We conducted greenhouse microcosm experiments to examine the biogeoche
mical effects of restoring seawater to historically diked Cape Cod sal
t marshes. Feat cores from both seasonally flooded and drained diked m
arshes were waterlogged with seawater, and porewater chemistry was sub
sequently monitored for 21 mo. The addition of seawater to highly orga
nic, seasonally flooded peat caused the death of freshwater wetland pl
ants, 6-8 cm of sediment subsidence, and increased N and P mineralizat
ion. Also, sulfides and alkalinity increased 10-fold, suggesting accel
erated decomposition by sulfate reduction. Addition of seawater to the
low-organic-content acidic peat from the drained marsh increased pore
water pH, alkalinity, PO4-P, and Fe(II), which we attribute to the ree
stablishment of SO4 and Fe(III) mineral reduction. Increased cation ex
change contributed to 6-fold increases in dissolved Fe(II) and Al and
60-fold increases in NH4-N within 6 mo of salination. Seawater reintro
ductions to seasonally flooded diked marshes will cause porewater sulf
ides to increase, likely reducing the success of revegetation efforts.
Sulfide toxicity is of less concern in resalinated drained peats beca
use of the abundance of Fe(II) to precipitate sulfides, and of NH4-N t
o offset sulfide inhibition of N uptake. Restoration of either seasona
lly flooded or drained diked marshes could stimulate potentially large
nutrient and Fe(II) releases, which could in turn increase primary pr
oduction and lower oxygen in receiving waters. These findings suggest
that tidal restoration be gradual and carefully monitored.