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Building ‘learning catchments’ for integrated catchment
managing: designing learning systems based on
experiences in the UK and South Africa
Kevin Collins, John Colvin and Ray Ison
ABSTRACT
Kevin Collins
Ray Ison
Open Systems Research Group,
Communication and Systems Department,
Faculty of Maths,
Computing and Technology,
Open University,
Walton Hall,
Milton Keynes MK7 6AA,
UK
E-mail: [email protected];
John Colvin
Strategy Unit, Research and Enterprise Office,
Open University,
Milton Keynes MK7 6AA,
UK
E-mail: [email protected]
We examine challenges and opportunities for developing ‘learning systems’ for integrated
catchment managing (ICMg) drawing on our experiences in two contexts: UK and South Africa
(SA). Our research question is: what is it that we would have to experience to claim that a
catchment was a learning catchment? We suggest that any valid answer to this question will
arise in social relations in context-determined ways. From this perspective ICMg is an emergent
‘performance’ of stakeholders engaged in mutual action, or social learning (SL), in which
understandings and practices are transformed in situation improving ways. These questions are
relevant given recent reviews suggesting that implementation of the European Water Framework
Directive (WFD) is not nurturing adaptive management. Our European and SA experiences
demonstrate that it is possible to invest in social learning as a governance mechanism for water
managing, but key constraints exist. Our SA work based on (i) appreciating the situation,
especially the history, and (ii) contextual appreciation and design of learning systems (as a result
of (i)) is described in response to these constraints. We conclude that more attention on
developing an effective praxis for ICMg is required.
Key words | capability building, emergence, integrated catchment managing, learning system,
social learning
INTRODUCTION
In this paper we examine challenges and opportunities for
developing learning systems for integrated catchment
managing (ICMg) based on experiences in two different
contexts: the UK and South Africa (SA). A starting point for
our research is the question: what is it that we would have
to experience to claim that a catchment was a learning
catchment? We will argue that any valid answer to this
question will arise in social relations in context-determined
ways and that the same rationale applies if the question
posed is: what it is that we would have to experience if we
were to claim we had experienced ICMg? From this
perspective ICMg is an emergent ‘performance’ of stake-
holders engaged in mutual action, or social learning, in
which understandings and practices are transformed
in situation improving ways. This is distinct from notions
of integrated catchment management (ICM) with the
implicit assumption that there are a set of known practices,
knowledges and skills that can be learned and transferred to
address catchment issues in different contexts.
The research questions we identify are relevant given
recent reviews suggesting the European Water Framework
Directive (WFD) (CEC 2000) is ‘far from nurturing a more
adaptive management approach as a way to tackle
uncertainty and change, and as a way to enhance the
resilience of freshwater systems’ (Galaz 2005, p. 9). The EU’s
own review of institutional arrangements for implementing
the WFD concluded that ‘although most of the adminis-
trative arrangements appear capable of ensuring proper
doi: 10.2166/wst.2009.889
687 Q IWA Publishing 2009 Water Science & Technology—WST | 59.4 | 2009
implementation, actual performance will only become
evident in practice over the coming years’ (CEC 2007, p. 6).
Based on European, South African, and also informed
by our Australian study, we argue that ‘administrative
arrangements’ though necessary are not sufficient to
create the conditions for ICMg. A major deficiency in
WFD implementation appears to be that of capacity and
capability building for ICMg i.e. a weakness of praxis,
or theory informed action. Our recent work exemplifies an
alternative approach based on ‘learning system’ design and
capability development. In this paper we draw primarily
on work in progress in the UK and SA which is enacting
praxis based on designs informed by earlier research
(SLIM 2004a; Collins et al. 2005; Blackmore et al. 2007;
Colvin et al. 2008).
METHODS
Our research is built upon certain theoretical understand-
ings which are not yet widely appreciated within the
‘natural and engineering sciences’. This has major
mplications for research design and methods. The first
departure point concerns how knowledge is constructed
(i.e. epistemology). In Figure 1 the area (a) on the left side of
the diagram describes what has been the historical and
dominant understanding of how knowledge is understood
and how this gives rise to particular governance mechan-
isms in environmental and natural resource management
(e.g. regulation). Figure 1 contrasts the traditional
approach, based on a fixed form of knowledge, with that
of ‘social learning’ depicted in area (b). Social learning,
understood as concerted action among stakeholders in
complex and uncertain situations (such as water catch-
ments), is based on the process of socially constructing
an issue i.e. knowledge construction by actors or stake-
holders in which their understandings and practices change
so as to transform the situation of concern (Figure 2a).
The theoretical and empirical evidence for this work can be
found in a recent special issue of Environmental Science
and Policy (Blackmore et al. 2007) based on SLIM (2004a).
