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Levels in body

Exposure Levels in Humans. The database for -hexane exposure levels in humans is limited to a few older detections of -hexane in breast milk and determinations of levels in body fluids and alveolar air collected in foreign countries. A more current and complete database would be helpful in determining the current exposure levels, thereby permitting the estimation of the average daily dose associated with various scenarios (e.g., living near a hazardous waste site). Since -hexane is rapidly metabolized within the human body, further studies correlating levels in the environment with the levels of metabolites and biomarkers in humans would be helpful. This information is necessary for assessing the need to conduct health studies on these populations. [Pg.205]

A much more serious genetic disease, first described by Foiling in 1934, is phenylketonuria. Here the disturbance in phenylalanine metabolism is due to an autosomal recessive deficiency in liver phenylalanine hydroxylase (Jervis, 1954) which normally converts significant amounts of phenylalanine to tyrosine. Phenylalanine can therefore only be metabolized to phenylpyruvate and other derivatives, a route which is inadequate to dispose of all the phenylalanine in the diet. The amino acid and phenylpyruvate therefore accummulate. The condition is characterized by serious mental retardation, for reasons which are unknown. By the early 1950s it was found that if the condition is diagnosed at birth and amounts of phenylalanine in the diet immediately and permamently reduced, mental retardation can be minimized. The defect is shown only in liver and is not detectable in amniotic fluid cells nor in fibroblasts. A very sensitive bacterial assay has therefore been developed for routine screening of phenylalanine levels in body fluids in newborn babies. [Pg.44]

Differences in metabolic detoxifIcatlon rates between linear and angular furanocoumarlns observed in our studies were not great. However, the fact that the angular furanocoumarln under study accumulated to appreciably higher levels in body tissues of polyxenes caterpillars than did the linear analog is... [Pg.460]

Exposure Levels in Humans. This information is necessary for assessing the need to conduct health studies on these populations. The nickel levels in body fluids, tissue, hair, nails, and breast milk are available (DiPietro et al. 1989 Hopfer et al. 1989 lARC 1990 Iyengar 1989 Takagi et al. 1986, 1988). Serum and urine levels in some exposed workers have also been published (Angerer and Lehnert 1990 Bencko et al. 1986 Bemacki et al. 1978 Elias et al. 1989 Ghezzi et al. 1989 Hassler et al. [Pg.206]

Morgan and Rouge 1984 Toijussen and Andersen 1979). These data do not refer to populations living aroimd the hazardous waste sites that contain elevated levels of nickel. Additional studies which examine nickel levels in body fluids and tissues from persons living near hazardous waste sites that contain elevated levels of nickel would be useful. [Pg.206]

However several POPs, particularly the OCPs and dioxins, remain at low levels in the Australian environment and several remain persistent at low levels in body fats and fluids of Australians. The levels reflect the past use and persistence of OCPs in the Australian environment, contamination of the food chain and the capacity of the body to metabolise and store in body fats. The dioxins remain due to the ubiquitous nature of their sources with combustion as a major source and their persistence. Future trends are likely to mean very low-level residues in human fats of DDE, cyclodienes, HCB, HCHs and dioxins in the long term. Their rate of decline will probably depend on removing HCB from chlorinated industrial chemicals and OCPs from the environment (e.g. remediation of contaminated soils) by hazardous waste treatment methods (e.g. physical, chemical and biological degradation or fixation) or secure landfill. [Pg.768]

In recent years, the importance of enzyme levels in body fluids for clinical diagnosis has been recognized. It has been established that activities of secreted enzymes and cellular enzymes in serum are a sensitive indication of the pathophysiological condition of the body. Specific and sensitive substrates play a prominent role for this purpose. Fluorogenic substrates, e.g., enable sensitive micro-analyses. [Pg.96]

Discuss the role of vitamin D in regulating calcium and phosphorus levels in body. [Pg.238]

