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I'r - Memorial University of Newfoundland

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originate from the Maumee River at Toledo and the Raisin River at Monroe. In addition,<br />

some diagenetic processes may contribute to the PAH assemblage in the southeastern part<br />

<strong>of</strong>the basin.<br />

Although the major po llution introduced by the Detroit River is distributed and<br />

deposited within the Western Basin.lhe major flow laden with contaminated sediment<br />

particles leaves the western part <strong>of</strong>lhe lake to enter the Central Basin (Fig. 53.1). 00<br />

ex iting the Peele Passage. the flow splits into two parts. The northern branch<br />

contam inates sediments <strong>of</strong>the central part <strong>of</strong>the lake. while lhe southern branch reaches<br />

the Ohio shore and turns east to become a part <strong>of</strong>a strong easterly directed drift following<br />

along the shore.<br />

At Cleveland. the flow bearing lhe residual pollution signal is joined by<br />

contami nated outflow <strong>of</strong>the Cuyaho ga River (Fig. 5.3.1). The compounds introduced<br />

here are predominantly <strong>of</strong>combustion origin with slight traces <strong>of</strong>oil. The PAH<br />

orig inating from both car emissions and fire places are further brought into the river with<br />

direct city run<strong>of</strong>fand may partially emanate from storm sewers. The polluted particles<br />

are further transported and deposited along the southern shore towards the Niagara River<br />

outlet. This contamination can also be partly distributed towards the central part <strong>of</strong>the<br />

lake by existing here compensatory bottom currents and temporary circulation patterns.<br />

Further east, a strong pollution signal is introduced by the Buffalo River at Buffalo<br />

(Fig. 5.3.1). The river flow contains only ccmbustt on-produced PAR originating from<br />

both car emissions and fire places. the latter possibly predominant. This pollutants are<br />

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