Give us feedback

Project part-financed by the European Union (European Regional Development Fund)

The Interreg IVB North Sea Region Programme

The authors are solely responsible for the content of this report. Material included herein does not represent the opinion of the European Community, and the European Community is not responsible for any use that might be made of it.
Back to overview reports

Ecosystem Service Assessment of TIDE Estuaries

5d. Functional ES supply

Following the separate descriptions of structures and processes involved in supply of these ecosystem services, the many interactions and interdependences between them are clear (see also Figure 10). The services described in TIDE are final services, directly linked to benefits, as well as intermediate services, which regulate processes involved in provision of other services. However, these intermediate services can also have direct benefits. All services impact on the main structures and processes which determine the overall functioning of the system, while finally all services are more or less dependent on habitat and supporting functions.

Assuming that all these services have to be provided sustainably, the effect of optimizing structures and processes in function of a (set of) services on the long-term supply of the other services should be estimated. Unavoidably, any use of the estuary will have an impact. The challenge is to assess the risk of this impact to provoke system shifts which cannot be undone. This can only be achieved through building a comprehensive integrated model of the estuary, including quantitative data, verified indicators for ecological functioning and best available estimates, including uncertainties and knowledge gaps as risk factors. An illustrative backbone of such a conceptual model is shown in Figure 28.

From Figure 28, it is clear that all services depend on certain common key drivers, such as discharge and tidal water quantity, morphology, pollution and nutrient loads. These affect services directly, or indirectly by impacting on quality and amount of certain habitats, or with a time lag, when (use of) services impacts future conditions (gray arrows in Figure 28). Adopting a functional approach requires a comprehensive ecological understanding and threshold estimation based on empirical data, through the integration of existing models, data and expertise gathered in TIDE and present in other estuaries.

Back to top