WELL FACTSHEET
Ecological
Sanitation
Authors:
Jo Smet and Steven Sugden, April 2006
Quality
Assurance: Sandy Cairncross
Ecological
sanitation - What is it?
Eco Sanitation works on the principle that urine
and faeces are not simply waste products of the human
digestion process, but rather are an asset that if
properly managed can contribute to better health and
food production and reduce pollution.
Eco-sanitation
latrines:
-
Store
and prepare faeces for use in agriculture by
encouraging the formation of humus by the
addition of wood ash and/or soil;
-
Allow
the application of urine as fertiliser in
agriculture, in case urine is separated;
-
Remove
faeces and urine from the immediate environment
thereby contributing to better health; and
-
Are dry systems that make contamination of
groundwater extremely unlikely.
An
old practice revisited
Since
early Chinese history, human excreta was commonly
used in agriculture to complement farm manure in
improving soil fertility. Farmers owned
‘Outhouses’ where they invited visitors to leave
behind their ‘valuable’ excreta. In
early Europe, Greek and Roman societies collected
human excreta and used it as fertilizer. The Romans
found that urine contained high value
nutrients and collecting it was a good business.
Emperor Vespasian introduced a ‘urine tax’ along
with the proverb pecunia
non olet (Money does
not smell).
In Britain, Queen Victoria used an earth-closet at
Windsor Castle, although many types of water-closet
were available. Henry Moule in 1840’s was the
champion of the earth-closet and backed up his
belief with a scientific experiment where he
persuaded a farmer to fertilise one half of a field
with earth from his closet, and the other with an
equal weight of superphosphate. Swedes were planted
in both halves, and those nurtured with earth manure
grew one third bigger than those given only
superphosphate. For
many years, the earth- and water-closets were rival
systems with champions and detractors on both sides.
The nutrition value of
urine and faeces as fertilizers
Fertilizer |
500 litres of Urine |
500 litres of Faeces |
Total |
Fertilizer needs of
250kgs of cereal |
Nitrogen |
5.6kg |
0.09kg |
5.7kg |
5.6kg |
Phosphorus |
0.4kg |
0.19kg |
0.6kg |
0.7kg |
Potassium |
1.0kg |
0.17kg |
1.2kg |
1.2kg |
(500
litres of urine and 50 litres of faeces are
about the amounts produced by one adult in a
year)
Note
that most of the nutrients are in the urine, though
the vast majority of the pathogens are in the
faeces. Although
faeces has a lower nutrient content, its
high organic matter aids water retention and
is a good soil improver.
Fig1:
Nutrients for plant growth present in human faeces
and urine
Ecological
latrine design
Ecological
latrines can be divided into two main types:
(i) dehydrating urine separating toilers and
(ii) composting toilets.
(i)
Dehydrating
urine separating toilets
The
urine and faeces are collected and stored separately
by the use of specially designed pedestals and
slabs.
Fig.2
Dehydrating latrine with urine diversion and
the principle of a urine diversion latrine
The urine is collected and stored until it can be used
as a fertilizer on plants or crops. The faeces drops
into a pit, vault or container to which a handful of either ash or
lime is added. This has the effect
of drying the faeces and increasing the pH which has
a positive impact on reducing smell (less ammonia
emission) and destroying
pathogens (see GTZ-EcoSan Datasheet-2).
After 12 months of storage the resulting
‘humanure’ can be applied to the land. Some form
of alternating double or multiple storage system is
required to avoid mixing fresh and composted manure.
(ii)
Composting
toilet
The double-pit or vault composting latrines do not
separate the faeces and urine, so that both
enter the same vault or pit. A handful of a mixture
of soil and ash is added to the pit after each use
which has the effect of keeping the pit contents
relatively dry and aerobic, as opposed to anaerobic and
smelly. ‘Composting’ is not technically the
correct name as the temperatures never rise high
enough to create themophilic composting conditions.
After 12 months of storage the resulting
‘humanure’ can be applied to thet land as a
fertilizer and soil conditioner. The simplest form
of composting latrine is called the Arborloo or
‘walking latrine’ (see below).
