Chronic atmospheric nitrogen deposition can alter the rate of internal
nitrogen cycling and increase the magnitude of N leaching losses in f
orested ecosystems, As fractionation of nitrogen in favour of the ligh
ter N-14 occurs during various transformations associated with N-enric
hment and nitrogen loss, it has been proposed that the N-15 Signal of
vegetation may provide a useful tool in evaluating the past and curren
t N status of forested ecosystems. A series of coniferous forests acro
ss a European nitrogen deposition gradient within the NITREX project p
rovided an opportunity to test the relationships between nitrogen supp
ly from atmospheric deposition and the relative N-15-enrichment of veg
etation to soil, across a large geographical area. Most delta(15)N val
ues for above-and below-ground tree components, soil at four depths, b
ulk precipitation and/or throughfall water and soil solution or outflo
w water values were within those observed elsewhere except for a few n
otable exceptions. There was a significant positive relationship betwe
en the delta(15)N enrichment of the tree foliage relative to the soil
horizons (or the enrichment factor), and nitrogen flux in the throughf
all if Aber forest, N. Wales, was excluded from the regression analysi
s. An unusually high enrichment factor at the Aber site indicated that
a the high rate of N cycling at the site was in excess of that predic
ted from current N deposition. This was attributed to the effect of pl
oughing and tree planting on the relatively N- and clay-rich mineral h
orizons at Aber compared to other sites. Highly significant relationsh
ips (P < 0.01) between enrichment factors and parameters describing in
ternal rates of N cycling, such as litterfall N flux and nitrification
rates in upper soil horizons, supported this conclusion. There appear
s to be a strong link between the rate of N cycling and the delta(15)N
enrichment factor, rather than N deposition or nitrate leaching per s
e. These results confirm the potential use of the delta(15)N enrichmen
t factor to identify sites influenced by nitrogen deposition. However,
consideration should be taken of other site characteristics and land
management practises which also influence soil N dynamics and N cyclin
g. (C) 1998 Elsevier Science B.V.