In this series, I explore the world of environmental indicators. In the journey from a polluting, carbon-intensive world to one with reduced emissions and protected nature, indicators point us to how progress is measured, what is happening, the direction of change, and whether policies are working.
Before discussing the wide world of environmental indicators, we must know what an indicator is. Here, I use widely known terminologies and seminal literature to clarify.
A weight loss journey is exactly that – loss of weight. In this case, the unit of measure is “mass” or “weight” measured in kilograms, pounds, stones. In this weight loss journey, we look at the metric “mass in kg” and track it from a starting point to a predicted future date, let’s say 1 year, i.e. N + 1, from Weight W to a new weight W-10. We also need a purpose and boundary to follow this decision and what is it tracking. As the decision maker, you decide the parameters by which you follow this change over time. You decide if you stop when you reach your goal or follow it over the whole 1 year, make changes, and so on.
Now, when the journey changes from weight loss example to “reducing global carbon emissions”, we go on a different journey. In this article, I break down the basics of indicator science.
1. Conceptual Foundations: Unit, Metric, Indicator, KPI
Unit – The measurement scale (e.g., tonnes, hectares, %, NOK)
Metric – A quantified measurement using a unit (e.g., tonnes of CO₂ emitted)
Indicator – A metric (or combination of metrics) interpreted within a defined purpose and boundary to inform a decision
KPI (Key Performance Indicator) – A strategically selected indicator tied explicitly to a goal or target and used to track performance
An indicator is not just a number. It is a decision tool.
A metric can be purely descriptive without a defined purpose and boundary. It becomes an indicator when it answers questions relevant to governance, strategy or policy. Questions to ask of a metric:
What decision is this informing?
What boundaries are assumed?
What does it exclude?
What progress does it measure?
When it moves from being a number (e.g. kilogram or tonnes of CO2) to representing change over time (tonnes of CO2 from 2020 to 2024), it starts to function as an indicator.
2. The purpose and boundary of an indicator
Indicators exist to simplify complexity. They remove layers of environmental complexity to small and often easy to comprehend ideas. When removing the unnecessary complexity, the nuance is reduced, and the indicator risks becoming oversimplified. To prevent this from occurring
The purpose of measurement is defined
The system boundary is explicit
The relationship to decisionmaking is clear and well defined
Within corporate environments, sustainability indicators like carbon emissions link to strategies and KPIs. These are also discussed in relation to economic and profitability outcomes in efficiency or risk management terms. ESG reporting must have demonstrated value – reduced carbon emissions, improved water quality, restored habitat, reduced exposure to human rights violations, and so on. These show movement towards targets, which depend on resource allocation.
Indicators internally support
Policy development
Identification of environmental drivers and pressures (e.g. increased water stress in a region with drought)
Monitoring of policy efficacy
Public health and awareness
Indicators are thus governance instruments. They structure attention and shape action.
3. The DPSIR Framework – another framework?
A common conceptual structure for environmental indicators used by the EEA is the DPSIR framework. See Fig.1.
D – Drivers (economic sectors, demographic changes)
P – Pressures (emissions, land-use change, resource extraction)
S – State (environmental condition)
I – Impacts (effects on ecosystems or human well-being)
R – Responses (policy, mitigation, adaptation measures)
DPSIR organizes indicators along causal chains. It links human activity to environmental outcomes and policy responses.
Importantly, the DPSIR framework is not merely classificatory. It encourages causal thinking:

Drivers create pressures
Pressures alter state
State changes generate impacts
Impacts trigger societal responses
This causal logic is crucial and is what drives indicator selection.
4. Types of Indicators
Indicators can serve different functions:
Descriptive (Type A) – Describe drivers, pressures, states, impacts, responses.
Performance (Type B) – Measure progress toward a defined target.
Efficiency (Type C) – Measure output relative to input.
Welfare (Type D) – Reflect broader societal well-being.
Each type answers different governance questions.
