integrated water resources management in the caribbean
TRANSCRIPT
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Integratedwater resources
management
in the Caribbean:
The challenges facing SmallIsland Developing States
T F PECHNICAL OCUS APER
www.gwp.org
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www.gwp.org2
Global Water Pa rtnership (GWP), es tablished in 1996, is an international network open to
a ll organisa tions involved in wa ter resources mana gement: developed a nd developing country
government institutions, a gencies of the United Na tions, b i- and multila tera l development
ba nks, professiona l as sociations, research institutions, non-governmenta l organisa tions, a nd
the priva te s ector. GWP wa s crea ted to fos ter Integrate d Water Resources Management (IWRM),
which aims to ensure the co-ordinated development and ma nagement of water, land, a nd
related resources by maximising economic a nd socia l welfa re without compromising the
sustainability of vital environmental systems.
GWP promotes IWRM by crea ting fora a t global, regional a nd national levels, des igned
to support sta keholders in the pra ctical implementation o f IWRM. The Pa rtnership's governance
includes the Technical Committee (TEC), a group of interna tionally recognised profess ionals and
scientists skilled in the different as pects of water management. This committee, whose
members come from different regions of the world, provides technical support and ad vice to theother governance a rms and to the Pa rtnership as a whole. The Technical Committee has been
charged with developing a n a nalytical framework of the water sector a nd proposing a ctions that
will promote s usta inable wa ter resources management. The Technical Committee maintains a n
open cha nnel with the GWP Regiona l Wa ter Partnerships (RWPs) around the world to facilita te
a pplica tion of IWRM regiona lly and na tionally.
Worldwide adoption and a pplica tion of IWRM req uires changing the way business is
conducted by the international wate r resources community, particula rly the way investments
a re made. To effect changes of this nature and scope, new ways to address the globa l, regionaland conceptual aspects and agendas of implementing actions are required.
ATechnical Focus Pa per is a publica tion of the GWP Technical Committee aimed a t harnessing
and sha ring knowledge and experiences genera ted by Knowledge Partners and Regional/Country
Water Partnerships through the GWP Knowledge Cha in.
© Globa l Wa ter Partnership, 2014. All rights reserved.
This publication is the property of Globa l Wate r Partnership (GWP) a nd is protected by intellectua l property
laws. Portions of the text may be reproduced for educational or non-commercial use without prior
permiss ion from GWP, provided tha t the source is a cknowledged, with mention of the complete na me of the
report, and that the portions are not used in a misleading context. No use of this publication may be made
for resa le or other commercial purposes . The findings, interpretations, a nd conclusions express ed a re tho se
of the author(s) and do not imply endorsement by GWP.
ISSN: 2001-4023
ISBN: 978-91-87823-01-5
Printed by LjungbergsDesign and layout by Scriptoria, www.s criptoria.co.uk
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Contents
Acronyms . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .4
Foreword . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .6Executive summary . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .71 Water challenges on small islands . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .102 The Caribbean . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .13
2.1 Clima te . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .15
2.2 Geogra phy . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .15
2.3 Demographics . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .16
2.4 Water resources and water services . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .17
2.5 Polit ics o f water management . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .19
3 Policy challenges . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .22
3.1 Challenges for IWRM . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .223.2 Challenges for water security . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .23
3.3 The Cartagena Convention . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .24
3.4 Challenges related to climate change . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .25
3.5 The challenges for regional approaches . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .25
4 Policy developments . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .274.1 Regional and sub-regional IWRM developments . . . . . . . . . . . . . . . . . . . . . . . .27
4.2 National developments . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .28
4.2.1 Anguilla . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .28
4.2.2 Antigua a nd Barbuda . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .28
4.2.3 The Ba ha ma s . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .294.2.4 Ba rba dos . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .29
4.2.5 Belize . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .30
4.2.6 British Virgin Islands . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .31
4.2.7 Dominica . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .31
4.2.8 Grena da . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .31
4.2.9 Guya na . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .32
4.2.10 Jamaica . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .33
4.2.11 Montserrat . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .34
4.2.12 Sa int Kitts and Nevis . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .34
4.2.13 Sa int Lucia . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .354.2.14 Sa int Vincent and the Grenad ines . . . . . . . . . . . . . . . . . . . . . . . . . . . . .36
4.2.15 Trinida d a nd Tob ago . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .37
5 Adoption of IWRM – so where a re we? . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .395.1 Public part icipation . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .39
5.2 Polit ica l support . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .39
5.3 Institutional and professional support . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .41
5.4 Project-based support . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .42
5.5 Stakeholder legitimacy . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .43
5.6 The Dublin Principles . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .44
5.7 Transforming water management . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .45References . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .47
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ACRONYMS
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ACS . . . . . . . . Association of Caribbean States
APUA . . . . . . . Antigua Public Utilities AuthorityBPOA . . . . . . . Barbados Programme of Action
BWA . . . . . . . . Barba dos Water Authority
Cap-Net . . . . . Capa city Development in Sustainable Water Mana gement
CAR/RCU . . . . Ca ribbean Regional Coordinating Unit
CARDI . . . . . . . Ca ribbean Agricultura l Resea rch and Development Institute
CARICOM . . . . Ca ribbean Community
CARIWIN . . . . . Ca ribbea n Water Initia tive
CAWASA . . . . . Ca ribbea n Water and Sewe ra ge Ass ocia tion Inc.
CBO . . . . . . . . Community-ba sed organisation
CDB . . . . . . . . Caribbean Development Bank
CEHI . . . . . . . . Ca ribbean Environmental Hea lth Institute
CIMH . . . . . . . Ca ribbean Institute for Meteorology and Hydrology
COTED . . . . . . Council for Trade and Economic Development
CWSA . . . . . . . Centra l Water and Sew erage Authority
CWWA . . . . . . Ca ribbean Water and Was tewa ter Association
DOWASCO . . . Dominica Water and S ewera ge Company
EC . . . . . . . . . European commission
ECLAC . . . . . . Economic Commiss ion for La tin American and the Caribbean
EU . . . . . . . . . European Union
FAO . . . . . . . . Food a nd Agriculture Organization of the United Na tions
GEF . . . . . . . . Global Environment Facility
GoB . . . . . . . . Government of Barbados
GoJ . . . . . . . . . Government of Jamaica
GoSL . . . . . . . Government of Saint Lucia
GoTT. . . . . . . . Government of Trinida d a nd Toba go
GWI . . . . . . . . Guyana Water Inc.GWP . . . . . . . . Globa l Water Partnership
GWP-C . . . . . . Globa l Wa ter Partnership Ca ribbea n
IDB . . . . . . . . . Inter-American Development Bank
IPCC . . . . . . . . Intergovernmental Panel on Clima te Change
IWCAM . . . . . . Integrating watersheds and coastal areas management
IWRM . . . . . . . Integrated wa ter resources management
JpoI . . . . . . . . Johannesburg Plan of Implementation
LBS . . . . . . . . Land-based sources
MoH . . . . . . . . Ministry of Health
Acronyms
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ACRONYMS
NAWASA . . . . Na tiona l Water and S ewerage Authority
NGO . . . . . . . . Non-governmental organisationNWC . . . . . . . . Na tional Wa ter Commiss ion
OECS . . . . . . . Organisation of Eas tern Ca ribbea n States
RIC . . . . . . . . . Regulated Industries Commission
SIDS . . . . . . . . Small Island Developing States
SVG . . . . . . . . Saint Vincent and the Grenadines
UNDP . . . . . . . United Na tions Development Progra mme
UNEP . . . . . . . United Nations Environment Progra mme
UNEP-CEP . . . UN Environment Progra mme-Caribbea n Environment Programme
UNFCCC . . . . . United Na tions Framework Convention on Climate Change
USACE . . . . . . United States Army Corps of Engineers
WASA . . . . . . . Water and S ewerage Authority
WASCO . . . . . Wa ter a nd Sewerage Company
WB . . . . . . . . . World Bank
WRA . . . . . . . . Wa ter resources agency
WSP . . . . . . . . Water safety plan
WUE . . . . . . . . Water use efficiency
Authors: Adrian Cashman, Christopher Cox, Judy Danie l, and Terrence Smith
Acknowledgments
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FOREWORD
www.gwp.org6
Foreword
Concerns about the rea lity of implementing integra ted water resources mana gement (IWRM) have
been raised many times. Although IWRM has gained worldwide acceptance over the past two
decad es and is now included in na tional policies, strategies, and laws, there are still questions
ab out how it is put into practice. So what is the current state of water resources planning and
implementation?
