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Information needs as the basis for monitoring

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Information needs as the basis for .. monl torlng Routine monitoring provides the basic information for water management. Howevet; often there is a gap between the information a monitoring network provides and the information water management needs. Next to this, increasing knowledge of the complexity of processes in water systems has led to a growing demand for information. Nevertheless, budgets for monitoring networks are limited. This causes the need to provide the right information at a low cost. Therefore, in designing a monitoring network specifying the information needs is essential. What is needed is a method to cope with all different and sometimes conflicting aspects, leading to specified information needs for the monitoring network. To develop a suitable method for this purpose, some case-studies have been carried out. From these studies it was concluded that the method should incorporate .communication between information producers and information users, .insight in the organisations involved in producing and using information and their responsibilities in the process and .a structure defining what activities to perform at what stage. These elements have been worked out in a method for specification of information needs. The method comprises five steps: 1. Exploration, to mark out the project; 2. Tuning, to communicate and verify the starting points; 3. Elaboration, to come to detail; 4. Conclusion, to communicate and verify the results; and 5. Completion, to document the results and to plan following steps. The method is described in this papel:
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J. G. TIMMERMAN1 AND W. H. MULDER2
Information needs as the basis for
..
monl torlng
Routine monitoring provides the basic information for water management. Howevet; often there is a gap between the
information a monitoring network provides and the information water management needs. Next to this, increasing
knowledge of the complexity of processes in water systems has led to a growing demand for information. Nevertheless,
budgets for monitoring networks are limited. This causes the need to provide the right information at a low cost.
Therefore, in designing a monitoring network specifying the information needs is essential. What is needed is a method
to cope with all different and sometimes conflicting aspects, leading to specified information needs for the monitoring
network.
To develop a suitable method for this purpose, some case-studies have been carried out. From these studies it was
concluded that the method should incorporate
.communication between information producers and information users,
.insight in the organisations involved in producing and using information and their responsibilities in the process and
.a structure defining what activities to perform at what stage.
These elements have been worked out in a method for specification of information needs. The method comprises five
steps:
1. Exploration, to mark out the project;
2. Tuning, to communicate and verify the starting points;
3. Elaboration, to come to detail;
4. Conclusion, to communicate and verify the results; and
5. Completion, to document the results and to plan following steps.
The method is described in this papel:
INTRODUCTION effective monitoring programme is 'tailor-made.' And as the
body of the "information need" grows fatter or loses weight,
the monitoring programme should regularly be tailored to
keep a perfect fit [1].
The monitoring cycle shows the different steps that must
be defined to be able to specify all requirements for a
(chemical) monitoring system. Information for one step is
used to develop and define information for the next step. By
theoretically going through the monitoring cycle both
clockwise and counter-clockwise, all requirements and
limitations may be made explicit [6].
Monitoring without specification of information needs
prior to the actual network design will be a waste of money
[7]. In literature, the need for specification of information
needs is recognised [among others 2, 8 and 9] and attempts
For water management, proper information on the status
of water systems is indispensable [I]. Usually, routine
monitoring provides the larger part of the basic information.
An increasing knowledge of the complexity of processes in
water systems has led to a growing demand for information.
Next to this, the current wish for integrated water
management calls for interrelation of disciplines and the need
to integrate different types of monitoring. Nevertheless,
budgets for monitoring networks are limited. Often a gap
exists between the information a monitoring network
provides and the information (water) management needs [2].
Therefore, more attention should be given to monitoring
networks that provide the right information at a low cost.
Under the UN/ECE Convention on the Protection and
Use of Transboundary Watercourses and International Lakes
[3], among others, Guidelines on Water Quality Monitoring
and Assessment of Transboundary Rivers have been
developed [4]. One of the basic principles of the guidelines is
the monitoring cycle, specifying steps in elaborating a
monitoring network. The monitoring cycle is shown in
Figure I. In this cycle, monitoring is regarded as a sequence
of related activities that ultimately lead to the management of
relevant information [5]. The cycle represents the repeating
evaluation and adaptation of the monitoring network. An
Iln!ititutc filr Inland Watcr :\Ianagcmcnt and Wao;tc Watcr 'I'rcatmcnt
(RIZA), P() Ilox 17, 1!2(KI AA 1.cIY!itad, 'I'hc Ncthcrland!i.
