Mb. David et al., EFFECT OF CHRONIC NITROGEN ADDITIONS ON SOIL-NITROGEN FRACTIONS IN RED SPRUCE STANDS, Water, air and soil pollution, 105(1-2), 1998, pp. 183-192
The responses of temperate and boreal forest ecosystems to increased n
itrogen (N) inputs have been varied, and the responses of soil N pools
have been difficult to measure. In this study, fractions and pool siz
es of N were determined in the forest floor of red spruce stands at fo
ur sites in the northeastern U.S. to evaluate the effect of increased
N inputs on forest floor N. Two of the stands received 100 kg N ha(-1)
yr(-1) for three years, one stand received 34 kg N ha(-1)yr(-1) for si
x years, and the remaining stand received only ambient N inputs. No di
fferences in total N content or N fractions were measured in samples o
f the Oie and Oa horizons between treated and control plots in the thr
ee sites that received N amendments. The predominant N fraction in the
se samples was amino acid N (31-45 % of total N), followed by hydrolyz
able unidentified N (16-31 % of total N), acid-soluble N (18-22 % of t
otal N), and NH4+-N (9-13 % of total N). Rates of atmospheric depositi
on varied greatly among the four stands. Ammonium N and amino acid N c
oncentrations in the Oie horizon were positively related to wet N depo
sition, with respective r(2) values of 0.92 and 0.94 (n = 4, p < 0.05)
. These relationships were somewhat stronger than that observed betwee
n atmospheric wet N deposition and total N content of the forest floor
, suggesting that these pools retain atmospherically deposited N. The
NH4+-N pool may represent atmospherically deposited N that is incorpor
ated into organic matter, whereas the amino acid N pool could result f
rom microbial immobilization of atmospheric N inputs. The response of
forest floor N pools to applications of N may be masked, possibly by t
he large soil N pool, which has been increased by the long-term input
of N from atmospheric deposition, thereby overwhelming the short-term
treatments.