Substantia l evidence to support an integra ted approach comes from the UN sta tus report on
Integra ted Approaches to Water Resources Management (UN, 2012) published in time for the Rio+ 20
Conference. Some 134 nations across the world responded to the survey to de termine progress
towards susta inab le water resources using integra ted a pproaches. These a pproaches were measured
against the practical elements of implementing integra ted water resources management, namely, a
strong enabling environment; s ound investments in infrastructure; clear, robust, a nd comprehensive
institutional roles; and effective use of available management and technical instruments.
Encouragingly, 82 percent of countries have embarked on reforms to improve the enabling
environment and integra ted approaches to wa ter resources management. The report rightly points
out that there is no quick fix for sustainable water mana gement and so na tional and international
leaders must demonstrate their commitment for the long haul if it is to succeed.
Many changes have indeed taken place in the a rea of water management, a nd it is highly likely that
the extent and timing of ad ditional changes will accelera te even further in the coming deca des. The
need for an objective, non-dogmatic scrutiny of the IWRM paradigm has never been stronger. But the
conceptual attractiveness of a pa radigm is not enough: it must be applicable in the real world to
improve the sustainable management of water resources.
This Technica l Focus Paper is the first in a series of papers to present a critica l review of progress
made in planning and then putting plans into practice. They synthesise the cha llenges, the
successes, the setba cks, and the d irection for further integra tion. They provide valuable insights from
which others can learn lessons and a pply them to their particular and often unique circumsta nces.
This paper dea ls with the 15 English-spea king Caribbea n States, which comprise some of the most
fragile economies in the region, and expla ins the specia l circumsta nces of Small Island Developing
States as they adopt and a dapt to a 'source to sea' approach as their integrating framework. After 15
years' experience, the tangible results serve as a tes tament to the effectiveness and importance of
taking an integra ted approach. They reinforce the messa ge tha t this works best when it addresses
real issues that resona te with people's everyday experiences with water and their environment.
My thanks to the authors of this report, who a re members of GWP-Caribbean, for their excellent
ana lysis of water security challenges in what is a most diverse a nd complex region. We would
particularly like to a cknowledge Adrian Cashman, Christopher Cox, and Terrence Smith as lead
authors and others within GWP-Caribbea n for their inva luable comments and suggestions during
the dra fting stages.
Dr Moha med Ait Kadi Judy Daniel
Cha ir, GWP Technica l Committee Cha ir of GWP-Ca ribbea n
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Executive summary
In 1998, the Forum of Ministers of the Environment of La tin America a nd the Caribbea n agreed
that integrating water and coasta l resources mana gement was a priority in the Caribbean region.
In 2002, at the Johannesburg World Summit on Susta inable Development, the Caribbea n States
a lso committed to work towa rds developing integra ted wa ter resources mana gement (IWRM)
plans and water use efficiency (WUE) plans by 2005. Some 15 years have now pass ed a nd this
paper as ks: What measures have been taken and what progress has been made towards
adopting an integra ted a pproach to wa ter mana gement in the Caribbean?
For Sma ll Island Developing States (SIDS), realising these a mbitious commitments was a lways
going to be challenging. These s ta tes a re particularly vulnerable to increased s tress es on their
water resources through the limitations of land, population, and water resources and the need
for economic development and socia l well-being. Hence in SIDS, IWRM has to adopt a 's ource to
sea ' approach as an integra ting framework. For the Caribbea n, with a large geographical
footprint, but small and dispersed popula tions and land mass , which face simila r clima tic
conditions that influence the availab ility of water resources, it makes sense to combine national
initiatives with a regional approa ch.
Much work has taken place in the region to push forward a process of integra tion, a nd examples
of initia tives and an eva lua tion of their outcomes and rela tive successes a re described. The focus
is on the 15 States in the English-speaking Caribbea n, the unifying effects of whose s hared
language a nd cultura l and politica l simila rities make this region a productive focus for the
evaluation. This area has some of the region's most vulnerable sta tes and territories in terms of
fragile economies, impact of clima te change, and constra ined development opportunities.
A feature of water resources in the Caribbean is the diverse organisational a rrangements
governing management. Jamaica and Guyana ha ve a ministry dedicated to water management,
but in most states, water mana gement forms just one part of a ministry portfolio, and often,
responsibility is spread across more tha n one ministry. Responsibility for ta riffs and economic
regula tion is ra rely exercised independently of ministeria l/cabinet control.
In most sta tes, water service providers a lso undertake wa ter resources management. Water
supply and was tewater services a re undertaken by a government-owned company or statutory
authority, with little independent oversight and eva lua tion. Little distinction is made be tween
responsibilities for water services and wa ter resources management, as they are centralised
within the same organisation. This reflects a predominant supply-side paradigm that sees water
resources as an integra l extension of water supply services. This centra lising tendency is
underpinned by the politica l dispensa tions that came into being after independence, which
sought to address a legacy of neglect and marginalisa tion of large sections of the population on
the grounds of colour and race. Programmes were implemented to grea tly expand provision a nd
access to bas ic services, such as health care, education, a nd water and sanitation. As a result,
the region made significant progress in water supply, a nd most countries report over 95 percent
access. Concomitantly, the public have come to expect that governments will provide services by
guaranteeing financial support to ensure minimal cost to the public so that services are
a fforda ble. The problems now being encountered include qua lity of service, maintenance a nd
operation of existing infra structure, a geing infrastructure, high levels of unaccounted for water,
and quality of potable water. This suggests difficulties with the mana gement of water services
and with securing the necessa ry levels of investment to a ddress the supply–demand gap.
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Water resources management faces challenges that affect water a vailability and long-term
freshwa ter security. An example is the increasing threa t to streamflows caus ed when catchments
a re converted for development and agriculture. Overa ll wa ter security is an emerging challenge,
which the present institutional frameworks and enabling environments are increas ingly
ill-eq uipped to dea l with. Although many governments acknowledge the need for change a ndto develop plans , existing efforts to put these plans into practice have not proved s ufficient.
Regional interventions have failed to get off the ground and na tiona l-level interventions have
fared little better. The main cha llenge facing regional approa ches is diversity, and so wa ter
resources management should focus on developing common frameworks and standa rds.
Over the past decad e, most of the many interventions designed to improve integra tion have been
initiated or promoted by international or regiona l actors. But a 'project approach' preferred by
such agencies, a nd the as sociated implica tions for funding activities, does not fit well with the
protracted process of transitioning and reforming national water sectors. Despite the fact that the
Caribbean region shows considerable understa nding of and sensitivity to the need for
integra tion, so fa r efforts to embed integra ted thinking have yielded few ta ngible benefits,particula rly when these efforts have focused on institutional frameworks.
The administrative and professional clas ses in the wa ter sector are very well acquainted with an
integra ted a pproa ch and a ctively include it, as far as they can, in the working environment. This
is due in large part to ongoing training, capacity building, and networking of va rious advocacy
organisa tions. However, the profess ionals have failed to capita lise on this, even when
opportunities, such a s the impact of natural hazards (e.g. droughts and hurricanes), have drawn
a ttention to the need for change. It may have been the cas e that the urgent need for short-term
crisis mana gement obscured the longer-term commitment req uired for more far-rea ching reforms.
Projects that add ress specific stakeholder concerns or issues at national and community levels
were the most successful and visible aspects of interventions. The greates t impact can be seen in
specific 'demonstration' projects, usually a t the community or wa tershed level. These results
reinforce the messa ge that an integrated a pproach works best when it addresses real issues that
resonate with people's everyday experiences with wa ter and their environment.
In spite of failings in water service delivery, consumers and the public have s hown very little
appetite for change, a nd there is implicit support for continuing with existing arrangements.
Customers have little influence over service providers and a re unab le to hold them to a ccount.
This lack of public interest in change is compounded by perceived political risks of change, such
as ra ising wa ter ra tes, improving collection of unpaid bills, a nd depoliticising investment
decisions by which potentia l influence is reduced. The ca binet-ba sed approach to politica l
decision-making could potentia lly provide a mechanism for mobilising politica l support if
ministers were to become champions of change. But this has seldom been the cas e.
