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People-Centred Integrated Water Resources Management
(IWRM)
Author:
John Butterworth, October 2006
Quality assurance:
Jeroen Ensink, Jeroen Warner, Kees Leedertse
and Andy Cotton
Abstract
Despite the guiding
principles upon which is it is based, in reality
people are rarely at the centre of Integrated Water
Resources Management (IWRM). Or put another way,
IWRM programmes are, in many respects, just
business as usual. This factsheet considers some
of the different approaches to promoting stakeholder
participation in IWRM, and especially entry-points
and strategies for more bottom-up implementation of
the concept. These alternative approaches include
building IWRM principles into projects and
programmes rather than focusing solely on the
catchment level, using local laws and institutions
as a basis for water management, linking to the
domestic water sector’s mission to supply water to
all and responding to peoples’ real demands for
water. Links are provided in this factsheet to a
variety of sources on innovative approaches to
making IWRM more people-centred, practical and
manageable to implement.
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Box 1:
Definition of IWRM
The Global Water
Partnership defines Integrated Water
Resources Management (IWRM) as "a process
which promotes the co-ordinated development
and management of water, land and related
resources, in order to maximize the
resultant economic and social welfare in an
equitable manner without compromising the
sustainability of vital eco-systems". |
Integrated Water Resources
Management (IWRM) is about integrated or ‘joined-up’
water management (Box 1: see Moriarty et al., 2004
for more introduction). Based upon a widely agreed
set of principles (see Box 2), it promotes better
management across sub-sectors (including
agriculture, industry, domestic water supply and
environment. Figure 1 shows a broad estimate of the
relative water use between the main sub-sectors.
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Box 2:
Guiding principles from the Dublin Statement
Principle No.1: Fresh
water is a finite and vulnerable resource,
essential to sustain life, development and
the environment.
Principle No.2: Water
development and management should be based
on a participatory approach, involving
users, planners and policy-makers at all
levels.
The participatory
approach involves raising awareness of the
importance of water among policy-makers and
the general public. It means that
decisions are taken at the lowest
appropriate level, with full public
consultation and involvement of users in the
planning and implementation of water
projects.
Principle No.3: Women
play a central part in the provision,
management and safeguarding of water.
Principle No.4: Water
has an economic value in all its competing
uses and should be recognized as an economic
good.
Based
on: The Dublin Statement on water and
sustainable development, 1992.
www.wmo.ch/web/homs/documents/english/icwedece.html
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The ‘integrated’ and
‘management’ parts of IWRM warrant some further
introduction. ‘Integrated’ management aims to
minimise the negative impacts that might be created
by the actions of one particular sub-sector,
stakeholder or time, on others. It seeks to avoid
inefficiencies and conflicts that are a feature of
less-integrated approaches. IWRM thus implies a move
away from traditional sub-sector foci that address
domestic water supply, wastewater, irrigation,
industry and the environment separately (often
within different agencies or government departments)
to a more holistic approach. This does not mean that
all actions have to be fully integrated and handled
by a super-agency that replaces the many actors in
water, rather it is about finding ways to
coordinate and address coordination problems.
Figure 1. Range of water
use by sectors in Africa, Asia and Latin America

Source: Comprehensive Assessment
of the Freshwater Resources of the World, Stockholm
Environment Institute, 1997
Management is sometimes very
narrowly interpreted, but here we take it to have a
broad meaning to cover all aspects of intervention
in the water cycle including planning, systems of
water rights and allocation of water resources,
development of infrastructure and monitoring.
IWRM
for whom?
IWRM
emerged in the 1990s as a response to the ‘water
crisis’: a widespread and well-articulated concern
that the planet’s freshwater resources are under
increasingly unsustainable pressure from rising
populations, growing demands for water and
increasing pollution. Almost all definitions of IWRM
stress that it is an approach to improve efficiency
in water use (has an economic rational), promotes
equity in access to water (has a social or
developmental rationale) and to achieve
sustainability (has an environmental rationale).
With all these different objectives, it can be a
challenging and sometimes unwieldy concept.
So, where do people fit into
IWRM? Underpinning values in IWRM stress the
promotion of participation in decision-making,
equity in the sharing of benefits between users and
decentralisation of water management to the lowest
appropriate level (Box 2). Yet, in practice, IWRM is
often translated into the establishment of
relatively centralised catchment or river basin
agencies. These agencies often cover areas of tens
of thousands of square kilometres with tens, or
hundreds, of thousands of inhabitants. How in
practise can people participate, and will it make
any difference?
This factsheet identifies
some possible mechanisms, with a focus on strategies
to craft more grassroots IWRM strategies to address
the needs of the poorest and most marginalized
Promoting participation in catchment level agencies
Peoples’ views can, of course, be taken into account
in the running of catchment level agencies. This may
be through direct involvement and consultation, for
example in the development of catchment plans. The
EC Water Framework Directive for example, requires
active involvement of all interested parties in
catchment planning and tools have been developed to
facilitate such processes (Harmonicop, 2005).
