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Looking
up the pipe and down the drain
Positioning
sanitation within Integrated Water Resource
Management
This
Briefing Note discusses the linkages between
sanitation options and water resources and the ways
in which concerns for both can be effectively
integrated and managed.
Compiled
by: Julie Fisher of WEDC
Briefing
Note Source Material: Stef Smits, IRC
Headline
facts
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At
a global level, the quality of water used for
sanitation is relatively minor compared with
productive use in agriculture. At a local
level, it may be much more significant due to
specific technologies such as flush toilets in
urban centres.
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From
an IWRM perspective, the provision of sanitation
should consider the potential risks of polluting
water resources and, where possible, reuse of
waste and wastewater.
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Complementary
management strategies exist for ensuring both
sufficient water resources and adequate
pollution control: firstly, for local
authorities to engage with water resource
management institutions and secondly, to apply
an integrated approach within the sanitation
sector.
IWRM,
Sanitation and the Water Cycle
The
various definitions of IWRM are all based on the
principles of equity (access and benefits),
efficiency (supply to the greatest number of
people) and sustainability of use.
The
Joint Monitoring Programme (JMP) of WHO/UNICEF
states that excreta disposal systems are adequate if
they are private and if they separate human excreta
from human contact. One of the main methods of
preventing pathogen transmission therefore, is an
effective disposal and removal facility for faecal
matter in the home. As sanitation is an
integral part of the water supply chain, safe
sanitation services traditionally consider all the
elements in Figure 1.

Figure
1. The traditional water and sanitation chain
With
increasing scarce water resources, using potable
water to transport human waste is inefficient and
wasteful. At the same time, seeing sanitation
as only the removal of waste, has led to pollution
of water resources.
The
impacts of sanitation should be key to IWRM, as part
of a broader focus on the water resources it is
using and polluting. This requires the water
and sanitation sector to look both 'up the pipe and
down the drain'.
Putting
Water Use for Sanitation into Perspective
The water demand for
sanitation depends on the type of technology used:

At
a global level, domestic water use accounts for only
about 10-20% of total water use, with sanitation at
less than 1%, compared to agriculture, which
accounts for 60-80%. At the local level,
however, the demand caused by sanitation can be an
important part of total domestic water consumption,
especially in large cities with full-flush toilets,
which puts a huge strain on water resources in some
regions.
Even
when water resources are in abundance, there are
still water-saving alternatives to flush toilets:
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Dry
sanitation (although this is a far from
mainstream approach)
-
Water
saving technologies exist for a wet sanitation
such as low-volume flush toilets
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Small-core
sewers require less water, as they only
transport settled sewage
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Trials
have been carried out using rainwater and grey
water for toilet use
Rainwater
for school sanitation
In
Chacon Nuevo, a village on the Columbian Pacific
coast, there is no water supply system. Few
premises have toilets, but those that do have
flush toilets are connected to rainwater
tanks. With over 3000mm of rain per year,
water resource availability is not a problem.
Pollution
from On-site Sanitation
The
type and amount of water pollution depends on the
sanitation option. There are three main
problems that arise: the transmission of
disease-causing organisms (pathogens); oxygen
depletion of receiving waters (rivers and lakes);
and eutrophication through excess nutrients in
receiving waters.
Pit
latrines
The
main risk posed by pit latrines is microbiological
contamination of groundwater. This mainly affects
only those who use water from boreholes or
wells. Water resource management should cover
risk assessment and alternative technologies for the
specific site conditions.
Sludge
disposal
Inappropriate
sludge disposal can also pollute groundwater and
open water bodies, making sludge management
important. It can be disposed of on water or
land (with risks of pathogen transmission), added to
wastewater treatment works, or turned into agricultural
compost and biogas.
Flush
toilet to septic tank
Similar
contamination issues apply. The various
management options for emptying septic tanks pose
risks, requiring careful planning of treatment
and/or disposal sites and awareness of potential
downstream impacts.
Sewers
The
only direct pollution caused by sewers is if they
leak, although cross contamination of piped water
systems is also common. More importantly,
sewerage systems collect all types of household,
industrial, hospital and solid waste, resulting in a
wide variety of pollutants. Wastewater
treatment can be most effective when waste flows are
separated and kept as homogeneous as possible.
Wastewater
treatment and disposal
Wastewater
treatment and effluent disposal is arguably the most
obvious point where sanitation and water resource
management meet. Treatment and disposal
options are largely determined by earlier activities
in the chain, but the main objective is to remove
the risks from the three main types of
contaminants. Despite this, wastewater
treatment occurs only to a very limited extent,
mainly due to the costs of construction, operation
and maintenance.
