Surface samples and cores were collected in 1993 from the Burlington Harbor
region of Lake Champlain. Sediment samples were analyzed for trace metals
(cadmium, copper, lead, nickel, silver and zinc), simultaneously extracted
metal/acid volatile sulfide (SEM-AVS), grain size, nutrients (carbon and ni
trogen) and organic contaminants (polycyclic aromatic hydrocarbons (PAHs) a
nd polychlorinated biphenyls (PCBs)). The concentrations of cadmium, copper
, silver and zinc from the partial sediment digestion of the surface sample
s correlated well with each other (r(2)>0.60) indicating that either a comm
on process, or group of processes determined the sediment concentrations of
these metals. In an analysis of the spatial distribution of the trace meta
ls and PAHs, high surficial concentrations were present in the southern por
tion of the Harbor. The trace metal trend was strengthened when the concent
rations were normalized by grain size. A sewage treatment plant outfall dis
charge was present in the southeastern portion of the Harbor at the time of
this study and is the major source of trace metal and PAH contamination. E
valuation of sediment cores provides a proxy record of historical trace met
al and organic inputs. The peak accumulation rate for copper, cadmium, lead
, and zinc was in the late 1960s and the peak silver accumulation rate was
later. The greatest accumulation of trace metals occurred in the late 1960s
after discharges from the STP began. Subsequent declines in trace metal co
ncentrations may be attributed to increased water and air regulations. The
potential toxicity of trace metals and organic contaminants was predicted b
y comparing contaminant concentrations to benchmark concentrations and pote
ntial trace metal bioavailability was predicted with SEM-AVS results. Surfa
ce sample results indicate lead, silver, Sigma PAHs and Sigma PCBs are pote
ntially toxic and/or bioavailable. These predictions were supported by stud
ies of biota in the Burlington Harbor watershed. There is a clear trend of
decreasing PAH and trace metal contaminant concentrations with distance fro
m the STP outfall.