We examined the fate of applied phosphorus (P) in a young
Pinus radiata plantation in south-eastern Australia,
spray-irrigated with secondary-treated municipal effluent. Measurements
included changes (before irrigation, and after 5 years) in total P, total
organic P, total inorganic P, labile P, and sorption and desorption
characteristics. During the first 5 years a total of 363 kg/ha of P was
applied at an average concentration of 5.4 mg/L. Irrigation changed the
forms and distribution of P throughout the profile (0–1 m). Increases in
labile inorganic P (membrane-exchangeable, bicarbonate-extractable, and in
soil solution) were confined mostly to the 0–0.5 m horizon, and wholly
within the 0–0.7 m horizon. In addition, large amounts of organic P (204
kg/ha) were mineralised within the surface 0.7 m, due to stimulation of
decomposer activity by increased soil water. Mineralisation, therefore,
provided a significant and additional input of inorganic P to soil.
Irrigation and P additions changed both the placement and curvature of soil
sorption isotherms. Retention capacity (0–0.5 m), calculated from P
sorption isotherms, decreased by 180 kg/ha. Desorbable P, determined by
sequential extraction with dilute acid, increased by 184 kg/ha. Thus,
these 2 independent methods of measuring the changes in exchangeable P gave
the same result. Of the total inorganic P added to the soil (in effluent and
mineralised), 25% remained in the exchangeable form; the rest was
retained unavailable for short-term exchange and migration through soil.
After 5 years, fluxes (kg/ha) of P in the 0–0.7 m horizon were:
input in effluent less storage in vegetation (323), change in total organic P
(–204), change in total inorganic P (517), net change in total P (313).
Thus, 97% of the net amount of P added in effluent was recovered in the
surface 0.7 m. Results have implications for the way in which P retention
capacity is calculated under effluent irrigation.