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Mikael Hildén Finnish Environment Institute, SYKE

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1 Mikael Hildén Finnish Environment Institute, SYKE
Thresholds and risks - tensions between policies and biological effects Mikael Hildén Finnish Environment Institute, SYKE

2 Starting points Present EU policies demand harmonisation and preferably unambiguous limits, goals and measures; Thresholds are entities that are related to sudden changes in biological and ecological systems; Biological systems are characterised by variability and time-space specificity.

3 Effects of agreed policies: Intended; Unintended.
Political and scientific debate: Analysis of thresholds and their consequences. Political negotiations on policy inter- ventions Agreement on policy= Specific policies, Directives Observations or fear of sudden change in ecological or biological systems Effects of agreed policies: Intended; Unintended. Feedback due to effects of agreed policies and interactions with other policies

4 Examples of references to proven or assumed thresholds in EU policy development
EU environmental policy has historically been driven strongly by health considerations. In health risk management of chemicals, standards/guidelines have been based either on threshold models (trad. toxicol) or linear models (many carcinogens). Ecological considerations have gained importance in policies, e.g. Dangerous Substances Directive (1976); Dioxin strategy (2001), however health focus in specific recommendations (for food and feeding-stuffs, 2002); Integrated pollution prevention and control; Marine Strategy (‘ecosystem approach’) Water Framework Directive

5 Standards & thresholds
Quality standard = a legal expression of a threshold or an assumed threshold. Relationship between standards and thresholds are complicated, because Ecological thresholds are not constant entities; Standards have to be constant in some bureaucratic /political time & space domain; Economic, social and political factors affect the design of standard, including the degree of precaution adopted; Legally binding quality standards must be translatable to specific places and cases.

6 The policy view on thresholds
Level of adverse impact hysteresis Toxicological threshold of no effects Observable level Risk averse standards Risk prone standards Pressure Area of rapidly increasing risk

7 Ways of dealing with thresholds in EU policy
Uniform standards (dioxins/chemicals/health); Uniform procedures for: Programmes maintaining/achieving desired states (Water Framework Directive) Permits protecting local state of the environment (IPPC) Environmental Quality Criteria / Objectives (EQCs) (partly unified) Note: e.g. WFD & Marine strategy based on mixed approaches

8 side-effects of standards
Level of adverse impact Social or economic effects Observable level Pressure Legally binding standard = potential point of discontinuity with respect to social and economic effects

9 Implementation problems
The narrow ”discretisation” of great variety and the aggregation of dimensions (typology); Risks and uncertainties with respect to thresholds are difficult to formalise; e.g., repeated safety factors in derivation of standard; selection of cut-off points in risk distributions. The specification and application of multiple standards for multiple but non-separable risk agents, such as mixtures. Economic, social and technical considerations cause tensions in the use of standards across EU.

10 Challenges Avoiding unjustified cementing of thresholds into EU-wide or regional legal norms through standards or rigid procedures; Development of procedures for providing information on and dealing with uncertainties concerning thresholds: finding reliable early signals – verification/falsification of the risks; Adaptive management and policy learning for developing appropriate use of thresholds, in particular in the case of multiple risks = non-normative presentation of thresholds.


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