12. Discussion and conclusions
This paper is an extension of the original work by the authors (Reggiani et al., 1999, 1998). The concept of Representative Elementary Watersheds introduced earlier has been revised and extended to include novel features. First we recall that an REW effectively is a “mixture” of zero-dimensional contiguous phases filling separate portions of space. Following the definitions by Gray et al. (1993) we adopt a “megascopic” perspective of the system. Through spatial and temporal averaging and zero-dimensional representation, the state variables and physical properties for an entity remain only time-dependent. This leads to a system of coupled ordinary differential governing equations (ODEs), which are computationally cheaper to solve than conventional distributed models (Abbott et al., 1986a,b). This can be a major advantage in probabilistic applications that require multiple consecutive model executions, as in real-time or long-term climate forecasting. To extend earlier work, we now accommodate a more flexible modelling of watersheds by allowing for a subdivision of an REW into Elements, for which we provide conservation equations and constitutive relationships. The sub-division of REWs can be dictated by either topographic features or geological formations, by landcover or landuse patterns, or by anthropic factors such as urbanization, all of which influence flow behaviour