and inorganic salts such as sodium chloride, which are also part of the wastes excreted by the renal system. Over-fertilization with urine or other nitrogen fertilizers can result in too much ammonia for plants to absorb, acidic conditions, or other phytotoxicity.[24] Important parameters to consider while fertilizing with urine include salinity tolerance of the plant, soil composition, addition of other fertilizing compounds, and quantity of rainfall or other irrigation.[16] It was reported in 1995 that urine nitrogen gaseous losses were relatively high and plant uptake lower than with labelled ammonium nitrate.[來源請求] In contrast, phosphorus was utilized at a higher rate than soluble phosphate.[18] Urine can also be used safely as a source of nitrogen in carbon-rich compost.[21]

Human urine can be collected with sanitation systems that utilize urinals or urine diversion toilets. If urine is to be separated and collected for use as a fertilizer in agriculture, then this can be done with sanitation systems that utilize waterless urinals, urine-diverting dry toilets (UDDTs) or urine diversion flush toilets.[26] During storage, the urea in urine is rapidly hydrolyzed by urease, creating ammonia.[28] Further treatment can be done with collected urine to stabilize the nitrogen and concentrate the fertilizer.[29] One low-tech solution to odor is to add citric acid or vinegar to the urine collection container, so that the urease is inactivated and any ammonia that do form are less volatile.[27] Besides concentration, simple chemical processes can be used to extract pure substances: nitrogen as nitrates (similar to medieval nitre beds) and phosphorus as struvite.[29]

The health risks of using urine as a source of fertilizer are generally regarded as negligible, especially when dispersed in soil rather than on the part of a plant that is consumed. Urine can be distributed via perforated hoses buried ~10 cm under the surface of the soil among crop plants, thus minimizing risk of odors, loss of nutrients due to votalization, or transmission of pathogens.[30] There are potentially more environmental problems (such as eutrophication resulting from the influx of nutrient rich effluent into aquatic or marine ecosystems) and a higher energy consumption when urine is treated as part of sewage in sewage treatment plants compared with when it is used directly as a fertilizer resource.[31][32]

In developing countries, the use of raw sewage or fecal sludge has been common throughout history, yet the application of pure urine to crops is still quite rare in 2021. This is despite many publications that advocate the use of urine as a fertilizer since at least 2001.[22][33] Since about 2011, the Bill and Melinda Gates Foundation is providing funding for research involving sanitation systems that recover the nutrients in urine.[34]

糞便

According to the 2004 "proposed Swedish default values", an average Swedish adult excretes 0.55 kg nitrogen, 0.18 kg phosphorus, and 0.36 kg potassium as feces per year. The yearly mass is 51 kg wet and 11 kg dried, so that wet feces would have a NPK% value of 1.1:0.8:0.9.[17]:5[a][c]

乾燥糞便

Reuse of dried feces from urine-diverting dry toilets after post-treatment can result in increased crop production through fertilizing effects of nitrogen, phosphorus, potassium and improved soil fertility through organic carbon.[35]

堆肥糞便

 
Cabbage grown in excreta-based compost (left) and without soil amendments (right), SOIL in Haiti

Compost derived from composting toilets (where organic kitchen waste is in some cases also added to the composting toilet) has, in principle, the same uses as compost derived from other organic waste products, such as sewage sludge or municipal organic waste. One limiting factor may be legal restrictions due to the possibility that pathogens remain in the compost. In any case, the use of compost from composting toilets in one's own garden can be regarded as safe and is the main method of use for compost from composting toilets. Hygienic measures for handling of the compost must be applied by all those people who are exposed to it, e.g. wearing gloves and boots.

Some of the urine will be part of the compost although some urine will be lost via leachate and evaporation. 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.[36]

The nutrients in compost from a composting toilet have a higher plant availability than dried feces from a typical urine-diverting dry toilet. The two processes are not mutually exclusive, however: some composting toilets do divert urine (to avoid over-saturation of water and nitrogen) and dried feces can still be composted.[37]

糞便污泥

Fecal sludge is defined as "coming from onsite sanitation technologies, and has not been transported through a sewer." Examples of onsite technologies include pit latrines, unsewered public ablution blocks, septic tanks and dry toilets. Fecal sludge can be treated by a variety of methods to render it suitable for reuse in agriculture. These include (usually carried out in combination) dewatering, thickening, drying (in sludge drying beds), composting, pelletization, and anaerobic digestion.[38]

市政廢水

更多信息：再生水

Reclaimed water can be reused for irrigation, industrial uses, replenishing natural water courses, water bodies, aquifers, and other potable and non-potable uses. These applications, however, focus usually on the water aspect, not on the nutrients and organic matter reuse aspect, which is the focus of "reuse of excreta".

