The Role of Formalisation, Participation and Context
in the Success of Public Involvement Mechanisms
in Resource Management1
Jens Newig 1*, Veronika Gaube 2, Karin Berkhoff 3, Kai Kaldrack 4, Britta Kastens 4,
Juliana Lutz 2, Bianca Schlußmeier 5, Heidelinde Adensam 2, Helmut Haberl 2
1
Institute for Environmental and Sustainability Communication, Leuphana University, Lüneburg, Germany
2
Institute of Social Ecology, IFF Vienna, Klagenfurt University, Vienna, Austria
3
Institute for Environmental Planning, Leibniz University, Hanover, Germany
4
Institute of Environmental Systems Research, Osnabrück University, Osnabrück, Germany
5
Natur, Kultur, Begegnung, Koblenz, Germany
Email address of corresponding author:
e-mail: newig@uni.leuphana.de
Key words: Public Participation, Participatory Methods, Information Flows, Learning,
Effectiveness, Case Study Comparison.
Published as:
Newig, Jens, Veronika Gaube, Karin Berkhoff, Kai Kaldrak, Britta Kastens, Juliana
Lutz, Bianca Schlussmeier, Heidi Adensam and Helmut Haberl. 2008. The Role of
Formalisation, Participation and Context in the Success of Public Involvement Mechanisms in Resource Management. Systemic Practice and Action Research 21(6), 423441. doi: 10.1007/s11213-008-9113-9
The original publication is available at
http://www.springerlink.com/content/c81p16u56m57743v/
1
This work was jointly funded as part of the ‘PartizipA’ project by the German Ministry of Education and
Research and the Austrian Ministry of Education, Science and Culture under grant no. 07 VPS 10
-2-
Abstract
In the face of complex and uncertain issues, one important goal of public participation
in resource management and research is to foster communication and the inclusion of
non-expert knowledge – thus the effective flow of information between project organisers and stakeholders. We compare different methods (instruments, tools) that were employed in the German-Austrian ‘PartizipA’ project to structure information flows in participatory processes. Depending on their goals and context, more or less ‘formalised’
and ‘participatory’ methods were applied, the most important being guided interviews,
focus groups, agent-based modelling, nutrient modelling, cognitive mapping and group
model building as well as the development of a common document. Two regional case
studies, both concerned with European-induced institutional change, are portrayed in
which the specific participatory methods were embedded. The Austrian case study involved the analysis and modelling of agricultural land use in the region of St. Pölten
against the background of the reform of the Common Agricultural Policy, while the implementation of recent European water policy was the issue in the German agricultural
region north of Osnabrück. Presenting both cases in their regional context, the applied
methods are first described according to the logic of the entire respective process. Subsequently, the specific methods are systematically analysed and compared according to
their objective, context and degrees of participation and formalisation. Finally, we
evaluate all methods regarding their effectiveness in terms of goal attainment and their
potential generalisation, seeking to respond to the question of when a particular method
might best be used.
1. Introduction
Participatory processes are becoming increasingly important in the management of natural resources. Policy makers, ‘experts’, and ‘lay persons’ – citizens or representatives of organised
interest groups – are collaborating increasingly in public decisions on issues such as water
management or land use planning (see, e.g. Beierle and Cayford 2002; Renn 2004). Likewise,
transdisciplinary research processes are opening up to include non-scientists, users and other
stakeholders not only as research subjects but, moreover, in a role to shape research agendas
or to provide various kinds of knowledge (Funtowicz and Ravetz 1993). Given the rising
complexity of issues to decide upon and the uncertainties involved, one main reason for the
involvement of non-state actors in public decisions is to incorporate different sources of
knowledge and to foster social learning. By ensuring an effective flow of information between
project organisers and stakeholders, it is expected that it will be possible to arrive at potentially better, i.e. more informed and creative, decision-making (Steele 2001; Pellizzoni 2003;
Lee and Abbot 2003; Newig et al. 2005). Classical typologies of participatory mechanisms
distinguish between ‘information’, ‘consultation’ and ‘participation’, depending on the way in
which information is flowing or being shared (see, e.g. Gramberger 2001; Rowe and Frewer
2005). At the same time, these types also mark the degree of involvement, ‘participation’ be-
Published as: Newig, Jens, Veronika Gaube, Karin Berkhoff, Kai Kaldrak, Britta Kastens, Juliana Lutz, Bianca Schlussmeier, Heidi
Adensam and Helmut Haberl. 2008. The Role of Formalisation, Participation and Context in the Success of Public Involvement
Mechanisms in Resource Management. Systemic Practice and Action Research 21(6), 423-441. doi: 10.1007/s11213-008-9113-9
-3ing labelled the most intensive form.2 In order to avoid terminological confusion, taking the
perspective of project organisers,3 in this paper we will refer to an information flow from organisers towards stakeholders as ‘giving information’, from stakeholders to organisers as ‘extracting information’ and an interactive information flow as ‘mutual exchange of information’.
A spectrum of methods (instruments, tools) is available to structure information flows in participatory processes. Depending on their goals and context, not only more or less ‘participatory’, but also and more or less ‘formalised’ (or structured) methods can be applied. In this
case, formalisation refers to the extent to which information is channelled in a certain way,
leaving more or less scope for open communication. Narrative interviews or open space meetings, for instance, are rather non-formalised methods, whereas standardised questionnaires,
multi-criteria analyses and modelling exercises involve a high degree of formalisation. In abstract terms, the more formalised a method, the more it serves as a filter, allowing only information of a particular nature to pass while excluding others. The selection and aggregation of
information is, of course, a vital element of all cognition, for it defines what is important and
what is not, and thus constructs meaning. This can be a tightrope walk, though, for while
highly formalised methods allow for a strict selection of relevant information, they risk insufficient information being collected and communicated. This calls for a combination of both
formalised and less formalised methods.
More specifically, formalised participatory methods have the advantage of eliciting, handling
and delivering focused, clear and unambiguous information (or of making uncertainties and
ambiguities transparent). What is more, they can counterbalance unwanted group dynamics
such as the tendency towards the convergence of ideas (Hinsz et al. 1997: 54) and thus can
also maintain the divergence of information. Finally, power asymmetries among participants
tend to play a weaker role in more formalised procedures (Rauschmayer and Wittmer 2006:
114). Yet their use also involves important challenges. One is that the process of formalisation
is usually more laborious, requires more time and specific expertise, or trained personnel, and
often technical equipment and is thus more costly. Secondly, stakeholders may have difficulties in accepting some more formalised methods as they might not comprehend all the modelling steps and may thus distrust certain model implications or simply wish to avoid the efforts
required.
