We examined the controls on summer CH4 emission from five sites in a peatla
nd complex near Thompson, Manitoba, Canada, representing a minerotrophic gr
adient from bog to rich fen at wet sites, where the water table positions r
anged from -10 to -1 cm. Average CH4 flux, determined by static chambers on
collars, ranged from 22 to 239 mg CH4-C m(-2) d(-1) and was related to pea
t temperature. There was an inverse relationship between water table positi
on and CH4 flux: higher water tables led to smaller fluxes. The determinati
on of anaerobic CH4 production and aerobic CH4 consumption potentials in la
boratory incubations of peat samples was unable to explain much of the vari
ation in CH4 flux. Average net ecosystem exchange of CO2 ranged from 1.4 to
2.5 g CO2-C m(-2) d(-1) and was strongly correlated with CH4 flux; CH4 emi
ssion averaged 4% of CO2 uptake. End-of-season sedge biomass was also stron
gly related to CH4 flux, indicating the important role that vascular plants
play in regulating CH4 flux. Determination of isotopic signatures in peat
pore water CH4 revealed average delta(13)C values of between -50 and -73 pa
rts per thousand and delta D of between -368 and -388 parts per thousand. S
ites with large CH4 emission rates also had high CO2 exchange rates and enr
iched delta(13)C CH4 signatures, suggesting the importance of the acetate f
ermentation pathway of methanogenesis. Comparison of delta D and delta(13)C
signatures in pore water CH4 revealed a slope shallow enough to suggest th
at oxidation is not an important overall control on CH4 emissions at these
sites, though it appeared to be important at one site. Analysis of C-14 in
pore water CH4 showed that most of the CH4 was of recent origin with percen
t of modern carbon values of between 112 and 128%. The study has shown the
importance of vascular plant activities in controlling CH4 emissions from t
hese wetland sites through influences on the availability of fresh plant ma
terial for methanogenesis, rhizospheric oxidation, and plant transport of C
H4.