INTRACELLULAR OSMOREGULATION IN THE ESTUARINE MOLLUSC VILLORITA CYPRINOIDES VAR. COCHINENSIS (Mollusca: Bivalvia) Hanley

The present investigation is dedicated to understanding various mechanisms of salinity tolerance in the estuarine clam V. cyprinoides var. cochinensis. Even though V. cyprinoids var. cochinensis and V. cyprinoides are found to coexist in the same area, V. cyprinoids is reported to tolerate higher salinities than variety cochinenesis. Variations in the salinity of sea water may affect the aquatic organisms through specific gravity control and variations in osmotic pressure. The specific gravity of most soft tissues is close to that of normal seawater. Many bottom living forms, both attached and motile, have very high specific gravities eg.villorita cyprinoids. Villorita spp. Occurs abundantly in the reaches of the estuary and backwaters of Kerala. In both marine and estuarine forms, it is observed that mantle employs a lesser quantity of amino acids compared to adductor and foot. The regulation of cell volume is not carried out equally in all types of tissues. The capability of salinity tolerance is an aggregate of both the capabilities of extra cellular anisosmotic and intracellular isosmotic regulations in osmoconforming animals. The ultimate aim of water regulation is to regulate the cell volume.T here are slight changes occur in cell volume even in osmoregulators. These studies can also help in revealing the changes brought about in the cellular organelles like lysosomes, which were found to have a role in the osmoregulatory process. The osmoregulatory machinery of estuarine animals is more streamlined for a successful life in the estuarine regime.

Studies on the effect of the organophosphorus pesticide Eka(Rlu) x EC 25 on the bacterial flora of Villorita cyprinoides var. cochinensis (Han1ey)

The thesis is Studies on the Effect or the Obganophosphorus Pesticide Ekalux(R) EC 25 on the Bacterial Flora or Villorita Cyprinoides Var.Cochinensis (Hanley). For the present investigation, the black clam Villorita gyprinoides var. cochinensis (Hanley), a most common clam genus present in this estuarine system has been selected as test organaism and Ekalux (R) EC 25 as toxicant. The aspects dealt with are 1. Total heterotrophic bacterial population, 2. Generic composition, 3. Hydrolytic enzyme producing bacteria, 4. Antibiotic resistance, 5. Heavy metal resistance, 6. The effect of pesticide concentration on the growth of the bacteria and 7. Effect of temperature, pH and sodium chloride on the growth and phosphate release of selected isolates.The samples for the experiment were collected from the Vembanad Lake, near Kumbalam Island during the period of September 1985 to May '86. The THB of the estuarine water and clams contained 6.5 x I04/ml and 2.975 x l06/g respectively, immediately after collection. Untreated water and clam samples showed enormous increase in THB from 0 hr population. The treated samples (water and clams) contained higher THB than 0 hr. In general, THB was observed to increase tremendously in the samples treated with pesticide when compared to their native flora. With reference to various concentrations of pesticides, THB recorded an increase with increase of concentration in water and clam samples.

Quantization of specific trace metals in bivalve, Villorita Cyprinoides Var Cochinensis in the Cochin estuary

Present study consists the quantization of specific metals-- Cr, Cd, Pb, Zn and Cu observed in the experimental bivalve, Villorita species. Bivalve specimens were collected seasonally from the identified three hot spots of Vembanad Lake. Soft tissue concentrations of metals are very sensitive in reflecting changes in the ambient environment and hence important in assessing the environmental quality. Concentrations of Zn in bivalves were fairly high compared to other metals. All the stations showed a maximum concentration during premonsoon and minimum during the other two seasons. Levels of Pb, Cu, Zn, Cd and Cr are between 0-6.17mg/kg, 0-17.224mg/kg, 1.916-255.163mg/kg, 0.325-4.133mg/kg, and 0-15.233mg/kg respectively

Sēfer Kōkev�� de-šāv��t : hû hak-kôkāv ašer ʿāvar ... hay-yir'at šāmayim le-nāšîm ... li-lešôn aškenaz û-niqrā šemô <šṭerin šus>

Digitalisat der Ausg. Amśṭrdm, 1694/95

Studies on the Intercompartmental Exchange of Trace Metals in an Estuarine System

The present study is an attempt at investigating the intercompartmental exchange of trace metals (copper, cadmium, zinc, lead and nickel) in the Cochin estuary. The nature and extent of distribution in the different compartments with special reference to the transport from environmental compartments to biological compartments have been dealt with in detail. The suitability of the shells of Villorita cyprinoides var cochinensis (Hanely) in pollution monitoring activities has been assessed. A mathematical model (SAAMPLE - Shells in the Assessment of Aquatic Metal Pollution Levels) based on kinetic laws that govern the intercompartmental exchange has been proposed.

Acerca de los tipos de dos Veronica rifeñas.

Hace unos años, se publicó en esta misma sección una nota sobre Veronica rosea (Soriano, 1996), en la que se anticipaba el tratamiento de este taxón en la checklist de la fl ora del norte de Marruecos (Valdés & al. 2002; Soriano, 2002). Entre otras cosas, se formalizaba en ella la descripción de V. rosea subsp. atlantica var. macrantha, propuesta por Pau como V. rosea var. macrantha y distribuida por Font Quer en el Iter maroccanum de 1930, aunque sin la diagnosis correspondiente.

Acerca de los tipos de dos Veronica rifeñas.

