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Sea bass

Michel XR, PM Cassand, DG Ribera, J-E Narbonne (1992) Metabolism and mutagenic activation of benzo(a)pyrene by subcellular fractions from mussel (Mytilus galloprovincialis) digestive gland and sea bass (Discenthrarcus labrax) liver. Comp Biochem Physiol 103C 43-51. [Pg.101]

Lemaire, P., Mathieu, A., Carriere, S., Drai, P., Giudicelli, J., Lafaurie, M. (1990) The uptake mechanism and biological half-life of benzo(a) pyrene in different tissues of sea bass, Dicentrarchus labrax. Ecotoxicol. Environ. Saf. 20, 223-233. [Pg.909]

Abreu SN, Pereira E, Vale C, Duarte AC (2000) Accumulation of mercury in sea bass from a contaminated lagoon (Ria de Aveiro, Portugal). Mar Pollut Bull 40 293-297... [Pg.257]

FIGURE 6. Triphenyltin chloride (TPTCl) level in fish (gray mullet, sea bass, young bass, flounder, greenling, crusian carp, flatfish and dace) collected from all over Japanese coasts (modified from Reference 66) (pg TPTCl g 1, wet wt.)... [Pg.889]

Viscera Sea bass, Lateolabrax japonicus, Tokyo Bay, Japan, Max. 95 FW 11... [Pg.846]

Fair, P.H. 1986. Interaction of benzo[a]pyrene and cadmium on GSH-S-transferase and benzo[a]pyrene hydroxylase in the black sea bass Centropristis striata. Arch. Environ. Contam. Toxicol. 15 257-263. [Pg.1399]

Lemaire, P., J. Berhaut, S. Lemaire-Gony, and M. Lafaurie. 1992a. Ultrastructural changes induced by benzo[a]pyrene in sea bass (Dicentrarchus labrax) liver and intestine importance of the intoxication route. Environ. Res. 57 59-72. [Pg.1402]

Lemaire, P., A. Mathieu, J. Giudicelli, and M. Lafaurie. 1992c. Effect of diet on the responses of hepatic biotransformation enzymes to benzo[a]pyrene in the European sea bass (Dicentrarchus labrax). Comp. Biochem. Physiol. 102C 413-420. [Pg.1402]

Black sea bass, Centropristis striata Muscle Elasmobranchs 6.4 DW 1... [Pg.1499]

BDE 47, 99 100 Fish (Muscle tissues of salmon and conger eel and liver tissues of sea bass) green mussel Homogenization, MSPD with sodium sulfate, microwave-assisted extraction with pentane-dichloromethane (1 1) and purification with GPC Gas Chromatography (DB-5MS) Q-MS <100 ng/Kg [41]... [Pg.10]

Fish Liver Poisoning. The livers of large fish species such as sharks, tunas, and sea bass may cause intense headaches, vomiting, facial edema, fever, and severe desquamation. Onset of symptoms is from 30 minutes to 12 hours. All of these fishes contain extremely high levels of vitamin A in their livers. As the fish grows, the concentration of vitamin A in the liver increases (94-96). ... [Pg.46]

Escolar and oilfish are of low commercial values because of their kerrior-rheic properties. They are considered as "not suitable for catering" or even banned from sale in various countries. However, they are commonly marketed as a result of their substantial by-catch with tuna and swordfish (Shadbolt et. ah, 2002 Tserpes et ah, 2006). According to the European Communities (Labelling of Fishery and Aquaculture Products) Regulations 2003 (S.I. No. 320 of 2003), L. flavobrunneum and R. pretiosus must be marketed as escolar and oilfish, respectively, and no other commercial names can be used alternatively. Yet, both species are usually mislabeled as sea bass, butterfish, rudderfish, white tuna, or codfish either... [Pg.13]

The pharmacokinetics of enrofloxacin and its active metabolite, ciprofloxacin, have been further extensively studied in sea bass after treatment by oral gavage or water, at a temperature of 15 C (157). Enrofloxacin was absorbed and eliminated slowly after oral administration to the sea bass. Following bath treatment, enrofloxacin efficiently penetrated fish tissues but it was poorly metabolized compared with mammals. On the other hand, ciprofloxacin was generally detected in very low concentrations (less than 0.02 ppm) in plasma samples after both oral and bath treatment. Liver levels of ciprofloxacin were found to be 0.12 ppm after a 5 ppm bathing for 24 h, 0.06 ppm after a 10 ppm bathing for 8 h, and 0.33 ppm after a 50 ppm bathing for 4 h, suggestive of hepatic metabolism of enrofloxacin. [Pg.78]

The residue depletion profile of flumequine in uout seems to be quite similar to that in the sea bass (174). When flumequine was administered to seabass as a mixture with the feed at a dosage of 12 mg/kg bw for 5 days, residues of flumequine in muscle tissue could be detected by 36 h after the last treatment. The relatively high temperature of the sea water (21-25.3 C) in this study was suggested as the primary factor determining the rapid depletion of residues from the fish tissue. In another study (175), flumequine disappeared from muscle of sea bream at 240 h after the end of treatment, but showed a longer depletion rate from skin and vertebrae that behaved in fact as reservoir tissues. Much slower depletion profiles have been reported in studies carried out with Atlantic salmon (158, 170, 176), rainbow trout (177), and some wild fish caught in the vicinity of fish farms such as saithe and cod (178). [Pg.80]

High Vitamin D content (1.000 — 25 / 106 1. U./100 grams ).- Liver oils from Bonito, cod, halibut, herring, lingcod. sablefish, sea bass, soupfin shark, swordfish, tuna. [Pg.1704]

GRASS SHRIMP, WHITE SHRIMP BANDED DRUM. SILVER JENNY POLYCHAETE SEA BASS... [Pg.130]

Pagliarani, A., Pirini, M., Trigari, G. and Ventrella, V. (1986). Effect of diets containing different oils on brain fatty acid composition in sea bass (Dicentrarchus labrax). Comparative Biochemistry and Physiology 83B, 277-282. [Pg.299]

Zanuy, S. and Carrillo, M. (1985). Annual cycles of growth, feeding rate, gross conversion efficiency and haematocrit levels of sea bass adapted to two different osmotic media. Aquaculture 44,11-25. [Pg.324]

Figure 1.3. p,p DDE levels (average of five specimens data in each location) in fishes (Sea bass) in Tokyo Bay, Osaka Bay and Seto Inland sea between 1978 and 2000. [Pg.10]

Similar trends are also observed in PCB levels in Sea bass in the three coastal water environments as shown in Fig. 1.4. Again a clear decreasing trend was seen in Seto Inland sea, while the levels in Tokyo Bay are rather flat with a couple of fluctuations. The time trend in Osaka Bay is more or less similar to Tokyo Bay but with no clear decrease in recent decades. The difference between / ,//-DDE and PCB time trends in Osaka Bay might reflect either the difference in recent loading of the compounds to the Bay or the difference in their pollution histories. [Pg.10]


See other pages where Sea bass is mentioned: [Pg.14]    [Pg.809]    [Pg.198]    [Pg.1377]    [Pg.824]    [Pg.824]    [Pg.5]    [Pg.28]    [Pg.41]    [Pg.747]    [Pg.198]    [Pg.1377]    [Pg.1499]    [Pg.360]    [Pg.462]    [Pg.14]    [Pg.101]    [Pg.54]    [Pg.329]   
See also in sourсe #XX -- [ Pg.243 , Pg.297 , Pg.438 , Pg.484 ]




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Sea bass Lateolabrax japonicus

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