Multi-stakeholder platforms have been a popular way
to encourage related dialogues (Warner, 2006).
Alternatively, or in combination, participation may
be by representation of different types. People may
be represented in catchment agencies by their
democratically elected bodies, such as local
government, who may be allocated a seat in the
decision-making organs of the agency (for example,
in South Africa). Or catchment agencies may set up
their own structures for water management to
represent different types and groups of
stakeholders, including platforms at different
levels (catchments, sub-catchments etc). In some
countries there is a mix of these types of
representation, and frequently, contestation over
roles, for example local governments taking over or
sidelining catchment agencies.
The problems
There
has, until recently, been a pre-occupation with the
river basin or large catchment as being the most
sensible unit for IWRM. While certainly some
functions are best handled at this scale, the second
Dublin principle speaks of acting at the lowest
appropriate level, and much water management has to
happen at far more local levels (Blomquist et al.,
2005). Administrative units also prove to be better
scales for much decision-making and implementation.
A further major criticism of
much IWRM activity is that it ignores politics (Gyawali
et al., 2006; Wester et al., 2003) which is one of
the main mechanisms in society for organising
participation. The water crisis is arguably more a
function of unfair distribution than an absolute
shortage of resources, and politics is the main
process that determines how water (among other)
resources are shared between potential uses. Real
participation, as opposed to token participation, is
always political because it implies a real sharing
of power in decision-making.
Many
attempts to encourage participation in IWRM score
poorly when assessed on a ladder of participation (Bruns,
2003). Rather than power-sharing and more empowering
forms of participation, most are limited to
activities about informing or consulting people. The
quality of participation in IWRM efforts is, amongst
other things, like a real commitment to shared
decision-making, limited by the human and financial
resources available to catchment management
agencies. Such agencies in many developing countries
often lack the capacity to fulfil even basic
functions. Developing comprehensive approaches to
participation will take considerable time under
these constraints.
At the local level, catchment
agencies in many developing countries may be
expected, at least in the short- and medium term, to
struggle to establish legitimacy and be effective
given their limited capacities. Fully-operational
and resourced catchment management agencies will
require decades of development. While this goes
ahead, how else can IWRM objectives be promoted?
Alternative strategies to build a grassroots IWRM
A number of different entry
points or strategies are suggested here to craft a
more grassroots IWRM that is based upon local
activities and actions. Alongside other approaches,
including a more political approach, these offer
practical ways forward in implementing IWRM.
Building IWRM principles into projects and
programmes
“The main management challenge is not a vision of
integrated water resources management but a
“pragmatic but principled” approach that respects
principles of efficiency, equity and sustainability”
(World Bank, 2003)
While basin-level IWRM by
representative bodies in which all stakeholders are
fully and fairly represented is a good target, or
endpoint, a strength of the IWRM paradigm is that
real and significant improvements in water
management can be made at all levels – from the
household to the international basin - by
individuals and institutions applying the Dublin
principles in the context of their own abilities and
opportunities (Moriarty et al., 2004).
Moriarty et al. 2000 call
this ‘light’ IWRM, and it is a local approach
similar to others called community water resources
management or local water management. ‘Light’
approaches aim to apply IWRM principles at all
stages of the project cycle (e.g. visioning,
assessment, planning, implementation, monitoring and
evaluating etc). The idea is that if sub-sector
actors apply good IWRM practice at their own level,
in their own work, this can lead to the emergence of
better local level water resource management, and be
an important first step in the process of IWRM.
An example of using
guidelines based on the Dublin principles to
implement ‘light’ IWRM at project or sub-sector
scales are the working principles for IWRM in WATSAN
(see Box 3) from field research involving eight
WATSAN and three IWRM projects in seven countries.
The principles were used as part of a process of
self assessment and improvement of IWRM practice.
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Box 3: Working
principles for WATSAN and IWRM
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Catchment
management and source protection are
essential to ensuring sustainability of
supply.
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Water use
efficiency and demand management must be
addressed to minimise the need for new
source development.
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Multiple uses of
water should be acknowledged and
encouraged.
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All stakeholders
should be involved in decision making,
but particular emphasis should be put on
the active participation of users.
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Gender and equity
issues must be addressed throughout the
project cycle.
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Water provision
should be priced so as to discourage
wasteful use, while ensuring the right
to access of a necessary minimum for
all.
Source: Visscher et al., 1999 |
Other examples of such an
approach include the EC Guidelines for Water
Resources Development Cooperation (1998) and the
Bellagio Principles for Environmental Sanitation (SANDEC/WSSCC,
2000) where many elements for applying IWRM to
sanitation are defined.
Using local institutional arrangements
Across
much of Africa and the Andes, for example,
decision-making on day-to-day water development and
management issues is in the hands of local
communities. Over centuries, local individuals and
communities have developed small irrigation systems,
springs and wells for domestic water supply and
small dams for livestock with limited external
assistance. These water systems are mainly governed
by customary water management arrangements that have
also been developed locally. These systems or rules
are specific to local environments and while always
changing, have stood the test of time in many
places.
