Design in the IEHIAS

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The text on this page is taken from an equivalent page of the IEHIAS-project.

The Design stage in an integrated environmental health impact assessment takes forward the 'conceptual model' of the issue, defined during issue framing, and converts it into a detailed protocol for assessment.

This is necessary because issue framing only defines what we would like to assess. It does not guarantee that an integrated assessment is worthwhile or can be done, nor does it set out how actually to do the assessment.

Designing the assessment requires three further preparatory steps:

  • Screening – to determine whether a full integrated impact assessment is necessary;
  • Piloting – to determine whether a full integrated impact assessment can be conducted successfully;
  • Protocol development – to specify in detail the study area and population, scenario, data and methods that will be used in the assessment.

None of these steps runs only one way. In many instances, they will reveal previously unforeseen factors that need to be included. They may also uncover contradicting evidence which cast doubt on some of the decisions or expectations in issue framing. As a consequence, the conceptual model of the issue may need to be reconsidered and revised.

Nor is the complete process necessarily carried out, for the first step in this stage of the assessment (screening) may show that an assessment is not merited, while feasibility testing may show that it cannot be done. In either of these situations, the assessment process can be terminated. In this case, further consultation with stakeholders will be required to explain this outcome, and to consider what should be done instead.

Key issues

Integrated assessments are complex things. They typically relate to issues that have many (and often remote) causes, which operate via different pathways and processes, and lead to a wide range of health and associated impacts. If the assessments are to deal effectively with these complexities, they often need to bring together different forms of information from a variety of different sources and to analyse and supplement these by different methods. Great care is therefore needed to ensure that the assessment remains:

  • Relevant - i.e. is faithful to, and targetted at, the issue that needs to be assessed;
  • Scientifically credible - i.e. provides results that are accurate and reliable;
  • Transparent - i.e. can be evaluated and understood by those not directly involved (and if necessary can be replicated or validated).

None of this is likely to occur unless the assessment is carefully designed. And the focus of design must be on identifying and eliminating (or at least minimising) the uncertainties that might arise. In this context, the most important rules for assessment design can be summarised as follows:

  1. All the most important hazards and benefits of relevance to the issue (and their interactions) must be included in the analysis, and must be properly represented by the data and models being used.
  2. Variations in the study population (especially in their differing susceptibility to potential health effects) must be allowed for, so that results of the assessment are not biased towards particular, non-representative groups.
  3. The value systems applied in converting the health outcomes to overall measures of impact (and in selecting the indicators to reflect these) must be explicit and appropiate, and should not unacceptably bias the results.
  4. The temporal and spatial 'dimensions' of the assessment must be valid and appropriate - i.e. the assessment should cover an appropriate geographical area and time scale, and analysis must be done at an appropriate resolution, so that key impacts are not omitted or blurred in the analysis;
  5. The overall analysis must be coherent and consistent - i.e. there should be no illogicalities or gaps in the way the causal chain has been represented or analysed.

Information on how to achieve each of these is available on these pages:

See also

Integrated Environmental Health Impact Assessment System
IEHIAS is a website developed by two large EU-funded projects Intarese and Heimtsa. The content from the original website was moved to Opasnet.
Topic Pages

Boundaries · Population: age+sex 100m LAU2 Totals Age and gender · ExpoPlatform · Agriculture emissions · Climate · Soil: Degredation · Atlases: Geochemical Urban · SoDa · PVGIS · CORINE 2000 · Biomarkers: AP As BPA BFRs Cd Dioxins DBPs Fluorinated surfactants Pb Organochlorine insecticides OPs Parabens Phthalates PAHs PCBs · Health: Effects Statistics · CARE · IRTAD · Functions: Impact Exposure-response · Monetary values · Morbidity · Mortality: Database

Examples and case studies Defining question: Agriculture Waste Water · Defining stakeholders: Agriculture Waste Water · Engaging stakeholders: Water · Scenarios: Agriculture Crop CAP Crop allocation Energy crop · Scenario examples: Transport Waste SRES-population UVR and Cancer
Models and methods Ind. select · Mindmap · Diagr. tools · Scen. constr. · Focal sum · Land use · Visual. toolbox · SIENA: Simulator Data Description · Mass balance · Matrix · Princ. comp. · ADMS · CAR · CHIMERE · EcoSenseWeb · H2O Quality · EMF loss · Geomorf · UVR models · INDEX · RISK IAQ · CalTOX · PANGEA · dynamiCROP · IndusChemFate · Transport · PBPK Cd · PBTK dioxin · Exp. Response · Impact calc. · Aguila · Protocol elic. · Info value · DST metadata · E & H: Monitoring Frameworks · Integrated monitoring: Concepts Framework Methods Needs
Listings Health impacts of agricultural land use change · Health impacts of regulative policies on use of DBP in consumer products
Guidance System
The concept
Issue framing Formulating scenarios · Scenarios: Prescriptive Descriptive Predictive Probabilistic · Scoping · Building a conceptual model · Causal chain · Other frameworks · Selecting indicators
Design Learning · Accuracy · Complex exposures · Matching exposure and health · Info needs · Vulnerable groups · Values · Variation · Location · Resolution · Zone design · Timeframes · Justice · Screening · Estimation · Elicitation · Delphi · Extrapolation · Transferring results · Temporal extrapolation · Spatial extrapolation · Triangulation · Rapid modelling · Intake fraction · iF reading · Piloting · Example · Piloting data · Protocol development
Execution Causal chain · Contaminant sources · Disaggregation · Contaminant release · Transport and fate · Source attribution · Multimedia models · Exposure · Exposure modelling · Intake fraction · Exposure-to-intake · Internal dose · Exposure-response · Impact analysis · Monetisation · Monetary values · Uncertainty