Today we see an increased use of wetlands for N removal in agricultural cat
chments. Since the most important process for nitrate (NO3-) removal, denit
rification, requires organic C, different soils could be expected to be dif
ferently suited for wetland construction. In this study, we evaluate the im
portance of soil organic C and the effects of added dissolved organic C on
N transformations in existing and proposed wetlands. We used N-15-labeled N
O3- to study N transformations in soil columns from five locations (a fores
t peaty soil, a field peaty soil, a silt loam, a loam, and a sandy loam). A
ll five soils removed NO3- at substantial rates (13-73% of the load). The h
eld peaty soil had highest denitrification rate (11 mmol m(-2) d(-1)), whil
e sandy loam soil had the lowest rate (2 mmol m(-2) d(-1)). Dissolved organ
ic C did not seem to limit N removal in the soils, as glucose additions aff
ected N turnover only slightly. The forest peat soil differed from the othe
rs by exhibiting low nitrification, and relatively high production of nitri
te (NO2-), probably a result of low pH, Nitrate removal in the field peat s
oil and the sandy loam soil was counteracted by production of ammonium (NH4
+) and dissolved organic N, causing net N release. Although there was a pos
itive relationship between soil organic matter and NO3- consumption, we con
clude that all soils were suited for N removal. The lack of response to glu
cose additions indicate that there was no short-term lack of electron donor
in any of the soils, including the sandy loam soil.