5. Indicator choice depends on Purpose
If the objective is:
To understand how serious a problem is → Use State or Impact indicators. State: % of natural habitat in “good ecological condition”, Impact: Number of threatened species affected by operations
To understand how to control or influence a situation → Use Pressure or Response indicators. (Pressure: Area of land converted per year, volume of groundwater extracted. Response: area of habitat restored, volume of water recycled)
To track structural economic trends → Use Driver indicators
At national or global scales, there is a tendency to rely on driver or pressure indicators due to data availability. However, this may obscure ecological condition (state) or consequences (impact). For instance, a reduction in fertilizer use does not automatically mean improved river health.
6. Indicator Selection: The Core Problem
The literature (e.g., Niemeijer & de Groot) identifies a major weakness in environmental reporting, i.e. insufficient rigor in selecting indicators, and little to no documentation of why other indicators were excluded.
Indicators are often selected based on historical practice, regulatory requirements or expert judgment, but not necessarily to answer the clearly defined environmental question. This risks making the indicator selection process less transparent.
Common shortcomings include:
No explanation of why a particular constellation of indicators was chosen.
No documentation of why certain indicators were rejected.
Lack of transparency in methodological reasoning.
Weak articulation of causal linkages.
This is not a minor issue. Indicator selection determines what becomes visible—and therefore governable. Without explicit reasoning, imbalances can arise in what is measured and what is overlooked.
Niemeijer and de Groot illustrate this by comparing two studies – one from OECD and the other from EEA. Despite similarities in mandates, institutional structures and subject matter, the two organisations chose different indicators that measured the same phenomenon: ozone depletion.
Niemeijer and De Groot have explained that this could be due to different “frames of reference”, but what was lacking in both studies was a clearly documented section articulating the logic behind indicator selection methodology.
In their paper, the authors call for a more systematic and structured methodology to maintain consistency and repeatability. Their approach, which they refer to as a causal network methodology and its implications for choosing environmental indicators will be explored in the next article.
7. Key Takeaways
That is the foundation for building serious environmental indicator architecture —whether at policy, national, or corporate level.
References:
Environmental Indicators: Typology and Review, Technical report 25/1999, Environmental indicators: Typology and overview | Publications | European Environment Agency (EEA)
David Niemeijer, Rudof S. de Groot, A conceptual framework for selecting environmental indicator sets, Ecological Indicators, Volume 8, Issue 1, 2008, Pages 14-25, ISSN 1470-160X https://doi.org/10.1016/j.ecolind.2006.11.012
In this series, I explore the world of environmental indicators. In the journey from a polluting, carbon-intensive world to one with reduced emissions and protected nature, indicators point us to how progress is measured, what is happening, the direction of change, and whether policies are working.
Before discussing the wide world of environmental indicators, we must know what an indicator is. Here, I use widely known terminologies and seminal literature to clarify.
A weight loss journey is exactly that – loss of weight. In this case, the unit of measure is “mass” or “weight” measured in kilograms, pounds, stones. In this weight loss journey, we look at the metric “mass in kg” and track it from a starting point to a predicted future date, let’s say 1 year, i.e. N + 1, from Weight W to a new weight W-10. We also need a purpose and boundary to follow this decision and what is it tracking. As the decision maker, you decide the parameters by which you follow this change over time. You decide if you stop when you reach your goal or follow it over the whole 1 year, make changes, and so on.
Now, when the journey changes from weight loss example to “reducing global carbon emissions”, we go on a different journey. In this article, I break down the basics of indicator science.
1. Conceptual Foundations: Unit, Metric, Indicator, KPI
Unit – The measurement scale (e.g., tonnes, hectares, %, NOK)
Metric – A quantified measurement using a unit (e.g., tonnes of CO₂ emitted)
Indicator – A metric (or combination of metrics) interpreted within a defined purpose and boundary to inform a decision
KPI (Key Performance Indicator) – A strategically selected indicator tied explicitly to a goal or target and used to track performance
An indicator is not just a number. It is a decision tool.
A metric can be purely descriptive without a defined purpose and boundary. It becomes an indicator when it answers questions relevant to governance, strategy or policy. Questions to ask of a metric:
What decision is this informing?
What boundaries are assumed?
What does it exclude?
What progress does it measure?
