Difference between revisions of "Guidance and methods for indicator selection and specification"

Revision as of 21:21, 1 May 2007

This is a guidance document for selecting and specifying indicators as a part of applying the Intarese method.

KTL/MNP (E. Kunseler, L. van Bree, M. van der Hoek, M. Pohjola, J. Tuomisto)

Introduction

Integrated risk assessment, as applied in the Intarese project, can be defined as the assessment of risks to human health from environmental stressors based on a ‘whole system’ approach. It thus endeavours to take account of all the main factors, links, effects and impacts relating to a defined issue or problem, and is deliberately more inclusive (less reductionist) than most traditional risk assessment procedures. (Briggs D, 16.05.06))

Key characteristics of integrated assessment are:

1. It is designed to assess complex policy-related issues and problems, in a more comprehensive and inclusive manner than that usually adopted by traditional risk assessment methods.
2. It takes a ‘full-chain’ approach – i.e. it explicitly attempts to define and assess all the important links between source and impact, in order to allow the determinants and consequences of risk to be tracked in either direction through the system (from source to impact, or from impact back to source).
3. It takes account of the additive, interactive and synergistic effects within this chain and uses assessment methods that allow these to be represented in a consistent and coherent way (i.e. without double-counting or exclusion of significant effects).
4. It presents results of the assessment as a linked set of policy-relevant ‘outcome indicators’.
5. It makes the best possible use of the available data and knowledge, whilst recognising the gaps and uncertainties that exist; it presents information on these uncertainties at all points in the chain. (Briggs D, 16.05.06)

The Intarese approach to risk assessment emphasizes on creation of causal linkages between the determinants and consequences in the integrated assessment process. The full chain approach includes interconnected variables which are the leading components. Causality if further discussed in section [no.] The full chain variables cover the source-impact chain, which is based on different frameworks developed from the pressure-state-response (PSR) concept originally proposed by the US-EPA (e.g. DPSIR, DPSEEA) and the source-receptor models widely used to represent the fate of pollutants in the environment. (Briggs D,16.05.06)

Need for guidance

At this project stage (18 months - May 2007), the assessment methodology is ready for application in policy assessment cases. Case studies have been selected and protocols for case study implementation are in process. The issue frameworks have been formulated and consequent full chain frameworks of the policy assessment case studies are being developed. This guidance document gives detailed information about development of the variables and indicators in the full chain framework. The guidance emphasizes on causality in the full-chain approach and the applicability of the indicators in relation to policy needs. The purpose of this guidance document is to provide practical and focused methodology for selection and specification of indicators. Main emphasis is on the formulation of criteria for indicator selection and specification and design of computational methods and user-friendly display. In the subsequent section, we first of all clarify the term indicator and the different perceptions towards the process of indicator development.

Approaches towards indicator development

The term indicator is a common but rather broad concept. In environment and health risk assessment, the term is widely used to estimate or model the risk of health exposure to an environmental pollutant or stressor. During this modelling process, we make use of proxy measures; approximate reflections of the complex reality. Proxies are used as inputs / elements of the assessment process, such as indicators of source activity to determine emissions. Indicators are also used to present and report the results of an assessment. Besides input or process indicators, also output or impact indicators are to be defined, such as DALYs or mean population exposures. For the latter type of indicator, the communication platform is highly important as well as the understandability of the computational method. Stakeholders such as policymakers and lay people are particularly interested in the assessment outcome. The outcome indicators may be designed for different users and for different purposes, including:

• Policy development or priority-setting
• Health impact assessment and monitoring
• Policy implementation or economic consequence assessment
• Public information and awareness rising or risk perception(WHO, 2002)

Independent of the conceptual interpretation of the term indicator, we can distinguish between three approaches towards indicator development. The distinctive feature of these approaches is the interpretation of the inherent objective of an indicator.

1. Indicators as individual components (WHO approach)
2. Indicators as policy deficit metrics (Leendert?)
3. Indicators as variables of specific interest representing all the main nodes and links that make up the source-impact chain (Jouni and David?)

Each of the approaches is clarified in terms of its inherent objective in integrated risk assessment.

Indicators as individual components

This approach creates indicators that are individual components in the overall assessment. Causal linkages between indicators are not explicitly defined. Computation methods and models as well as data requirements are principal attributes of each indicator. Instead of being part of risk assessment development, indicators can be selected and plugged in when their method specifications produce useful indicator values. Both input/process and outcome/imcpact indicators are available from earlier projects, such as WHO ECOEHIS and ENHIS.