2RWS Programmc Ollicc :\Ionitoring Stratcgy 2(I(KI+, PO Ilox 20')07,
25(KI i':X 'I'hc Haguc, 'l'hc Ncthcrland!i. Figure. The monitoring cycle [4]
41
Volume 2. Number 2. 1999
are made to offer starting points [among others 10, 11 and
12]. In this paper, a method is presented to specify
information needs. The method is based on literature,
experience and special studies. A number of pilot projects are
carried out to test and improve the method.
WHY SPECIFY INFORMATION NEEDS?
As stated above, the questions in water management
become increasingly complex. The complexity of the issues
calls for the reconciliation of disparate, often contradictory
information from many fields. However, unfortunately people
can handle only about three to seven (5 :t 2) different units of
information or thoughts at a time. This leads to the situation
where, as an estimate, 9()°/cJ of the effort in problem solving is
spent on [13]
.solving the wrong problem
.stating the problem so that it cannot be solved
.solving a solution
.stating problems too generally
.or trying to get agreement on the solution before
there is agreement on the problem.
Even if exaggerated, this suggests why water (quality)
monitoring suffers from a constant failure to establish
meaningful programme objectives [8] and it consequently
shows reasons for the existing of the "data-rich but
information-poor" syndrome [14].
The crux of problem-solving is problem definition. "The
problem definition ramifies throughout the problem-solving
process, reflecting values and assumptions, determining
strategies, and profoundly impacting upon the quality of
solutions" [13]. Therefore, to design a monitoring network so
that it provides the right information, the problem should be
stated as "what is the right information"? In other words:
"What is the information needed?" What is needed to solve
this problem is a framework for the specification of
information needs. Such a framework will be discussed in this
paper.
.Co1/l1/luniclI.(ion: Information producers should take
more interest in the problems information users are
involved in, while information users should try to
specify better what exact information is useful to
them. This can be achieved only by bringing both
groups together. What may seem obvious to
experts of a specific group may be unknown to
experts of another group. Information producers often
do not 'speak the same language' as information users
[15]. That is why it is so important that these groups
meet to make sure that all assumptions are made
explicit.
.In.ftitutionlll 1I.fpect.f: What organisations are
involved in producing and using information and what
are their responsibilities in the process. These
organisations have to be involved in the process of
specification of information needs to specify their
requirements for distinct steps in the monitoring
process. This information is essential to under-
stand what information should be and can be
produced.
.Structure: By dividing a process in well-defined
pieces, this process may be better managed. All pieces
together provide an overall structure, while
elaboration of each piece supports progress of the
process. The process of specification of information
needs is complex and therefore needs a structure
defining what activities to perform at what stage.
Visualising techniques, like diagrams, are essential
elements in such a structure. In this way, structure
provides 'externalised memory' [16], to be able to keep
track of the process and handle all different aspects at
the right time.
These elements have been worked out in a method for
specification of information needs. This year a project has
started to specify the information needs for management of
the national waters, on the basis of the recently finalised
Dutch national policy document on water management,
using this method. The goal of this project and other, smaller,
pilot projects is to start the general application of this method
in Rijkswaterstaat. Findings from these projects will be used
to improve the method.
HOW TO SPECIFY INFORMATION NEEDS?
METHOD FOR SPECIFICATION OF
INFORMATION NEEDS
Defining information needs involves asking many
questions until the right questions come up. These questions
should be specified further against the background of the
overall water management objectives and should consider the
requirements that result from preceding and following steps
in the information cycle. Most questions will be related to
specific functions or uses of the water under consideration.
However, different functions and uses may have conflicting
requirements to fulfil. A method is needed to cope with all
different and sometimes conflicting aspects, leading to
specified information needs for the monitoring network.