Given the level of consensus among the va rious actors in the water sector and their commonly
held beliefs about what constitutes good water governance, the necessary conditions for
improving water management a re in place. However, the slow pace of change suggests that these
conditions and the presence of champions a lone are not sufficient; that something else is
necessary. Recent research suggests that advocacy needs to be complemented by so-called
'brokering' a ctions, which ca ll for different approa ches for different countries. Brokering is about
recognising and reconciling the needs and a spira tions of different sta keholders, pa rticula rly the
politicians. This is achieved by ensuring a 'fit' between the problem perceived by politicians and
decision-makers and the proposed s olution. This suggests that approaches that seek wholesale
wa ter mana gement reform will seldom 'fit'. What a re req uired a re more incremental approa ches,
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EXECUTIVE S UMMARY
peculiar to each country, coupled with internat ional financia l contributions. Such approa ches
may be more successful, particularly if they have support a t the very highest politica l level. The
challenge for the Caribbean is how to secure that level of support, which to date is missing.
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1 WATER CHALLENGES ON SMALLISLANDS
www.gwp.org10
Small Island Developing Sta tes (SIDS) are pa rticularly vulnerable to increased stresses on their
wa ter resources (Cas hman et a l., 2010; Fa lkland, 1999; Pa yet a nd Agricole, 2006). Thelimitations of land, population, a nd wa ter resources and the need for economic development
and social well-being place pa rticular press ures on them. Furthermore, a pa rticular fea ture of
SIDS, which sets them apa rt from their continental neighbours, is the close interconnection
between land a nd sea and the role of water as the medium of connection between them.
Run-off genera ted by ra infall events can travel quickly through the terrestrial environment and
enter the ma rine environment within a very short spa ce of time. The use and mana gement of
land a nd water resources have a direct and immediate effect on the health and vitality of
marine resources, so it is important to link water and watershed management with the
management of coasta l areas. This is necessa ry in order to support livelihoods and ecosystems
services of both terrestria l and ma rine environments. Hence in SIDS, integra ted wa ter resources
management must ad opt a 'source to sea ' a pproach a s an integrating framework (UNEP, 2012a).
In 2002 a t the Johannesburg World Summit on Susta ina ble Development, the Caribbean Sta tes,
a long with the rest of the global community, signed up to the Johannesburg Pla n of
Implementation (JPoI). One of the provisions under JPoI was a commitment to work towards the
development of IWRM plans and wa ter use efficiency (WUE) plans , to be in place by 2005. In
large part this recognised that the limitations of existing water management arrangements were
imposing obstacles to national development, as well as having a n increasingly ad verse impact
on the integrity of ecos ystems. For developing countries, a nd particula rly for SIDS, the
realisation of the ambitious commitments made in respect of water management was always
going to be cha llenging. A regiona l a pproa ch to the problem, in conjunction with na tional
initia tives, is an effective approa ch to the problem for a region such as the Ca ribbean with alarge geographical footprint and small and dispersed popula tions and la nd mass . The countries
face simila r climatic conditions that influence the availability of wa ter resources. This was
recognised a t a Caribbea n Ministers of Environment meeting in April 2008 a t the Caribbean
Community's (CARICOM) Council for Trade a nd Economic Development (COTED) (CARICOM,
2011). It expressed the concern that the ma jority of Ca ribbea n States had not been able to
a chieve the JPoI goals and that the need for policy and governance reform was not being met.
Ministers recognised that in order to support this process there was a need to develop a
common approa ch to wate r resources management in the Caribbean tha t would contribute to
developing and s trengthening nat ional wa ter policies, IWRM, a nd WUE plans .
Preceding, but overlapping these events , was another IWRM-relate d development. At the 11th
Meeting of the Forum of Ministers of Environment of La tin America and the Ca ribbean in Ma rch
1998 (UNEP, 1998), it was agreed tha t there was a priority need to include a project in the
Regional Programme of Action to address integrated mana gement of water and coas tal
resources in the Caribbea n region. Following this, CARICOM a nd the Secretariat of the Cartagena
Convention, the Caribb ea n Environmenta l Hea lth Inst itute (CEHI), the United Na tions
Environment Programme-Caribb ea n Regiona l Coordinat ing Unit (UNEP-CAR/RCU), a nd the
United Na tions Development Programme (UNDP) proceed ed to develop a project to strengthen
institutional capacities a t national and regional levels, and a ssist countries in integrating their
management of watersheds and coasta l areas (Merla a nd Simmons, 2012). The project was
funded through the Globa l Environment Facility (GEF) with co-funding from na tional
governments and partner organisa tions a nd was referred to a s the GEF-funded Integra ting
Watershed a nd Coa sta l Area Mana gement (IWCAM) project. It was approved in Ma y 2004 and
became operational in 2006. One of the anticipated outcomes of the project was to implement
1 Water cha llenges on sma ll islands
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1 WATER CHALLENGES ON SMALLISLANDS
overall na tiona l a nd regiona l reforms in support of the GEF-IWCAM PROJECTapproach. This
would be primarily achieved through policy, legislation, and institutional reforms of the way in
which water resources were managed.
A related de velopment contributing to and supporting improvements in wa ter resourcesmanagement was the formation of a regional Global Water Partnership network of partners.
Globa l Water Partnership Caribbean (GWP-C) was esta blished in 2004 a t a meeting a ttended by
67 representa tives from 14 countries and 36 organisa tions in the Caribbean region. As of
December 2013, GWP-C has 80 pa rtners in over 20 Caribbea n territories (GWP-C, 2014a). One
of the goals of the partnership is to promote and facilitate better water resources management
through the a doption of IWRM. To this end it supports the development of IWRM roa d maps a nd
undertakes awareness -ra ising activities. GWP-C co-hosts the a nnua l High Level Forum for
Ministers with responsibility for water (GWP-C, 2014b), which provides a platform for them to
meet with other decision-makers, wa ter experts and professionals, a nd representa tives of
regional organisa tions active in the water sector to discuss policy and water-related matters,
under the umbrella of IWRM.
The 2012 Ministe rial Forum recognised the importance of ensuring long-term wa ter security as a
driver for economic and s ocial development a nd the urgent need to address water scarcity in
the region. From this (GWP-C, 2014c) came a clea r understanding tha t more politica l a ttention
was needed to promote meas ures that increas e water security. The prominence of the iss ue
indicated the growing concern over the ability of the governments to ensure good ma nagement
a nd provision of wa ter without jeopardising economic growth and the ma intenance of social
well-being. Of concern were the impacts of clima te change, tariffs and the financia l
susta ina bility of service provision, the need to upgrade existing wa ter infra structure a nd
improve resource use efficiency, the prevention of pollution of wa ter sources, a nd the
management of resources a nd services in the face of natura l hazards. While IWRM seeks toaddress all of these issues, there appears to be a long way to go and governments are
struggling to ma instrea m IWRM.
The sha red a nd multifaceted nature of water presents special cha llenges for its management
a nd the problems faced. The professional and institutional sta keholders in the region clea rly
show no shortage of interest in water management and the potential threats to water security.
But this interest is not, on the whole, reflected by the genera l public, whose interests are often
more immedia te. The vulnerabilities of, in pa rticular, tropical island s tates and territories have
long bee n recognised. For example, the 1994 Ba rbad os Progra mme of Action (BPOA) for the
Sustainable Development of SIDS, identified priority areas a nd specific actions necessa ry for
a ddressing the special cha llenges faced by SIDS. Priorities included coasta l and marine
freshwater and land resources, a s well as strengthening nationa l and regional institutions (UN,
1994). This was followed by the Mauritius Stra tegy of Implementation in 2005 which recognised
that there were still constra ints in fulfilling the a ctivities of the BPOA. So, some 15 years a fter
the 1998 a greement that recognised the need for a n integrated approach to wa ter and coasta l
a reas management, and nearly 20 years after the BPOA, what meas ures have been taken and
what progress has been mad e in the Ca ribbean to adopt IWRM?
This paper a ttempts to answer this question. It takes stock of how much progress the Caribbea n
has made in improving wa ter resources management a nd builds on this experience to better
inform the future direction of movement. Future a ctions must be informed by past lessons and
a chievements in order to formulate answers to the question: Should things be done differently
or should different things be done? The extent to which the management of wate r resources will
be mainstreamed in the future will be determined by how well it resonates with Caribbea n
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realities a nd circumsta nces. This means that it will have to incorporate changing conceptua l
frameworks, such as the green economy, the la nd–wa ter–energy nexus, and the successors to
the UN Millennium Development Goals on susta inability, a s well as building upon the less ons
of the past .