In the light of these considerations, the question arises as to which kinds of methods (more or
less formalised, more or less participatory) are best used under which circumstances. We seek
to contribute to a response with insights from the participatory processes conducted as part of
the German-Austrian project ‘PartizipA’ (Participative Modelling, Actor and Ecosystem
Analysis in Regions with Intensive Agriculture; www.partizipa.net), carried out at the University of Osnabrück and the IFF Social Ecology in Vienna from October 2003 to March 2007.
Two case studies involving agricultural regions, both set against the background of European2
Typologies of public involvement mechanisms that build on information or uncertainty are offered by (in
brackets: categorising variables): Catt and Murphy 2003 (information provision, contestation, synthesis);
Renn 2004 (complexity, uncertainty, ambiguity); Newig et al. 2005 (normative and informational uncertainties); Rauschmayer and Wittmer 2006 (complexity, information, uncertainty). Similar typologies, some
also including the nature of environmental conflict and the policy context, are provided by Fiorino 1990;
Renn et al. 1995; Bishop and Davis 2002; Green and Hunton-Clarke 2003; Carter 2005.
3
Project organisers are those who are responsible for conducting the participatory process, e.g. competent
public authorities, research teams, etc.
Published as: Newig, Jens, Veronika Gaube, Karin Berkhoff, Kai Kaldrak, Britta Kastens, Juliana Lutz, Bianca Schlussmeier, Heidi
Adensam and Helmut Haberl. 2008. The Role of Formalisation, Participation and Context in the Success of Public Involvement
Mechanisms in Resource Management. Systemic Practice and Action Research 21(6), 423-441. doi: 10.1007/s11213-008-9113-9
-4induced institutional change, are portrayed in which a number of specific engagement methods were embedded. The most important methods were guided interviews, focus groups,
agent-based modelling, nutrient modelling, cognitive mapping and group model building as
well as the development of a common document. The Austrian case involved the analysis and
modelling of agricultural land use in the region of St. Pölten against the background of the reform of the Common Agricultural Policy, while the implementation of recent European water
policy was the issue in the agricultural region north of Osnabrück.
Our analysis proceeds as follows. Presenting both cases in their regional context, methods are
first described according to the logic of the entire project process (sections 2 and 3). Subsequently, the specific methods are systematically analysed and compared according to their objective, context and degrees of ‘participation’ and ‘formalisation’ (section 4). By participation
we understand the level of information flow (from project organiser to stakeholder and vice
versa and mutual exchange of information) as well as the potential influence of participants.
Drawing on the model by Rowe and Frewer (2005), a method’s degree of formalisation will
be defined by its openness towards participants’ response modes and the structuredness of information aggregation. We conclude by evaluating all methods regarding the effectiveness of
their goal attainment and their potential for generalisation, seeking to respond to the question
of when to best use which method (section 5).
2. Regional case study: St. Pölten Umland (Austria)
2.1 Background and research objectives
The European Union’s Common Agricultural Policy (CAP) reform, implemented on 1 January 2006, shifts incentives for farmers from the current situation in which certain products
have been subsidised to allocating resources according to market demand and prevailing natural conditions through decoupled transfer payments. The Austrian case study analysed the effects of the CAP reform on the social and economic situation of farm households, changes in
farming practices and, ultimately, land use in a rural region of Lower Austria. The scientific
purpose was to evaluate how social and political interventions, in this case the CAP reform,
affect patterns of land use as well as socio-economic conditions in rural regions, using an
agent-based model embedded in a participatory project design.
2.2 Study area
The region of the Traisen valley in Lower Austria, as defined in this project, is made up of 29
municipalities along the Traisen river and around Lower Austria’s capital, St. Pölten. The
study region has an area of 700 km2 and is characterised by diverse land use. In the north, a
part of the region characterised by flatland, agricultural production is dominated by cropland
and wine production. In the south, however, the alpine character of the landscape generally
favours milk production, pastures and forestry. Forestry holdings occupy over 200 km2, milk
production accounts for another 100 km2 and the remaining 400 km2 is distributed over all
other production types. The farms situated in the study region include all farming types usually practiced in Austria. Farms commonly have a size of between 20 and 50 ha. Nearly half
Published as: Newig, Jens, Veronika Gaube, Karin Berkhoff, Kai Kaldrak, Britta Kastens, Juliana Lutz, Bianca Schlussmeier, Heidi
Adensam and Helmut Haberl. 2008. The Role of Formalisation, Participation and Context in the Success of Public Involvement
Mechanisms in Resource Management. Systemic Practice and Action Research 21(6), 423-441. doi: 10.1007/s11213-008-9113-9
-5of all farms are full-time farms, with the remaining half being run by part-time farmers. The
number of part-time farms is increasing from year to year.
2.3 Participatory process
Originally, the intention was to analyse the social and environmental aspects of the implementation of the European Water Framework Directive (WFD). During the kick-off workshop
with regional representatives from the local administration and the government, it became
clear, however, that the local stakeholders were much more interested in: (1) an analysis of
the impact of the common agricultural policy (CAP 2006) instead of the proposed focus on
the WFD, (2) the impact of structural changes in agriculture on the quality of life of women
living in agrarian households. For this reason, the research team reframed the main research
questions towards an analysis of the impact of CAP reforms, with a focus on gender-related
aspects. This shift in the project’s focus of course also fundamentally affected the remaining
participatory process.
Methodologically, the Austrian case study aimed to generate an agent-based model in close
co-operation with the relevant actors. Throughout the research, the participatory process reflected the information requirements of designing the agent-based model. In turn, the agentbased model was applied as a guiding tool in the participatory process to help local stakeholders reflect on the future, developing strategies and policy priorities. The process of agentbased model (ABM) building allows different forms of participation at different stages of the
modelling process. An ABM consists of a set of virtual agents that encapsulate the behaviour
of the various individuals that make up the system. Hence, when designing the model concept
it was necessary to analyse the behaviour of agents.