"Monitoring Strategy 2000+" is a programme of the
Dutch Directorate General of Public Works and Water
Management (in Dutch: Rijkswaterstaat) to innovate the
measuring sector. This innovation is done by discussing the
design of the future organisation, investigating information
needs and by implementing new technologies like remote
sensing and models in operational practice. In this
programme, a methodology has been developed to specify
information needs. Three case-studies have been carried
out to develop the method. From these studies it was
concluded that the method should incorporate the next three
elements:
The method consists of a five-step plan, all steps being
interrelated. The connection between the steps is shown in
Figure 2. All steps should be filled in, starting from the left.
The Figure symbolises the initial diverging character of the
process that at a certain point should converge into a coherent
plan.
European Water Management
42
Step I: Exploration
In the first step a survey is carried out to mark out the
project. In this step, the focus is on 'institutional aspects'.
This first step covers three items:
.Starting point.f: What will be the subject of the study?
This may be for example policy aims. Next to this it
should be stated if the resulting information will be
used for instance for policy evaluation, for policy
preparation or maybe for operational purposes. In
connection with this, the time scale should be
determined, for instance long-term policy or short-
term operational management.
.I~fi)rnlatilln U.fer.f: Who will be using the information?
Information users should specify what information
they need and what the use of this information is.
There may be a wide variety of information users.
Therefore, the focus should be on those information
users that can determine what information should be
collected, usually because they provide funding.
.Prllce.f.f chain: What organisations/ departments/
people are involved in producing and using the
information? Next to knowing the information users,
knowing the producers of the information is
important. These are the people that can determine
whether all requirements for information production
can be met. By stating the organisations or people
involved in all steps of the monitoring cycle, the
process chain may be made explicit.
Step 2: Tuning
To verify the starting points as stated in step 1,
communication should take place with all involved, both
information users and information producers. Because all
involved should have a general idea of each other's problems,
this step should be carried out as a workshop. In this step,
'communication' is the keyword.
Step 3: Elaboration
In this step, emphasis is on 'structure.' The information
need should be specified. Keeping track of the problem is
important. Therefore, 'externalising memory' by visualising
the problem is useful [16]. An important structure to visualise
information need is the 'information need hierarchy.' Going
from general to very detailed, a hierarchy in information need
is described. Starting with a general concern, through
specifying different aspects of this concern a more detailed
information need can be developed. Bernstein [10] describes
the following aspects:
I. Public concerns2.
Assessmentissues
3. Policy goals
4. Scientific and management monitoring objectives
5. Potential measurements
In his example he states the public concern: 'How safe is
it to swim in the bay?' This is translated into assessment
issues, like the health risks from swimming and surfing. The
policy goals are to protect the public from health risks. From
this, scientific and management monitoring objectives can be
stated, like using a suite of effective microbial indicators and
communicating the information rapidly to the public.
Potential measurements in this case may be beach warnings
and closings.
In this paper a more generic method is suggested which
includes the following aspects:
I. State the functions or uses of the water systems as related
to the general concern (for example the policy aim as
stated in step I: exploration);
2. For each function or use, state the issues at hand. This may
be summarised in a 'function and issue table' (Figure 3);
3. Define the problems related to the function -issue
combination;
4. List existing or potential measures for these problems;
5. Specify exactly what information is needed to deal with
the problems and measures and what this information will
be used for (for instance to indicate a trend or as input for
a model).
The result of this procedure is an information needs
hierarchy. An example of an information needs hierarchy is
shown in Figure 4.
The information need hierarchy is developed through a
stepwise refinement of the concerns at hand. It should be
further developed until the individual parameters of interest
are stated. From combining different concerns, duplication of
parameters may occur. Through the scheme it may be
obvious that parameters that become obsolete because of
disappearing of a concern may still be relevant through
another concern.
By going upward in the hierarchy and choosing another
viewpoint, another set of parameters may be chosen, without
changing the initial concern. In this way for instance, a
parameter-oriented monitoring network can be altered into a
more effect-oriented network.
The information needs hierarchy also supports priority
setting. By prioritising issues on a high level, the priority
parameters can be determined. Prioritisation can be done on
each level in the hierarchy and even over different levels.