When wastewater is reused in agriculture, its nutrient (nitrogen and phosphorus) content may be useful for additional fertilizer application.[39] Work by the International Water Management Institute and others has led to guidelines on how reuse of municipal wastewater in agriculture for irrigation and fertilizer application can be safely implemented in low income countries.[40][3]

污泥

The use of treated sewage sludge (after treatment also called "biosolids") as a soil conditioner or fertilizer is possible but is a controversial topic in some countries (such as USA, some countries in Europe) due to the chemical pollutants it may contain, such as heavy metals and environmental persistent pharmaceutical pollutants.

Northumbrian Water in the United Kingdom uses two biogas plants to produce what the company calls "poo power"—using sewage sludge to produce energy to generate income. Biogas production has reduced its pre-1996 electricity expenditure of 20 million GBP by about 20%. Severn Trent and Wessex Water also have similar projects.[41]

污泥處理液體

Sludge treatment liquids (after anaerobic digestion) can be used as an input source for a process to recover phosphorus in the form of struvite for use as fertilizer. For example, the Canadian company Ostara Nutrient Recovery Technologies is marketing a process based on controlled chemical precipitation of phosphorus in a fluidized bed reactor that recovers struvite in the form of crystalline pellets from sludge dewatering streams. The resulting crystalline product is sold to the agriculture, turf, and ornamental plants sectors as fertilizer under the registered trade name "Crystal Green".[42]

磷高峰

In the case of phosphorus in particular, reuse of excreta is one known method to recover phosphorus to mitigate the looming shortage (also known as "peak phosphorus") of economical mined phosphorus. Mined phosphorus is a limited resource that is being used up for fertilizer production at an ever-increasing rate, which is threatening worldwide food security. Therefore, phosphorus from excreta-based fertilizers is an interesting alternative to fertilizers containing mined phosphate ore.[43]

農業用途的健康與環境問題

病原體

農業安全使用的多重屏障概念

Research into how to make reuse of urine and feces safe in agriculture has been carried out in Sweden since the 1990s.[16] In 2006 the World Health Organization (WHO) provided guidelines on safe reuse of wastewater, excreta, and greywater.[3] The multiple barrier concept to reuse, which is the key cornerstone of this publication, has led to a clear understanding of how excreta reuse can be done safely. The concept is also used in water supply and food production, and is generally understood as a series of treatment steps and other safety precautions to prevent the spread of pathogens.

The degree of treatment required for excreta-based fertilizers before they can safely be used in agriculture depends on a number of factors. It mainly depends on which other barriers will be put in place according to the multiple barrier concept. Such barriers might be selecting a suitable crop, farming methods, methods of applying the fertilizer, education of the farmers, and so forth.[44]

For example, in the case of urine-diverting dry toilets secondary treatment of dried feces can be performed at community level rather than at household level and can include thermophilic composting where fecal material is composted at over 50 °C, prolonged storage with a duration of 1.5 to two years, chemical treatment with ammonia from urine to inactivate the pathogens, solar sanitation for further drying or heat treatment to eliminate pathogens.[45][35]

Exposure of farm workers to untreated excreta constitutes a significant health risk due to its pathogen content. There can be a large amount of enteric bacteria, virus, protozoa, and helminth eggs in feces.[2] This risk also extends to consumers of crops fertilized with untreated excreta. Therefore, excreta needs to be appropriately treated before reuse, and health aspects need to be managed for all reuse applications as the excreta can contain pathogens even after treatment.

處理排泄物以移除病原體

Temperature is a treatment parameter with an established relation to pathogen inactivation for all pathogen groups: Temperatures above 50 °C（122 °F） have the potential to inactivate most pathogens.[4]:101 Therefore, thermal sanitization is utilized in several technologies, such as thermophilic composting and thermophilic anaerobic digestion and potentially in sun drying. Alkaline conditions (pH value above 10) can also deactivate pathogens. This can be achieved with ammonia sanitization or lime treatment.[4]:101

The treatment of excreta and wastewater for pathogen removal can take place:

藥物殘留

Excreta from humans contains hormones and pharmaceutical drug residues which could in theory enter the food chain via fertilized crops but are currently not fully removed by conventional wastewater treatment plants anyway and can enter drinking water sources via household wastewater (sewage).[26] In fact, the pharmaceutical residues in the excreta are degraded better in terrestrial systems (soil) than in aquatic systems.[26]