Hace unos años, se publicó en esta misma sección una nota sobre Veronica rosea (Soriano, 1996), en la que se anticipaba el tratamiento de este taxón en la checklist de la fl ora del norte de Marruecos (Valdés & al. 2002; Soriano, 2002). Entre otras cosas, se formalizaba en ella la descripción de V. rosea subsp. atlantica var. macrantha, propuesta por Pau como V. rosea var. macrantha y distribuida por Font Quer en el Iter maroccanum de 1930, aunque sin la diagnosis correspondiente.

Acerca de los tipos de dos Veronica rifeñas.

Hace unos años, se publicó en esta misma sección una nota sobre Veronica rosea (Soriano, 1996), en la que se anticipaba el tratamiento de este taxón en la checklist de la fl ora del norte de Marruecos (Valdés & al. 2002; Soriano, 2002). Entre otras cosas, se formalizaba en ella la descripción de V. rosea subsp. atlantica var. macrantha, propuesta por Pau como V. rosea var. macrantha y distribuida por Font Quer en el Iter maroccanum de 1930, aunque sin la diagnosis correspondiente.

Acerca de los tipos de dos Veronica rifeñas.

Hace unos años, se publicó en esta misma sección una nota sobre Veronica rosea (Soriano, 1996), en la que se anticipaba el tratamiento de este taxón en la checklist de la fl ora del norte de Marruecos (Valdés & al. 2002; Soriano, 2002). Entre otras cosas, se formalizaba en ella la descripción de V. rosea subsp. atlantica var. macrantha, propuesta por Pau como V. rosea var. macrantha y distribuida por Font Quer en el Iter maroccanum de 1930, aunque sin la diagnosis correspondiente.

Acerca de los tipos de dos Veronica rifeñas.

Hace unos años, se publicó en esta misma sección una nota sobre Veronica rosea (Soriano, 1996), en la que se anticipaba el tratamiento de este taxón en la checklist de la fl ora del norte de Marruecos (Valdés & al. 2002; Soriano, 2002). Entre otras cosas, se formalizaba en ella la descripción de V. rosea subsp. atlantica var. macrantha, propuesta por Pau como V. rosea var. macrantha y distribuida por Font Quer en el Iter maroccanum de 1930, aunque sin la diagnosis correspondiente.

Acerca de los tipos de dos Veronica rifeñas.

Hace unos años, se publicó en esta misma sección una nota sobre Veronica rosea (Soriano, 1996), en la que se anticipaba el tratamiento de este taxón en la checklist de la fl ora del norte de Marruecos (Valdés & al. 2002; Soriano, 2002). Entre otras cosas, se formalizaba en ella la descripción de V. rosea subsp. atlantica var. macrantha, propuesta por Pau como V. rosea var. macrantha y distribuida por Font Quer en el Iter maroccanum de 1930, aunque sin la diagnosis correspondiente.

Acerca de los tipos de dos Veronica rifeñas.

Hace unos años, se publicó en esta misma sección una nota sobre Veronica rosea (Soriano, 1996), en la que se anticipaba el tratamiento de este taxón en la checklist de la fl ora del norte de Marruecos (Valdés & al. 2002; Soriano, 2002). Entre otras cosas, se formalizaba en ella la descripción de V. rosea subsp. atlantica var. macrantha, propuesta por Pau como V. rosea var. macrantha y distribuida por Font Quer en el Iter maroccanum de 1930, aunque sin la diagnosis correspondiente.

Corrosión

UANL

Megabenthic communities in the waters around Svalbard during POLARSTERN cruise ARK-VIII/2 (EPOS II)

Composition and distribution of megabenthic communities around Svalbard were investigated in June/July 1991 with 20 Agassiz trawl and 5 bottom trawl hauls in depths between 100 and 2100 m. About 370 species, ranging from sponges to fish, were identified in the catches. Species numbers per station ranged from 21 to 86. Brittle stars, such as Ophiacantha bidentata, Ophiura sarsi and Ophiocten sericeum, were most important in terms of constancy and relative abundance in the catches. Other prominent faunal elements were eunephthyid alcyonarians, bivalves, shrimps, sea stars and fish (Gadidae, Zoarcidae, Cottidae). Multivariate analyses of the species and environmental data sets showed that the spatial distribution of the megabenthos was characterized by a pronounced depth zonation: abyssal, bathyal, off-shore shelf and fjordic communities were discriminated. However, a gradient in sediment properties, especially the organic carbon content, seemed to superimpose on the bathymetric pattern. Both main factors are interpreted as proxies of the average food availability, which is, hence, suggested to have the strongest influence in structuring megabenthic communities off Svalbard.

Benthic foraminifera of cores from ODP Leg 117

The relative abundances of benthic foraminifers from the Oman margin have been analyzed from ODP Sites 725 and 726 near the upper boundary of the oxygen-minimum zone (OMZ) and 728 near the lower boundary. The relative abundance pattern of the benthic foraminiferal species in the two shallow sites show synchronous changes, which, together with variations in the faunal composition, may be attributed to changes in the location of the upper boundary of the OMZ during the last 7 million years. At the deeper site, the relative abundance pattern shows considerable variation in the faunal composition during the last 8 million years. The strong dominance of the shallow-water species Ammonia beccarii during the early Pliocene at Site 728 suggests a water depth less than 400 m during the early Pliocene and subsequent subsidence during the middle and late Pliocene to the present > 1400 m water depth.