The information need and the type of information they
use should be assigned to information users, together with an
indication of the desired accuracy of the information that is
needed.
An overview of the existing information network will be
the basis for evaluating what part of the new information need
is covered by the network and what changes will be necessary.
Also prerequisites, like available finances and capacity, and
also legal obligations have to be inventoried.
Based on this information, the desired information
Figure 3. Function and issue table. V = function that is conflicting with specific pressures linked with an issue; VV = more strongly conflicting
[17]
Volume 2, Number 2, 1999 43
Public concern: How safe is it to swim in the bay?
Health risks from swimming and surfing
Protect the public from health risks
Ensure that public health standards are met
L Bight-wide water quality measurements
Provide information on sv..;mming conditions
L Beach warnings and closings
~ Reduce pollutant inputs
L Eliminate illegal discharges
L Measurements on sewage spills
Figure 4. Information needs hierarchy (after [10])
network may be formulated. The information need now sets
the path for the design of the information strategy. development of the information needs hierarchy is the key-
factor in specification of information needs.
The method appears to be a genuine tool to improve the
specification of information needs and as a result lead to a
better fit of monitoring networks. An essential factor is that
the method provides a framework for communication.
Step 4: C.onclusion
In this step, emphasis is again on 'communication.' The
"concept information network" should now be agreed upon
by all involved. To do this, the people of the first workshop
should be brought together to discuss and adapt results. ACKNOWLEDGEMENTS
Step 5: Completion
Finally, results of the process and agreements of this
workshop have to be documented. The result is a 'blueprint'
for the new information network. Also, the result of the
process is needed to evaluate if the information needs as
specified are produced.
Many thanks to Dr ]anneke Ottens and the unknown
referee for their valuable comments to the manuscript.
Special thanks to the members of the WAT-group of
Monitoring Strategy 2000+ for their contributions in the
development of the method.
REFERENCES
CONCLUSION
2
4
The method comprises five sequential steps. However,
these steps provide a structure and not all elements will be
completed sequentially. Sometimes returning to previous
steps will be inevitable. Nevertheless, three elements in this
method are essential: structure as a mean to keep track of the
activities, providing the right information at the right time,
communication as a way to ensure the right decisions are
made and to assure commitment of those involved, and
institutional aspects as a way to ensure the involvement of the
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First results from application of the method in the pilot
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a better link of information to policy in a more integrated
manner, thus better covering policy items, becomes possible.
The information needs hierarchy provides a tool to
maintain a good perception of the way the information need
has been developed. It provides an overview of the choices
made, it supports changes in information needs and is a basis
for prioritising monitoring effort. In this way the
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Volume 2, Number 2, 1999
... The method consists of a five-step plan, all steps being interrelated: 1) exploration, to mark out the project; 2) tuning, to communicate and verify the starting points; 3) elaboration, to come to detail; 4) conclusion, to communicate and verify the results; and 5) completion, to document the results and to plan subsequent steps. The method is further described in Timmerman and Mulder (1999). Although the method provided a good basis for linking policy to information production, experience in using the method showed that the major obstacle was to define the information needs in such a way that a monitoring network could be defined from it. ...
... Figure 6.2 The five-step method for specification of information needs (Timmerman and Mulder 1999) ...
Thesis
Full-text available
Water is een essentiële maar schaarse natuurlijke hulpbron en is cruciaal voor de samenleving. Goede besluitvorming is in het watermanagement nodig om deze hulpbron op een duurzame wijze te beheren en informatie is nodig om deze besluitvorming te ondersteunen. Water monitoring heeft zich in de loop van de tijd ontwikkeld van het meten van een paar eenvoudige parameters tot een complex proces waarin een groot aantal verschillende parameters in verschillende frequenties en op verschillende locaties gemeten worden. De informatie die door monitoring wordt verzameld voldoet helaas niet altijd aan de behoeften van beleidsmakers
...  Interviews with key persons within CVC, stakeholders and key partners to identify their operational information needs and the possibilities for CVC to improve their communication with stakeholders;  Workshops to specify information needs following the rugby ball methodology ( Figure 4) and function-issue matrix (see Table 1);  Interactive sessions (role play calamity on the Cauca River) and plenary discussions;  Presentations on a variety of topics, including information needs, CVC's monitoring network, mandates and roles of Regional Water Authorities (RWAs) and Water Management Information Centres in the Netherlands, FEWS-IDEAM, FEWS-ESCACES, InfoSequía, dashboard mock-ups, HydroNET, and stakeholder participation for the development of groundwater policies;  Questionnaires on (i) the decision-making process (steps, nature, sources of information); (ii) information needs (related to the function-issue matrix); and (iii) indicators/parameters (visualization of HERMANA);  Field visits; and  Review of policy documents. (Timmerman & Mulder, 1999). ...