However, many current
investments and efforts do not really build upon
these existing arrangements. There are opportunities
not just to build upon the existing infrastructure,
but even more importantly, upon the existing
indigenous institutions that already have the
experience, knowledge and systems needed to manage
water effectively at the local level (Box 4).
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Box 4:
Collaboration between the formal and
informal institutions
Given its limited
capacity in terms of its human and financial
resources, the Rufiji Basin Water Office in
Tanzania has been forced to depend on the
collaboration between a number of existing
and new institutions in the regulation and
distribution of river water flows during the
dry season; the collection of water user
fees; the construction of new infrastructure
and, most importantly, the mediation and
resolution of water conflicts.
To realise potential
advantages associated with the alignment of
formal and informal institutions, grassroots
water users have been mobilized to discuss
and agree on the amount of water to be
allocated to various uses and users, and are
authorised to oversee and regulate the
allocation. Similarly, village
leaders, both formal and informal, have
been, monitoring water availability and
quality through gauge reading and through
development and implementation of by-laws
for pollution prevention.
Source: Sokile, Mwaruvanda and van Koppen,
2005 |
Utilising the universal coverage objectives of the
domestic sector
Forging
better links between the water, sanitation and
hygiene (WASH) sub-sector and IWRM is another way to
strengthen grassroots participation in IWRM. Since
all people are domestic water consumers, building
upon WASH service delivery is an obvious way to
strengthen participation by providing people with a
reason and motivation to become involved in IWRM.
A good example is the Save
the Sand project in Limpopo Province, South Africa,
where development of community water supplies has
been integrated with programmes focusing on
catchment scale water resources and environmental
improvement. As part of this, local government (the
responsible agent for WATSAN services) has been
actively involved in establishing a catchment level
management forum.
WATSAN activities can often
be an appropriate entry point for area-based
management initiatives, such as Integrated Catchment
Management (ICM) and watershed development projects,
as it responds to what is often peoples’ most
pressing water-related need, and provides immediate
benefits, but more importantly gives people a stake
in water resource management related issues. In this
case, integration of WASH can be a means to an end,
a way to address other pressing development or
environmental issues.
Responding to peoples’ real demands for water
Responding to wider ‘domestic’ needs of many
consumers, such as for small-scale productive uses
of water, is another way to implement IWRM (IWMI,
IRC, GWP, 2006; Moriarty et al., 2004b).
Poor rural and peri-urban
families often use water for a range of domestic and
productive purposes: drinking and other household
water uses, gardening, keeping livestock and small
enterprises. However, water services providers tend
to work in 'sectors' providing 'domestic' water
supply systems, 'irrigation schemes' or 'livestock
ponds' that only meet a part of people's water
needs. These services fail to support poor men and
women's livelihoods and are often unsustainable. It
is possible to design multiple use water services
that meet people’s needs, contribute to more
sustainable systems and provide an unreached group
of people with water to support their livelihoods
(Box 5)
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Box 5:
Domestic systems also provide water for
productive uses
Around the city of
Cochabamba in Bolivia, there are an
estimated 800 locally-managed water supply
systems serving communities living in the
peri-urban areas. One such system in
Challacaba is fairly typical, with a deep
borehole linked to a piped network serving
the 435 inhabitants. Like many other
community-managed systems if offers a
comparably high quality, dependable service
at very low costs. Unlike other
systems, it specifically aims to supply
water for productive (mainly small numbers
of dairy animals) as well as domestic users.
There is an apparently self-reinforcing,
virtuous-loop between a good low cost water
service, productive uses to derive
maximum benefits from the water service,
improved willingness to pay for the water
supply and an ability to continually invest
to maintain and improve the system.
Source: Heredia, 2006 |
Conclusion
This factsheet offers
some examples of how IWRM may be made more
people-centred than the prevailing approaches. IWRM
and participation may well pull in different
directions. In particular, people-centred IWRM will
sometimes be at odds with a more environmental
approach because people who participate in
implementing IWRM will not necessarily make
sustainable decisions. The factsheet aims to
contribute to striking a good balance between equity
and environmental integrity in implementation of
IWRM
References
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Blomquist, W., Dinar, A., Kemper, K.
2005. Comparison of institutional arrangements for river basin
management in eight basins. Policy, Research
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http://econ.worldbank.org
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Bryan, B. 2003.
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Sokile, C.S., Mwaruvanda, W., and van Koppen, B.
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Websites
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Cap-Net Capacity Building for Integrated Water
Resources Management
www.cap-net.org/
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Eldis Participation Resource Guide
www.eldis.org/participation/index.htm
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Global Water Partnership
www.gwpforum.org
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Legal Pluralism & Integrated Water Resources
Management: including cases and outcomes of a
workshop on African Water Laws
www.nri.org/waterlaw
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Productive uses of water at the household level
(PRODWAT) thematic group
www.prodwat.watsan.net
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Save the Sand project, South Africa
www.award.org.za
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Water Household and Rural Livelihoods Project
www.nri.org/whirl
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