" In the series of things those which follow are always aptly fitted to those which have gone before; for this series is
not like a mere enumeration of disjointed things, which has only a necessary seq uence, but it is a rational
connection."
The Meditation s, Book 4. Marcus Aurelius (121–180 AD)
Firstly, the pa per presents an overview of the wa tersca pe of the Caribbean region, in order to
set the context within which the water a ffa irs of the region a re loca ted a nd ma naged . Thisincludes the social, economic, and cultura l factors which modulate the intera ction between
society and water and which shape water use and mana gement. A number of challenges and
concerns a rise from this that have a direct bea ring on policy development. These include
questions of how climate change a nd was tewater management might be addressed through
policy a nd programme interventions. Much work has taken place and examples of initia tives
a nd an evaluation of their outcomes and relative successes a re described. The paper then
describes the significance of a dopting a n integrated approa ch to wa ter resources management
within a Caribbean context, the extent to which it may be influencing the development of the
enab ling regional a nd national environment, and the prospects for the more widespread
adoption of appropriate management instruments to underpin eq uitab le, efficient, and
susta inable pra ctices.
The geogra phic area of interest of this paper is confined to the 15 States in English-speaking
Caribbean.1 The choice of the Ca ribbea n region as the focus of interest of this paper is outlined,
a nd the region described. This a rea has some of the most vulnerab le sta tes and territories, in
terms of the fragility of the respective economies, the impact of climate change, and
constra ined development opportunities. While these factors, a long with the unifying effects of
the sha red language, a nd cultura l and politica l simila rities, ma ke this region a productive focus
for this eva luation, this in no way diminishes the importance of, or interest in, other parts of the
Caribbea n. Indeed Cuba , Dominican Republic, and Ha iti together account for the overwhelming
bulk of the region's popula tion – some 31 million people out of a tota l of 40 million. It does,
however, highlight the sometimes problematic concept of what constitutes the Caribbea n.
1 Anguilla, Antigua a nd Ba rbuda , Baha mas, Barbados , Belize, British Virgin Islands , Dominica, Grenada , Guyana , Jama ica,
Montserrat, Sa int Kitts and Nevis, S aint Lucia, Sa int Vincent and the Grenad ines, a nd Trinidad and Toba go.
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2 The Caribbea n
Figure 1. The Caribbean region
The waterscape of the Caribbea n is rich and diverse; it is home to some of the most water-
scarce nations on the pla net, such as Barbados and the Baha mas. Yet in close proximity there
a re countries with a bunda nt freshwater resources, such as Guyana a nd Belize.
The term 'Ca ribbea n region' provides a unifying idea, yet it has multiple uses and masks many
differences among the sovereign states , oversea s departments, a nd dependent territories that
exist within the region (see Table 1). Some of the former colonial powers still hold swa y.
Guad alupe, Ma rtinique, Saint Martin, a nd Sa int Barthélemy are pa rt of metropolitan France.
Puerto Rico and the US Virgin Islands a re unincorpora ted pa rts of the USA. The United
Kingdom's Overseas Territories consist of Anguilla, British Virgin Islands , Cayman Islands ,
Monts erra t, a nd Turks and Ca icos Isla nds . The Netherlands Antilles include Aruba , Curaça o, a ndSint Maa rten as autonomous countries and Bonaire, Sint Eustatius, and Saba a s municipalities
of the Netherlands. The rema inder of the countries beca me independent during the period of
decolonisa tion that las ted from the early 19th century, in the cas e of Ha iti, to the 1980s.
Geographica lly the Ca ribbean is diverse, a nd, given its different geologic histories, it displays a
marked variety of different landforms, from small inhabited islands with populations of a few
thousand people to la rge islands , such as Cuba , with populations in the millions. It ranges from
flat low-lying islands a few metres ab ove sea level, such as the Bahamas , to those with
mountains up to 3,000 metres in height. It includes , a ccording to some cla ssifications,
countries on the mainland of Centra l and South America – Belize, Guyana, and Suriname. The
va rious population mixes, la nguages, a nd cultures reflect the colonial and political histories of
the va rious sta tes and territories. In terms of politica l economy, regionalism and collective
coalitions have provided a means for the Caribbea n States to play an important role in
Source: Adapted from CIA World Factbook (https://www.cia.gov/library/publications/the-world-factbook/)
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Table 1. Isla nds of the Caribbean
French Departments
and Overseas
Territories
Guadaloupe
Martinique
Saint Barthélemy
Saint Martin
Netherlands
Antilles
Aruba
Bonaire
Curaçao
Saba
Sint Eustatius
Sint Maa rten
United Kingdom
Overseas Territories
Anguilla
British Virgin
Islands
Cayman Islands
Montserrat
Turks a nd Ca icos
Islands
Independent
nations
Antigua and
Barbuda
The Ba ha mas
Barbados
Cuba
Dominica
Grenada
Haiti
Jamaica
Saint Kitts and
Nevis
Sa int Lucia
Saint Vincent and
the Grenadines
Trinida d and
Toba go
United Sta tes
Puerto Rico
US Virgin
Islands
Central a nd
South American
countries
Belize
Guyana
Islands
Suriname
international politics that their individual sma ll size might otherwise have prevented. This is
facilita ted through a number of institutions, such a s the Caribbea n Community (CARICOM), the
Association of Caribbean Sta tes (ACS), the Organisa tion of Eas tern Caribbean Sta tes (OECS),
and others. Thus the term Caribbean region can b e interpreted in differing ways and a s a result
is often deliberately used loosely.
The GWP-C has partners from almost every country and territory in the Caribbean with the
exception of Belize, Bonaire, Cayman Islands , Curaçao, Sa ba , Sa int Barthélemy, Sint Eusta tius,
Sa int Martin, a nd Turks a nd Ca icos Islands . The majority of the pa rtners a re located in English-
spea king countries (GWP-C, 2014a) and mos t of the work of GWP-C is carried out in the English-
spea king Caribbean, with the exception of Suriname. Simila rly, many of the efforts to promote
IWRM by other organisa tions apart from GWP-C have taken place in the English-spea king
Ca ribbean. In the case of both US and French West Indies, given their politica l sta tus,
approaches to wa ter resources management are largely governed by sets of laws, policies, and
regula tions that a re, for the most part, exogenously determined. For the large Spanish-spea king
countries, s hared cultura l a ffilia tions, traditions, and language predispose them to identify moreclosely with La tin America.
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2.1 Climate
The Caribbea n is a humid tropical region in which the climate is dete rmined b y the Trade Winds
as well as the inter-tropical convergence, and it varies with both elevation and the size of the
land mass. Temperatures a re strongly eleva tion dependent. In coasta l areas they vary between
32OC and 24OC, but with increasing elevation tempera tures can d rop to 10OC. Tempera tures tend
to vary little throughout the yea r, particularly at sea level, so that for a significant part of the
year eva pora tion ra tes exceed precipitation. There a re two distinct sea sons during the yea r: a
dry sea son (Ja nuary to April) a nd a wet summer hurricane sea son. While hurricanes a re a feature
of the region, with tracks that pas s from south-eas t to north-west, the southern Caribbean ra rely
experiences their effects. Precipita tion varies grea tly, with the windward sides of the islands
receiving much more rain (sometimes up to 5,000 mm per year) tha n the rain-sha dowe d
leeward sides (sometimes less than 600 mm per year) (Cashman, 2013; FRD, 1988–1999). In
the southern Ca ribbean there can be a second mini dry sea son betwee n July and September.
Rain often occurs in short and heavy downpours.
2.2 Geography
A broad geogra phical grouping of the principal islands may be taken as : the Bahamas , the
Grea ter Antilles, the Leewa rd Island s, the Windward Islands, and the Southern Offshore Islands
(FRD, 1988–1999). The Ba hamas are a low-lying archipelago of cora l islands , being no more
than 60 metres above sea level. Wea thering of the cora lline deposits has resulted in ka rstic
formations, with many solution conduits. The result is that ra infa ll run-off infiltra tes q uickly so
that there are no freshwater rivers, but instead, lenses of freshwater that 'sit' on top of more
sa line waters.
