Passive evaporation of source-separated urine from dry
toilets: a lab study
David N. Bethune, Angus Chu and M. Cathryn Ryan
ABSTRACT
A methodology for evaporating human urine from dry toilets using gravity-drainage
through vertically stacked plastic ‘cafeteria-type’ trays was tested. A thin layer (500 g) of
medium-grained sand on the bottom of each tray enhanced evaporation, ammonia stabilization
and solid product removal. A prototype laboratory unit initially evaporated up to 8.5 L m
2
d
1
but decreased to 1.5 L m
2
d
1
over time as salinity increased. The evaporation process produces
a dark, highly saline, brine solution before drying to a solid product. The solid product has almost
no odor and is mostly comprised of Na, Cl, N, P and K. Nitrogen loss, primarily by ammonia
volatilization, significantly decreased the amount of N relative to P and K in the brine and solid
product. About 90% of the NH
4
/NH
3
initially present in the input urine was lost in the evaporator
system.
David N. Bethune (corresponding author)
Angus Chu
Civil Engineering,
University of Calgary,
2500 University Drive NW,
Calgary, Alberta,
Canada, T2N 1N4
E-mail: bethuned@ucalgary.ca
M. Cathryn Ryan
Geoscience,
University of Calgary,
2500 University Drive NW,
Calgary, Alberta,
Canada, T2N 1N4
Key words | diversion, evaporation, sanitation, source-separation, urine
INTRODUCTION
Rural sanitation systems based on the separation of urine
and feces from the toilet onward (a.k.a. urine diversion
[UD] or urine source separation; Larsen & Gujer ;
Hanæus et al. ; Hellstrom & Johansson ) offer
some very distinct advantages over traditional urine-feces
mixed (a.k.a. blackwater) systems. Urine and feces have
several important differences that make their separation
advantageous to each. Urine has a much higher water con-
tent than feces (96% vs 70%) which, when combined with
the annual rates of per capita production (500 L of urine
vs. 50 L of feces), makes the onsite disposal or transport
of urine challenging (Del Porto & Steinfeld ). Nutrient
recovery from urine is also safer than from feces (which
contain relatively high numbers of pathogens; Schonning
& Stenstrom ), although some pathogen cross-con-
tamination to urine can occur at the UD toilet
(Schonning et al. ; Höglund et al. ). Finally,
source-separated feces are drier, less odorous, and are
more easily stabilized or composted than feces mixed
with urine (Hill et al. ).
Urine is a saline (3.5%), normally sterile solution con-
taining soluble salts, nutrients and organic compounds
dominated by the nitrogen-rich urea. Immediately after
urine exits the human body it enters a non-sterile environ-
ment and undergoes a spontaneous, irreversible process
called urea hydrolysis (Warner ; Andrews et al. ).
This conversion of organic urea nitrogen to inorganic
ammonia leads to a dramatic pH increase from about 6 to 9
(Ciba-Geigy ; Kirchmann & Pettersson ; Jonsson
et al. ; Udert et al. ) leading to high levels of ammo-
nia gas producing a strong odor, and a substantial increase
in alkalinity. The high ammonia levels naturally hygenize
or sterilize urine over time (Höglund et al. ; Höglund
et al. ) eliminating any potential pathogens within 4–6
months (Höglund ; Schonning & Stenstrom ).
Urine contains most of the nutrients excreted by humans
(85–90% nitrogen, 50–80% phosphorus, and 80–90% potass-
ium; Larsen & Gujer ). On average, each person
produces about 15 g d
1
of combined nutrients (N, P, and
K) in urine, and only about 3 g d
1
in feces (Del Porto &
654 © IWA Publishing 2014 Journal of Water, Sanitation and Hygiene for Development | 04.4 | 2014
doi: 10.2166/washdev.2014.058
Downloaded from https://iwaponline.com/washdev/article-pdf/4/4/654/384974/654.pdf
by guest
on 21 May 2020