When it moves from being a number (e.g. kilogram or tonnes of CO2) to representing change over time (tonnes of CO2 from 2020 to 2024), it starts to function as an indicator.
2. The purpose and boundary of an indicator
Indicators exist to simplify complexity. They remove layers of environmental complexity to small and often easy to comprehend ideas. When removing the unnecessary complexity, the nuance is reduced, and the indicator risks becoming oversimplified. To prevent this from occurring
The purpose of measurement is defined
The system boundary is explicit
The relationship to decisionmaking is clear and well defined
Within corporate environments, sustainability indicators like carbon emissions link to strategies and KPIs. These are also discussed in relation to economic and profitability outcomes in efficiency or risk management terms. ESG reporting must have demonstrated value – reduced carbon emissions, improved water quality, restored habitat, reduced exposure to human rights violations, and so on. These show movement towards targets, which depend on resource allocation.
Indicators internally support
Policy development
Identification of environmental drivers and pressures (e.g. increased water stress in a region with drought)
Monitoring of policy efficacy
Public health and awareness
Indicators are thus governance instruments. They structure attention and shape action.
3. The DPSIR Framework – another framework?
A common conceptual structure for environmental indicators used by the EEA is the DPSIR framework. See Fig.1.
D – Drivers (economic sectors, demographic changes)
P – Pressures (emissions, land-use change, resource extraction)
S – State (environmental condition)
I – Impacts (effects on ecosystems or human well-being)
R – Responses (policy, mitigation, adaptation measures)
DPSIR organizes indicators along causal chains. It links human activity to environmental outcomes and policy responses.
Importantly, the DPSIR framework is not merely classificatory. It encourages causal thinking:

Drivers create pressures
Pressures alter state
State changes generate impacts
Impacts trigger societal responses
This causal logic is crucial and is what drives indicator selection.
4. Types of Indicators
Indicators can serve different functions:
Descriptive (Type A) – Describe drivers, pressures, states, impacts, responses.
Performance (Type B) – Measure progress toward a defined target.
Efficiency (Type C) – Measure output relative to input.
Welfare (Type D) – Reflect broader societal well-being.
Each type answers different governance questions.
5. Indicator choice depends on Purpose
If the objective is:
To understand how serious a problem is → Use State or Impact indicators. State: % of natural habitat in “good ecological condition”, Impact: Number of threatened species affected by operations
To understand how to control or influence a situation → Use Pressure or Response indicators. (Pressure: Area of land converted per year, volume of groundwater extracted. Response: area of habitat restored, volume of water recycled)
To track structural economic trends → Use Driver indicators
At national or global scales, there is a tendency to rely on driver or pressure indicators due to data availability. However, this may obscure ecological condition (state) or consequences (impact). For instance, a reduction in fertilizer use does not automatically mean improved river health.
6. Indicator Selection: The Core Problem
The literature (e.g., Niemeijer & de Groot) identifies a major weakness in environmental reporting, i.e. insufficient rigor in selecting indicators, and little to no documentation of why other indicators were excluded.
Indicators are often selected based on historical practice, regulatory requirements or expert judgment, but not necessarily to answer the clearly defined environmental question. This risks making the indicator selection process less transparent.
Common shortcomings include:
No explanation of why a particular constellation of indicators was chosen.
No documentation of why certain indicators were rejected.
Lack of transparency in methodological reasoning.
Weak articulation of causal linkages.
This is not a minor issue. Indicator selection determines what becomes visible—and therefore governable. Without explicit reasoning, imbalances can arise in what is measured and what is overlooked.
Niemeijer and de Groot illustrate this by comparing two studies – one from OECD and the other from EEA. Despite similarities in mandates, institutional structures and subject matter, the two organisations chose different indicators that measured the same phenomenon: ozone depletion.
Niemeijer and De Groot have explained that this could be due to different “frames of reference”, but what was lacking in both studies was a clearly documented section articulating the logic behind indicator selection methodology.
In their paper, the authors call for a more systematic and structured methodology to maintain consistency and repeatability. Their approach, which they refer to as a causal network methodology and its implications for choosing environmental indicators will be explored in the next article.
