Recent efforts to quantify the terrestrial inputs and cycling of P in agric
ultural systems are allowing management strategies to be developed to minim
ize the loss of P. While this approach has had clear advantages for standin
g waters, potential benefits for flowing freshwater systems are more diffic
ult to predict. As a consequence of the unidirectional and dynamic nature o
f flow in rivers, temporal and spatial separations between the source of P
and the point of potential impact are introduced when considering a whole w
atershed. The ability to quantify the residence time of P within any partic
ular part of a river system is therefore essential so that the specific con
tribution of individual P sources to biological demand ran be determined. T
he smaller algal biomass productivity measured in flowing, compared with st
anding, waters at a similar supply rate of P indicates the need to consider
the roles of other watershed factors in modifying the relationship between
growth and P supply. The site-specific nature of responses to P suggests a
need to develop a hierarchical classification system where individual rive
r sections can be ranked according to their likely responsiveness to P. The
ecoregion concept, combined with stream order, would integrate spatial and
temporal aspects of gradient, land use, flow velocity, and water quality.
For this to be successful, we must demonstrate a link between perturbations
to the terrestrial P cycle, the delivery of P to flowing waters, and a bio
logical impact.