To determine atmospheric deposition of anthropogenic
contaminants to the Great Lakes, the United States and
Canada established the Integrated Atmospheric Deposition
Network (IADN), designed to collect regional data
representative of the air over the lakes. In this paper, we
present an update of atmospheric loadings to the Great
Lakes for seven organochlorine pesticides, four polychlorinated biphenyl (PCB) congeners and total-PCBs, four
polycyclic aromatic hydrocarbons (PAHs), and four trace
metals. Calculations are based on gas, particle, and
precipitation samples obtained in 1993 and 1994 at the
five master IADN sampling stations. Air−water exchange
is the dominant process for most organochlorines and
lower molecular weight PAHs. Within the uncertainty in
the data given here, current atmospheric loadings are
indistinguishable from air−water equilibrium having been
achieved over the lakes. In other words, the deposition
of most organochlorine compounds into the Great Lakes is
about balanced by the evaporation of these compounds
from the lakes. Uncertainties in gas-transfer loadings are
due to our inexact knowledge of physiochemical parameters,
averaging of data over long time scales, and insufficient data
for nonatmospheric sources.
A chlorinated compound (Chlordene Plus, CP), structurally related to Dechloranes (Dec) 602, 603, 604, and Dechlorane Plus (DP), was identified, and concentrations and spatial trends of Dec 602, 603, 604, CP, and DP in tributary sediments of the Laurentian Great Lakes are reported. The dechloranes were widely detected with their concentrations varying considerably across the Great Lakes basin. Spatial trends of Dec 602, 604, and DP in Canadian tributary sediments were similar to that of BDE 209, which suggested these flame retardant chemicals in tributaries were associated with industrial and urban areas. The highest concentrations of Dec 602, 604, and DP observed in tributaries of the Niagara River confirmed that past or ongoing manufacturing of these compounds at plants along the river were important sources to Lake Ontario. Dec 603 was detected in technical products of aldrin and dieldrin, and its spatial trend was consistent with historic pesticide usage. Similarly, CP was detected in technical products of chlordene and chlordane, and it was found in higher concentrations in sediments near urban areas, possibly related to past chlordane use in home termite control.
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