Phosphorus (P) related eutrophication of surface water is of increasin
g concern in many areas of the U.S. This concern has arisen where inpu
ts of P in fertilizer and manure to agricultural systems have exceeded
output in harvested crops for several years. As the loss of P in surf
ace (r(2) 0.85 to 0.96) and subsurface drainage (r(2) 0.86) have Seen
shown to be related to soil P content, measures to minimize nonpoint s
ource losses of agricultural P are most effective when implemented at
the source. To achieve this, identification of soils and management sy
stems vulnerable to P loss and an understanding of the main factors co
ntrolling soil P bioavailability is essential. Soil P bioavailability
is determined by reaction with hydrous oxides, amorphous and crystalli
ne complexes of Al, Fe and Ca, and organic matter. The rate and extent
of these reactions is influenced by soil management and drainage. In
wetlands for example, Fe redox dominates P solubility, while organic P
mineralization can contribute up to 25 kg P ha(-1) yr(-1) in temperat
e mineral soils and up to 160 kg P ha(-1) yr(-1) in organic soils. How
ever, it is critical that we are able to reliably determine threshold
soil P values at which agronomic issues become environmental concerns.
Agronomic soil P tests may target problem soils on which environmenta
l soil tests will assess P bioavailability and P sorption capacity. Cl
early, soil P dynamics are of agronomic and environmental importance,
influencing both crop productivity and eutrophication and thus, must b
e considered in developing effective management plans.