Conference Paper
This paper presents the developments of a tool for integrated water management (Herramienta para el Manejo Integral del Agua – HERMANA). HERMANA combines: real-time meteorological, hydrological, and water quality data and forecasts; information from an institutional database; surface water and groundwater models; and, drought indicators based on satellite data into a web-based platform. Together, these tools provide the basis to plan for integrated, operational water management. To optimize the usability of these tools, we implemented an intensive co-design framework that consisted of developing a number of use cases in collaboration with the end user, the Corporación Autónoma Regional del Valle del Cauca (CVC). These use cases provide CVC with a step-wise approach to deal with a number of water management issues. Results show the impact that an integrated operational tool can have at a number of levels within the organization by making the water resources information accessible and visible in a tailored way. However, the largest hurdle is not the integration of data systems and models, which is usually technically feasible, but rather the sustainable implementation and integration into the decision-making process of a water management authority’s organization. Our co-design approach included numerous interviews and workshops with CVC’s staff to better understand the decision-making process within the organization, the requisite data and information, how the data and information are used, and how it can be presented in such a way that it facilitates decision-making processes. Outcomes from these discussions and a roadmap for future implementation are presented.
... By prioritizing issues on a high level, the priority determinands are derived. Prioritization helps in choosing what part of the information needs must be realized given the limitations in capacity and budgets [314] . ...
Book
This book provides the necessary elements to determine exactly what information should be collected to make the collected information relevant for policy makers. It highlights the dissatisfaction of information users about the information they get and the reasons for this dissatisfaction. It also discusses general issues around the role and use of information in policy making. The book then describes how to develop a full understanding of the policy makers’ information needs and will describe how policy makers can be included in the process. Finally, the book describes how the results from this process are input for the information production process.
... In practice, the pilot projects have ended at the stage of recommending improvements, because in order to implement the recommendations, important decisions about institutional responsibilities and additional funding are required. Phases 1 and 2 in Table 2 can, therefore, be considered together as preparatory steps before the actual implementation of transboundary monitoring and assessment in Phase 3, which becomes a continuous process (the monitoring cycle, Timmerman and Mulder, 1999), with regular feedback loops and evaluation and design modification processes to keep abreast of changing functions, uses, issues, legislative requirements and funding availability. ...
... The work programme for the pilot projects commenced in 1997, and the main phases and activities that were originally anticipated for each pilot project were described by Roncak et al (1997) and are shown inTable 2. In practice, the pilot projects have ended at the stage of recommending improvements, because in order to implement the recommendations, important decisions about institutional responsibilities and additional funding are required. Phases 1 and 2 inTable 2 can, therefore, be considered together as preparatory steps before the actual implementation of transboundary monitoring and assessment in Phase 3, which becomes a continuous process (the monitoring cycle, Timmerman and Mulder, 1999), with regular feedback loops and evaluation and design modification processes to keep abreast of changing functions, uses, issues, legislative requirements and funding availability. ...
... By working systematically, with the use of a few simple questions and schemes a person can give an extensive view of his/her information needs. This idea has been worked out in a methodology that allows the process of specifying information needs to be managed and that provides the questions and schemes needed Timmerman and Mulder 1999). Essentially, this methodology focuses on the fundamental objectives for the water body. ...