At the beginning, 15 guided interviews were conducted with experts from the provincial government, the federal government, the agency of agriculture and regional stakeholders. In combination with a broad literature research on the CAP reform and the expected impact on agricultural activities, these interviews were an effective instrument for making contact with relevant stakeholders, gaining local knowledge related to our research questions, stimulating actors’ interests and making them feel represented in the ongoing research.
A second element in the participatory process was a series of focus groups for female stakeholders that were designed to obtain an insight into women’s perspectives. The group met
four times over a period of one-and-a-half years. Each meeting ran for about three hours. In
this project, the setting of the focus group was designed together with the head of the Department of Education of the Agency of Agriculture. She invited six female farmers and three female stakeholders from different departments of the Agency of Agriculture. Important criteria
for the selection of the female farmers were a good representation of different production sectors (cropland / grassland) and a balanced age pattern. The process of the focus groups was
adapted to the whole participatory process. The intention of the first meeting was to test predefined hypotheses concerning the ratio between income and working time. These hypotheses
were generated by the analysis of the above-mentioned guided interviews. The outcome of the
first focus group meeting and the information about stakeholders’ motivation and behaviour
derived from the interviews helped to develop the first version of the ABM design. At this
stage of model building, the first simulation runs required evaluation. Several evaluation
methods are available. One involves the discussion of the output with stakeholders, followed
Published as: Newig, Jens, Veronika Gaube, Karin Berkhoff, Kai Kaldrak, Britta Kastens, Juliana Lutz, Bianca Schlussmeier, Heidi
Adensam and Helmut Haberl. 2008. The Role of Formalisation, Participation and Context in the Success of Public Involvement
Mechanisms in Resource Management. Systemic Practice and Action Research 21(6), 423-441. doi: 10.1007/s11213-008-9113-9
-6– if necessary – by the redesigning and ‘reformalisation’ of the ABM. Accordingly, the task
of the second focus group meeting was to discuss the design and initial output of the agentbased model, where hitherto generated insight was translated into formalised language and
diagrams. Concrete decisions on the relevant model output (e.g. labour time per farm, cropland area per farm, etc.) and adjustable model parameters required were taken together with
the stakeholders. The third focus group concentrated on developing four ‘storyline’ scenarios
for the region. The outcome of this focus group meeting was again incorporated in the ongoing modelling process. Finally, the well-designed and well-evaluated model was used in the
fourth and final focus group meeting as a tool to demonstrate the impact of different actions
under different framework conditions. Group meetings were moderated by one of the researchers.
The most crucial aspect for the participatory process described in the Austrian part of the project was the application of an ABM as a guiding tool to develop scenarios for sustainable resource use (see Rothman and Coppock 1996) together with regional actors. The incorporation
in the project team of a representative (Josef Breinesberger) of the regional consulting company Agrar Plus, an individual regarded highly by key regional stakeholders due to his huge
practical expertise and local embeddedness, was crucial in terms of giving the stakeholders
confidence in the project team. Consequently, stakeholders accepted the research team as ‘one
of us’ and were more willing to contribute to the participatory research process. Besides organising contacts, the function of Josef Breinesberger in the project was to directly feed information into the research process and to take responsibility for the outcome of both the participatory process and the ABM.
3. Regional case study: Osnabrück (Germany)
3.1 Background and research objectives
The European Water Framework Directive (Directive 2000/60/EC; WFD), which entered into
force in December 2000, demands that all European waters achieve “good status” by the year
2015. The WFD, moreover, calls for various modes of public participation and involvement,
which the Commission judges as key factors in supporting the successful implementation of
policy goals (EU 2002; Newig 2005). Presently, a range of forms of public participation is being put in place (see Kastens and Newig accepted for German examples). Comparable to the
process of stakeholder involvement as demanded by the WFD, the German project team established an actors’ platform in a region with intensive agriculture, aiming to investigate and
discuss measures for the reduction of diffuse pollution. Methodologically, participatory methods were tested and partly developed which have the potential to be applied in the official
processes within the WFD implementation.
Published as: Newig, Jens, Veronika Gaube, Karin Berkhoff, Kai Kaldrak, Britta Kastens, Juliana Lutz, Bianca Schlussmeier, Heidi
Adensam and Helmut Haberl. 2008. The Role of Formalisation, Participation and Context in the Success of Public Involvement
Mechanisms in Resource Management. Systemic Practice and Action Research 21(6), 423-441. doi: 10.1007/s11213-008-9113-9
-7-
3.2 Study area
The study area comprises the Hase river catchment north of Osnabrück. A sub-catchment of
the Ems in northwest Germany, the Hase covers an area of 3000 km2, 68 percent of which is
agricultural land. With 4.7 million livestock, 20 percent of all German pigs are kept in this
small region (Klohn and Windhorst 2003). This high livestock density leads to a remarkable
amount of organic fertilizer, which involves the risk of nitrogen emissions entering the
groundwater. Moreover, according to vulnerability assessment performed in the catchment,
the groundwater pollution potential is high in at least parts of the catchment (Berkhoff 2005).
The first inventory that was required by the WFD states that 98 percent of the region’s
groundwater is unlikely to attain a good status by 2015 due to nitrogen from diffuse sources
(NLWKN 2005). On the basis of these facts, the project focused on diffuse nitrogen pollution
of groundwater bodies as one of the main ecological threats to the region.
3.3 Participatory process
The regional actors’ platform (AP) was established in September 2004, involving 14 representatives from agriculture, water management, environmental protection and administration.
Seven meetings took place over a period of 20 months. The main objectives of the AP were:
to reduce uncertainties among stakeholders concerning the new regulations of the
WFD in dialogue with other experts;
to investigate distinct measures to mitigate diffuse groundwater pollution in the Hase /
Osnabrück region, including their costs and potential for realisation.
Information flows and discussions during the platform meetings were supported by different
consultative and participatory methods that were flexibly adapted to the participants’ requests
and discussion shifts.
Since participants’ knowledge of the WFD and of groundwater protection varied, it was important to generate a common state of knowledge regarding the most central issues in order to
enable all stakeholders to participate equally in the discussions. Hence, the first two meetings
concentrated on providing actors with essential information on the WFD and its challenges.