硝酸鹽污染

Only a fraction of the nitrogen-based fertilizers is converted to produce plant matter. The remainder accumulates in the soil or is lost as run-off.[46] This also applies to excreta-based fertilizer since it also contains nitrogen. Excessive nitrogen which is not taken up by plants is transformed into nitrate which is easily leached.[47] High application rates combined with the high water-solubility of nitrate leads to increased runoff into surface water as well as leaching into groundwater.[48][49][50] Nitrate levels above 10 mg/L (10 ppm) in groundwater can cause 'blue baby syndrome' (acquired methemoglobinemia).[51] The nutrients, especially nitrates, in fertilizers can cause problems for ecosystems and for human health if they are washed off into surface water or leached through the soil into groundwater.

其他用途

Apart from use in agriculture, there are other possible uses of excreta. For example, in the case of fecal sludge, it can be treated and then serve as protein (black soldier fly process), fodder, fish food, building materials, and biofuels (biogas from anaerobic digestion, incineration or co-combustion of dried sludge, pyrolysis of fecal sludge, and biodiesel from fecal sludge).[38][6]

燃料

固體燃料、熱能、電力

Pilot scale research in Uganda and Senegal has shown that it is viable to use dry feces as for combustion in industry, provided it has been dried to a minimum of 28% dry solids.[52]

Dried sewage sludge can be burned in sludge incineration plants and generate heat and electricity (the waste-to-energy process is one example).

Resource recovery of fecal sludge as a solid fuel has been found to have high market potential in Sub-Saharan Africa.[11]

氫燃料

更多信息：氫燃料

Urine has also been investigated as a potential source of hydrogen fuel.[53][54] Urine was found to be a suitable wastewater for high rate hydrogen production in a microbial electrolysis cell (MEC).[53]

沼氣

更多信息：生物燃氣

Small-scale biogas plants are being utilized in many countries, including Ghana,[55] Vietnam[56] and many others.[57] Larger centralized systems are being planned that mix animal and human feces to produce biogas.[52] Biogas is also produced during sewage sludge treatment processes with anaerobic digestion. Here, it can be used for heating the digesters and for generating electricity.[58]

Biogas is an important waste-to-energy resource which plays a huge role in reducing environmental pollution and most importantly in reducing greenhouse gases effect caused by the waste. Utilization of raw material such as human waste for biogas generation is considered beneficial because it does not require additional starters such as microorganism seeds for methane production, and a supply of microorganisms occurs continuously during the feeding of raw materials.[59]

牲畜的食物來源

参见：豬廁

Combination outhouses/feeding troughs were used in several countries since ancient times. They are generally being phased out.

生產動物飼料蛋白質的食物來源

Pilot facilities are being developed for feeding black soldier fly larvae with feces. The mature flies would then be a source of protein to be included in the production of feed for chickens in South Africa.[52]

Black soldier fly (BSF) bio-waste processing is a relatively new treatment technology that has received increasing attention over the last decades. Larvae grown on bio-waste can be a necessary raw material for animal feed production, and can therefore provide revenues for financially applicable waste management systems. In addition, when produced on bio-waste, insect-based feeds can be more sustainable than conventional feeds.[60]

建築材料

It is known that additions of fecal matter up to 20% by dried weight in clay bricks does not make a significant functional difference to bricks.[52]

貴金屬回收

A Japanese sewage treatment facility extracts precious metals from sewage sludge, "high percentage of gold found at the Suwa facility was probably due to the large number of precision equipment manufacturers in the vicinity that use [gold]. The facility recently recorded finding 1,890 grammes of gold per tonne of ash from incinerated sludge. That is a far higher gold content than Japan’s Hishikari Mine, one of the world’s top gold mines, [...] which contains 20–40 grammes of the precious metal per tonne of ore."[61] This idea was also tested by the US Geological Survey (USGS) which found that the yearly sewage sludge generated by 1 million people contained 13 million dollars worth of precious metals.[61]

其他材料

With pyrolysis, urine is turned into a pre-doped, highly porous, carbon material termed "urine carbon" (URC). URC is cheaper than current fuel cell catalysts while performing better.[62]

Society and culture

Economics

Debate is ongoing about whether reuse of excreta is cost effective.[63] The terms "sanitation economy" and "toilet resources" have been introduced to describe the potential for selling products made from human feces or urine.[63][64]

