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, 1996) Similarly, catalase activity has been induced in the livers of rainbow trout injected with cipro brate, Ictalurus punctatus exposed to BKME, Anguilla anguilla exposed to dinitro-o-cresol and I punctatus and Limanda limanda exposed to PAHs (Yang et al, 1990; Mather-Mihaich & Di Giulio, 1991; Braunbeck & V lkl, 1991; Di Giulio et al, 1993; Livingstone et al, 1993) However, the combined exposure to disulphoton and endosulphan had no effects on catalase activity in rainbow trout (Arnold et al, 1995) In sea bass (Dicentrarchus labrax) and dab (L limanda), intraperitoneal injection of 3-methylcholanthrene caused only slight and transient induction of catalase and SOD (Lemaire et al, 1996) Injection of -naphtho avone in rainbow trout marginally and transiently induced SOD while catalase activity was reduced (Lemaire et al, 1996).

5. Write the reference map xij, 1 5 i 5 A l l , 1 5 j 5 h , f o r the element KZJon l the position ( i ,j ) in the mesh. Write its Jacobi matrix, Jacobian, and inverse Jacobi matrix.

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In eld studies, catalase and other antioxidant enzyme activities increased in the livers of grey mullets (Mugil sp) sampled from an area polluted with metals, polyaromatic hydrocarbons, polychlorinated biphenyls and pesticides when compared with a reference area (Rodr guez-Ariza et al, 1993) Similarly, catalase and SOD activities decrease away from coastal organic contamination in liver of dab (L limanda), from the North Sea and, with some exceptions, in larvae of sardine (Sardina pilchardus), from the Biscay Gulf (Livingstone et al, 1992; Peters et al, 1994) In a eld study carried out in the Mediterranean Sea with red mullet (Mullus barbatus), catalase activity was maximal in the site with highest levels of pollution and minimal in a reference site, but varying responses were found regarding SOD, GPX and DT-diaphorase (Burgeot et al, 1996a).

This result closes the gap between the so far best upper and lower bounds of O(2d d d+1 ) and (d d/2 ) from the work by Awarbuch et al. [8]. Aland et al. [3] show that the above values on the price of anarchy also hold for the subclasses of unweighted and weighted network congestion games. For the upper bounds, the authors use a similar analysis as in the work by Christodoulou et al. [15]. The core of their analysis is to simultaneously determine parameters c1 and c2 such that yf (x + 1) c1 xf (x) + c2 yf (y) for all polynomial latency functions of maximum degree d and for all reals x, y 0. For the case of unweighted users, it suf ces to show the inequality for all pairs of integers x and y. (In order to prove their upper bound, Christodoulou and Koutsoupias [15] looked at the inequality with c1 = 1/2 and gave an asymptotic estimate for c2 .) In the analysis presented in the work by Aland et al. [3], both parameters c1 and c2 are optimized. This optimization process required new mathematical ideas and is highly nontrivial. This optimization was successfully applied by Dumrauf and Gairing [24] to the so-called polynomial Wardrop games, where it yielded almost exact bounds on price of stability.

Having shapes on a single shape layer is also great for exporting to other packages such as Illustrator, because Photoshop only lets you export one shape layer at a time. If your shape is spread across more than one layer you have to export each layer separately, then realign them in Illustrator.

No changes in SOD activity were detected in chub (Leuciscus cephalus) from a polluted river when compared with those from reference river areas, although livers of polluted sh contained higher concentrations of transition metals, especially copper and iron, which are known redox cycling compounds (Len rtov et al, 1997) In a study carried out in the Great Lakes, the activity of catalase was higher in lake trout (Salvelinus namaycush) from a reference lake when compared with those from a contaminated lake (Palace et al, 1998) Consequently, it appears that oxyradical-generating contaminant exposure is not always matched by antioxidant enzyme induction in sh Furthermore, the interpretation of data on antioxidant enzyme activities is often obscured by the fact that several abiotic and biotic variables may also in uence their activity.

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