A central aspect of discussions in the AP was the individual perception of each stakeholder. In
order to identify different interests, causes of conflicts and individual views on possible solutions towards groundwater protection, face-to-face interviews of about 90 minutes duration
were conducted with each participant. The interviews were supported by the use of cognitive
mapping methods (Vennix 1996, Hodgson 1992). Starting with the regional challenges due to
WFD, the interviewees developed interdependencies, causal relations and solutions, all of
which were visualised in a poster-like diagram (‘cognitive map’).
In three small groups, each involving about five of the interview partners, the participants presented their cognitive maps in order to discuss similarities and differences in their perspectives and to merge their views in one synthesis poster. This forced the actors to be exact in
their concepts and helped to build up a common understanding of all the viewpoints and factors involved. The actors’ implicit beliefs became explicit and could then be discussed. The
main foci of the synthesis phase were to determine open questions, to collect a list of possible
Published as: Newig, Jens, Veronika Gaube, Karin Berkhoff, Kai Kaldrak, Britta Kastens, Juliana Lutz, Bianca Schlussmeier, Heidi
Adensam and Helmut Haberl. 2008. The Role of Formalisation, Participation and Context in the Success of Public Involvement
Mechanisms in Resource Management. Systemic Practice and Action Research 21(6), 423-441. doi: 10.1007/s11213-008-9113-9
-8regional groundwater protection measures and to identify criteria for their evaluation in terms
of suitability and effectiveness. In a subsequent AP session, the synthesis diagrams of the
three small groups were presented, resulting in intensive and critical discussions which also
raised further open questions. In order to respond to these, the participants agreed upon a
common strategy to search for missing information by contacting further experts and to distribute working tasks between stakeholders and the research team.
Moreover, the AP developed an evaluation matrix for the measures discussed in the three
small groups in order to determine groundwater protection measures for the region. Besides
ecological criteria, the matrix involved social and economic parameters that were based on
scientific research as well as on evaluations of the stakeholders. This procedure structured the
analysis across a range of aspects which the actors assumed to be important. The matrix also
served as a concise discussion basis for the development of problem-oriented action recommendations.
In order to estimate ecological criteria in the matrix, the computer model STOFFBILANZ (cf.
Gebel et al. 2005) was introduced within the platform. STOFFBILANZ was used to evaluate
the effectiveness of groundwater protection measures concerning their ability to reduce nitrogen charges. In order to gain the participants’ acceptance, the model was presented and discussed extensively in the AP before scenarios with a particular focus on the amount of organic fertilizer application were calculated and visualised in maps (Berkhoff 2006). Since the
implementation of the model took longer than expected and the actors could not agree on
quantitative descriptions of required parameters, model results, although discussed intensively
in the platform, were not generally accepted by all participants and were therefore not used in
the further discussion process.
Finally, the actors agreed to summarise the evaluations of discussed measures in a common
document (Berkhoff et al. 2006), based on protocols and working documents that had been
discussed and adopted previously during the AP process. Corrections and additions to the first
draft prepared by the research team were provided by the stakeholders through a questionnaire
and were incorporated in a new version, which the actors discussed and adopted in the final
AP session. Both stakeholders and project organisers judged this iterative process as highly
fruitful in terms of clearly mapping out the common ground as well as shedding light on the
remaining differences in perceptions and interests. At the actors’ special request, the document also portrays the methodological AP process and its appraisal. In order to communicate
the results of the AP, the participants and the research team jointly presented the document to
a broad regional audience in May 2006. The document was distributed as a hard copy and
also published on the internet.
4. Comparative analysis
In this section, the six different participatory mechanisms applied in the project are analysed
with reference to five aspects:
1. The intention of method application refers to the idea that certain methods are assumed to be suitable for specific outcomes the project organisers have in mind. Intentions can be, for instance, to elicit or exchange knowledge, to gain acceptance of or
among stakeholders, or to develop a common decision.
Published as: Newig, Jens, Veronika Gaube, Karin Berkhoff, Kai Kaldrak, Britta Kastens, Juliana Lutz, Bianca Schlussmeier, Heidi
Adensam and Helmut Haberl. 2008. The Role of Formalisation, Participation and Context in the Success of Public Involvement
Mechanisms in Resource Management. Systemic Practice and Action Research 21(6), 423-441. doi: 10.1007/s11213-008-9113-9
-92. The second aspect concerns the degree of participation. Depending on the direction of
information flow, methods differ in their modes of participation: by ‘giving information’, project organisers intend to inform actors, e.g. in the form of leaflets or internet
sites, but in factual terms do not aim at gaining any response. By ‘extracting information’, information is proposed to be elicited from the actors, and project organisers
usually prepare specified mechanisms to deal with this information (Rowe and Frewer
2005: 255). Finally, by ‘mutual exchange of information’, project organisers intend to
exchange information with actors. A certain degree of dialogue takes place, which
serves to transform the opinions of both organisers and actors (cf. ibid.: 256). Moreover, the degree of participation can vary in terms of the capacity for action provided
to the actors. Depending on the context, the opportunities for stakeholders to influence
or monitor a process and/or its outcome might be either wide or narrow (cf. UNESCO
2006: 46; Haugaard 2003: 95; Rauschmayer and Wittmer 2006: 114).
3. The degree of formalisation depends either on an open or closed response mode and
more or less structuredness of information aggregation. While methods with an open
response mode allow for free responses from actors to organisers, mechanisms with a
closed response mode restrict stakeholders to choosing from among pre-set response
options (Rowe and Frewer 2005: 269). Facilitation of aggregation is structured if clear
rules for information elicitation and combination are set out (by organisers and/or actors) and followed during the process. Where no facilitation of elicitation and aggregation of information is given, the process is unstructured. But where facilitation is provided, it can still be structured or unstructured (ibid.: 273).
4. Context refers to the conditions under which the method was applied, such as the stage
of application, resource needs and actor attributes (e.g. in terms of group heterogeneity, interest of actors, their knowledge, etc.).
5. Finally, an evaluation of the method takes place, addressing the question of goal attainment in the specific application context as well as the effects of the method on project organisers and/or actors. Furthermore and independently from the context, the
generalisability of the method is evaluated.
