wAbstract
@Settling particulate matter was collected in sediment traps from
the major depositional basin of Onondaga Lake, a calcareous, eutrophic
lake in Syracuse, New York, U.S.A. Sediment traps were deployed
at three depths from July to November and for a brief period under
ice cover in February to investigate both vertical and seasonal
variations in sedimentation. A sequential chemical extraction
(fractionation) method was applied to the collected material to
quantify the following phosphorus (P) fractions, or forms: loosely
bound-P (sorbed-P, CaCO3 associated-P, and
Fe and Al bound-P), extractable biogenic-P (easily degradable
organic-P and biogenic inorganic polyphosphates), calcium mineral-P
(e.g., apatite), and refractory organic-P. Extractable biogenic-P
and refractory organic-P were strongly correlated, suggesting
a common, autochthonous origin in plankton. Calcium mineral-P
appears to be of terrigenous origin. A dramatic increase in the
loosely bound-P content of the particulate matter was observed
during fall turnover when dissolved Fe2+, which had
accumulated in the anoxic hypolimnion, mixed with the surface
waters and oxidized with attendant adsorption of P. We estimate
that the labile-, or exchangeable-P (i.e. loosely bound- and extractable
biogenic-P forms) content of the settling particulates constitutes
`50 of the total P influx to the sediments over the period of
study. The labile-P flux over the July-November study period was
11 mg P m-2 day-1 and the labile-P flux
estimated from sediment traps deployed under ice cover was 6 mg
P m-2 day-1. From these values the annual
average labile-P flux to the sediments was estimated to be 9 mg
P m-2 day-1, only slightly less than the
estimated annual average sediment P release rate of 10 mg P m-2
day-1. This indicates that the sediments are approximately
at steady state with respect to current external P loadings to
the lake.
Keywords: Phosphorus; Sedimentation; Fractionation; Speciation;
Calcareousx
1. Introduction
2. Study system
3. Methods
4. Results and discussion
@4.1. Seston dry weight and total phosphorus fluxes
@4.2. Seasonal particulate phosphorus speciation
@4.3. labile phosphorus
5. Summary and conclusions
Acknowledgements
References