Source:
Scott et al., 2004.
Reuse
of wastewater
Reuse
of wastewater is emerging as an important issue
relating to both pollution prevention and minimising
treatment costs.
A
typology of wastewater use:
-
Direct
use to land of untreated wastewater from a
sewerage system or other purpose-built
wastewater conveyance system.
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Direct
use of treated wastewater to a controlled area
for irrigation
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Indirect
use of wastewater which may be treated or not,
but is partially diluted in the receiving
water body.
Van
der Hoek, in Scott et al, (2004).
Wastewater
treatment technologies suitable for meeting
microbiological guidelines for reuse of wastewater
in agriculture include the use of waste
stabilisation ponds, wastewater storage and
treatment reservoirs, or conventional treatment
processes.
A
range of health protection measures including crop
restriction, irrigation techniques and human
exposure control should all be considered in
conjunction with partial wastewater treatment.
In some cases, community interventions using health
promotion programmes could be considered.
Sanitation
in Water Resource Management
The
way in which sanitation is managed has an impact
on water resources, while at the same time,
sanitation is heavily dependent on them.
The water and sanitation sector needs to manage
this dual role and two strategies exist for
this: to position sanitation more effectively in
water resource platforms, and to apply an
integrated approach within sanitation
development. Both are important and their
suitability depends on the case in question.
Sanitation
in water resource management platforms The
known linkages between sanitation options and water
resources require local authorities, who are
responsible for sanitation, to engage with the water
resource management institutions that are being
established in many countries. Some cautionary
lessons for these local authorities are:
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Local
authorities may not see the need for water
resource management, as the water and sanitation
chain is based on the idea of "beyond the
end of the pipeline", which is outside of
their responsibility.
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The
difficulties of one government body enforcing
control over another can hinder the discharge of
untreated wastewater. Political issues may
also hamper its effectiveness.
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Internal
conflicts may arise if increased sanitation
coverage also increases the adverse impacts
caused by sanitation.
An
integrated approach to sanitation
An
alternative can be to follow an integrated
approach within the sanitation sector,
maintaining the sector's own mandate of equity,
efficiency and sustainability. Key guiding
principles should include:
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sustainable
access to water resources for sanitation;
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water
use, efficiency and impact on water resources;
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multiple
and alternative water sources for sanitation;
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reduced
pollution and waste management;
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reuse
and management of wastewater and desiccated
waste products;
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separation
and concentration of waste flows;
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downstream
water uses and the self-purifying capacity of
receiving water bodies;
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stakeholder
and user involvement in active decision making;
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linkages
with stakeholders involved in WRM; and
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gender
and equity issues
Conclusions
As
delivery of both rural and urban sanitation services
is scaled up, there is a tendency to focus only on
the household level, ignoring the subsequent stages
of waste management. Where there is
water-borne sanitation in the growing urban
centres, there is a significant impact on
water resources. These linkages require those
responsible to implement processes by which they can
be strategically managed and any potential problems
overcome.
Key
References
-
Cave,
B. and Kolsky, P. (1999). Groundwater, latrines
and health. WELL Task 163. www.lboro.ac.uk/well/resources/well-studies/summaries-htm/task0163.htm
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Kalbermatten,
J . M., Middleton, R. and Schertenleib, R.
(1999). Household-Centred Environmental
Sanitation. WSSCC Working Group Environmental
Sanitation, Switzerland. www.sandec.ch/environmentalsanitation/documents/paper_
description_HCES_july99.pdf
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Moriarty,
P., Butterworth, J. and Batchelor, C. (2004).
Integrated Water Resources Management and the
domestic water and sanitation sub-sector.
Thematic Overview Paper. IRC International Water
and Sanitation Centre, The Netherlands. www.irc.nl/page/10431
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Scott,
C.A., Faruqui, N.I. and Raschid-Sally, L.
(2004). Wastewater use in irrigated agriculture:
confronting the livelihood and environmental
realities. CABI Publications, United
Kingdom.
-
Blumenthal,
U.J. et al., (2000). Guidelines for wastewater
reuse in agriculture and aquaculture:
recommended revision based on new research
evidence. WELL Task 68 Part 1. www.lboro.ac.uk/well/resources/well-studies/full-reports-pdf/task0068i.pdf
Background Report
containing
full details of all the materials used in support of
this Briefing Note
For
further information contact:
WELL Water,
Engineering and Development Centre (WEDC) Loughborough
University Leicestershire
LE11 3TU UK Email:
well@lboro.ac.uk Phone:
+44 (0)1509 228304 Fax:
+44 (0)1509 223970
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