Published as: Newig, Jens, Veronika Gaube, Karin Berkhoff, Kai Kaldrak, Britta Kastens, Juliana Lutz, Bianca Schlussmeier, Heidi
Adensam and Helmut Haberl. 2008. The Role of Formalisation, Participation and Context in the Success of Public Involvement
Mechanisms in Resource Management. Systemic Practice and Action Research 21(6), 423-441. doi: 10.1007/s11213-008-9113-9
- 10 -
An overview of the six methods concerning these aspects can be found in Table 1.
Guided
interviews
Agent-based
modelling
(ABM)
Cognitive mapNutrient
ping (CM) /
modelling
Group model
(STOFFBILANZ)
building (GMB)
Elicitation of
individual
perspectives;
information
reduction; development of
shared problem
perception
Development
of common
document
Summary of
results of
participation process; input
for policy
makers
Elicit
information from
stakeholders,
stimulate
their interest
Test hypotheses,
educe information
on time use
and decision making
processes,
discuss
scenarios
Develop a
tool for
participatory scenario building, characterising and
evaluating
potential
future developments
Adjustment of
resource flow
model to regional conditions; evaluation of
groundwater
protection
measures;
model results
as a basis
for further
discussion
Direction
of information
flow
Extraction of
information
Extraction
of information and
information
flow between
stakeholders
Mutual exchange of
information
Mutual exExtraction of
change of in- information
formation
and information flow between stakeholders
Influence
on the
process
Incorporation of
results
in further
methods
Incorporation of
common
knowledge
in ABM
Influence on
complete
model input
and structure, not on
participation process
Influence on
parts of
model input,
not on model
structure;
free decision
on further
use of model
Influence on
complete model
input and
structure, incorporation of
results in
further methods
Influence
on complete
document
input
Response
mode
(open /
closed)
Open;
free responses
Open: free
responses
Model design: open;
parameter
estimation:
closed
Partly open:
free responses restricted by
predetermined
model structure
Mixed: predefined questions and result representations, free
responses
(GMB)
Mixed: free
responses
and yes /
nodecisions
Group opinion is aggregated
and performed by
the stakeholders
Model design: unstructured;
parameter
estimation:
structured
Stringent
model structure, but unstructured
due to free
discussions
Structured
(but flexible): rules
for aggregation, visualisation, discussion
Structured:
rules for
aggregation, discussion,
decision
Intention
Degree of participation
Degree of formalisation
Context
Focus
groups
Facilitation of
aggregation
(structured /
unstructured)
Mutual exchange of
information
Resource
needs
(very low
– very
high)
Interviewer
/analyser
qualification:
high;
time:
very high
Facilitator
qualification: high;
time, particularly
for preparation:
high
Modeller /
facilitator
qualification: very
high; time:
very high
Modeller / facilitator
qualification: very
high; time:
very high
Modeller / facilitator
qualification:
high; time:
very high
Author / facilitator
qualification: very
high; time;
very high
Actor
attributes
Heterogeneous
group of
interviewees,
high expertise
and interest
Only partly
heterogeneous group
(only females)
Homogeneous
and heterogeneous
groups; high
engagement
and openness; continuity
Heterogeneous
group re
model expertise and
openness;
highly sensitive issue
Heterogeneous
group re. expertise, problem perception
and interest;
high openness
Heterogeneous group
re. interest, dedication and
willingness
to compromise
Stage in
process
Beginning Second half
phase
of process
Whole process
Middle phase
Beginning
phase
End of
process
Published as: Newig, Jens, Veronika Gaube, Karin Berkhoff, Kai Kaldrak, Britta Kastens, Juliana Lutz, Bianca Schlussmeier, Heidi
Adensam and Helmut Haberl. 2008. The Role of Formalisation, Participation and Context in the Success of Public Involvement
Mechanisms in Resource Management. Systemic Practice and Action Research 21(6), 423-441. doi: 10.1007/s11213-008-9113-9
Evaluation
- 11 -
Agent-based
modelling
(ABM)
Cognitive mapNutrient
ping (CM) /
modelling
Group model
(STOFFBILANZ)
building (GMB)
Development
of common
document
Guided
interviews
Focus
groups
Effectiveness
Information
elicited
as input
of the
ABM
Successful
information
elicitation
from different perspectives
Successful
creation of
model and
successful
in structuring and reducing of
complex information
Model adjusted to regional conditions (for
research
use), no further use as
tool for
evaluation of
measures
Successful information
elicitation
and aggregation; support
for focussing
discussions
and conflict
resolution
Development
of valuable
document;
support for
focussing
discussions; difficulties
of merging
perspectives
Generalisability
High,
classical
consultation
method
High, concrete design depends on
the group
Partly useful; depends
on research
focus and
system under
consideration.
High (used by
many German
public authorities);
in participatory processes: rather
for less
critical issues
High if stakeholder perspectives differ
High, as
long as resources are
available
Acceptance
High,
since actors felt
they were
being
taken seriously
High, especially after first
meeting,
when scepticism diminished
High, scepticism diminished
gradually
during process
Very low:
usefulness
was not recognised;
critical view
on data input
High, apart
from difficulties of understanding complex individual models
Mixed: high
for most
participants, very
low for
some others
Table 1: Comparison of the methods used in the Austrian and German case studies. See main text for
a detailed discussion of how the methods were conducted.
4.1 Guided interviews
Guided or semi-structured interviews (Patton 1990; Froschauer and Lueger 1992) are not participatory techniques per se. Interviews can be assumed to be a classical consultation method
as the flow of information goes primarily from interview partners to the research team. At the
same time, interviews might influence the whole participatory process. Interviews can promote the arousal of actors’ interest in the ongoing research and might further help to determine the participants and issues to be involved in later group processes.
To some extent, qualitative interviewing follows a certain interview structure to ensure that
information about similar topics is obtained from each person (Kvale 1996; Hoepfl 1997).
Otherwise, it utilises open-ended questions, seeking individual responses (Rowe and Frewer
2005: 269) which are not predetermined but flexible in terms of information input. The response mode is open, since stakeholders are allowed to give free input. Even though leeway is
given to the interviewees to introduce further issues to be discussed, facilitation of aggregation is structured, since questions are set beforehand. Topics to be discussed during the interview provide at least an initial structure to aggregate stakeholders’ interests and to reveal
which proportion of respondents holds certain views (cf. ibid.: 273).