The islands of the Grea ter Antilles a re geologically more complex, with sedimentary,
metamorphic, and igneous rocks, the weathering of which had been affected by tectonic
movements as well as other cha nges over geologic time. These islands are more mountainous
and with va ried topography. All have significant rivers and groundwater sources. The Less er
Antillean isla nds (Leewa rd a nd Windwa rd) are predominantly of volcanic a nd s edimenta ry origin
and are characterised by steep a nd sometimes mountainous terrain. They too have a n
ab unda nce of rivers and s treams, but no significant groundwater, except where these might be
a lluvial aquifers ass ociated with river systems. The rivers in genera l a re short in length, dra in
relatively small catchments, a nd thus have lower volumes of water that a re more susceptible to
sea sona l and climatic variations. This is particula rly true in those Grea ter Antillean isla ndswhich have karstic limestone formations which serve to modify surface wate r flow
characteristics.
The islands of the outer Less er Antilles, s uch as Antigua, Ba rbuda , and Barbad os, d o not fit this
pattern. These are coralline islands formed as a result of tectonic uplift at the edge of the
Caribbean plate. As such, they exhibit many of the same geological features as the Bahamas,
but with more pronounced topography and a lack of fresh surfa ce waters. The most significant
of the Southern Offshore Islands a re Trinidad and Toba go, which geologically a re pa rt of South
America . The mountain ra nges consist of metamorphic rocks, with the lower lying a reas formed
from erosional and sed imentary deposits. There a re rivers ass ociated with the mounta inous
areas, but a feature is that once they reach the lower areas they form wetland a reas, many ofwhich have been drained for development purposes . For completeness Belize, Guya na, a nd
Suriname are included, though they a re not part of the insula r Caribbean. All a re continental
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The Caribbean region is one of the most demogra phically diverse regions in the world.
Historica lly, popula tion growth in the region has largely been via migra tion, but has slowed
markedly since the mid-20th century. This Technical Pa per focuses specifically on the English-
spea king Caribb ea n (Ta ble 2).
2.3 Demographics
countries and all host major transboundary river systems as well as significant groundwater
resources.
Table 2. Demographics for Englis h-spea king Caribbea n countries
Total population (thousands)
343
273
312
104
754
9,993
2741
174
109
1,341
109
Population density (persons/km2)
25
636
14
304
4
360
249
323
282
261
314
Annual population grow th (%)
1.4
0.2
2.1
0.3
0.2
1.3
0.4
1.1
0.1
0.4
-0.1
Country
Bahamas
Barbados
Belize
Grenada
Guyana
Haiti
Jamaica
Sa int Lucia
Saint Vincent and the
Grenadines
Trinida d a nd Toba go
US Virgin Island s
Source: UNDESA Population Division (2013)
According to UN da ta , the Caribbea n population ha s more tha n doubled from 17 million in 1950
to 41 million in 2010, and popula tion density has increas ed by more than 100 percent during
the s ame period (UNDESA, 2013). However, a s a general rule, wa ter distribution infra structure
built in the 19th and early 20th century did not anticipate this growth. This has led to many cases
of water stress and s carcity, particula rly in Antigua a nd Barbuda , Barbados , a nd Saint Kitts and
Nevis (UNEP, 2008). Since a high proportion of the popula tion in many Ca ribbean S tate s a nd
territories live in urba n areas, the re is a two-fold challenge to delivering potab le water to
densely popula ted communities, while a ddressing the stormwater and wa stewa ter challenges
typical of urba n environments. All English-spea king Caribbean islands and territories show a
consistent trend o f migra tion from rura l to urban a reas (UNEP, 2008).
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Table 3. Urba n popula tion
Urba n popula tion (%)
100
30
47
84
44
41
100
75
67
69
39
98
Country
Haiti
Jamaica
Martinique
Montserrat
Netherlands Antilles
Puerto Rico
Saint Kitts and Nevis
Saint Lucia
Saint Vincent and the Grenadines
Trinida d a nd Tob ago
Turks and Caicos Islands
United Sta tes Virgin Isla nds
Urban population (%)
52
52
89
14
93
99
32
28
49
14
93
95
Country
Anguilla
Antigua a nd Ba rbuda
Aruba
The Ba ha mas
Barbados
British Virgin Islands
Cayman Islands
Cuba
Dominica
Dominican Republic
Grenada
Guadeloupe
Source: UNDESA Population Division (2013); 'Urban Population, Development and the Environment 2011'
2.4 Water resources and wa ter services
A feature of the water resources of the Caribbean is the diversity, from country to country, of the
organisa tional a rrangements which govern them. In Ja maica a nd Guyana , there is a ministry
dedicated to the oversight of water, but in most states, water management forms just one part
of a ministry portfolio, and ra rely enjoys a high degree of prominence. Furthermore,
responsibility for different as pects of water management is dispersed across more than one
ministry, which often results in wa ter q uality and environmenta l mana gement being sha red
between ministries of health and environment and governed sepa rately from water
management (Cashman, 2012; McIntosh a nd Leota ud, 2007).
In most states , wa ter resources management is a function performed by the water service
provider. Only in Ja maica , Sa int Lucia , and Trinida d and Toba go is the responsibility separa ted
from tha t of wa ter service de livery. Wa ter services, whether water supply or wastewa ter, a re
undertaken by government-owned a gencies, usually a government-owned company or statutory
authority, and it is only in a few cas es that there is more than one body responsible for water
services within a country. In Jamaica there is a Na tional Water Commiss ion and a Rura l Water
Supply company, but parish councils and a small number of independent water service
providers hold time-limited licences. In Belize, urba n areas a re supplied by the Belize Water
Services, while rural areas a re handled by the Department of Local Government and Rural
Development. In contras t, Guya na provides wa ter to both urba n and rura l a reas through Guyana
Water Inc., with the compa ny providing support to community-ba sed o rganisa tions (CBOs)
which provide s ervices in those a reas.
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Table 4. Water resources for the English-spea king Caribbea n islands
Land area (km²)
91
443
13,880
430
22,966
153
263
751
344
214,970
10,991
102
9,104
261
616
389
5,128
616
346
Total average
annual rainfall
(mm)
890
1,030
1,292
1,422
1,705
1,117
135
2,083
2,350
2,387
2,051
1,143
2,054
1,427
2,301
1,583
2,200
559
998
Total renewable
wa ter resources
(mm³/year)
Not given
52
20
80
16,000
Not stated
Not stated
Not stated
Not stated
241,000
9,404
Not stated
71
24
Not stated
Not stated
3,840
Not stated
Not stated
Country
Anguilla
Antigua and
Barbuda
The Ba ha mas
Barbados
Belize
British VirginIslands
Cayman Islands
Dominica
Grenada
Guyana
Jamaica
Montserrat
Puerto Rico
Saint Kitts and
Nevis
Sa int Lucia
Saint Vincent and
the Grenadines
Trinida d and
Toba go
Turks and Caicos
United Sta tes
Virgin Islands
Municipal wa ter
withdrawal
(mm³/year)
Not given
5.3
Not stated
19.8
10.0
Not stated
Not stated
Not stated
Not stated
61.3
274.9
Not stated
904.0
Not stated
9.8
Not stated
173.6
Not stated
Not stated
Tota l water
withdraw al per
capita
(m³/capita/year)
Not given
97.67
Not stated
371.30
Not stated
Not stated
Not stated
244.10
97.09
2,222.00
370.00
Not stated
264.00
Not stated
98.22
Not stated
177.90
Not stated
Not stated
Total renewable
water per capita
(m³/capita/year)
571.40
57.00
291.00
51,779.00
Not stated
Not stated
Not stated
Not stated
317,942.00
3,406.00
Not stated
1,897.00
444.00
Not stated
Not stated
2,842.00
Not stated
Not stated
Source: CIA World Factbook (https://www.cia.gov/library/publications/the-world-factbook/); FAO Aquastat database
(http://www.fao.org/nr/water/aquastat/main/index.stm)
Responsibility for ta riffs and economic regula tion is ra rely exercised independently of
ministeria l/cab inet control, with possibly five exceptions – Belize, Guyana, Ja maica, Sa int Lucia ,
and Trinidad a nd Toba go. In each cas e there is a d egree of independent oversight andevaluation of tariff ad justments, a lthough the responsible minister does have the final sa y when
it comes to approving a ny ta riff adjustments. With respect to environmenta l regula tion, each
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Table 5. Water ma nag ement responsibilities
Activity
Climatic da ta gathering
Wa ter reso urces monitoring and e valua tion
Wa ter resource q uality monitoring
Abstraction a nd withdrawa l licences
Wa ter production a nd consumption d a ta
Drinking wa ter qua lity monitoring
Discharge licences and environmental regulation
Economic regulat ion
Service regula tion
Principal responsible agency
Meteorological service
Water s ervice provider
Ministry of Environment
Water s ervice provider
Water s ervice provider
Ministry of Health
Ministry of Environment
Minister with responsibility for wa ter
Unclear
country has an established system of oversight of potable water qua lity, usually overseen by the
Ministry of Hea lth, which also ha ndles pollution control. However, in all cas es the existing Water
Acts do vest some responsibility for pollution control, which is seldom if a t a ll exercised , in the
utilities. These remain government functions, a nd, a s a result, the a ctivities of other government
a gencies a re not rigorously held to a ccount. Fa ilures are also evident in the oversight ofdischarge a nd effluent standa rds in the private s ector, though this is primarily because of low
pena lties a nd enforcement rather than a lack of legislation. The use of management instruments
in water ma nagement are limited to the use of volumetric charges and block tariffs for
increas ing levels of consumption, differentia ted water ra tes between domestic and commercia l
users, a nd irrigato rs. Abs traction licences a re req uired, a s a re discha rge permits. These are
relia nt on the use of command a nd control approaches rather than economic incentives.