Within a social learning paradigm a priority in research
practice is to know how to create the circumstances for
social learning to occur. This can be described as ‘design’
research where design is concerned with a process, rather
than with a blueprint or model, and where the output can be
conceptualised as a learning system (see Ison et al. 2007b).
As outlined by Ison et al. (2007b) the design of a learning
system might seemingly involve combining elements and
processes in some interconnected way as well as specifying
some boundary conditions—what is in, what is out—for the
purpose of learning. But this is a first-order perspective
resulting in the specification of learning outcomes in
the absence of any real contextual understanding about
learners. Blackmore (2005), reviewing claims that appreci-
ative systems (sensu3 e.g. Vickers 1983) are learning
systems, suggests something more organic and observer
dependent. This perspective invites inquiry in terms of: ‘let
us consider this situation as if it were a learning system’, or,
in Vickers’ terms: ‘I have found it useful to think of my life’s
work in terms of appreciative systems’. With this shift,
a ‘learning system’ changes from some-thing having a clear
ontological status (e.g. this specification, this course) to
becoming an epistemic device, a way of knowing and doing.
Reflecting this turn, Ison & Russell (2000) suggest it is a
first-order logic that makes it possible to speak about, and
act purposefully to design or model a ‘learning system’.
In contrast, a second-order logic appreciates the limitations
of the first-order position and leads to the claim that
a ‘learning system’ exists when it has been experienced
through participation in the activities in which the thinking
and techniques of the design or model are enacted
and embodied. An implication of this logic is that a
Figure 1 | Policy coordination mechanisms compared: (a) the current paradigm
of environmental management comprising hierarchy and the market used
to address pre-determined environmental problems based on a fixed form
of knowledge; and (b) social learning for concerted action based on the
process of knowing (Source: Ison et al. 2007a).
688 K. Collins et al. | Learning systems in integrated catchment management Water Science & Technology—WST | 59.4 | 2009
‘learning system’ can only ever be said to exist after
its enactment—that is on reflection. The second-order pers-
pective is not a negation of the first—they can be understood
as a duality (comprising a whole).
The research reported here is based on two research
settings: (i) two years of co-research with scientists
concerned with ‘integrated catchment science’ in England
& Wales (Collins & Ison 2007); and (ii) two years of activity,
which is ongoing, in SA where the design to date has
focused on three distinct stages, described below (Colvin
et al. 2008). The findings are also informed by a desk study
of the complexity of institutional arrangements for catch-
ment managing in Australia (Godden & Ison 2007). Because
our research is as much about methodology as situation, we
discuss what was done, and why in the two research
settings, in the next section.
RESULTS AND DISCUSSION
Doing integrated catchment science: UK
Within the EA (Environment Agency, the main environ-
mental regulatory body for England & Wales), the WFD
has increasingly come to dominate the water and land
management science agenda and is a principal driver in
efforts for more integrated approaches. We have spent
two years in a co-researching process designed to create
the circumstances for a community of practice (CoP;
Wenger 1998) in Integrated Catchment Science (ICS)
to emerge. A particular feature of this work has been the
use of systems thinking to promote and inform the work of
the CoP in determining the EA’s ICS strategy. We did this
because we found the evolving practice of the ICS CoP to be
constrained by the lack of a common conceptual framing of
integrated catchment management (ICM) within the CoP,
the EA and beyond at national and international levels. Our
approach (learning system design) involved a series
of workshops in 2006 and 2007 using systems approaches
(see Checkland & Scholes 1999; Ison 2008) to help develop
the conceptual thinking about the nature of ICS. Rather
than attempting to define and pre-determine the direction
and outcomes of the work, our methodological approach
was rooted in trusting the systemic notion of emergence.
Through the use of systems diagramming techniques
(see Open University 2002), three closely related insights
emerged: i) ICS as an organising notion is meaningless
without reference to an agreed purpose in context;
ii) purpose can be determined by reference to policy; and
iii) integration of catchment sciences is possible at the level
of policy objectives rather than at the level of scientific
disciplines and research findings.
The emergent learning about the nature of ICS through
systemic diagramming techniques represents a significant
Figure 2 | (a) Situations of complexity, uncertainty, and conflict associated with water management are transformed through concerted action by stakeholders, who build their
stakeholding in the process. This leads to changed understandings, i.e., knowledge in action, and practices. (b) In the SLIM (Social Learning for the Integrated Management
and sustainable use of water) research, we have been concerned in particular with how six variables interact and are mediated by learning processes to shape issues and
transform particular situations. These variables include history, stakeholding, facilitation, institutions and policies, and ecological constraints (Source: SLIM 2004a; Ison &
Watson 2007).
689 K. Collins et al. | Learning systems in integrated catchment management Water Science & Technology—WST | 59.4 | 2009
development in the thinking of the CoP about its own work.