7. Key Takeaways
That is the foundation for building serious environmental indicator architecture —whether at policy, national, or corporate level.
References:
Environmental Indicators: Typology and Review, Technical report 25/1999, Environmental indicators: Typology and overview | Publications | European Environment Agency (EEA)
David Niemeijer, Rudof S. de Groot, A conceptual framework for selecting environmental indicator sets, Ecological Indicators, Volume 8, Issue 1, 2008, Pages 14-25, ISSN 1470-160X https://doi.org/10.1016/j.ecolind.2006.11.012
In Part 1, we explored a basic but essential question – What is an indicator? We introduced the idea of the causal chain as a starting point for thinking about indicators and capturing cause-effect relationships in environmental systems.
“Indicators are decision tools that exist to simplify complexity.”
In this article, we take a step deeper, exploring the Causal Network concept, as described by Niemeijer and de Groot (2006). The causal network creates a system for choosing indicators, clarifies what indicators represent, and guides the analysis of complex environmental systems.
The causal network sets an explicit request at the outset. Mapping the processes that shape the environmental issue that is particular to the organisation. Once the whole system is mapped, indicator selection becomes more purposeful, answering the question that is based on the scope of the study.
Purpose of environmental indicators
Environmental indicators reveal trends or phenomena that are not immediately detectable. They simplify complex ecological processes into signals that can be monitored and interpreted over time.
Dale and Beyler (2001) describe indicators as tools that capture aspects of ecological systems while remaining practical for monitoring and management.
Dale and Beyeler are of the opinion that indicator selection should be guided by the concept of ecological integrity. Imagine seeing it as a hierarchy
and that indicators should ideally capture processes across hierarchies to reflect structural, functional and composition of ecosystems.
Ecological indicators, which are indicators specifically representing ecosystems should do the following, according to Dale and Beyler:
Why do we need causal networks?
Environmental analysis begins with a causal chain, describing cause and effect and linking human/ industry activities to an environmental outcome/ consequence. An example of this can be seen in eutrophication processes in freshwater ecosystems.
Fertilizer use à nutrient runoff à increases nitrogen content in lakes à algal blooms à organic matter decomposition à decline in oxygen content à decline in aquatic species

This clarifies cause and effect in a linear fashion.
However, environmental systems rarely follow a simple linear pathway. Activities may produce multiple environmental pressures. Ecological changes may be caused by several interacting causes, or feedback loops, between ecological processes and social processes. Processes occurring in one part of the system can have influence over others across space and time.
A single causal chain may therefore overlook important relationships or even fail to capture the complexity of the entire system and/or consequences associated with an activity.
The Causal Network Concept
A causal network brings an issue into perspective through variables that can influence it. This shows the environmental issue as a network of interacting pathways where
Multiple causal chains intersect within the network. Variables may influence several other variables simultaneously, and feedback loops may emerge between ecological and social processes.
This approach better reflects the complexity of environmental systems, where ecological, economic and social dynamics are closely intertwined.
By explicitly mapping these relationships, the causal network helps analysts understand where indicators should be placed to capture key system dynamics.
Building a Causal Network
Niemeijer and de Groot propose a structured method for constructing causal networks before selecting indicators.
Step 1 — Define the Issue
The issue must be clearly defined and bounded. In many ways, this step corresponds to defining the research question.
For example, the Figure 1 is taken from Niemeijer and de Groot where the clearly defined issue in question is “ecological impacts of nitrogen fertilization on surface water ecosystems adjacent to agricultural land” (in the Netherlands).
Keeping the scope relatively narrow helps keep the causal network manageable.
Step 2 — Define Scope
The next step is to define the boundaries of the system or the scope of the study being studied.
This includes specifying:
Boundary conditions also determine what is excluded from the analysis. For example, a study may focus on nitrogen impacts within agricultural landscapes while excluding upstream processes such as fertilizer manufacturing. In the example, the study considers in situ temperate climate conditions for the Netherlands.
