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Urine treatment: from trial and error to exciting innovation

May 4, 2022 | Andri Bryner

What has been a purification process in wastewater treatment plants for decades can also be used decentrally or semi-centrally as a recycling process for nutrients. Early separation of "solid and liquid" plays a key role here. It allows for flexible solutions in terms of process technology, especially in the treatment of urine. New studies also show that the processes can be used not only for human urine, but also for that of cows or pigs.

Worldwide, the demand for fertiliser for agriculture is increasing. This makes the recovery of nutrients from wastewater interesting. Switzerland, for example, is completely dependent on imports for phosphorus. Phosphorus reserves (which are also finite) are controlled by a few countries such as China and the USA. Large reserves claimed by Morocco are located in annexed territories of the Western Sahara.

Dead zones in the sea grow

Parallel to the large-scale trade in fertilisers, inadequate removal of nutrients from wastewater is leading to over-fertilised waters in many places around the world. "Dead zones" in the North Sea and in offshore stretches of sea are not primarily due to chemical residues, but to excessive inputs of nitrogen and phosphorus. In 2021, the UN's second "World Ocean Assessment" report noted that the number of these areas where life is barely possible is rising sharply. "Pressures are destroying important habitats and hampering the ability of the oceans to cope with the impacts of climate change," said UN Secretary-General António Guterres.
 

The Blue Diversion Autarky toilet in test on the outskirts of Durban, South Africa. The evaporation module is visible in the front right.
(Michel Riechmann, Eawag)

Early separation instead of "end of pipe

Nutrients can be removed from wastewater in conventional wastewater treatment plants, processed and returned to regional material cycles. But end-of-pipe processes require space, technical effort, energy and chemicals. It is not the case that all this is omitted with decentralised or semi-centralised treatment of wastewater. But an early separation of the different material flows enables more flexible solutions, especially in terms of process technology. One example of this is the Blue Diversion Autarky Toilet developed at Eawag. It relies on on-site measures and technology that turns wastewater into useful products. At the same time, with Autarky, Eawag staff are researching and developing a platform that will gradually bring modern on-site technology to bathroom scale: What was still the vision of a few pioneers 20 years ago is now an interesting innovation in which more and more process engineers and companies are collaborating.
 

Autonomous urine treatment with nutrient recovery is also being tested in the innovative Tinyhome "Tilla". The evaporation module can be seen small on the back right.
(Michel Riechmann, Eawag)

The six-step plan with urine

Recently, Eawag researchers published an overview in the journal Water Research of the processes and process steps being worked on for the treatment of urine. The focus is on urine because, although it accounts for less than 1% of the volume of wastewater, it contains 80 to 90% of the nutrients. The review covers all six areas currently covered in urine treatment - not all of them need to be implemented in one system at the same time.

  • Stabilisation: If fresh urine is not stabilised, a lot of nitrogen is lost as ammonia (NH3). In addition, unstabilised urine stinks and precipitates (urine scale) can clog pipes. The researchers have identified biological processes as being well suited for urine stabilisation, because they require little energy and hardly any chemicals. Biological stabilisation is used by Vuna, among others, to produce the fertiliser product Aurin.
  • Volume reduction: Volume reduction is often accompanied by the recovery of nutrients. The focus is on evaporation and membrane filtration, the latter also combined with electrochemical processes. But research is also being conducted on the uptake of nutrients via algae. Pathogens are often removed or inactivated in this step at the same time.
  • Recovery of individual nutrients: The targeted recovery of certain nutrients (essentially nitrogen and/or phosphorus) can be interesting because a fertiliser product can then be produced with a nutrient mix that is precisely tailored to the needs of individual crops. For nitrogen, stripping, adsorption and electrochemical processes can be used; for phosphorus, precipitation and adsorption.
  • Disinfection: Although urine is normally free of pathogens, it may have been contaminated with faecal germs, e.g. salmonella or enterococci, before separate collection. Therefore, treatment, for example brief heating above 55 °C, is useful in order to be able to use a fertiliser end product safely.
  • Removal of micropollutants: Particularly traces of pharmaceuticals in urine can make its use as a fertiliser tricky. Eawag researchers have therefore also been looking for methods to remove organic micropollutants from urine. Some, such as ozonation, are effective but require a lot of energy. Currently, adsorption with activated carbon is the main method used, for example for the urine fertiliser "Aurin", which is already commercially available.
  • Energy generation: Electricity can be produced from urine using microbiological fuel cells. However, the yield (less than 1 W per person) is modest compared to the electricity demand (CH: 760 W per person). In addition, costly anodes are needed, which are platinum-coated, for example, to achieve the highest possible yields. However, urine-powered fuel cells could become interesting for special applications such as operating pacemakers, charging mobile phones or transmitting data from sensors.

