Increment formation in otoliths of slow-growing winter flounder (Pleuronectes americanus) larvae in cold water

1998 ◽  
Vol 55 (1) ◽  
pp. 162-169 ◽  
Author(s):  
Maria C Casas

Known-age winter flounder (Pleuronectes americanus) larvae were reared in large outdoor mesocosms where the temperatures were <5°C for the first 40 days and increased slowly after this and in field enclosures where the temperature ranged between 12.3 and 19.6°C. In the cold-water group, somatic and otolith growth were suppressed at the low initial temperatures and no increments were visible. After temperatures increased, somatic growth was evident and a variable number of initial narrow increments (0.2-0.6 µm) was observed. As larvae emerged from this initial period of slow growth, they began to develop rapidly and otolith increment widths increased to 1.0-3.0 µm. In contrast, larvae reared at the warmer temperature grew rapidly and laid down daily increments beginning 5 days after hatching.


1991 ◽  
Vol 48 (10) ◽  
pp. 1862-1871 ◽  
Author(s):  
Susan M. Sogard

In winter flounder (Pseudopleuronectes americanus), sagittae developed secondary origins of calcium carbonate deposition during metamorphosis just prior to completion of eye migration. Sagittae and lapilli of larvae were bilaterally symmetrical, but those of postmetamorphic individuals showed increasing morphological asymmetry between the left and right side. In juveniles marked with oxytetracycline and maintained in field enclosures for 10 d, increment deposition on sagittae was daily if somatic growth following marking was good (> 0.25 mm∙d−1), but less than daily in individuals with poor or negative somatic growth (< 0.25 mm∙d−1). Narrowly spaced increments or divergence of otolith growth from the main rostral–postrostral growth axis, where counts were made, may have limited detection of daily deposition. Lack of detectable daily increments occurred primarily in larger juveniles (> 50 mm total length), which had lower absolute growth rates than newly settled juveniles. In oxytetracycline-marked fish there was a significant correspondence between otolith growth and somatic growth in both length and weight. The strength of this relationship, which varied with the specific radius used, was highest (r = 0.854) for the rostral radius of the left sagitta; increment widths along this radius are reliable estimators of prior somatic growth rates.



1993 ◽  
Vol 24 (4) ◽  
pp. 427-431 ◽  
Author(s):  
J. J. Pereira ◽  
R. Mercaldo-Allen ◽  
C. Kuropat ◽  
D. Luedke ◽  
G. Sennefelder


1994 ◽  
Vol 51 (4) ◽  
pp. 933-941 ◽  
Author(s):  
Emily Monosson ◽  
John J. Stegeman

Cytochrome P4501A (CYP1A), Aroclor 1254 (A1254), and 3,3′,4,4′-tetrachlorobiphenyl (TCB) were measured in liver of winter flounder, Pleuronectes americanus, from Boston Harbor, Mass., Hempsted Harbor, N.Y., Niantic, Conn., and an offshore site, Georges Bank. We also measured CYP1A content and activity in flounder from Passamaquoddy Bay, N.B. Concentrations of A1254 and TCB were the least in fish from Georges Bank (0.46 and 0.002 μg∙g dry weight−1, respectively); concentrations in fish from Boston, Niantic, and Hempsted ranged from 7.6 to 11.3 μg∙g−1 and from 0.013 to 0.024 μg∙g−1. Immunodetected microsomal CYP1A contents (expressed as scup P450E equivalents) were 0.17 and 0.19 nmol∙mg−1 in fish from Georges Bank and Passamaquoddy and 0.25–0.41 nmol∙mg−1 in fish from Boston, Niantic, and Hempsted. Ethoxyresorufin-O-deethylase specific activities likewise were greater in fish from Boston, Niantic, and Hempsted (1.7–2.4 nmol∙min−1∙mg−1) than in fish from Georges Bank or Passamaquoddy (0.83 and 0.61 nmol∙min−1∙mg−1). CYP1A content and activity were correlated with hepatic concentrations of A1254 and TCB. These data, together with data reported in previous studies, indicate that strong induction of CYP1A protein occurs in winter flounder populations along most of the industrialized east coast and that induction of CYP1A is common, but less strong, at sites distant from the urban centers of the Northeast.



1993 ◽  
Vol 27 (13) ◽  
pp. 2759-2771 ◽  
Author(s):  
Lyndal L. Johnson ◽  
Carla M. Stehr ◽  
O. Paul Olson ◽  
Mark S. Myers ◽  
Susan M. Pierce ◽  
...  


1992 ◽  
Vol 41 (2) ◽  
pp. 327-338 ◽  
Author(s):  
J. J. Pereira ◽  
E. J. Lewis ◽  
R. L. Spallone ◽  
C. Sword




1994 ◽  
Vol 51 (6) ◽  
pp. 1368-1375 ◽  
Author(s):  
V. Vignier ◽  
J. H. Vandermeulen ◽  
J. Singh ◽  
D. Mossman

7-Ethoxyresorufin-O-deethylase (EROD), benzo[a]pyrene hydroxylase (BaPH), and cytochromes P-450 (cyt-P450) and b5 (cyt-b5) varied annually in winter flounder (Pleuronectes americanus) collected in August of 1987, 1988, and 1989 from a coal tar contaminated estuary (Sydney, Nova Scotia, Canada). For August 1989, with fish available from all estuary areas, these indices correlated strongly with a spatial (along estuary) gradient in PAH in bottom sediments (7.19 ± 6.59–191 ± 184 μg g dry weight−1). Mean EROD activities in flounder near the coal tar source were up to seven times those in other estuary areas and paralleled sediment PAH loadings; however, standard deviations were high. Correlations for all MFO indices and sediment PAH were obtained in female flounder (P < 0.01: EROD, cyt-b5, cyt-P450; P < 0.02: BaPH). For male flounder the trend was similar, but only cyt-P450 correlated with sediment PAH (P < 0.017). BaPH activity was highest near the coal tar source but was more variable and less sensitive to pollutant levels than EROD activity. Somatic indices in fish from Sydney estuary and St. George's Bay were similar. Winter flounder are vulnerable to PAH-induced MFO activities from coal tar contaminated sediments, but MFO induction does not occur equally in all fish; single-season or single-year data must be interpreted with caution.



Author(s):  
H.M Murray ◽  
J.C Perez-Casanova ◽  
J.W Gallant ◽  
S.C Johnson ◽  
S.E Douglas


1995 ◽  
Vol 52 (12) ◽  
pp. 2724-2735 ◽  
Author(s):  
J. F. Payne ◽  
L. L Fancey ◽  
J. Hellou ◽  
M. J. King ◽  
G. L. Fletcher

Most studies on the chronic toxicity of hydrocarbons have focused on the polycyclic aromatic component; however, information is also required on the chronic toxicity of other classes of hydrocarbons. This need has been brought to the forefront by the controversy about the use of aliphatic hydrocarbon-based drilling fluids at petroleum development sites in the marine environment. Dose–response relationships were studied for a variety of indices in a chronic toxicity study with winter flounder (Pleuronectes americanus) exposed to sediments contaminated with drill cuttings enriched in hydrocarbons. The indices investigated were biologically meaningful and included organ and body condition indices, muscle and liver energy reserves, mixed-function oxygenase detoxification enzymes, blood parameters, and liver and gill histopathology. There was no evidence of dose–response relationships and most indices remained unaffected even at the highest exposure level. The study supports the hypothesis that the aliphatic component of complex hydrocarbon mixtures is relatively nontoxic, and it will be of particular interest for evaluating the scope of environmental risks associated with the use of oil-base drilling fluids in the marine environment.





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