Step 3 — Identify potential Indicators
Before selecting measurable indicators, the analysis begins by identifying conceptual variables that represent key processes in the system.
Examples might include:
At this stage, the focus is on capturing the major processes and relationships relevant to the issue.
Step 4 — Construct the Causal Network
Once the conceptual variables are identified, they can be organized into a network of cause–effect relationships.
Niemeijer and de Groot suggest grouping variables into three broad domains:
Environment-related variables such as soil, water, air and biodiversity.
Society-related variables such as policy decisions, market demand, agricultural practices or consumer behaviour.
Pressure interface where societal activities interact directly with environmental systems. Agricultural production using nitrogen fertilizer is one such interface.
The variables are then connected through directional links representing causal relationships.
Rather than forming a single chain, the variables form a network of interacting pathways.
How the Causal Network Guides Indicator Selection
Once the causal network has been constructed, indicator selection becomes a more systematic process.
Several practical considerations must then be addressed:
Key nodes within the causal network can then be identified. Indicators are selected to represent these nodes in a way that captures the most important processes within the system.
The starting point remains the research question. Without a clearly defined question, indicator selection risks becoming arbitrary or driven by data availability rather than conceptual relevance.
A short note on Nodes
Nodes are points in the network that are centers of activity. They can be root nodes, central nodes or end-of-chain nodes.
End-of-chain nodes have multiple incoming arrows showing long range of causes and effects. Take for example Water fauna.
Central nodes are those that typically have multiple incoming and outgoing arrows. In this example, they can be N concentrations in water or N emissions.
Root nodes – there are not so many here, but one could imagine that manure use or fertilizer use is a root node in this example. They have multiple outgoing arcs in Crop production.
In practice, not every node has a corresponding indicator. It is therefore important to identify key nodes where measurement provides most insight into system behaviour or where management interventions can influence outcomes.
Implications for Corporate Sustainability
The causal network approach also has implications beyond ecological research.
In corporate sustainability contexts, indicators are often selected to satisfy requirements for internal audits, environmental management systems or sustainability reporting. Causal networks see companies as inherently nested in physical, ecological systems where risks from loss of ecosystems are real.
However, without a clear conceptual foundation, these indicators may fail to reflect the underlying environmental processes associated with a company’s activities.
Applying a causal network approach requires that organizations:
This approach increases transparency and improves the credibility of environmental reporting.
Indicators should therefore not be treated as decorative elements in sustainability reports. They are analytical tools that shape how environmental issues are understood and addressed.
Robust indicator selection strengthens:
For example, a food processing company assessing water-related risks may construct a causal network linking sourcing of agricultural raw materials, nutrient runoff from processing, watershed conditions around the factory, and ecosystem impacts such as eutrophication.
Ultimately, indicators influence not only how environmental change is measured, but also how it is interpreted and managed.
In our next article, we look at indicators in different corporate contexts to see how they were chosen and find the causal network. We also discuss how indicators enable decision-making in corporate contexts.
Demystifying Indicators Part 2
From Causal Chains to Causal Networks
In Part 1, we explored a basic but essential question – What is an indicator? We introduced the idea of the causal chain as a starting point for thinking about indicators and capturing cause-effect relationships in environmental systems.
“Indicators are decision tools that exist to simplify complexity.”
In this article, we take a step deeper, exploring the Causal Network concept, as described by Niemeijer and de Groot (2006). The causal network creates a system for choosing indicators, clarifies what indicators represent, and guides the analysis of complex environmental systems.
The causal network sets an explicit request at the outset. Mapping the processes that shape the environmental issue that is particular to the organisation. Once the whole system is mapped, indicator selection becomes more purposeful, answering the question that is based on the scope of the study.
Purpose of environmental indicators
Environmental indicators reveal trends or phenomena that are not immediately detectable. They simplify complex ecological processes into signals that can be monitored and interpreted over time.
Dale and Beyler (2001) describe indicators as tools that capture aspects of ecological systems while remaining practical for monitoring and management.
Dale and Beyeler are of the opinion that indicator selection should be guided by the concept of ecological integrity. Imagine seeing it as a hierarchy
and that indicators should ideally capture processes across hierarchies to reflect structural, functional and composition of ecosystems.