Bathroom scale remains high hurdle

The Eawag researchers involved in the review conclude that the potential for nutrient recovery from urine is great. This is especially true if the treatment is carried out close to the "source", because transport costs are then eliminated. However, urine treatment in the bathroom remains a major challenge. This is because those processes that are suitable for this scale require the addition of chemicals and considerable maintenance (for cleaning membranes, for example). Simpler, biological processes have so far only been robust in larger facilities.
 

Different technologies of urine treatment and their current practical readiness.
(Graphic: Eawag)

In the compact "all-in-one" Blue Diversion Autarky (BDA) toilet, the researchers rely on two treatment steps for urine: Stabilisation with calcium hydroxide is followed by energy-efficient evaporation of the excess water, powered by ambient air. The hurdle to the small, technically not too complex and at the same time as robust as possible bathroom scale has thus at least been overcome for the volume reduction step. And because the first step greatly increases the pH value in the urine, germs are also killed. At the same time, handwashing and rinsing water is treated in the BDA module to such an extent that it can be reused for these purposes.

Prototypes of BDA urine treatment have already undergone intensive testing, from the Eawag campus in Dübendorf, to a Tiny Home and an SAC hut, to a site in Durban, South Africa . In collaboration with the University of Applied Sciences Northwestern Switzerland FNHW and the PSI, research has also been carried out on an extension to include a module with hydrothermal oxidation. This would also allow the faeces to be treated on site - leaving only water, carbon dioxide and a minimal amount of ash from inorganic substances.
 

NoMix on the farm is coming

The nitrogen surpluses in agriculture are still enormous, ammonia evaporates into the air, nitrate enters the groundwater. The cause: too much manure, unstabilised and occasionally applied at the wrong time. What could be more obvious than to separate the solid and the liquid in the stable at an early stage? Researchers at Eawag and the spin-off Vuna are therefore testing how urine treatment processes also work for liquid manure. The tests were successful: fresh cattle urine can be stabilised with nitrification - as has been used in wastewater treatment for decades. Together with the Strickhof Centre of Competence, an agricultural technology company and supported by the Federal Office for Agriculture, initial projects have already been extended from laboratory scale to "real" farms. The goal here is not only the controlled recovery of nutrients, but above all a reduction in nitrogen losses via ammonia and nitrous oxide. Stabilised slurry or even specifically compounded fertilisers from liquid manure have further advantages: they do not stink and can be stored. This is interesting, as the prices for imported fertilisers are currently rising sharply. And one more thing: if slurry and dung are separated at an early stage, i.e. already in the barn, this is also good for animal welfare, because the cows are less exposed to the ammonia-laden air.

NoMix on the farm could avoid losses and climate-damaging emissions at many points in the nitrogen cycle.
(Graphic: Schauer Agrotronic)


Cover picture: Energy-efficient evaporation of excess water in a test at the SAC's Legler Hut at 2280 m a.s.l. (Michel Riechmann, Eawag)

