Nr. Urban et al., SOLUTE TRANSFER ACROSS THE SEDIMENT SURFACE OF A EUTROPHIC LAKE .1. POREWATER PROFILES FROM DIALYSIS SAMPLERS, Aquatic sciences, 59(1), 1997, pp. 1-25
Citations number
72
Categorie Soggetti
Water Resources",Limnology,"Marine & Freshwater Biology
Porewater profiles often are used to identify and quantify important b
iogeochemical processes occurring in lake sediments. In this study, mu
ltiple porewater profiles were obtained from two eutrophic Swiss lakes
using porewater equilibrators (peepers) in order to examine spatial a
nd seasonal trends in biogeochemical processes. Variability in profile
shapes and concentrations was small on spatial scales of a few meters
, but the uncertainty in calculated diffusive fluxes across the sedime
nt surface was, on average, 35%. Focusing of Fe and Mn oxides toward t
he lake center resulted in systematic increases in porewater concentra
tions and diffusive fluxes of Fe2+ and Mn2+ with increasing water dept
h; these fluxes are postulated to be regulated by the pH-dependent dis
solution of reduced-metal phases. Despite higher concentrations of ino
rganic carbon, NH,, Si and P in pelagic compared to littoral sites, di
ffusive fluxes of these substances across the sediment surface increas
ed only slightly or not at all with increasing water depth. Porewater
profiles did reveal temporal changes in Fe2+, Mn2+, Ca2+ and Mg2+ that
were an indirect result of the large, seasonal changes in seston depo
sition, but no clear seasonal variations were found in diffusive fluxe
s of nutrients across the sediment surface. The intense mineralization
occurring at the sediment surface was not reflected in the porewater
profiles nor in the calculated diffusive fluxes. Calculated diffusive
fluxes across the sediment surface resulted from decomposition occurri
ng primarily in the top 5-7 cm of sediment. Diffusive fluxes from this
subsurface mineralization were equal to the solute release from miner
alization occurring at the sediment-water interface. Buried organic ma
tter acts as a memory of previous lake conditons; it will require at l
east a decade before reductions in nutrient inputs to lakes fully redu
ce the diffusive fluxes into the lake from the buried reservoir of org
anic matter.