However, practices a round monitoring, reporting, and enforcement of permit conditions a re
loose and reflect the d ifficulties experienced in enforcement.
The genera l situation with respect to the management of wa ter, including the collection of da ta
a nd regula tion within the wa ter sector, is summarised in Table 5 below. The exceptions to thisgenera lisa tion are noted a bove.
2.5 Politics of water management
The varied history of Europea n colonisa tion in the Caribbea n gave rise to differing lega l
a rrangements with respect to water management. The growth of urba n centres and the diffusion
of ideas ab out providing water services in the middle to late 19 th century influenced the
institutional and legal a rrangements governing those s ervices. The predominant a rrangement
was for island a dministrations to provide water services as a municipal or government
responsibility. Such arrangements survived well into the pos t-colonial period (Cashma n, 2012).
In Barbados, which became independent in 1966, it was not until 1980 that the Barbados WaterAuthority took over from the Waterworks Department. This is not untypica l for the region. In
Jamaica the Na tional Water Commiss ion, responsible for water service provision, a lso ca me into
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being in 1980. Little distinction was made b etween responsibilities for wa ter services and wa ter
resources management as these were centra lised within the same organisa tion, aga in reflecting
a predominant supply-side paradigm tha t conceived of water resources narrowly as an integra l
extension of water supply services (Cas hman, 2012). One of the features of this dispensation
was the relatively high ra tio of semi-skilled and skilled to professional sta ff, which has tendedto privilege the da y-to-da y operation a nd ma intenance a ctivities. This provided governments
with the means to provide employment opportunities. However, this focus on opera tion a nd
maintenance has resulted in a relative deficiency of resources in the professional cadre, whose
role is to develop the planned, strategic a ctions req uired to ensure the long-term susta inable
management of the services and resources.
The centra lising tendency within wa ter sector ma nagement was underpinned by the politica l
dispensa tions that came into being after independence. These sought to address a legacy of
neglect and marginalisa tion of large sections of the population on the grounds of colour and
race. Part of the measures implemented were progra mmes to greatly expand provision and
access to ba sic services, such as health care, education, and wa ter a nd sanitation. A strongsocial welfa re sta nce characterised governments throughout the region, in which the state
as sumed an important role in the economy and a cted as a provider or guara ntor of essential
services, water being the prime exa mple of this (Portes et al., 1997). Evidence of this can be
seen in the development of varying forms of social partnerships between government, trad e
unions, a nd the priva te sector that sought to improve the conditions of the workforce and
provide a way to mitigate fluctua tions in the economy, particula rly economic downturns,
through a collective shouldering of the burden by ea ch actor (Springer, 2010).
Consequently, the public have come to expect that governments will provide services by
guaranteeing financial support to ensure tha t services a re afforda ble. Almost inevitably, wa ter
services have become politicised (Ba tley, 2004). For example, with the possible exceptions of
Jamaica a nd Saint Lucia, a ny changes in water tariffs have to be approved by the responsible
minister. Hence, it is political rather tha n financia l considera tions that play a significant role in
any decision about price rises. Many wate r service providers were constituted as government
agencies a nd, as such, are governed by boa rds. The boards a re appointed by ministers and a re
req uired to resign at a change of government. In effect, therefore, members of the boa rd a re
politica l appointees whose positions depend on their a cceptability to the incoming regime.
Such a system of governance provides parties with opportunities to forward their particula r
interests a nd ga in fa vour with their electora tes. As one politica l commentator obs erved, " The
Caribbean's politica l culture [is] ba sed on a uthorita rian governance" (Hinds, 2001). It is
characterised by a tendency to centra lise executive power and decision-making within a cab inet
ra ther than in parliament.
This is not to say that the role of politics or of politicians is a bad thing. On the contrary, they
play a necessa ry and vital part in giving leadership, shaping policies, a nd ensuring that a
ba lance is achieved betwe en s ocial, environmental, a nd economic concerns. Through their
accountab ility to their electora te, politicians can ensure that public concerns and sensitivities
a re brought into the boa rdroom of wa ter service providers, which in turn provide a necess a ry
counterba lance to an otherwise technocra tic approa ch.
In terms of governance of the water sector, a distinction ca n be made between the regional level
a nd the national one. There a re a number of dispa rate international bodies that have an interest
in the regional wa ter secto r. They include the Ca ribbea n Development Bank, Inter-American
Development Ba nk (IDB), Europea n Commiss ion, Food a nd Agriculture Orga nization o f the UN
(FAO), US Agency for Internationa l Development and o thers. The ma jority a re primarily funding
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2 THE CARIBBEAN
bodies operating on a bilateral bas is and generally have had little specific interest in
institutional reform or policy matters, though this may be changing. The exceptions to this a re
UNDP a nd the UN Environment Programme-Caribb ea n Environment Programme (UNEP-CEP),
although the la tter is not a 'donor agency', but acts to support sustainable development. While
FAO opera tes on a bila tera l ba sis UNEP-CEP does have a more regionally focused involvement inwa ter governance through its programmes ass ociated with promoting the Cartagena Convention.
The Convention relates to water governance because it is a regiona l mechanism to as sist in the
ad option of laws and regulations to add ress pollution of the marine environment from land-
ba sed activities, such as wastewa ter discharges. Although this is a regional umbrella
mechanism, implementation occurs a t the na tional levels.
Regional level governance of the wa ter sector is loose a nd periphera l. The key regional
institution, CARICOM, has not been ab le to develop any overa rching influence, though wa ter
matters a re subs umed in the Susta inable Development Directora te. The initiat ive in 2008 to
form the Consortium of CARICOM Institutions on Water, whos e te rms of reference were a pproved
in 2010, had s ought to develop a common wa ter fra mework for the community for wa terresources mana gement (CARICOM, 2011). However, failure to provide the necess a ry resources
has meant that it has had little if any impact on the region. Somewhat more successfully, other
regional institutions have played a direct role in s upporting initiatives at the national level.
These ha ve come a bout either through regional projects that include a portfolio of national-level
interventions or through their involvement in na tional and local projects. Examples include the
other CARICOM institutions such a s the Caribbean Environmenta l Hea lth Inst itute (CEHI), the
Caribbea n Institute for Meteorology a nd Hydrology (CIMH), and the Ca ribbea n Agricultura l
Resea rch and Development Institute (CARDI), as well a s thos e outside of CARICOM, such as
GWP-C, the Caribbean Wa ter a nd Wastewa ter Ass ocia tion (CWWA), and Caribb ea n Water and
Sewera ge Associa tion Inc. (CAWASA).
Regional bodies tend to focus their a ttention on opera tiona l level activities, working within the
current set of governance a rra ngements. This is characterised a s strengthening existing
capa cities, both human resources and opera tiona l infra structure, with a view to strengthening
their efficiency and effectiveness. Occasionally the focus has been on re-ordering the national-
level institutional framework, a nd this was linked to financing infras tructure projects with a
req uirement for structura l adjustment of the governance a rra ngements.
