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Biomedical subjects

F A Vega

Publications and source records attributed to F A Vega.

15 recordsLinked to original sources
PubMed2007

Accidental organochlorine pesticide contamination of soil in Porrino, Spain.

In the 1960s at Porriño, Spain, soil from a pesticide factory dump was placed in an uncontrolled land infill during demolition. Since then, organochlorine pesticides have degraded and migrated from their original location. Concentrations of lindane, DDT, dicofol, and related side products or degradation products were determined at depths of 0 to 20, 20 to 60 and 60 to 100 cm along a 300-m transect running between the land infill and a nearby river. Depthwise nonmonotonicities (lowest concentrations of DDT and dicofol were found in the 20- to 60-cm layer) were attributed to the occurrence of several successive spill episodes; in general, concentrations were highest or near-highest in the 0- to 20-cm layer. At the dump site, the analyte contents of the 0- to 20-cm layer were as follows: alpha-hexachlorocyclohexane (alpha-HCH), 25 mg kg-1; beta-HCH, 15 mg kg-1; gamma-HCH (lindane), 1.3 mg kg-1; delta-HCH, 0.5 mg kg-1; DDT, 2.5 mg kg-1; dicofol, 0.05 mg kg-1; DDD+DDE, 2.2 mg kg-1. The alpha-HCH/gamma-HCH ratio was higher than in commercial products, and the DDT/(DDD + DDE) ratio lower, suggesting the degradation of lindane and DDT with time. In general, the concentrations of HCH isomers, DDT, and dicofol fell with increasing distance from the dump site; in particular, the rapid fall in HCH concentrations illustrates the marked immobility of these species in the soil. By contrast, the combined concentration of the DDT degradation products DDD and DDE rose with distance from the dump site, which is attributed to their higher mobility.

Hydrocarbons, Chlorinated↗
PubMed2006

Competitive sorption and desorption of heavy metals by individual soil components.

Knowledge of sorption and desorption of heavy metals by individual soil components should be useful for modelling the behaviour of soils of arbitrary composition when contaminated by heavy metals, and for designing amendments increasing the fixation of heavy metals by soils polluted by these species. In this study the competitive sorption and desorption of Cd, Cr, Cu, Ni, Pb and Zn by humified organic matter, Fe and Mn oxides, kaolinite, vermiculite and mica were investigated. Due to the homogeneity of the sorbents, between-metal competition for binding sites led to their preferences for one or another metal being much more manifest than in the case of whole soils. On the basis of k(d100) values (distribution coefficients calculated in sorption-desorption experiments in which the initial sorption solution contained 100mgL(-1) of each metal), kaolinite and mica preferentially sorbed and retained chromium; vermiculite, copper and zinc; HOM, Fe oxide and Mn oxide, lead (HOM and Mn oxide also sorbed and retained considerable amounts of copper). Mica only retained sorbed chromium, Fe oxide sorbed cadmium and lead, and kaolinite did not retain sorbed copper. The sorbents retaining the greatest proportions of sorbed metals were vermiculite and Mn oxide, but the ratios of k(d100) values for retention and sorption suggest that cations were least reversibly bound by Mn oxide, and most reversibly by vermiculite.

Adsorption↗
PubMed2006

Competitive sorption and desorption of heavy metals in mine soils: influence of mine soil characteristics.

Many mine soils are chemically, physically, and biologically unstable and deficient. They are sometimes amended with sewage sludge and ashes but often contain heavy metals that increase the already high mine soils' heavy metal contents. Cd, Cr, Cu, Ni, Pb, and Zn in mutual competition were added to five mine soils (Galicia, Spain). Soil capacities for heavy metal sorption and retention were determined by means of distribution coefficients and selectivity sequences among metals. Influence of soil characteristics on sorption and retention was also examined. Retention selectivity sequences indicate that, in most of the soils, Pb is the preferred retained metal, followed by Cr. The last metals in these sequences are Ni, Cd, and Zn. Soil organic matter content plays a fundamental role in control of Pb sorption. Gibbsite, goethite, and mica influence Cr retention. Soil organic matter, oxides, and chlorite contents are correlated with K(d sigma sp medium). Heavy metals are weakly adsorbed by soils and then desorbed in high amounts. To recover these soils it is necessary to avoid the use of residues or ashes that contain heavy metals due to their low heavy metal retention capacity.

