Cl. Goodale et al., The long-term effects of disturbance on organic and inorganic nitrogen export in the White Mountains, New Hampshire, ECOSYSTEMS, 3(5), 2000, pp. 433-450
Traditional biogeochemicaI theories suggest that ecosystem nitrogen retenti
on is controlled by biotic N limitation, that stream N losses should increa
se with successional age, and that increasing N deposition will accelerate
this process. These theories ignore the role of dissolved organic nitrogen
(DON) as a mechanism of N loss. We examined patterns of organic and inorgan
ic N export from sets of old-growth and historically (80-110 years ago) log
ged and burned watersheds in the northeastern US, a region of moderate, ele
vated N deposition. Stream nitrate concentrations were strongly seasonal, a
nd mean (+/- SD) nitrate export from old-growth watersheds (1.4 +/- 0.6 kg
N ha(-1) y(-1)) was four times greater than from disturbed watersheds (0.3
+/- 0.3 kg N ha(-1) y(-1)), suggesting that biotic control over nitrate los
s can persist for a century. DON loss averaged 0.7 (+/- 0.2) kg N ha(-1) y(
-1) and accounted for 28-87% of total dissolved N (TDN) export. DON concent
rations did not vary seasonally or with successional status, but correlated
with dissolved organic carbon (DOC), which varied inversely with hardwood
forest cover. The patterns of DON loss did not follow expected differences
in biotic N demand but instead were consistent with expected differences in
DOC production and sorption. Despite decades of moderate N deposition, TDN
export was low, and even old-growth forests retained at least 65% of N inp
uts. The reasons for this high N retention are unclear: if due to a large c
apacity for N storage or biological removal, N saturation may require sever
al decades to occur; if due to interannual climate variability, large losse
s of nitrate may occur much sooner.