Sale of compost

The NGO SOIL in Haiti began building urine-diverting dry toilets and composting the waste produced for agricultural use in 2006.[65] SOIL's two composting waste treatment facilities currently transform over 20,000 gallons (75,708 liters) of human excreta into organic, agricultural-grade compost every month.[66] The compost produced at these facilities is sold to farmers, organizations, businesses, and institutions around the country to help finance SOIL's waste treatment operations.[67] Crops grown with this soil amendment include spinach, peppers, sorghum, maize, and more. Each batch of compost produced is tested for the indicator organism E. coli to ensure that complete pathogen kill has taken place during the thermophilic composting process.[68]

Policies

There is still a lack of examples of implemented policy where the reuse aspect is fully integrated in policy and advocacy.[69] When considering drivers for policy change in this respect, the following lessons learned should be taken into consideration: Revising legislation does not necessarily lead to functioning reuse systems; it is important to describe the “institutional landscape” and involve all actors; parallel processes should be initiated at all levels of government (i.e. national, regional and local level); country specific strategies and approaches are needed; and strategies supporting newly developed policies need to be developed).[69]

Regulatory considerations

Regulations such as Global Good Agricultural Practices may hinder export and import of agricultural products that have been grown with the application of human excreta-derived fertilisers.[70][71]

Urine use in organic farming in Europe

The European Union allows the use of source separated urine only in conventional farming within the EU, but not yet in organic farming. This is a situation that many agricultural experts, especially in Sweden, would like to see changed.[25] This ban may also reduce the options to use urine as a fertilizer in other countries if they wish to export their products to the EU.[70]

Dried feces from urine-diverting dry toilets in the U.S.

In the United States, the EPA regulation governs the management of sewage sludge but has no jurisdiction over the byproducts of a urine-diverting dry toilet. Oversight of these materials falls to the states.[72][73]

參見

筆記

  1. ^ 1.0 1.1 A formula for adjustment of excreta N and P values based on dietary characteristics is found in Jönsson 2004.[17]:5
  2. ^ For the amount of other elements in urine, see Rose 2015[15] and Rich Earth 2021.[27]
  3. ^ For the amount of other elements in feces, see Rose 2015.[15]

參考資料

  1. ^ 1.0 1.1 1.2 Tilley, Elizabeth; Ulrich, Lukas; Lüthi, Christoph; Reymond, Philippe; Zurbrügg, Chris. Septic tanks. Compendium of Sanitation Systems and Technologies 2nd. Duebendorf, Switzerland: Swiss Federal Institute of Aquatic Science and Technology (Eawag). 2014. ISBN 978-3-906484-57-0. 
  2. ^ 2.0 2.1 2.2 Harder, Robin; Wielemaker, Rosanne; Larsen, Tove A.; Zeeman, Grietje; Öberg, Gunilla. Recycling nutrients contained in human excreta to agriculture: Pathways, processes, and products. Critical Reviews in Environmental Science and Technology. 2019-04-18, 49 (8): 695–743. Bibcode:2019CREST..49..695H. ISSN 1064-3389. doi:10.1080/10643389.2018.1558889  . 
  3. ^ 3.0 3.1 3.2 3.3 3.4 WHO (2006). WHO Guidelines for the Safe Use of Wastewater, Excreta and Greywater - Volume IV: Excreta and greywater use in agriculture. World Health Organization (WHO), Geneva, Switzerland
  4. ^ 4.0 4.1 4.2 4.3 4.4 4.5 McConville, J., Niwagaba, C., Nordin, A., Ahlström, M., Namboozo, V. and Kiffe, M. (2020). Guide to Sanitation Resource-Recovery Products & Technologies: A supplement to the Compendium of Sanitation Systems and Technologies. 1st Edition. Swedish University of Agricultural Sciences (SLU), Department of Energy and Technology, Uppsala, Sweden.
  5. ^ Andersson, Kim; Dickin, Sarah; Rosemarin, Arno. Towards "Sustainable" Sanitation: Challenges and Opportunities in Urban Areas. Sustainability. 2016-12-08, 8 (12): 1289. doi:10.3390/su8121289   （英语）. 
  6. ^ 6.0 6.1 6.2 6.3 Andersson, K., Rosemarin, A., Lamizana, B., Kvarnström, E., McConville, J., Seidu, R., Dickin, S. and Trimmer, C. (2016). Sanitation, Wastewater Management and Sustainability: from Waste Disposal to Resource Recovery. Nairobi and Stockholm: United Nations Environment Programme and Stockholm Environment Institute. ISBN 978-92-807-3488-1
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外部連結

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