Loss of organic N in land drainage may contribute to water pollution. This
study was conducted to quantify the loss of organic nitrogen in drainage wa
ter from grazed grassland (Lolium perenne L. cv. Talbot) swards receiving a
range of fertilizer N inputs for 9 yr. Plots (each 0.2 ha) received 100, 2
00, 300, 400, or 500 kg N ha(-1) yr(-1) as calcium ammonium nitrate and wer
e hydrologically isolated and drained to V-notch weirs with automatic sampl
ing of drainage water. For comparison, organic N loss was quantified in riv
ers draining six predominantly grassland catchments. The European Community
maximum admissible concentration of total Kjeldahl N for drinking water of
1.0 mg N L-1 was exceeded in both land drainage and river water. Total org
anic N accounted for up to 54.7 and 20.2% of the annual N drainage losses f
rom the plots receiving 100 and 500 kg N ha(-1) yr(-1), respectively. Loads
of soluble organic N were greater than particulate N but there was no sign
ificant relationship with fertilizer N input for either fraction. The avera
ge annual loss of total organic N in drainage water ranged from 3.5 to 9.1
kg N ha(-1). However, this loss cannot explain the large amount of unaccoun
ted for N in calculations of nutrient balances where inputs invariably exce
ed outputs. In comparison, the average annual loss of organic N from the si
x river catchments ranged from 4.7 to 8.1 kg N ha(-1), which suggested that
a large proportion of the organic N in river water was originating from la
nd drainage.