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THESIS APPROVAL

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7. Toxic Effects in Aquatic Organisms<br />

PAHs readily have biological effects in aquatic organisms. They may interact<br />

physically with hydrophobic sites in the cell, causing molecular deformation and<br />

perturbation. Alternatively, PAHs metabolites may undergo a variety of spontaneous<br />

or enzyme-mediated chemical reaction leading to cell damage, mutagenesis,<br />

teratogenesis and cancer (Neff, 1985). Furthermore, these chemicals appear to bind<br />

selective to the surface of plasma membranes (Roubal and Collier, 1975). This<br />

binding causes perturbations in surface organization, increasing membrane<br />

permeability (Goldacre, 1968). By disrupting, PAHs might also affect the activity of<br />

the many enzymes bound to plasma membranes and essential for cell function.<br />

The toxicity of PAHs will be proportional to the concentration associated with<br />

the membrane surface. Less soluble aromatics tend to have s greater effect at a given<br />

concentration than more soluble ones (Neff, 1985). Although acute toxicity of PAHs<br />

to aquatic organisms increases as molecular weight increases, the relationship is not<br />

absolute. Only low molecular weight including naphthalene, fluoranthene and pyrene<br />

are acutely toxic to aquatic organisms, while the higher molecular weight PAHs are<br />

not acutely toxic. Variability in response to water-borne PAHs and sedimentassociated<br />

PAHs in several species of aquatic animals were shown in Table 6 and<br />

Table 7, respectively.<br />

It should be recognized that the acute toxicity data do not adequately reflect<br />

the potential impact of chronic low-level PAH contamination produced sublethal<br />

responses in aquatic organisms. These sublethal effects may be detrimental to the<br />

long-term survival. In addition, chronic exposure to certain PAH, such as 4-6 rings<br />

and highly angular configurations, may induce mutation and cancer in sensitive<br />

species (Zedeck, 1980). Several experimental conducted on sublethal effect of PAH<br />

in aquatic biota have reported particularly on naphthalene. The behavioral response<br />

had been studied in blue crabs Callinectes sapidus which detected extremely low<br />

concentrations of naphthalene in solution and responded by increased antennular<br />

flicking rate (Pearson and Olla, 1980). Donahue et al. (1977) found that several<br />

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