At the nationa l level, water governance is rooted in a sta te-bas ed model of management, with
the majority of the sa lient sta keholders being located within the public sectors. Caribbea n
actors outside the public sector, such as the priva te sector, customers, non-governmenta l
organisa tions (NGOs), a nd community-ba sed organisa tions (CBOs), seldom a chieve the level of
influence tha t can be witnessed in other parts of the world. Furthermore, a feature of this
general arrangement is a lack of a s ystem of checks and ba lances which would allow a degree
of accountability on the part of those responsible for the mana gement a nd provision of water
services. The system of wa ter governance, which has evolved s ince the mid-20th century, has
proved itself to be resilient to change , exhibiting not so much inertia but ra ther 'lock-in' (Neff,
2013). With the exception of Ja maica , Sa int Lucia, a nd Trinida d a nd Toba go there has been little
funda mental reform of the na tiona l institutional frameworks governing wa ter. In Trinida d a nd
Toba go, a process of change is presently being undertaken by the utility sector, with the
intention of separa ting the service function from resource management. However, there a re
various emerging policy cha llenges that demand a number of reforms which ha ve the potential
to change the current sta te of affairs. One of the more important is the cross-cutting issue of
land use a nd land use change, which contributes to land d egrada tion, pollution from
developments and activities, dema nd for services, a nd increas ed levels of flood risk.
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3 Policy challenges
The clear implica tion of Article 26 of the Plan of Implementa tion of the World Summit for
Susta ina ble Development in 2002 wa s that IWRM, b ased on the four Dublin Principles, wa s
seen a t the internationa l level as the framework within which countries should seek to organise
a nd mana ge their water sectors. Part of the appeal is that IWRM stresses cross-sector
integration not only as a support to development, but as a process and framework that is
sensitive to country-specific geographic, historica l, cultura l, social, and economic conditions.
The impetus to embark on a process of integra tion is rooted in a recognition that existing wa ter
governance arra ngements within countries a re weak and not capable of ad dressing the water
challenges that they a re facing. These challenges include water scarcity, deteriora ting water
q uality, the impact of extreme events, a nd the provision and maintenance of wate r services
(Cashma n, 2012; UNEP, 2012b ). Critica l issues identified include s upply-driven mana gement,
fragmented a nd subsector approaches to wa ter management, lack of information, ina dequa te
technical competencies, and low levels of inves tment in the water sector (GEF-IWCAM, 2008;
UNEP-DHI, 2007). The conseq uences a re tha t poor ma nagement is impeding economic and
social development and that these deficiencies are most a cute in developing countries which
can least a fford them (Cas hman et al., 2010).
The converse is that good wa ter sector mana gement makes an important contribution to the
goa ls of poverty reduction, improved public health, and environmenta l susta ina bility. It
provides infra structure tha t underpins economic development (WHO, 2004). The implication is
that IWRM is a political process in which societal, developmental, a nd ideological factors have
to be reconciled, a nd one that will involve the resolution of conflicts of interests at many
different levels. Implementation builds on three pilla rs: an enabling environment of a ppropriate
policies, s trategies, a nd legislation; an institutiona l fra mework that a llows the enabling
environment to be opera tionalised; a nd the esta blishment of management instruments that
a llow institutions to do their job.
3.1 Cha llenges for IWRM
Figure 2. The t hree pilla rs of IWRM
Source: GWP (http://www.gwp.org/The-Challenge/What-is-IWRM/IWRM-pillars/)
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Although countries signa lled their intentions to develop IWRM plans through the 2002 JPoI, in
many cases , actually turning intentions into actions required a n a dditional set of dynamics,
which might broad ly be characterised as the realisa tion that the cost of not doing something is
greater than the cost of taking action. In this context, cost is understood to mean more than just
a financia l cost; it includes social, environmental, and political costs as well. The exa ct nature ofsome of those driving forces in the Caribbea n context is ad dressed in subsequent sections.
3.2 Challenges for wa ter security
The long-term availa bility of freshwater has been of concern in the region for at leas t the last 30
years (CEHI, 2002). Given increas ing levels of demand a nd expected changes in ra infall patterns
brought on by climate change, even a s light reduction in ra infa ll would have serious
conseq uences (IPCC, 2007; UNEP, 2003). There is a lread y a gap betwee n the a bility to s upply
and the level of demand in ma ny Caribbea n countries. Ba rba dos is using close to 100 percent of
its a va ilab le water resources, Saint Lucia has a 35 percent water supply deficit, Nevis 40percent, and Trinidad and Toba go ha s had a deficit since 2000 (WASA, 2005). Jama ica is
projected to experience deficits in a reas of important economic activity by 2015 (GoJ, 2011),
Antigua a nd Barbuda is reliant on desa lination to meet demand s, while in Dominica, Grenad a ,
and Sa int Vincent and the Grenadines demand can exceed supply during the dry sea son as a
result of reduced s tream flows (USACE, 2004). The s itua tion is compounded by high levels of
unaccounted for wate r (for exa mple, 67 percent in Jamaica , 40 percent in Trinida d a nd Toba go,
and 50 percent in Ba rba dos). The paradox is that many of these countries have sufficient water
resources to meet demand, but do not have the infras tructure or institutional frameworks to
close the supply–demand ga p. It is only in some of the drier islands, s uch as Antigua a nd
Barbuda , Barbados , and the Baha mas, that the water resources can be considered scarce.
The region as a whole has made significant progress in water supply a nd most countries report
over 95 percent access to improved water supplies. Problems are primarily as sociated with the
q uality of service, maintenance a nd opera tion of existing infra structure, ageing infra structure,
and high levels of unaccounted for water, together with concerns over potab le water q uality. This
suggests difficulties with the ma nagement of water services and with securing the necessa ry
levels of investment to a ddress the supply–demand gap.
The a va ilab ility and security of water is another challenge for the effective management of water
resources. An increas ing threa t to streamflows is the conversion of catchments for development
and a griculture. The urba nisa tion of the upper wa tershed a reas a round Port of Spa in, Trinidad
and Castries, a nd Sa int Lucia has resulted in higher peak flows, d ownstream flooding, an overa lldecrease in base streamflows (Edwa rds , 2011; Williams, 2010), a nd higher sediment loads . The
conseq uences are most keenly felt during the dry sea son and often lead to s ignificant reduction
in water availab ility. In Dominica, this may be as much as 50 percent. Many catchments a nd
watersheds used for water supply are essentially without gauges, and ra infall measurements are
sparse.
Groundwater aq uifer yields are threatened by prolonged periods of low rainfall and abs traction
levels that exceed the sustainab le long-term aq uifer recharge. This is especially the case for
coasta l aq uifers where a bstractions have resulted in 'up-coning' a nd increased levels of sa linity
as the fresh– sa line water interface has migra ted inland. In Saint Kitts and Nevis, s uch concerns
provided the ca ta lyst for government action and intervention in the Bass eterre a q uifer. Highconcentra tions of nitra tes obs erved in a bstractions from the Liguanea a quifer in Kingston and
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St Andrew, Jamaica a nd the Belle a rea , Barbados have been attributed to inappropriate sewa ge
disposa l in urba n areas (Manda l a nd Ha iduk, 2011). Such contamination of groundwater makes
it unusa ble unless expensive treatment is provided. A major challenge facing wa ter resources
managers is the difficulty of determining sa fe yields and undertaking assess ments of the yield-
demand b a lance. Often, the req uired da ta, the models, and the s killed personnel a re a ll inshort supply.
One of the reasons for this state of affairs is that responsibility for water resources management
is vested in the water service provider. Only in Ja maica a nd Sa int Lucia , a nd to some extent in
Trinida d a nd Toba go, has it been constituted a s a sepa ra te mana ging body. Another reas on is
the la ck of formal mechanisms for cross -sector collaboration, which would a llow water, land,
and development issues to be coordina ted.
Overa ll wa ter security is an emerging challenge which the present institutional frameworks and
enabling environments a re increas ingly ill-eq uipped to dea l with. In particula r, a ccess to a nd
investment in accepta ble sa nita tion is limited in lower income communities (WHO/UNICEF,2013). Those in coasta l areas underlain by high wa ter tables have issues opera ting on-site
septic systems and hence there is an increased risk of contamina tion of local areas. This
becomes particula rly acute a nd a public health threat during s evere flood events.
3.3 The Carta gena Convention
The Cartagena Convention is a protocol concerning pollution of the Caribbea n Sea from land-
ba sed sources a nd a ctivities (LBS Protocol). This Protocol came into force in 2010 with the
objective of protecting the na tura l resources of the Caribbean Sea (fish stocks, cora l reefs, fra gile
ecosystems, and recrea tiona l wa ters) from ha rm a rising out of activities taking pla ce on la nd.
