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1.
Environ Health Perspect ; 102(2): 200-15, 1994 Feb.
Article in English | MEDLINE | ID: mdl-8033852

ABSTRACT

Relationships between hepatic lesions and chemical contaminant concentrations in sediments, stomach contents, liver tissue, and bile were statistically evaluated in three species of bottomfish, English sole (Pleuronectes vetulus), starry flounder (Platichthys stellatus), and white croaker (Genyonemus lineatus), captured from 27 urban and nonurban sites on the Pacific Coast from Alaska to southern California. Lesions detected were neoplasms, preneoplastic foci of cellular alteration, nonneoplastic proliferative lesions, unique or specific degenerative/necrotic lesions, nonspecific degenerative/necrotic lesions, and hydropic vacuolation of biliary epithelial cells and hepatocytes. In general, lesion prevalences were significantly higher in all three species captured at chemically contaminated urban sites, and certain lesions had significantly higher relative risks of occurrence at urban sites in Puget Sound, San Francisco Bay, the vicinity of Los Angeles, and San Diego Bay. Concentrations of polycyclic aromatic hydrocarbons, polychlorinated biphenyls, DDT and its derivatives, and chlordanes and dieldrin in sediment, stomach contents, liver, and fluorescent aromatic compounds in bile were significant risk factors for the occurrence of neoplastic, preneoplastic, nonneoplastic proliferative, and specific degenerative/necrotic lesions, as well as hydropic vacuolation. Fish age also had a significant influence on occurrence of several hepatic lesions, but gender was rarely a significant risk factor. These relationships provide strong evidence for the involvement of environmental contaminants in the etiology of hepatic lesions in several marine bottomfish species and clearly indicate the utility of these lesions as biomarkers of contaminant-induced effects in wild fish.


Subject(s)
Chemical and Drug Induced Liver Injury/etiology , Environmental Monitoring , Fishes/metabolism , Flounder/metabolism , Water Pollutants, Chemical/adverse effects , Animals , Bile/metabolism , Chemical and Drug Induced Liver Injury/epidemiology , Chemical and Drug Induced Liver Injury/metabolism , Epidemiological Monitoring , Female , Gastric Mucosa/metabolism , Liver/metabolism , Logistic Models , Male , Pacific Ocean , Prevalence , Risk Factors , Water Pollutants, Chemical/pharmacokinetics
3.
Cell Tissue Res ; 211(2): 303-16, 1980.
Article in English | MEDLINE | ID: mdl-7417988

ABSTRACT

Scale formation in Cyprinodon variegatus was found to be initiated at about 26 to 30 days after hatching. Ultrastructural investigation revealed that within 4 to 6 h in the first-formed scales the marginal cells begin to flatten and differentiate into osteogenic cells, which later change to osteoblasts and fibroblasts. These cells are separated from the surrounding epithelial cells by a basal lamina. The osteoid is formed by the marginal and osteogenic cells; the osseous layer by the osteoblasts; and the fibrillary plate by the fibroblasts. The osteoid is formed within 2 to 3 h after the initiation of the scale, and within 20 to 24 h the osseous layer is formed. Hydroxyapatite crystals are deposited in the matrix of the osseous layer without apparent association with collagen fibers. No matrix vesicles or dense bodies are evident at the sites of calcification. The fibrillary plate arises 18 to 20 h after the initiation of the scale. It is also partially calcified, but not before the third week of scale formation. The crystals develop almost exclusively between the collagen fibers at the extreme edge of the calcifying front, but solid calcification of the fibers results with futher growth of the crystals. The fibroblasts appear to participate in calcification of the fibrillary plate.


Subject(s)
Carps/anatomy & histology , Cyprinidae/anatomy & histology , Animals , Calcification, Physiologic , Carps/physiology , Cell Differentiation , Fibroblasts/ultrastructure , Microscopy, Electron , Osteoblasts/ultrastructure
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