Besides expertise in the area of study as well as in qualitative interviewing, interpersonal
skills are essential for researchers to draw out information (Patton 1990). Moreover, time resources are needed to post-process individual interviews.
Interviews are generally well accepted by the actors, since they do not necessarily require involvement throughout the entire project process. Thus they serve as a beneficial starting point
Published as: Newig, Jens, Veronika Gaube, Karin Berkhoff, Kai Kaldrak, Britta Kastens, Juliana Lutz, Bianca Schlussmeier, Heidi
Adensam and Helmut Haberl. 2008. The Role of Formalisation, Participation and Context in the Success of Public Involvement
Mechanisms in Resource Management. Systemic Practice and Action Research 21(6), 423-441. doi: 10.1007/s11213-008-9113-9
- 12 for participatory processes. A mediator who establishes initial contacts to individual stakeholders can be of particular assistance, thus supporting an atmosphere of trust between the actors and researchers.
In the Austrian case study, guided interviews initially served to elicit information from the
stakeholders. They further stimulated the stakeholders’ interests by visualising the significance of the project and by treating them as experts, able to tell their own 'story' on the issue
at stake. This created an atmosphere of trust, additionally supported by a mediator person,
who enabled the project organisers to use interviews as a tool to design subsequent participatory events and processes, such as focus groups and work shops.
4.2 Focus groups
In general, the intention to organise focus groups is to provide a discussion forum, collecting
various perspectives on a specific topic (see, for example, Littig and Wallace 1997)4. With regard to participatory processes, focus groups are suitable for involving actors in the ongoing
research. In contrast to interviews, the moderator in focus groups only initiates the discussion
by providing start-up questions and comments, but hardly influences the discussion during the
group process unless it stagnates or goes astray. Thus, information input is very flexible, since
respondents are influenced not only by the moderator but also by other respondents. This
group process in turn causes the response mode to be open and spontaneous, since stakeholders are allowed to make free responses not only to the moderator’s initial input but particularly to the views and statements of other participants. Unless facilitated group aggregation, such as the Delphi technique, or comparable methods are applied in the focus groups
(Rowe and Frewer 2005: 274), group opinion is aggregated and performed by the stakeholders, structuring the discussion according to their own intentions.
Moderation skills are essential to guarantee a dense information flow and to encourage all
participants to contribute to discussions. Organising a series of focus groups that will meet
several times during the research process requires a high degree of motivation on the part of
the actors involved. To enable this, both the topic of discussion and the group setting can be
assumed to be of particular importance. As experienced in the Austrian case study, a mediator
who facilitates these aspects (selection of topic, selection and invitation of participants) is
supportive.
The intention behind organising focus groups was to test several hypotheses that arose out of
the interviews and to educe different scenarios regarding structural agricultural change.
With regard to the participatory process, focus groups were the most important tool for involving actors in the ongoing research over a certain period of time. This was mainly
achieved because the female farmers felt and behaved as a group of experts, sharing similar
problems and visions and helping researchers to generate a computer model that would be
close to reality. Furthermore, the focus groups provided a forum to visualise and discuss
shared problems and solutions that might be useful for female farmers’ everyday lives and for
further activities to be organised by the female farmers and/or by their representatives.
4
On focus groups as a qualitative research method, see: Dürrenberger et al. 1997; Jaeger et al. 1999;
Stewart and Shamadasani 1990 and Morgan 1993.
Published as: Newig, Jens, Veronika Gaube, Karin Berkhoff, Kai Kaldrak, Britta Kastens, Juliana Lutz, Bianca Schlussmeier, Heidi
Adensam and Helmut Haberl. 2008. The Role of Formalisation, Participation and Context in the Success of Public Involvement
Mechanisms in Resource Management. Systemic Practice and Action Research 21(6), 423-441. doi: 10.1007/s11213-008-9113-9
- 13 -
4.3 Agent-based modelling
Agent-based modelling (ABM) is often used when interactions between agents are complex
and non-linear (see Bonabeau 2002). In the Austrian case study, ABM both facilitates and is
based on participatory processes. In this sense, agent-based modelling aims at eliciting and
structuring information about the behaviour of agents and systems (see, e.g., Grimm and
Railsback 2005) in cooperation with the relevant actors. With this, it develops a tool for participatory scenario building, characterising and evaluating potential future developments.
Participative agent-based modelling could be defined as a process of mutual exchange of information. This is due to the iterative process in which information flows vary according to
the different phases of research. First, in the design of the ABM, information is extracted from
the relevant actors and processed into the first model version. Subsequently, this first model
version is evaluated by the actors and additional information is elicited to correct the model.
Finally, the model is used as a tool to define scenarios in cooperation with the actors.
The ABM is per se a formalised tool, since actors, actions and interactions have to be characterised in a formalised, computer-based language. In contrast, the process of gaining information relevant to model building varies according to the phases of modelling and in order to parameterise the model as closely as possible with real-world data (see Berger et al. 2001).
While in the first phase, open responses are required to obtain a broad overview of existing
information, the later phases aim at reducing broad information to relevant information - relevant to both the model and the actors.
In general, ABM is very resource-intensive in terms of working time, expertise and money.
Especially the implementation of the model as a computer simulation requires specialised expertise and a great amount of working hours. Furthermore, as actors need to participate
throughout the entire model-building process, a flexible and work-intensive participatory
process has to be designed and accomplished. Moreover, the actors face the challenge of becoming accustomed to the method of modelling and being confronted with a formalised reduction of information.
The Austrian case study shows that, in combining a high degree of formalisation with a high
degree of participation, ABM serves as an adequate tool to structure and reduce complex information in a way that is useful for both stakeholders and researchers.
4.4 Nutrient modelling
Nutrient modelling is not a participatory mechanism itself, but a tool that can be implemented
within a participatory process. The aim is to discuss land use changes and different groundwater protection measures in the context of the practical experiences of stakeholders (cf. Kunst et
al. 2004).