Fig3: Arborloo as introduced in Southern
Africa
Arborloo
A
shallow (1-1.5m) unlined pit covered by a
concrete slab and a movable simple
superstructure. Once the pit is 2/3
filled (usually after some 4-6 months), the superstructure
and slab are removed to a new pit. The old pit
is further filled up with soil and a young
tree is planted in the pit. Banana and Paw Paw
grow particularly well in the old pit. |
Reasons
to adopt ecological sanitation
In
many Developing Countries poor soil fertility and
the increasing cost of artificial fertilizer is
making it difficult for subsistence farmers to grow
enough food to feed their families. Survival becomes
more perilous as population growth means new land to
cultivate is not available. The fertilizer producing
qualities of ecological latrines can help the
household economy of poor families as demonstrated
by the following comments collected from Malawian
farmers who have been using eco-sanitation for a
number of years,
In
their testimony, these farmers allude not only to the
nutrient quality of the ‘humanure’, but also how
the organic matter from the faeces improves soil
structure.
The
act of adding ash and/or soil and separating the
urine has the effect of drying the faeces and the
possibility of pathogen transmission to the water
table is eliminated. This makes eco sanitation a
particularly good option in areas where
contamination of groundwater is a sensitive issue.
In
water stressed or arid areas, ecological
sanitation (which needs no water for flushing) can help save this valuable resource.
In the developed countries of
the north it has been estimated that use of
ecological sanitation could reduce domestic water
consumption by 20-40%.
Conventional
sewage systems effectively remove faecal material and the
pathogens it contains from the immediate household
and community environment and deliver it to a sewage
treatment works. In many countries the sewage works
are incapable of effectively treating the waste as
the volume entering the plant exceeds its design
capacity (either because of population growth, the
high cost of electricity or the
mixing of sewage with storm water). The result is
that poorly treated sewage is discharged into
streams and rivers with detrimental effects on the
rivers' flora and fauna. It is argued that if
eco-sanitation was more widely used, the need to
build and operate expensive sewage works would
diminish and the water quality in the rivers would
improve.
In
developing countries, areas with high groundwater
tables and collapsing sandy soils are notoriously
difficult in which to build permanent traditional
latrines. Ecological
latrines with their shallow pits or vaults can
provide good, sustainable affordable solutions.
Reasons
NOT to adopt ecological sanitation
Faeces
in all cultures is regarded as disgusting
and to
many people, the thought of using it for
food production is
repulsive. In addition, many cultures have
strongly-held beliefs and taboos regarding faeces that make
ecological sanitation unworkable. This
avoidance
instinct has self preservation at its heart
as
faeces contains many pathogens that are
harmful to
man if ingested. Even where there is no risk
of
disease transmission, the cultural
perception may be
different as demonstrated by this Malawian
farmer:
“If I eat crops and fruit grown in my own excreta, it can provide
disease”.
People
generally prefer toilets where faeces cannot be seen
and where no further handling by the users is
required. With a water closet the only necessary
further user action is the pulling of a handle; out
of sight out of mind. With eco-sanitation there is
always some form of secondary handling of the faeces
and user reluctance to do this could be high. Even
if an individual is willing to adopt eco-sanitation,
they may be put off from doing so by the fear of
being ridiculed by the rest of the community.
Sanitation
systems are one of the key defences in breaking the
faecal-oral transmission routes of many diseases.
The capacity of a latrine to either ensure no
further human contact with faeces or to reduce the
pathogens to safe levels is an essential
prerequisite. With ecological
latrines, their ability to perform the latter is
questionable.
The
potential health risks associated with ecological
sanitation
Ecological
latrines use the following techniques to ensure
pathogens die off:
Long storage
times |
Must be 12 months
or more |
Low moisture
contents |
Must be 25% or
less |
Low pH |
Must be pH 10 or
more |
High temperatures |
Must be 36°C
or higher |
Encouraging
predation |
Must be presence
of ovicidal fungi |
Ascaris is the most persistent pathogen in
faeces and is therefore used as an indicator of
pathogen removal efficiency. In a well managed ecological latrine where one or a
combination of the above environmental conditions
has been acgieved in
the pit or vault, Ascaris eggs will be reduced to a level where they do not present
a risk to public health. Problems arise when the
latrine is not well managed and the user has either
misunderstood or does not followo the management
regime stipulated by the designers. Unfortunately
this is common and is one of
the major weaknesses of ecological sanitation.