... It comprises five steps: 1) Exploration, to mark out the project; 2) Tuning, to communicate and verify the starting points; 3) Elaboration, to come to detail; 4) Conclusion, to communicate and verify the results; and 5) Completion, to document the results and to plan following steps. Major issues for this method are insight in the organizations involved in producing and using information and their responsibilities in the process, which is elaborated in the step 1: Elaboration, and the communication between information users and information producers in the steps 2: Tuning and 4: Conclusion (Timmerman and Mulder 1999). The next step in the monitoring cycle is elaboration of the monitoring strategy, which is needed to make monitoring efficient. ...
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Authors work as senior projectleaders at RIZA at the Department of Information and Measurement technologies and are involved in the Dutch national inland water quality and quantity monitoring. They are also involved in the development of guidelines for river water monitoring under the Helsinki 1992 Convention on the Protection and Use of Transboundary Watercourses and International Lakes of the United nations Economic Commission for Europe. In their position, they have contributed to the development of the concepts and ideas in the various projects, as described in this paper. Abstract Various initiatives in Europe in the 1990's have led to a working concept in providing information for water management; tailor-made monitoring. This concept comprises providing accountable and cost-effective information that supports water management action. The concept has been thoroughly discussed and tested and has proven to be a valuable addition to monitoring practices in Europe. Major elements of the concept are: 1) water management analysis, to identify the major issues in a water body; 2) inventories and surveys, to provide additional information to the water management analysis; 3) evaluation of legislation, to find if the aims of legislation are fulfilled; and 4) specification of information needs, as the basic step for the development of a monitoring network. The paper discusses the backgrounds of the tailor-made concept and the monitoring practices in Europe.
... The first two steps have to restrain the maximum scope of the project. Towards the end of the project the scope has to converge to a comprehensive overview (Timmerman and Mulder 1999). The steps in the project, following the steps of the method, were: 1. Exploration, to mark out the project. ...
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Acceptation of the fourth national policy document on water management by the Dutch parliament was the starting point for inventorying the information needs to evaluate this new policy. The project was carried out along the lines of the five-step method for specification of information needs, and was restricted to the information needs of the Dutch Directorate General of Public Works and Water Management. Apart from an overview of information needs on a high level of abstraction, some conclusions were drawn on the future changes in monitoring. The conclusions were: 1) 'policy-monitoring' is needed to enable to evaluate progress in policy measures; 2) spatial planning should be based on hydrological conditions; 3) expansion of transboundary co-operation in water management is inevitable; 4) a limited number of indicators for water policy evaluation should be developed; and 5) monitoring networks should be made more flexible. These future developments are subject to study in the next few years.
Article
A 3-D cloud-resolving model including an explicit aerosol module is used to examine the influence of a range of hygroscopic (CCN) and hydrophobic (IN) aerosol concentrations on the development of a mid-latitude, continental deep convective cloud. The model reproduces a response to changes in CCN which is in agreement with previous studies of continental convection, i.e. lower precipitation rates and a later onset of deep convection for high CCN concentrations. However, the response is non-linear and for low increments of CCN, coalescence and graupel formation becomes more efficient, which increases the total precipitation, i.e. a response similar to what has been obtained for oceanic deep convection. This result indicates the importance of using a range of CCN concentrations when examining aerosol influence on deep convection. The simulations show that an increased IN concentration has a substantial influence on the convective cloud development. Higher IN concentrations generally result in higher updraught velocities, a prolonged precipitation event and larger total precipitation amounts. The radiative forcing exerted by the cloud is determined by the anvil extent and ice crystal size. The anvil area is linked to the average updraught velocity which in turn is found to be correlated with the IN concentration. Homogeneously nucleated ice crystals dominate the total anvil ice mass formed, but heterogeneously formed ice crystals may significantly alter the homogeneous freezing process. For the simulated case, a key parameter for determining whether the number of homogeneously nucleated ice crystals will decrease or increase with increasing IN concentration is the initial updraught velocity. This dependence makes the results sensitive to the amount of heterogeneously formed ice crystals. Copyright © 2007 Royal Meteorological Society
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We present a planning framework that structures thelarge amount of interrelated information involved indeveloping regional monitoring programs. By regionalwe mean programs that recognize the importance ofprocesses that occur on larger geographic scales andthat cut across more than one ecosystem component. Theframework helps visualize functional relationshipsamong qualitative ingredients such as public concernsand more concrete details such as individual dataelements. It portrays the flow of information amongthe components of a regional program and ties eachaspect of the program to management decision-makingneeds. This makes it easier, during the planningprocess, to ensure that monitoring will actuallyproduce useful information. Further, the frameworksnovel, graphically oriented, and readily accessibleformat makes key information equally available to thewide range of participants (regulators, scientists,managers, public) whose input and support arenecessary for program success.