The approach developed by the CoP and the commitment
to trusting emergence runs counter to the experiences
of most management protocols and is not without problems
within organisational settings (Collins & Ison 2007). What
is clear, however, is that ICM can never be a blueprint
independent of context and some of the ‘variables’ depicted
in Figure 2a. Our experience also suggests that it is futile to
imagine that scientific findings can define what ICM is;
we suggest instead that scientific explanations, and thus
scientists, have much to contribute to developing a praxis
for ICMg, seen as a process of managing for emergence.
We further claim that we are still a long way from
experiencing the interplay between human activity and
biophysical processes that would lead us to describe
catchments as learning catchments.
Building capacity for co-operative governance: South
Africa
A major deficiency in implementation of ICM-like policies
in Europe (the WFD), SA and Australia appears to be that
of capacity and capability building for ICMg (SLIM 2004b).
This is an issue that our research is addressing. Stimulated
by experiences of working on capacity building issues in the
England and Wales context—particularly the shared EA-OU
experience of working with both institutional opportunities
and barriers—our work in SA takes a novel approach to
‘learning system’ design and capability development. The
approach involves:
(i) appreciating the situation, especially the history
(see Figure 2a). During an initial 18-month phase
(April 05 to December 06) this involved (a) building
understanding of the SA context for water managing
by directly engaging with the ‘water system’ at
a number of different levels namely: national water
(resources and services) policy; regional water
resources policy implementation; sub-regional (river
basin) water resources policy implementation;
municipal water services implementation; research
with local communities on water for productive
use and (b) engagement that was experimental and
took the form either of interviews, study tours or
action/social learning workshops;
(ii) ‘learning system design’ based on contextual appreci-
ation—as a result of the first phase a view could be
formed of which types of capacity building interven-
tions worked best at different ‘levels’ of engagement
and with different groups of beneficiaries. It also
became clear that in terms of institutional capacity
building across the whole ‘water system’ in SA,
engaging at different geographical levels, and making
connections between these, was valued and valuable
as an intervention, even with a very light touch.
Based on the experience and insights from the first
phase an intensive period of ‘design’ emerged (phase
2: December 06–August 07). This involved co-designing a
more structured capacity building ‘programme’, again
working at multiple geographical levels and with a rich
mix of water stakeholders both within and across these
levels. During phase 2 funding for the programme was
agreed. These negotiations produced agreement on (i) an
overall focus for the programme (on co-operative and
adaptive water governance), (ii) a broad outline of the key
skills and knowledges (including governance, ecosystem
functioning, and communication and facilitation skills for
integrated catchment managing) required, and (iii) the mix
of learning approaches that would be employed.
Phase 3 (implementation of this capacity building
programme) began in September 07 and will run through
to June 09. The programme currently includes 2 £ 8-day
staff development ‘watercourses’ (SLIM 2004c), two facili-
tated stakeholder dialogues, one at a catchment and one at
a sub-catchment level (in the Inkomati and Mvoti catch-
ments), and a series of national policy learning workshops
and policy briefings. Work is also being undertaken with
a growing network of SA facilitators to develop and
co-facilitate this programme and to plan for up-scaling.
The approach adopted in SA, shown in Figure 3,
is different to the dominant paradigm for capacity or
capability building (Colvin et al. 2008). The main difference
is that the approach does not see capability building as
something at the end of a policy plus implementation
(or end-of pipe) process; rather capability comes through
the act of jointly constructing the issue (Figure 1b) and
building a ‘learning system’ in which those who participate
are able to transform the situation through concerted action
690 K. Collins et al. | Learning systems in integrated catchment management Water Science & Technology—WST | 59.4 | 2009
(Figure 2a). The SLIM framework (Figure 2) has informed
the ‘learning system’ design and enabled achievements to
date. Here we provide examples of two of the ‘variables’:
(i) history: following the end of the apartheid era the new
SA government was determined to create new and
progressive Water Laws that drew on the best elements
of water policy worldwide, with an emphasis on
sustainable development underpinned by principles of
IWRM and co-operative governance. This resulted in
the National Water Act (1998) and the National Water
Resources Strategy (2004). Throughout the past 13
years the sense of hope and the desire to deliver the
best for the new South Africa has remained strong;
(ii) ecological constraints: SA is both a water-stressed
country and one whose economic success over the
past 100 years has been underpinned by its ‘hydraulic
mission’: to make the most of its water resources,
primarily through an inventive mix of dam-building and
inter-basin transfers throughout the country. In terms of
capacity building work these ecological conditions have
proved both an opportunity and a constraint: an
opportunity to the extent that SA recognizes it has to
manage its water resources well if it is to guarantee water
security, and to do this it has to work out how to
implement its fine policies; a constraint is the extent that
otherwater stakeholders (e.g. industry)would rathernot
face the realities of increasingly limited water resources
and what this might imply for cooperative water
governance.