Journal Article↗
PubMed2004

Zn adsorption by different fractions of Galician soils.

To evaluate the contribution of organic matter, oxides, and clay fraction to Zn adsorption in six soils from Galicia (Spain), after soil characterization, adsorption isotherms were obtained by adding nine solutions containing between 20 and 500 mg L(-1) concentrations of Zn(NO(3))(2). Distribution coefficients were obtained from the data of adsorption isotherms. Zn adsorption isotherms corresponding to untreated soil and to the organic matter removed samples and organic matter and oxides removed samples were compared with curves pattern and adjusted to Langmuir and Freundlich empirical models. Untreated soils described L-curves whereas when soils were deprived of any component, the curves described were S-type. Distribution coefficients allowed knowing the Zn adsorption capacity of the untreated soil, and of the organic matter, oxides, and clay fraction. Soil organic matter is the main component that affects Zn adsorption as long as soil pH is near neutrality. At acid pH, the oxides are the main component that affects Zn adsorption, although to a much smaller extent than the organic matter near neutral conditions. So soil pH is the main soil factor that determines Zn adsorption, before any other soil property.

Journal Article↗
PubMed2004

Heavy metal adsorption by humic umbrisols: selectivity sequences and competitive sorption kinetics.

This work examines sorption kinetics of Cd, Cr, Cu, Ni, Pb, and Zn adsorbed simultaneously by four humic umbrisols, as well as the influence of the soil components on the adsorption rate. Starting from the value of K(d), the metals most adsorbed by the soils are Cu, Cr, and Pb. The soils that adsorb the largest amounts of metals have also the highest organic matter, oxide, and clay content. In general, the most common selectivity sequence of adsorption is Pb > Cr > Cu > Cd approximately Ni approximately Zn. Sorption kinetics is rapid for Cr, Cu, and Pb in all the soils studied and competes favorably for the adsorption sites with Cd, Ni, and Zn. Various rate equations (zero-order, first-order, second-order, Elovich, and power function) were applied to the kinetic data to obtain the corresponding rate coefficients. A second-order reaction best represents the kinetic data for Cr in most of the soils.

Journal Article↗
PubMed1993

Stability of some phenolic antioxidants in fatty preparations.

Stability of butylated hydroxyanisole (BHA), propyl gallate (PG), trihydroxy butyrophenone (THBP), tert-butyl hydroquinone (TBHQ) and a mixture of PG and BHA (1:1) in fatty preparations stored under three different conditions was studied. Each antioxidant was added to a fatty model to determine its degradation kinetics and its evolution during the oxidation of the fatty product. Their degradation was adequately described by a first-order kinetic process. An opposite relationship between the stability of antioxidants and their rate protection against oxidation of the fatty product was obtained. At 25 degrees C, t90 values ranged between 10 days for TBHQ and 61 days for BHA. On the other hand, compared when they were formulated alone, the increase of PG and the diminution of BHA degradation kinetics were observed. A degradation product arising from TBHQ was found in samples and stock solutions; an HPLC method for its identification is proposed with detection at 254 nm.

Antioxidants↗
PubMed1992

Antioxidants in some pharmaceuticals, cosmetics and food from the European market.