However, pathogen destruction in ecological
sanitation is often viewed from the negative angle
of what it does not achieve with regard to Ascaris
die-off, and never from the angle of what it does
achieve with a whole host of other pathogens. Ecological latrines, where
storage times are greater than 3 months, will reduce
to safe levels the pathogens responsible for Ameobiasis, ,
Giardiasis, Hepatitis A, hookworm, Trichuris
(whipwork), Enteribius
vermicularis (threadworm), Hymenolepis
nana, Rotavirus, Cholera, Campylobacter,
Eschericia coli, Salmonellosis, Shigellosis and
Typhoid.
The debate about the safety of ecological
sanitation often occurs in isolation of the context
in which it is being practiced and the larger
question of whether the introduction and practice of ecological sanitation will improve the
overall health of a community is never addressed.
Generally speaking, from a health perspective an
ecological latrine is better than no latrine at all
and any possible health risks must be weighed
against the potential improvement in the household
economy and a family's ability to feed themselves.
Ongoing
research and learning on EcoSan
Research,
demonstration and full-scale programmes are
financed by many Southern and Northern
governments and organizations. Some major
donor-supported programmes are GTZ EcoSan (www.gtz.de/ecosan),
Sida-supported EcoSanRes (www.ecosanres.org).
The websites give also reference to
other ongoing research. Three international
EcoSan Conferences/Symposia have been
organised (China, Germany and South Africa).
References
-
GTZ (2002) Ecological
Housing Estate, Luebeck, Germany.
Datasheet for EcoSan Projects 004. GTZ, Eschborn,
Germany. www2.gtz.de/ecosan/download/ecosan-pds-004-Germany-Luebeck-Flinenbreite.pdf
-
Jenssen, D. et al. (2004)
Ecological Sanitation and Reuse of
Wastewater. A think piece on ecological
sanitation. Agricultural University of Norway http://www.dep.no/archive/mdbilder/01/34/ecosan034.pdf
-
Luo Shiming (2001) the
utilization of human excreta in Chinese
agriculture and the challenge faced. South China
Agricultural University www.ias.unu.edu/proceedings/icibs/ecosan/luo-02.html
-
Mara, D. and Cairncross,
S. (1989) Guidelines for the Safe Use of
Wastewater and Excreta in Agriculture and
Aquaculture. WHO, Geneva.
-
Medina, Martin (1998)
Scavenging and Integrated Bio Systems: some past
and present examples www.ias.unu.edu/proceedings/icibs/medina/paper.htm
-
Morgan, P. (2004). An
Ecological Approach to Sanitation in
Africa. A compilation of experiences.
Aquamore, Zimbabwe www.ecosanres.org/PM%20Report.htm
-
Sawyer, R. (2003)
Sanitation as if it really matters Mexico www.gtz.de/ecosan/download/sawyer-toiletsoutofcloset.pdf
-
Stenstrom, T.A. (2002)
Reduction Efficiency of Index Pathogens in Dry
Sanitation compared with Traditional and
Alternative Wastewater Treatment Systems www.ias.unu.edu/proceedings/icibs/ecosan/stenstrom.html
-
WASTE (2005). At
the End of the Pipe? Insights, visions and ideas
on a shift in the sanitation paradigm. Summary
from expert meetings 2005. Gouda, The
Netherlands http://www.ecosan.nl/page/828
-
Werner, Ch. (2003)
Reasons for and principles of EcoSan. Paper at
2nd Int. Symp. on EcoSan, GTZ, Luebeck, Germany www2.gtz.de/publikationen/isissearch.Publikationen/details.aspx?RecID=BIB-GTZ063412
-
Winblad, U. et al (2004)
Ecological Sanitation. Revised and enlarged
edition. Stockholm Environmental Institute,
Sweden http://www.ecosanres.org/PDF%20files/Ecological%20Sanitation%202004.pdf
Major
Websites and Contacts
-
EcoSanRes (Sweden) www.ecosanres.org
with many publications and links
-
www.gtz.de/ecosan
with many EcoSan publications and links
-
www.ecosan.nl
by WASTE
-
www.sanicon.net
with oublications, websites and FAQs
-
EcoSolutions India
www.eco-solutions.org , Paul
Calvert, Kerala, India paulc@vsnl.com
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