Article
This keynote paper addresses four rhetorical questions regarding water quality monitoring which are paramount in formulating network-design strategies. These consist of (1) why, (2) how, and (3) for whom do we collect monitoring data, and (4) how do we evaluate monitoring-programme effectiveness in considering future information needs? Aspects of these rhetorical issues are discussed in this keynote paper, along with some recommended guidelines for setting of goals and objectives, specifying network-design functions, identifying information users, and anticipating future monitoring perspectives. The paper's intent is to focus on topics relevant to deliberations resulting from technical papers presented at the Symposium on Monitoring to Detect Changes in Water Quality Series, Budapest, July 1986.
Article
Water quality monitoring conducted routinely over time at fixed sites has been a part of most water quality management efforts for many years. It has been assumed that such monitoring plays a major role in management. However, the lack of routine data analysis, and reporting of information derived from such analysis, points up the fact that the exact nature of the role of routine, fixed-station monitoring is poorly defined. There is a need to very clearly define this role in the design of such systems if routine monitoring is to efficiently and effectively meet the information expectations placed on it. Design of routine monitoring systems will therefore have to consider not only the where, what, and when of sampling, but also why. A framework for including the “why” of monitoring in the design process is proposed and experience with using the framework in New Zealand is discussed.
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The specter of environmental calamity calls for the best efforts of an involved public. Ironically, the way people understand the issues all too often serves to discourage and frustrate rather than motivate them to action. This article draws from problem-solving perspectives offered by cognitive psychology and conflict management to examine a framework for thinking about environmental problems that promises to help rather than hinder efforts to address them. Problem-framing emphasizes focusing on the problem definition. Since how one defines a problem determines one's understanding of and approach to that problem, being able to redefine or reframe a problem and to explore the “problem space” can help broaden the range of alternatives and solutions examined. Problem-framing incorporates a cognitive perspective on how people respond to information. It explains why an emphasis on problem definition is not part of people's typical approach to problems. It recognizes the importance of structure and of having ways to organize that information on one's problem-solving effort. Finally, problem-framing draws on both cognitive psychology and conflict management for strategies to manage information and to create a problem-solving environment that not only encourages participation but can yield better approaches to our environmental problems.
Demand for information as the basis for groundwater monitoring strategies. Pages 134 -144
  • M J Van Bracht
12 Van Bracht, M. J., 1994. Demand for information as the basis for groundwater monitoring strategies. Pages 134 -144 in: Adriaanse, M., J. van de Kraats, P. G. Stoks and R. C. Ward (Eds.), Proceedings of the international workshop Monitoring Tailor-made, Beekbergen, The Netherlands.
Information systems. Pages 245 -274 in: R. Helmer and I Water pollution control; a guide to the use of water quality management principles
  • M Adriaanse
  • P Lindgaard-Jergensen
Adriaanse, M. and P. Lindgaard-Jergensen, 1997. Information systems. Pages 245 -274 in: R. Helmer and I. Hespanol (Eds.) Water pollution control; a guide to the use of water quality management principles. UNEP, E&FN Spon, London, UK. 9
Conclusions and recommendations. Pages 401 -403
  • A B Van Luin
  • J J Ottens
Van Luin, A. B. and J. J. Ottens. 1997. Conclusions and recommendations. Pages 401 -403 in: J. J. Ottens, E A. M.