Ecological indicators, which are indicators specifically representing ecosystems should do the following, according to Dale and Beyler:
Why do we need causal networks?
Environmental analysis begins with a causal chain, describing cause and effect and linking human/ industry activities to an environmental outcome/ consequence. An example of this can be seen in eutrophication processes in freshwater ecosystems.
Fertilizer use à nutrient runoff à increases nitrogen content in lakes à algal blooms à organic matter decomposition à decline in oxygen content à decline in aquatic species
This clarifies cause and effect in a linear fashion.
However, environmental systems rarely follow a simple linear pathway. Activities may produce multiple environmental pressures. Ecological changes may be caused by several interacting causes, or feedback loops, between ecological processes and social processes. Processes occurring in one part of the system can have influence over others across space and time.
A single causal chain may therefore overlook important relationships or even fail to capture the complexity of the entire system and/or consequences associated with an activity.
The Causal Network Concept
A causal network brings an issue into perspective through variables that can influence it. This shows the environmental issue as a network of interacting pathways where
Multiple causal chains intersect within the network. Variables may influence several other variables simultaneously, and feedback loops may emerge between ecological and social processes.
This approach better reflects the complexity of environmental systems, where ecological, economic and social dynamics are closely intertwined.
By explicitly mapping these relationships, the causal network helps analysts understand where indicators should be placed to capture key system dynamics.
The causal network approach proposed by Niemeijer and de Groot provides a framework for achieving this.
Figure 1: Taken from Niemeijer and de Groot (2008). A structured method for depicting causal networks
Building a Causal Network
Niemeijer and de Groot propose a structured method for constructing causal networks before selecting indicators.
Step 1 — Define the Issue
The issue must be clearly defined and bounded. In many ways, this step corresponds to defining the research question.
For example, the Figure 1 is taken from Niemeijer and de Groot where the clearly defined issue in question is “ecological impacts of nitrogen fertilization on surface water ecosystems adjacent to agricultural land” (in the Netherlands).
Keeping the scope relatively narrow helps keep the causal network manageable.
Step 2 — Define Scope
The next step is to define the boundaries of the system or the scope of the study being studied.
This includes specifying:
Boundary conditions also determine what is excluded from the analysis. For example, a study may focus on nitrogen impacts within agricultural landscapes while excluding upstream processes such as fertilizer manufacturing. In the example, the study considers in situ temperate climate conditions for the Netherlands.
Step 3 — Identify potential Indicators
Before selecting measurable indicators, the analysis begins by identifying conceptual variables that represent key processes in the system.
Examples might include:
At this stage, the focus is on capturing the major processes and relationships relevant to the issue.
Step 4 — Construct the Causal Network
Once the conceptual variables are identified, they can be organized into a network of cause–effect relationships.
Niemeijer and de Groot suggest grouping variables into three broad domains:
Environment-related variables such as soil, water, air and biodiversity.
Society-related variables such as policy decisions, market demand, agricultural practices or consumer behaviour.
Pressure interface where societal activities interact directly with environmental systems. Agricultural production using nitrogen fertilizer is one such interface.
The variables are then connected through directional links representing causal relationships.
Rather than forming a single chain, the variables form a network of interacting pathways.
How the Causal Network Guides Indicator Selection
Once the causal network has been constructed, indicator selection becomes a more systematic process.
Several practical considerations must then be addressed:
Key nodes within the causal network can then be identified. Indicators are selected to represent these nodes in a way that captures the most important processes within the system.
The starting point remains the research question. Without a clearly defined question, indicator selection risks becoming arbitrary or driven by data availability rather than conceptual relevance.
A short note on Nodes
Nodes are points in the network that are centers of activity. They can be root nodes, central nodes or end-of-chain nodes.
End-of-chain nodes have multiple incoming arrows showing long range of causes and effects. Take for example Water fauna.
Central nodes are those that typically have multiple incoming and outgoing arrows. In this example, they can be N concentrations in water or N emissions.