Within two meetings of the Osnabrück actors’ platform, the STOFFBILANZ model (Gebel et
al. 2005) was introduced and discussed. Mutual exchange of information took place by considering input variables for a reference scenario and the initial model output that helped
stakeholders to decide upon suitable groundwater protection measures for the region. Likewise, project organisers received further input from practice to improve model input and outPublished as: Newig, Jens, Veronika Gaube, Karin Berkhoff, Kai Kaldrak, Britta Kastens, Juliana Lutz, Bianca Schlussmeier, Heidi
Adensam and Helmut Haberl. 2008. The Role of Formalisation, Participation and Context in the Success of Public Involvement
Mechanisms in Resource Management. Systemic Practice and Action Research 21(6), 423-441. doi: 10.1007/s11213-008-9113-9
- 14 put. Participation opportunities were provided by leaving the decision open as to whether or
not the model would be used in further AP meetings. Moreover, the participants could choose
among the land use measures to be modelled and were also able to suggest additional measures. On the other hand, STOFFBILANZ follows a stringent model structure. Accordingly, the
sessions in which the model was used were organised in strict compliance with this structure
in order to gather detailed answers on specific model-related questions. In terms of the degree
of formalisation, the process was thus only partly open in the response mode by focussing the
discussion on the model structure, but it also allowed free comments on the modelling procedure. The structuredness of information aggregation differed: According to the model structure, information aggregation had to be very formalised. On the other hand, free discussions
and the responses of the stakeholders led to unstructured aggregation.
The model application in the participatory process was designed as an iterative procedure.
Hence, provisional model results were presented to the stakeholders, who had very different
backgrounds on modelling practice. Within the time provided, it was impossible to establish
confidence in the model and its results on the part of the actors. Instead of a participatory
modelling process, the stakeholders asked for complete and validated model results. This was
neither intended nor possible within the project, since the modelling process is very timeconsuming and demands detailed expert knowledge that partly had to be provided by the participants (Berkhoff 2006: 4). A further – but probably far more important – reason for the participants’ critical reaction lies in the general context of agricultural groundwater pollution,
which is a politically sensitive issue in the region.
4.5 Cognitive Mapping and Group Model Building
Cognitive mapping (Vennix 1996, Hodgson 1992) as a special form of guided interview was
used in the German case study to elicit broad information about the individual stakeholders’
perspectives on causes of conflicts and possible solutions concerning agricultural groundwater
pollution. The resulting visualisations (causal loop diagrams) formed the basis for a twostaged group model building exercise, which served to develop a common understanding
among stakeholders and to reduce information to the relevant aspects. The participants persented their causal loop diagrams in small groups, discussed the different perspectives and
merged them where possible. The resulting shared group models were then presented and discussed in the larger group and delivered the criteria for the above-mentioned evaluation matrix (see 3.3). In contrast to the ABM, these models were not implemented as a computer
simulation.
Both cognitive mapping and group model building are tools to extract information from the
stakeholders. Their contributions formed the basis for the further participation process by influencing the topics to be discussed and the further methods to be used within the AP. A high
degree of participation was combined with a high degree of formalisation. The interviewer /
facilitator asked for specific variables (e.g. aims of WFD, potential measures) and required
the participants to identify causal relationships between them. The group model building exercise was highly structured, demanding that stakeholders present individual models in a specific manner and limited time, choose a certain number of relevant variables, and classify
them according to a prepared structure.
Published as: Newig, Jens, Veronika Gaube, Karin Berkhoff, Kai Kaldrak, Britta Kastens, Juliana Lutz, Bianca Schlussmeier, Heidi
Adensam and Helmut Haberl. 2008. The Role of Formalisation, Participation and Context in the Success of Public Involvement
Mechanisms in Resource Management. Systemic Practice and Action Research 21(6), 423-441. doi: 10.1007/s11213-008-9113-9
- 15 Again, the interviewer / facilitator needed great expertise. In addition, cooperativeness on the
part of the participants was vital because they were not used to such methods and needed to
become accustomed to the high degree of formalisation, which often meant that discussions
were interrupted. The presentation of their individual and often complex models also demanded special presentation skills on the part of the presenters and information processing
skills on the part of the audience. Common work on the shared model led to fruitful discussions between stakeholders, who reported that this method helped them understand the perspectives of others. They highly appreciated the entire modelling process. For the project organisers it was advantageous that the need for important changes of process organisation had
already become apparent at an early stage. Less participatory methods might have postponed
this consequence, leading to more difficulties in the course of adapting to participants’ perspectives.
According to our experience, the described combination of methods should be applicable in
any other context.
4.6 Development of a Common Document
In order to summarise the results of the Osnabrück actors’ platform and to support the official
implementation process of the WFD, a common document was developed. During the writing
process, conflict resolution turned out to be a prerequisite and an important side-effect. The
whole document was based on stakeholders’ contributions, and both content and structure
were revised several times according to the participants’ comments. The final version was
jointly edited in an AP session by both stakeholders and process organisers. The high degree
of participation was also characterised by the stakeholders’ ability to decide whether or not to
write the document at all and whether or not to publish it. By deciding to do both, they retained the chance to influence the official implementation process of the WFD.
The participatory phases of document development had to be highly structured in order to
gather relevant information in a short period of time. The process included closed as well as
open response modes. Concrete questions were posed to obtain stakeholders’ specific comments and their agreement to concluding statements was measured by ticking ‘yes’ or ‘no’.
However, participants also had the opportunity to make free comments whenever they
wanted. In the final editing session, the facilitator structured information aggregation. Stringent rules defined how many comments were allowed and how to decide on the final formulations. Altogether, the entire development process was rather formalised.
Eliciting the common views from many documents produced earlier within the AP and incorporating the stakeholders’ statements turned out to be more complicated than expected, which
prolonged the writing time for the project organisers. Moreover, many contradicting comments upon the first draft made a careful preparation of the closing discussion necessary. The
method required very dedicated participants, because they had to spend additional time between platform meetings. The document was impressive in terms of showing the breadth of
information that had been gathered, discussed and evaluated throughout the whole participation process and which might have been lost if it had not been thus summarised. The document has the potential to support other WFD and participation processes, since much can be
learned from it, for example regarding evaluation of groundwater protection measures or faPublished as: Newig, Jens, Veronika Gaube, Karin Berkhoff, Kai Kaldrak, Britta Kastens, Juliana Lutz, Bianca Schlussmeier, Heidi
Adensam and Helmut Haberl. 2008. The Role of Formalisation, Participation and Context in the Success of Public Involvement
Mechanisms in Resource Management. Systemic Practice and Action Research 21(6), 423-441. doi: 10.1007/s11213-008-9113-9
- 16 cilitation tools. The work on a common product, be it a final document, a model or the like,
turned out to be a very useful method for exchanging relevant information.
