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4. Distribution in the Aquatic Environment<br />

PAHs entering water from various sources quickly become adsorbed on<br />

organic and inorganic particulate matter in water, and large amounts are deposited in<br />

bottom sediment. Herbes (1977) said that organic particles tend to adsorb PAHs more<br />

readily than clay particle. Once deposited on the bottom, the PAHs are much less<br />

subject to photochemical, chemical or biological degradation than they were in the<br />

water column (Neff, 1985). However, leaching or biological activities in the<br />

sediments may return a small fraction of these PAHs to the water column. The<br />

composition and relative concentrations of the PAH assemblage in the sediment may<br />

be differed from those in the PAHs source because of differential partitioning of<br />

PAHs between sediment and aqueous phases (Hase and Hites, 1977). The distribution<br />

of PAHs in aquatic environment is described in Figure 9.<br />

PAHs<br />

Evaporation Photo-oxidation<br />

Dissolution<br />

Water surface<br />

Water column<br />

Photo degradation Biodegradation<br />

Chemical degradation<br />

Bioaccumulation<br />

Sedimentation<br />

Attachment to particulate matter<br />

Figure 9 Distribution of PAHs in aquatic environment.<br />

Bioaccumulation<br />

Biodegradation<br />

Chemical degradation<br />

Bottom sediment<br />

Most of the PAHs entering the aquatic environment are localized in rivers,<br />

estuaries and coastal marine waters. Table 3 and Table 4 show the concentration of<br />

22

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