A specific and sensitive reverse phase HPLC method (AO-1) for the quantitative determination of ten phenolic antioxidants and propyl paraben in fatty products (food, pharmaceuticals and cosmetics) has been developed. Extraction with acetonitrile from a hexane dilution of the products; acetic acid-water-acetonitrile-methanol solvent system and detection at 280 nm and quantification by internal standard procedure (reference compound: DMP, dimethylphenol) were used. Good resolutions for all peaks, especially BHT and DG, and no interferences with others common additives were achieved. Mean recoveries, by addition of standards to sample at 20, 50 and 100 micrograms/g, were 96-101% (BHT, 84-86%); minimal quantifiable levels were 0.5-1.6 micrograms/g. Two simple isocratic methods for the confirmation of data obtained by AO-1 were also developed: AO-2 for seven phenolic antioxidants and propyl paraben with DMP as internal standard, AO-3 for four lipophilic antioxidants with di-tert-butylphenol (DTBP) as internal standard.

Antioxidants↗
PubMed1982

Failure of periodic ultraviolet radiation treatments to prevent sensitization to nitrogen mustard: a case report.

We have reported that prior ultraviolet radiation (UVR) exposure significantly delayed development of contact sensitivity to nitrogen mustard (Halprin et al., 1981). We felt that this effect was due to disruption of functional Langerhans cells in skin by UVR and suggested that periodic UVR treatments might prevent sensitization to the mustard. We now report on a patient with mycosis fungoides whose epidermal Langerhans cell count was monitored with the ATP-ase stain in order to determine when such 'booster" UVR therapy was to be given. Our attempts to interfere with Langerhans cell function in this manner failed to prevent delayed contact sensitivity to nitrogen mustard and may have been partly responsible for the development of contact urticaria to nitrogen mustard after 28 days of use. Whether the reaction was a delayed, cell-mediated reaction, or an antibody mediated reaction is not clear, but the use of UVR did fail to prevent contact sensitivity to the nitrogen mustard in our patient.

Cell Count↗
PubMedDate not supplied

Effect of the Prestige oil spill on salt marsh soils on the coast of Galicia (northwestern Spain).

At four estuarine sites on the coast of Galicia (northwestern Spain), all of which were affected by the Prestige oil spill, soil samples were taken from polluted and unpolluted areas and their petroleum hydrocarbon contents, heavy metal contents, and other chemical and physical characteristics were measured. Oil pollution altered both chemical and physical soil properties, aggregating soil particles in plaques, lowering porosity, and increasing resistance to penetration and hydrophobicity. The chromium, nickel, copper, iron, lead, and vanadium contents of polluted soils were between 2 and 2500 times higher than those of their unpolluted counterparts and the background concentrations in Galician coastal sediments. In the cases of Cr, Cu, Ni, Pb, and V, their origin in the polluting oil was corroborated by the high correlation (r >/= 0.74) between the concentrations of these metals and the total petroleum hydrocarbon (TPH) content of the polluted soils. Soil redox potentials ranged from -19 to -114 mV in polluted soils and 112 to 164 mV in unpolluted soils, and were negatively correlated with TPH content (p < 0.01). The low values in the polluted soils explain why the soluble fractions of their total heavy metal contents were very small (generally less than 3%, and in many cases undetectable).

Accidents↗
PubMedDate not supplied

Pyrogens in small-volume parenterals prepared in hospital pharmacy.

Three pyrogen assay methods [the rabbit method, Limulus Amebocyte Lysate (LAL) gelation and chromogenic substrate, and bioburden prior to sterilization] were evaluated in three standard batches of small-volume parenteral preparations; i.e., water for injection, sodium chloride 0.9% injection, and sodium bicarbonate 8.4% injection. The same preparations were also assayed after contamination with Escherichia coli followed by sterilization. All methods gave the same results with the water for injection and the sodium chloride 0.9%. With sodium bicarbonate 8.4%, only the rabbit method was valid. For sodium chloride 0.9%, the chromogenic substrate method was valid; the gelation method was not valid. Endotoxins from the manufacturing plant were less pyrogenic in rabbits than were standard endotoxins or those from hospital E. coli.

Drug Contamination↗