WHO has identified different types of policy-relevant indicators which can be applied at different stages of the DPSEEA or risk assessment chain. In terms of policy relevance, exposure-side indicators and health-side indicators are of highest interest. These types cover the forward looking indicators of exposure (i.e. those that presage, and need to be linked to, a potential health effect) and the backward looking indicators of outcome or effect (i.e. those that imply, and need to be attributed to, an exposure or source). Exposure-side indicators are clearly relevant for policy, since they often provide the first indications of the potential for health risk, and the first evidence of the effects of intervention (since many policies are focused on the upper links in the source-impact chain). To be meaningful in the context of health risks, however, they must relate to factors with definable (or at least strongly plausible) links to health outcome. (Briggs D, 16.5.06) Dose-Response indicators are necessary for clarifying the exposure to health linkage. Moreover, the exposure-side indicators should linked back to its emissions and sources. Exposures can only be reduced when its sources or emission activities are known, therefore source or emission indicators should be introduced as a third type of policy-relevant indicators. Health-side (or impact) indicators represent the consequences of exposures in terms of health effect (e.g. mortality, morbidity, DALYs) or its further societal impacts (e.g. economic costs, quality of life). Again, to be meaningful in the context of the full-chain approach, they need to have an explicit link back to causal environmental exposures and risk factors. (Briggs D, 16.5.06)

A fifth type of indicator is the action or policy indicator. WHO developed this outcome indicator to assess the policy situation with regard to policy existence, implementation and enforcement. Qualitative information is classified in quantitative numbers in order to make country comparisons possible. The importance of these outcome indicators lies in their ability to express priorities for policy action. (WHO, ENHIS project)

Indicators as policy deficit metrics

[The text in this section has been taken from the EEA Technical report No 25, Environmental indicators: Typology and overview, EEA, Copenhagen,1999)].

A wide variety of environmental indicators is presently in use. These indicators reflect trends in the state of the environment and monitor the progress made in realising environmental policy targets. As such, environmental indicators have become indispensable to policy-makers. However, it is becoming more and more difficult for policy-makers to grab the relevance and meaning of the existing environmental indicators, given the number and diversity of indicators presently in use. And new sets of environmental indicators are still to be expected. Therefore, some means of structuring and analysing indicators and related environment/society inter-connections is needed.

For the purpose of this INTARESE indicator paper the European Environment Agency (EEA) indicator typology and the DPSIR framework (Driving forces, Pressure, State, Impact,Response) is used.

In relation to policy-making, environmental indicators are used for three major purposes:

1. to supply information on environmental problems, in order to enable policy-makers to value their seriousness; 2. to support policy development and priority setting, by identifying key factors that cause pressure on the environment; 3. to monitor the effects of policy responses.

In addition, environmental indicators may be used as a powerful tool to raise public awareness on environmental issues. Providing information on driving forces, impacts and policy responses, is a common strategy to strengthen public support for policy measures.

EEA Typology of Indicators Indicators can be classified into 4 simple groups which address the following questions: · ‘What is happening to the environment and to humans?’ (Type A or Descriptive Indicators) · ‘Does it matter?’ (Type B or Performance indicators) · ‘Are we improving?’ (Type C or Efficiency indicators) · ‘Are we on the whole better off?’ (Type D or Total Welfare indicators)

Descriptive indicators (Type A – What is happening to the environment and to humans?) Most sets of indicators presently used by nations and international bodies are based on the DPSIR-framework or a subset of it. These sets describe the actual situation with regard to the main environmental issues, such as climate change, acidification, toxic contamination and wastes in relation to the geographical levels at which these issues manifest themselves. With respect to environmental health, these indicators may also be specified with respect to (personal) (source-specific) exposure indicators and health effects indicators (## of people affected, YLL, DALY, or QUALY).

Performance indicators (Type B – Does it matter?) The indicators mentioned above all reflect the situation as it is, without reference to how the situation should be. In contrast, performance indicators compare (f)actual conditions with a specific set of reference conditions. They measure the ‘distance(s)’ between the current environmental situation and the desired situation (target): ‘distance to target’ assessment. Performance indicators are relevant if specific groups or institutions may be held accountable for changes in environmental pressures or states.

Most countries and international bodies currently develop performance indicators for monitoring their progress towards environmental targets. These performance indicators may refer to different kind of reference conditions/values, such as:

· national policy targets; · international policy targets, accepted by governments; · tentative approximations of sustainability levels.