5. Discussion and conclusion
Having reviewed six more or less formalised public involvement methods in resource management research, what can we learn from this experience?
Generally, we find that the applied methods were adequately chosen and served their intended
purposes rather well, with the exception of the nutrient modelling exercise, which was virtually rejected by the participants. While guided interviews and focus groups were mainly employed to extract information from stakeholders, the latter, together with cognitive mapping
(CM) and group model building (GMB), also successfully served to foster a flow of information among the stakeholders. Furthermore, the joint construction of the agent-based model
(ABM) and the development of a common final document were both well suited to fostering
the mutual exchange of information between stakeholders and project organisers.
On the basis of the information exchange, learning took place. In terms of effective information uptake, project organisers explored participants’ knowledge and views and accordingly
and continuously adapted the (participatory) research design, while participants learned about
the regulatory challenges at stake. Furthermore, the mutual information exchange both between participants and project organisers and among stakeholders themselves facilitated collective learning about the causal relations in the socio-environmental systems at stake. The
chosen methods not only fostered a fruitful deliberative process but, moreover, managed to
eventually ‘get things done’. Thus, the Austrian process yielded an executable and thoroughly
validated agent-based model as a resource management tool, while the German actors’ platform produced a diligently crafted and balanced final document as a policy recommendation
for the further regional implementation process of the Water Framework Directive.
As regards formalisation, we observe in both case studies a shift from rather open and less
formalised methods at the outset towards less open, more stringent and on the whole more
formalised methods towards the end of the process. This holds both within specific methods
and across the spectrum of methods. In general, it seems advisable to commence with rather
unstructured methods to collect information that is as complete as possible. In the phases of
information reduction and aggregation, more formalised methods turn out to be appropriate.
In the case of the Osnabrück actors’ platform, where time pressures to finalise the common
document became a problem at the end of the process, the stringent structuring of discussions
and decisions turned out to be absolutely necessary. Here, the formalised approach was also
able to counterbalance unwanted group dynamics in the production of the final document,
which was eventually accepted and endorsed by all actors, although some had previously
questioned the approach as a whole. Likewise, the ABM constructed in the Austrian case began with rather open discussions and moved in the implementation phase towards a more
structured and formalised approach.
The application of formalised computer models, such as agent-based and nutrient models in
participatory processes, always involves risks for the project organisers. It is difficult to assess
the actors’ acceptance of these methods. The experiences in the PartizipA project suggest, for
once, that stakeholders’ acceptance could depend on the stage when computer models are apPublished as: Newig, Jens, Veronika Gaube, Karin Berkhoff, Kai Kaldrak, Britta Kastens, Juliana Lutz, Bianca Schlussmeier, Heidi
Adensam and Helmut Haberl. 2008. The Role of Formalisation, Participation and Context in the Success of Public Involvement
Mechanisms in Resource Management. Systemic Practice and Action Research 21(6), 423-441. doi: 10.1007/s11213-008-9113-9
- 17 plied in the participatory process. Computer models that are explicitly used to demonstrate the
impact of different actions encounter resistance concerning the plausibility of the model. If
stakeholders are strongly involved in the designing process of the model from the very beginning, and if the outcome of the model is regularly evaluated by the actors, acceptance seems
to be higher. Firstly, the stakeholders in their role as ‘model designers’ are very much responsible for the model and its outcome. Secondly, they have a much better understanding of the
internal structure of the model. Thus if stakeholders feel that the model was built or designed
by themselves, it is easier for them to accept the results of the model – even if not everything
in the computer model can be made visible to them. On the other hand, not all models suit
such an open procedure. Where existing modelling frameworks are to be applied in a participatory setting, stakeholders’ input is restricted by the model structure. In relation to this, we
should like to stress the crucial importance of the context in which the various available
methods are applied. The willingness of stakeholders to participate and accept model results
depends largely on their personal interests – and thus the policy setting of the process – their
apprehension and expertise, the composition of the actor group and whether financial compensation is provided.
The assumption that more formalisation correlates with less participation holds true to a certain extent, namely in terms of the stakeholders’ possibility to influence the process or the
specific method. Concerning the direction of information flow, formalisation and participation
seem to be independent of each other. Thus, a high degree of formalisation could be linked
with the giving or the extraction of information (e.g. cognitive mapping) as well as with mutual exchange (e.g. ABM).
In terms of generalisability, finally, we found that this is rather high for ‘established’ methods
such as guided interviews and focus groups. We judge ABM, which implies very high resource needs and the willingness of stakeholders, as a partly useful tool, depending largely on
the respective context. With nutrient modelling, although a useful a tool as such and scientifically acknowledged for the applied issue, we encountered severe difficulties in the participatory setting, largely due to the highly sensitive issue that did not, in the given context, allow
for a high degree of formalisation and thus the precise determination of variables that could
oblige certain actors in particular ways. Rather, a more ambiguous documentation of environmental states and desired measures as laid down in the common final document did prove
possible and, as such, successful. Cognitive mapping and group model building can again be
judged as usable tools, in cases where the stakeholders’ perspectives actually differ and need
to be brought together.
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Published as: Newig, Jens, Veronika Gaube, Karin Berkhoff, Kai Kaldrak, Britta Kastens, Juliana Lutz, Bianca Schlussmeier, Heidi
Adensam and Helmut Haberl. 2008. The Role of Formalisation, Participation and Context in the Success of Public Involvement
Mechanisms in Resource Management. Systemic Practice and Action Research 21(6), 423-441. doi: 10.1007/s11213-008-9113-9
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Published as: Newig, Jens, Veronika Gaube, Karin Berkhoff, Kai Kaldrak, Britta Kastens, Juliana Lutz, Bianca Schlussmeier, Heidi
Adensam and Helmut Haberl. 2008. The Role of Formalisation, Participation and Context in the Success of Public Involvement
Mechanisms in Resource Management. Systemic Practice and Action Research 21(6), 423-441. doi: 10.1007/s11213-008-9113-9