Root nodes – there are not so many here, but one could imagine that manure use or fertilizer use is a root node in this example. They have multiple outgoing arcs in Crop production.
In practice, not every node has a corresponding indicator. It is therefore important to identify key nodes where measurement provides most insight into system behaviour or where management interventions can influence outcomes.
Implications for Corporate Sustainability
The causal network approach also has implications beyond ecological research.
In corporate sustainability contexts, indicators are often selected to satisfy requirements for internal audits, environmental management systems or sustainability reporting. Causal networks see companies as inherently nested in physical, ecological systems where risks from loss of ecosystems are real.
However, without a clear conceptual foundation, these indicators may fail to reflect the underlying environmental processes associated with a company’s activities.
Applying a causal network approach requires that organizations:
This approach increases transparency and improves the credibility of environmental reporting.
Indicators should therefore not be treated as decorative elements in sustainability reports. They are analytical tools that shape how environmental issues are understood and addressed.
Robust indicator selection strengthens:
For example, a food processing company assessing water-related risks may construct a causal network linking sourcing of agricultural raw materials, nutrient runoff from processing, watershed conditions around the factory, and ecosystem impacts such as eutrophication.
Ultimately, indicators influence not only how environmental change is measured, but also how it is interpreted and managed.
In our next article, we look at indicators in different corporate contexts to see how they were chosen and find the causal network. We also discuss how indicators enable decision-making in corporate contexts.

However, environmental systems rarely follow a simple linear pathway. Activities may produce multiple environmental pressures. Ecological changes may be caused by several interacting causes, or feedback loops, between ecological processes and social processes. Processes occurring in one part of the system can have influence over others across space and time.
A single causal chain may therefore overlook important relationships or even fail to capture the complexity of the entire system and/or consequences associated with an activity.
The Causal Network Concept
A causal network brings an issue into perspective through variables that can influence it. This shows the environmental issue as a network of interacting pathways where
Multiple causal chains intersect within the network. Variables may influence several other variables simultaneously, and feedback loops may emerge between ecological and social processes.
This approach better reflects the complexity of environmental systems, where ecological, economic and social dynamics are closely intertwined.
By explicitly mapping these relationships, the causal network helps analysts understand where indicators should be placed to capture key system dynamics.
Demystifying Indicators Part 2
From Causal Chains to Causal Networks
In Part 1, we explored a basic but essential question – What is an indicator? We introduced the idea of the causal chain as a starting point for thinking about indicators and capturing cause-effect relationships in environmental systems.
“Indicators are decision tools that exist to simplify complexity.”
In this article, we take a step deeper, exploring the Causal Network concept, as described by Niemeijer and de Groot (2006). The causal network creates a system for choosing indicators, clarifies what indicators represent, and guides the analysis of complex environmental systems.
The causal network sets an explicit request at the outset. Mapping the processes that shape the environmental issue that is particular to the organisation. Once the whole system is mapped, indicator selection becomes more purposeful, answering the question that is based on the scope of the study.
Purpose of environmental indicators
Environmental indicators reveal trends or phenomena that are not immediately detectable. They simplify complex ecological processes into signals that can be monitored and interpreted over time.
Dale and Beyler (2001) describe indicators as tools that capture aspects of ecological systems while remaining practical for monitoring and management.
Dale and Beyeler are of the opinion that indicator selection should be guided by the concept of ecological integrity. Imagine seeing it as a hierarchy
and that indicators should ideally capture processes across hierarchies to reflect structural, functional and composition of ecosystems.
Ecological indicators, which are indicators specifically representing ecosystems should do the following, according to Dale and Beyler:
Why do we need causal networks?
Environmental analysis begins with a causal chain, describing cause and effect and linking human/ industry activities to an environmental outcome/ consequence. An example of this can be seen in eutrophication processes in freshwater ecosystems.
Fertilizer use à nutrient runoff à increases nitrogen content in lakes à algal blooms à organic matter decomposition à decline in oxygen content à decline in aquatic species
This clarifies cause and effect in a linear fashion.

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We combine rigorous analysis, practical tools and cross-sector insight to support decision-making in a rapidly changing world.