These a ctivities include pollution from the disposa l of domestic sewa ge, oil refineries, chemica l
industries , mining, and a gro-industries . However, the bigges t threats identified were from
domestic sewa ge and run-off from la nd as a diffuse source of pollution. The objective of the
Protocol is to dea l with the sources of pollution through the use of a ppropriate technologies
and by setting pollution standa rds and water quality objectives. By 2020 all existing domestic
wastewa ter systems (other than community wastewa ter systems) must comply with the
provisions of the Protocol, a nd a ll community systems other than individual household
systems must comply by 2030.
In order to achieve this, a ll countries of the wider Caribbean region will have to es tab lish the
appropriate policies, legislation, a nd regula tions to support the implementation of the Protocol,
create the necessa ry institutional fra mework and capacities, and make a vailable the finances to
put in place the s ewerage infra structure. The Protocol provides a legal framework for regional
coopera tion to achieve the objectives of the agreement, esta blishing regional effluent limita tions
for domestic sewage and manda ting specific pla ns to address agricultura l non-point sources of
pollution. It a lso provides for the future inclusion of other priority sources of pollution and
activities.
The provision of centra lised wa stewa ter services throughout the Caribbean fa lls to the water
service providers a nd, as such, the requirements of the LBS Protocol will have a major impact on
them up to and b eyond 2020. The numbers of people with a ccess to improved sa nita tion in the
Caribbean exceeds 90 percent, in most cas es. However, the numbers with access to centra lised
was tewa ter service systems which collect and treat was tewa ter a re low, ra nging from 3 percent
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3 POLICYCHALLENGES
in Sa int Vincent to 30 percent in Trinidad and Toba go. In a s itua tiona l analysis, was tewa ter
treatment was considered a low priority by water utility managers a nd sta keholders. Countries
were shown to be failing to take an integrate d a pproa ch to wastewa ter management and there
was inadeq uate provision for infra structure investment, policy reform, and public educa tion. All
these elements present challenges to water managers. But they are also directly relevant to thedevelopment of IWRM strategies and plans a t the national level.
3.4 Challenges related t o climate change
Ca ribbean isla nds a re especia lly vulnerable to the effects of climate change (IPCC, 2007) and as a
result a re likely to experience increas ed wate r stress . The Caribbea n may experience s ea level rise,
temperature rise (2.5 to 3OC rise for the northern a nd s outhern Caribbean a nd 2 to 2.5OC for the
eas tern Ca ribbean from 2075 to 2099), a nd changes in ra infall patterns. An increas e in the
number of days and nights with very high temperatures (in excess of 35
O
C during the day and 25
O
Cat night) is expected. Such changes will have a significant impact on soil moisture and
evapotranspiration.
Rainfall is generally expected to decrease by between 25 and 50 percent by 2080 (Ca mpbell et a l.,
2010), b ut in the Baha mas and Cuba increases are projected. The s easona l rainfa ll distribution
shows significant decreases in the wet sea son a cross the region (UN ECLAC, 2010). The northern
Ca ribbean will experience more intense ra infall a nd fewer ra iny da ys, while the s outhern pa rt will
experience the opposite effect (Campbell et a l., 2010). The reduced we t sea son rainfa ll, es pecia lly
when coupled with the projected higher temperatures, is problema tic, and the likely outcome is
significantly reduced water availab ility.
A bas ic interpretation of the climate change projections suggests that surface water flows will be
reduced a nd, potentia lly, wa ter qua lity will be a ffected, a nd less water will be a vailable for
recharge. But these potentia l impacts req uire much more investiga tion. With water a vailability
already a challenge, the prospect of further reductions in water availa bility because of climate
change only increas es the need for improved management of water resources a nd mechanisms to
ensure that scarce resources are a llocated a nd used in the most efficient and effective manner.
Current institutional a rrangements a re struggling to cope with the existing situation, so they a re
not as fit for purpose as would be desired. The impact of recent extreme events, such as
Hurricanes Tomas (UN ECLAC, 2011) and the regional drought of 2009 to 2010 (Fa rrell et a l.,
2010), ha ve highlighted the vulnerability of the current infras tructure a nd the cha llenges to des ign
standa rds and codes of pra ctice in providing robust a nd resilient infras tructure that can cope with
such events.
3.5 The challenges for regional approaches
The ma in challenge for regiona l approa ches is diversity. The English-spea king Caribbea n is
home to some 5 million people, spread a cross 15 island s tates and territories. Popula tions
range from a few thousa nd to over 3 million in Jamaica . Land a rea s range from 11,000 km2 to
under 10 km2. Such diversity, a long with the composition and size of the economies and the
press ure on limited human a nd financial resources, presents challenges in underta king
ad equa te management of water resources a nd services. Politicians have long recognised this,and one o f the main reasons for forming CARICOM was to ena ble the region to engage with the
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globa l community on a more equa l footing. Regional approaches to water resources management
suggest that the focus should be placed on developing common frameworks and s tanda rds.
Given the development of strong national identities since independence there would be
difficulties in developing mutually acceptable funding arrangements, especially if coopera tion
req uired more than the development of common fra meworks. Sha ring jurisdictions has beenproblematic in the pas t, and there is no tra dition of formal government-level coopera tion in the
wa ter sector.
There a re, however, precedents in the electricity sector, notably in the Organisa tion of Eas tern
Caribbean States (Grenad a , Sa int Vincent and the Grenad ines, Sa int Lucia , Dominica , Antigua,
a nd Ba rbuda , a nd Sa int Kitts a nd Nevis). Nevertheless, the difficulties in securing s ufficient
expertise and the financial cost of providing the orga nisa tional infras tructure a t the national
level a re being increas ingly recognised. This has led some opinion formers to seriously propose
a greater level of regional cooperation between governments on water matters (Fa rrell et a l.,
2007). This change in thinking is being reflected in the level of informal coopera tion between
practitioners, as well as that by NGOs involved in the wa ter sector.
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4 Policy developments
4.1 Regional and sub-regional IWRM developments
A number of policy initia tives which support IWRM have taken place over the pas t six years a t
regional and national levels.
In 2008 a CARICOM resolution to institute a consortium of wa ter institutions was meant to lead
to the development of a Common Water Fra mework for the Community to a ssist member states
with developing and implementing their IWRM plans. It was only in 2010 that the terms of
reference of the cons ortium, which included representa tion from regiona l non-CARICOM
institutional partners, were a pproved. The immediate a ims were to develop a consolida ted work
programme and to s et up a clea ring house and libra ry of wate r resource projects and a s kills
da taba se. In the longer term the consortium was to facilitate the as sess ment of national waterresources, identify priority issues, building up capa city, a nd updating water legisla tion as a
means of moving forward with the development of a common wate r framework. However, the
la ck of a ny available funds and the voluntary nature of the consortium have severely hampered
its ability to address any of the objectives set out in the terms of reference. In 2014 this may
change as GWP-C (one of the regional non-CARICOM institutiona l partners of the consortium)
has committed to provide a t leas t one year's funding for a person to work for the consortium.
Further funding for the consortium's activities may be forthcoming a s part of other regional
initiatives under development by CARICOM consortium partners.
The GEF-IWCAM project , up to its completion in 2011, provided support in developing na tiona l
IWRM plans and a lso reviewed policy, legislat ion, and institutional structures in the pa rtici-pa ting countries (GEF-IWCAM, 2014). The outcome wa s the pub licat ion of a Toolkit fo r
institut iona l, po licy, a nd legisla tive improvements in support o f the GEF-IWCAM project
approa ch in Ca ribbea n SIDS , which provided a platform to a id IWRM implementa tion a nd
specifica lly the LBS Protocol of the Cartagena Convention. The Toolkit was designed for
technocra ts, policy-makers, planners, developers, a nd legisla tors and provided model examples
and la ws , including legisla tive drafting guide lines for the GEF-IWCAM project. In add ition,
national and sub-national IWRM roa d maps were prepared in Antigua a nd Barbuda , Ba rba dos ,
Grenad a , Sa int Lucia , and Union Island in Saint Vincent a nd the Grenad ines. Dra ft policy
sta tements were developed in Antigua a nd Barbuda a nd Dominica, a nd support to dialogue
and issue papers in Cuba , Jamaica, Sa int Kitts and Nevis, a nd Trinidad .