The first and second type of reference conditions, the national policy targets and the internationally agreed targets, rarely reflect sustainability considerations as they are often compromises reached through (international) negotiation and subject to periodic review and modification. Up to now, only very limited experience exists with so-called sustainability indicators that relate to target levels of environmental quality set from the perspective of sustainable development (Sustainable Reference Values, or SRVs).

Performance indicators monitor the effect of policy measures. They indicate whether or not targets will be met, and communicate the need for additional measures.

Efficiency indicators (Type C – Are we improving?) It is important to note that some indicators express the relation between separate elements of the causal chain. Most relevant for policy-making are the indicators that relate environmental pressures to human activities. These indicators provide insight in the efficiency of products and processes. Efficiency in terms of the resources used, the emissions and waste generated per unit of desired output.

The environmental efficiency of a nation may be described in terms of the level of emissions and waste generated per unit of GDP. The energy efficiency of cars may be described as the volume of fuel used per person per mile travelled. Apart from efficiency indicators dealing with one variable only, also aggregated efficiency indicators have been constructed. The best-known aggregated efficiency indicator is the MIPS-indicator (not covered in this report). It is used to express the Material Intensity Per Service unit and is very useful to compare the efficiency of the various ways of performing a similar function.

Efficiency indicators present information that is important both from the environmental and the economic point of view. ‘Do more with less’ is not only a slogan of environmentalists. It is also a challenge to governments, industries and researchers to develop technologies that radically reduce the level of environmental and economic resources needed for performing societal functions. Since the world population is expected to grow substantially during the next decades, raising environmental efficiency may be the only option for preventing depletion of natural resources and controlling the level of pollution.

The relevance of these and other efficiency indicators is that they reflect whether or not society is improving the quality of its products and processes in terms of resources, emissions and waste per unit output.

Total welfare indicators (Type D – Are we on whole better off?) Some measure of total sustainability is needed in order to answer this question, for example, a kind of ‘Green GDP’, such as the Index of Sustainable Economic Welfare (ISEW). As these indicators are, however, currently outside of the EEA’s work programme, there are not further covered here.

MNP example on policy deficit indicators To illustrate policy deficit indicators used in various environmental themes, an example has been taken from the (annual) Environmental Balance report (2006) of the Netherlands Environmental Assessment Agency visualizing a simple table format, using different colours to show what the time trends and target achievement are.

Indicators as variables of specific interest

This approach starts from issue framing by translating the assessment steps into a set of variables (circles) and their causal relations (connecting arrows), representing the outline of the system to be assessed. The result of this is a (draft) causal chain description of the phenomena to be assessed, on a relatively high level of abstraction, representing the determinants across the chain as variables. At this point the variables do not necessarily need to be specified into any more detail than to have a name and to have some draft specification of its scope. Also the causal relations at this point need not be any more detailed than to just imply that a causal relation between certain variables exists.

Once the causality between stages in the assessment framework have been defined, the main nodes and links stand out. Key variables can be selected as indicators and further specified. Selected indicators should be internally coherent – i.e. they should have clear and definable relationships within the context of this chain. The idea behind the indicator selection, specification and use is to highlight the most important and/or significant parts of the source-impact chain which has been/is to be assessed. Indicator selection provides the bridge between the issue framework and the assessment process. The third approach could be referred to as developing indicators as a continuous process. The variable specifications including their outcome values and causal descriptions are iteratively improved throughout the course of the assessment process as the knowledge and understanding increases. The causal descriptions of variables influence the estimation of the output value with the aid of data, measurements and models and vice versa. Accordingly, also indicator selection is an iterative process. In order to make this process explicit, it is likely to be helpful to produce shadow versions of the issue and full chain frameworks, showing the indicators selection during different stages of the full chain development.

Causality in the full chain (requires major revision and elaboration)

⇤#(number): : Insert figure --Eva Kunseler 13:59, 30 April 2007 (EEST)

The variables of specific interest can be chosen among a set of variables (in line with the third approach to indicator development). If necessary, new indicator variables can be added to the description. This may be the case for example if a desired indicator is e.g. a ratio of two variable's result values, but this indicator is not relevant in estimating the outcome variables downstream in the causal chain.

Throughout the full chain, causality can be further improved as seen necessary by combining (too detailed level) variables into more general variables, dividing (too general level) variables into more detailed ones, adding needed variables to the chain, removing variables that turn out irrelevant, changing the causal links etc. For example, the air pollutant variable can be divided into specific pollutant variables, e.g. for NOx, PM2.5 /PM10, BS etc. Each of these pollutants has a different relation to the consequent health effect / impact variables.

