THESIS APPROVAL
THESIS APPROVAL
THESIS APPROVAL
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Capitella capitata sp.1 with fluoranthene (Forbes et al., 1996), Arenicola marina with<br />
pyrene (Christensen et al., 2002), Armandia brevis with naphthalene (Meador et al.,<br />
1995) and Abarenicola pacifica with benzo (a) pyrene (Weston, 1990). In contrast<br />
with some aquatic oligochaetes species, slow biotransformation rate to metabolize<br />
PAHs is observed including Lumbriculus variegatus with pyrene and benzo (a)<br />
pyrene (Harkey et al., 1994a; Leppanen and Kukkonen, 2000b) and Monopylephorus<br />
rubroniveus with fluoranthene (Weinstein et al., 2003).<br />
In fish, several studies reported that many species have a MFO enzyme<br />
system, such as mosquito fish Gambusia affinis (Chamber, 1979), killi fish Fundulus<br />
heteroclitus (Stegeman, 1979) and rainbow trout Salmo gairdneri (Stegeman and<br />
Chevion, 1980), etc. Most MFO activity is localized in the liver, gills and kidney<br />
(Lindstorm-Seppa et al., 1981). When the parent compounds are broken down, the<br />
polar metabolites are then ultimately excreted via the gallbladder or the urine<br />
(Howard, 1989; Varanasi et al., 1989; Hellou et al., 1999; Klumpp et al., 2002).<br />
6. Accumulation and Release by Aquatic Organisms<br />
PAHs can be accumulated by aquatic organism (Vijayavel and<br />
Balasubramanian, 2006b). The concentrations detected in tissues of both freshwater<br />
and marine animals are generally found in the low ppb range, except near point<br />
sources of PAH pollution (Neff, 1985). For instance, the surveys of PAHs in marine<br />
bivalve mollusks along the Pacific coast of Canada and the United States have<br />
confirmed a high degree of correlation with industrial, urban and recreational uses of<br />
the coastal water (Dunn and Stich, 1976; Dunn and Young, 1976; Mix and Schaffer,<br />
1979). Residues of total PAHs in many aquatic species investigated from field survey<br />
were recorded in Table 5. Additionally, lower molecular weight compound, such as<br />
naphthalene, was also observed. For example, naphthalene constituted 75-80% of<br />
total PAHs found in the muscle, liver and gonads of American plaice and yellow tail<br />
flounder (Hellou and Warren, 1996), and 57% of total PAHs found in edible clams<br />
Tapes philippinarum and Venus gallina (Binelli and Provini, 2003). Average<br />
naphthalene residue in fish was determined at a concentration of 8.1 µg/g (Anyakora<br />
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