P. Gundersen et al., IMPACT OF NITROGEN DEPOSITION ON NITROGEN CYCLING IN FORESTS - A SYNTHESIS OF NITREX DATA, Forest ecology and management, 101(1-3), 1998, pp. 37-55
Impact of nitrogen (N) deposition was studied by comparing N fluxes, N
concentrations and N pool sizes in vegetation and soil in five conife
rous forest stands at the NITREX sites: Gardsjon (GD), Sweden, Kloster
hede (KH), Denmark, Aber (AB), Wales, UK, Speuld (SP), the Netherlands
, and Ysselsteyn (YS), the Netherlands. The sites span a N-deposition
gradient from 13 to 59 kg N ha(-1) yr(-1). Measurements of soil N tran
sformation rates by laboratory and field incubations were part of the
site comparison. Further, results from 4-5 yr of NH4NO3, addition (35
kg N ha(-1) yr(-1)) at low deposition sites (GD, KH, AB) and 6 yr of N
removal (roofs) at high deposition sites (SP, YS) were included in th
e analysis. Significant correlations were found between a range of var
iables including N concentrations in foliage and litter, soil N transf
ormation rates and forest floor characteristics. Using the methods fro
m principal component analysis (PCA) these variables were summarized t
o an index of site N status that assigned the lowest N status to GD an
d the highest to YS. Site N status increased with N deposition with th
e exception that AB was naturally rich in N. Nitrate leaching was sign
ificantly correlated with N status but not correlated with N depositio
n. Forest floor mass and root biomass decreased with increased N statu
s, Characteristics of the mineral soil were not correlated with vegeta
tion and forest floor variables. High C/N ratios in the mineral soil a
t the high-N deposition sites (SP, YS) suggest that the mineral soil p
ool changes slowly and need not change for N saturation to occur. Nitr
ogen transformation rates measured in laboratory incubations did not a
gree well with rates measured in the field except for a good correlati
on between 'gross' mineralization in the laboratory and 'net' minerali
zation in the field. The changes in N concentrations and fluxes after
manipulation of N input followed the direction expected from the site
comparison: increases at N addition and decreases at N removal sites.
Nitrate leaching responded within the first year of treatment at all s
ites, whereas responses in vegetation and soil were delayed. Changes i
n N status by the manipulation treatments were small compared to the d
ifferences between sites. Changes in nitrate leaching were small at th
e low-N status sites and substantial at the high-N status sites. Nitro
gen-limited and N-saturated forest ecosystems could be characterized q
uantitatively. (C) 1998 Elsevier Science B.V.