A set of variables can be covered in one model which requires input and outcome indicators to be defined, while the process variables require less elaboration. Difference between an internal and external model ⇤#(number): : (elaborate) --Eva Kunseler 13:59, 30 April 2007 (EEST)

Selecting indicators

In line with the third approach to indicator development, the variables of specific interest can be chosen in relation to the purpose of the assessment and the needs of the intended users. In principle, any variable could be chosen as an indicator and the set of indicators could be composed of any types but should cover the steps in the full-chain description. In practice, the generally relevant types of indicators can be somewhat predefined and even some detailed indicators can be defined in relation to commonly existing purposes and user needs. This kind of generality is also helpful in bringing coherence between the assessments and their uses.

When selecting the indicators in the full chain framework, the application should be a leading consideration and result in mutually consistent indicators (over time, space and target group). WHO has for example developed children's environmental health indicators which measure the implementation of CEHAPE priority goals. (WHO, ENHIS project) Subsidiarity is important as well; information need to be collected at the most relevant level or for specific policy/management purposes. Detailed indicators for local level or specific purposes might feed into broader (core) indicators that can be used at higher policy level or for general public information. Moreover, the indicators need to be associated with a suite of methods to derive them and with methods and approaches to link the indicators across the causal chain. Also incorporation of available information from monitoring and surveillance systems on environmental stressors and health provide selection criteria for indicator development. (WHO, 2002 and Lebret E & Knol A, 2007)

Besides these principal criteria for indicator selection, which can be summarized as (i) relevance to users and acceptability, (ii) consistency, (iii) measurability there are several other issues to be taken into consideration. Indicators must be based on known and validated processes or principles; scientific credibility. Sensitivity and robustness are a precondition for indicators, since a change must be responded to while slight variations should be coped with. Moreover, the indicator must be understandable and user-friendly. (Briggs D, 2006)

WHO has selected as set of environmental health indicators based on these criteria and expert judgements, see http://www.euro.who.int/EHindicators. Other organisations are developing either environmental indicators, such as EEA (see: http://themes.eea.europa.eu/indicators/) or health indicators e.g. the European Community Health Indicators (ECHI). (⇤#(number): : Search for indicator selection guidance) --Eva Kunseler 13:59, 30 April 2007 (EEST)

Specifying indicators

In each type, the indicators may be expressed in different ways, depending on:

• Whether they are static (state, condition) or dynamic (process, flux) indicators;
• Whether they are expressed in quantitative (‘objective’) or qualitative (perception) measures;
• Whether or not they relate to a formal (and internal) reference level or target (performance indicators).(Briggs D, 16.5.06)

We suggest that all variables, and thus also all indicators, are specified using a fixed set of attributes. The reasoning behind is to secure coherence between variable/indicator specifications and to enhance efficiency of assessment work and re-usability of the outputs of assessment work. Moreover, it helps in ensuring that all the terms used in the assessment are consistent and explicit. Descriptions should cover the scope of each variable, methods/models used to compute or derive the variable, and the data (and associated data sources) on which these are based. Variables in this context may take different forms and serve different roles (often simultaneously). They may represent inputs to models (derived variables), interim steps in the calculation process (derived variables) and single or combined output values (indicators).We suggest a method for indicator development, including characteristics from both approaches towards indicator development as explained in the previous section.

Below is a suggested list of variable/indicator attributes. The list has been developed based on the several principles including, but not limited to, the following:

• Variables are the basic building blocks of risk assessments
• Everything in risk assessments is to be described as variables
• Risk assessments are causal-chain descriptions of (a chosen part) of reality
• All variables in a causal-chain description must be causally linked
  • Also the causal links are described within the variable specifications (definition:causality)
    • In a diagram representation arrows only state the existence of a causal relation, it does not specify the causality
• The risk assessment process proceeds iteratively through specifications and re-specifications of variables (and their causal relations)

Suggested Intarese variable/indicator attributes

1. Name
2. Scope
3. Description
   • Scale
   • Averaging period
   • References
4. Unit
5. Definition
   • Causality
   • Data
   • Formula
     • Variations and alternatives
6. Result
7. Discussion

Appendix: comparison of different approaches to specifying variables

Table. A comparison of attributes used in Intarese (suggestions), ENHIS indicators, pyrkilo method, and David's earlier version.