Original publications

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      originalId => protected23878 (integer)
      authors => protected'Larsen, T. A.; Riechmann, M. E.; Udert, K. M.' (75 chars)
      title => protected'State of the art of urine treatment technologies: a critical review.' (68 chars)
      journal => protected'Water Research X' (16 chars)
      year => protected2021 (integer)
      volume => protected13 (integer)
      issue => protected'' (0 chars)
      startpage => protected'100114 (20 pp.)' (15 chars)
      otherpage => protected'' (0 chars)
      categories => protected'nitrogen recovery; phosphorus recovery; pharmaceutical removal; environmenta
         l protection; volume reduction; energy production
' (125 chars) description => protected'Over the last 15 years, urine treatment technologies have developed from lab
          studies of a few pioneers to an interesting innovation, attracting attentio
         n from a growing number of process engineers. In this broad review, we prese
         nt literature from more than a decade on biological, physical-chemical and e
         lectrochemical urine treatment processes. Like in the first review on urine
         treatment from 2006, we categorize the technologies according to the followi
         ng objectives: stabilization, volume reduction, targeted N-recovery, targete
         d P-recovery, nutrient removal, sanitization, and handling of organic microp
         ollutants. We add energy recovery as a new objective, because extensive work
          has been done on electrochemical energy harvesting, especially with bio-ele
         ctrochemical systems. Our review reveals that biological processes are a goo
         d choice for urine stabilization. They have the advantage of little demand f
         or chemicals and energy. Due to instabilities, however, they are not suited
         for bathroom applications and they cannot provide the desired volume reducti
         on on their own. A number of physical-chemical treatment technologies are ap
         plicable at bathroom scale and can provide the necessary volume reduction, b
         ut only with a steady supply of chemicals and often with high demand for ene
         rgy and maintenance. Electrochemical processes is a recent, but rapidly grow
         ing field, which could give rise to exciting technologies at bathroom scale,
          although energy production might only be interesting for niche applications
         . The review includes a qualitative assessment of all unit processes. A quan
         titative comparison of treatment performance was not the goal of the study a
         nd could anyway only be done for complete treatment trains. An important nex
         t step in urine technology research and development will be the combination
         of unit processes to set up and test robust treatment trains. We hope that t
         he present review will help guide these efforts to accelerate the developmen
         t towards a mature techn...
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1 => Snowflake\Publications\Domain\Model\Publicationprototypepersistent entity (uid=24043, pid=124) originalId => protected24043 (integer) authors => protected'Riechmann, M. E.; Ndwandwe, B.; Greenwood, E. E.; R
         eynaert, E.; Morgenroth, E.; Udert, K. M.
' (137 chars) title => protected'On-site urine treatment combining Ca(OH)<sub>2</sub> dissolution and dehydra
         tion with ambient air
' (97 chars) journal => protected'Water Research X' (16 chars) year => protected2021 (integer) volume => protected13 (integer) issue => protected'' (0 chars) startpage => protected'100124 (12 pp.)' (15 chars) otherpage => protected'' (0 chars) categories => protected'field testing; resource recovery; urine stabilization; calcium hydroxide; so
         urce separation; Blue Diversion Autarky
' (115 chars) description => protected'We present the results of three field tests and three laboratory tests of a
         new physical-chemical urine treatment system, which can recover all nutrient
         s, while pathogens are inactivated. The system consists of two steps. In the
          first reactor, biological processes including urea hydrolysis are prevented
          by mixing fresh urine with calcium hydroxide (Ca(OH)<sub>2</sub>). Due to t
         he high pH value and the high availability of calcium, phosphate can be reco
         vered by precipitation. The high pH value also fosters the inactivation of m
         icroorganisms, including pathogens. In the second reactor, water is evaporat
         ed at low energy consumption by blowing unheated ambient air over the stabil
         ized urine. Stabilization in the first reactor was successful in all field a
         nd laboratory tests. The pH value remained between 12 and 13, except for sho
         rt dips due to shortages of Ca(OH)<sub>2</sub>. Nearly all phosphorus (92-96
         %) precipitated and could be recovered as calcium phosphate in the first rea
         ctor, while nitrogen and potassium overflowed with the urine into the evapor
         ation reactor. The efficiency of the second treatment step was very differen
         t for field and laboratory experiments and depended on the duration of the e
         xperiment. During a four-day laboratory test, nitrogen recovery was 98%. In
         contrast, nitrogen recovery was only around 20% in the long-term field exper
         iments. The high nitrogen losses occurred, because biological urea hydrolysi
         s was not inhibited anymore, when the pH value in the second reactor decreas
         ed due to the dissolution of high amounts of carbon dioxide from the ambient
          air. Potassium was not subject to any significant loss, and the measured re
         covery in the solid evaporation product was 98%. Evaporation rates ranged be
         tween 50 g m<sup>-2</sup> h<sup>-1</sup> (RH = 82±13%, T = 12±6°C) and 13
         0 g m<sup>-2</sup> h<sup>-1</sup> (RH = 60±19%, T = 24±5°C) in the three
         field tests. Apart from some disturbances due to low supply of Ca(OH)<sub>2<
         /sub>, the urine module ...
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Larsen, T. A.; Riechmann, M. E.; Udert, K. M. (2021) State of the art of urine treatment technologies: a critical review., Water Research X, 13, 100114 (20 pp.), doi:10.1016/j.wroa.2021.100114, Institutional Repository
Riechmann, M. E.; Ndwandwe, B.; Greenwood, E. E.; Reynaert, E.; Morgenroth, E.; Udert, K. M. (2021) On-site urine treatment combining Ca(OH)2 dissolution and dehydration with ambient air, Water Research X, 13, 100124 (12 pp.), doi:10.1016/j.wroa.2021.100124, Institutional Repository