While Phase 3 (dialogue processes, Figure 3) is still at
an early stage, the approaches used, drawing eclectically
from a range of social learning practices, have so far proven
robust. At the same time there are challenges to address in
terms of building dialogue between less and more powerful
groups, which will test the skilfulness and ingenuity of those
involved to develop appropriate governance spaces and
‘languages’ through which to create inter-disciplinary
dialogue and action. Nonetheless, action to date has
explored and demonstrated approaches to capacity building
both of stakeholders and of Inkomati CMA and DWAF
(Department of Water and Forestry) staff. These are based
on an interactive rather than passive model of learning,
opening up spaces for ‘making sense’ of progressive policies
seeking to create change in complex situations against
a background of highly uneven development. Colvin et al.
(2008) contend that experiments of this type are critical
if DWAF is to implement its progressive water laws and
policies effectively.
Implications for integrated catchment managing
The systemic relationships between the SLIM variables
in Figure 2 suggest that efforts towards building learning
catchments require new forms of praxis which are sensitive
to how these variables are played out in particular contexts.
For example, in SA different understandings of water needs
for social transformation and those for ecosystem function-
ing (constraints) are also the basis of conflict (sometimes
unexpressed) and these tensions limit the effective imple-
mentation of Catchment Management Agencies (CMAs), a
particular type of institutional arrangement.
Challenges to our understanding of ecological con-
straints pertaining to water under climate change con-
ditions offer new opportunities to reconceptualise the praxis
of managing catchments. The increasing policy emphasis on
adaptation requires, in our view, some element of learning.
The extent to which this is recognised varies. Discussions
about the kinds of future institutional arrangements for
water management in the UK, for example, are only just
beginning (DEFRA 2008). In comparison, climate change
impacts on water in Australia are already recognised and
climate change adaptation ‘strategies’ are being vigorously
pursued. However, even with major drought issues, ‘old
Figure 3 | U-process metaphor, used to frame the Mvoti Catchment dialogue in South
Africa (Source: approach adapted from Kahane & Jaworski 2005).
691 K. Collins et al. | Learning systems in integrated catchment management Water Science & Technology—WST | 59.4 | 2009
thinking’ perpetuates with little evidence to suggest that
there has been a reconceptualisation of the adequacy of
current institutional structures and practices in the face of
climate change, the effects of which are essentially unknow-
able (Ison 2007).
In such situations of complexity, dis-connectedness,
conflict and multiple perspectives, we suggest building
a learning catchment by investing in ‘social learning’ as a
deliberate policy mechanism for catchment managing
(Blackmore et al. 2007; see also Moberg & Galaz 2005).
Through social learning approaches, resilience and adaptive
capacity in the form of relational capital can be built or
sustained through the governance arrangements for water.
CONCLUSIONS
This paper has examined some of the challenges and
opportunities for developing learning systems for integrated
catchment managing (ICMg) based on experiences in two
different contexts: UK and South Africa (SA) and informed
by our developing work in Australia. In response to
deficiencies in WFD implementation, particularly a lack of
praxis for capacity and capability building for ICMg, we offer
an alternative approach based on ‘learning system’ design
and capability development.
Focussing on the epistemologies of knowledge in policy
mechanisms, we suggest that social learning, understood as
concerted action among stakeholders in complex and
uncertain situations (such as water catchments), is based
on the process of socially constructing an issue. From this
perspective, a ‘learning catchment’ will arise in social
relations in context-determined ways such that ICMg is
an emergent ‘performance’ of stakeholders engaged in
mutual action in which understandings and practices are
transformed in situation improving ways.
Within a social learning paradigm a priority in research
practice is to know how to create the circumstances for
social learning to occur as part of a learning system.
Our work in the UK reveals the contextual nature of ICS;
suggesting that ICM can never be a blueprint independent
of context. In our view, science has much to contribute to
developing a praxis for ICMg, seen as a process of managing
for emergence. In South Africa, we adopt a novel approach
to ‘learning system’ design and capability development for
jointly constructing the issue and building a ‘learning
system’ in which those who participate are able to transform
the situation through concerted action.
Our experiences in the UK and SA and with awareness
of recent experiences in Australia, while encouraging in
some aspects, suggest we are still a long way from
experiencing the interplay between human activity and
biophysical processes that would lead us to describe
catchments as ‘learning catchments’. Climate change and
related policy responses, particularly adaptation, perhaps
represent an opportunity to reconceptualise the praxis
of managing catchments with greater significance given to
designing learning systems as part of the adaptive process.
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