The relatively small difference between the acute-duration MRL (0.007 mg/kg/day) and the intermediate-duration MRL (0.002 mg/kg/day) is not meant, nor is it considered, to imply a high level of precision in the calculation of these health guidance values. Rather, this difference of 5 g/kg/day reflects the increased toxicity of continued low-dose exposure for longer periods of time and is consistent with the known build-up of mercury levels in body tissues over a prolonged course of continued exposure. The actual precision of any derived (actually estimated) MRL is dependent upon an encompassing, but not sharply defined, area of uncertainty based upon the database used in its determination. [Pg.261]

Figure 5.11 Drug level in body tissue (e.g. blood) in case of (a) traditional drug delivery system (TDS) (b) controlled drug delivery system(CDS). Figure 5.11 Drug level in body tissue (e.g. blood) in case of (a) traditional drug delivery system (TDS) (b) controlled drug delivery system(CDS).
A. Specific levels. Drug levels in body fluids are not generally useful or available. [Pg.110]

A substantial part of our knowledge stems from studies on, first, the direct effects of the prostaglandins as described above or the effects of prostaglandin precursors second, from measurements of prostaglandin levels in body fluids or tissues and third, from registered biological effects of inhibitors of prostaglandin biosynthesis. [Pg.13]

Anoxia—decrease in oxygen levels in body tissues below physiological levels Ataxia—failure of muscular coordination irregularity of muscular action Atrial—referring to an upper chamber of the heart... [Pg.156]

Normal levels in body fluids and tissues depend mainly on food and less on environmental influences. The daily intake of arsenic with food is estimated as 0.05-0.1 mg [11,39] 0.4 mg is assumed to be safe but doubts are likely on account of its carcinogenic character [55]. Total body content of arsenic may be 0.31. 0 mg [4,19,60]. [Pg.243]

A Gas Chromatographic Method for Determination of Acetate Levels in Body Fluids... [Pg.145]

Most of the assays of isoprostanes to date have focused on assessing 8-iso-PGF levels in body fluids, since this is a major product of the total peroxidation process in vivo. When measuring the urinary metabolites of S-iso-PGF, the correct choice of the appropriate metabolite is important since the metabolic profile and appearance of the different metabolites vary between species (Roberts et al, 1996 Basu, 1998c Chiabrando et al, 1999). The tetranor metabolite of 8-iso-PGFj is the major urinary product in the rabbit, whereas the dinor metabolite is the dominant product in humans. [Pg.272]

Amino acid levels in body fluids are influenced by a number of factors, such as age, physiological changes, nutritional status, illness and disease, medications and toxins. It is notable that medications can cause artifacts that interfere with the analysis or can disrupt the body s metabolism of amino acids, leading to an abnormal amino acid pattern which, although suggestive of an inborn error, is actually an acquired condition. These factors are discussed below. [Pg.20]

Individual sensors are often nonspecific, but selectivity (Topic A3) can be improved by using groups or arrays of several sensors to monitor one or more analytes using different instrumental parameters and/or different sensor elements. Sensors in an array may be operated at different electrical potentials, frequencies or optical wavelengths. A sensor array for the simultaneous monitoring of pH, sodium and potassium levels in body fluids can be constructed from three ion-selective field effect transistors (Fig. 5), each with an appropriate sensitivity to one of the three analytes. [Pg.326]

In recent years, a number of Mg alloys have been tested under in vitro and in vivo conditions to understand their corrosion behaviour and mechanisms (Witte et al. 2006 Kannan and Raman, 2008, 2010 Kannan, 2010 Walter and Kannan, 2011). AZ series alloys show a lower corrosion current than that of pure Mg. However, aluminium-containing Mg alloys may not be the ultimate choice, simply because of the potentially toxic effects of high aluminium levels in body fluid. The influence on corrosion properties of calcium and rare-earth elements added to Mg and its alloys has been investigated, but the improvement was not significant. [Pg.386]


See other pages where Levels in body is mentioned: [Pg.148]    [Pg.25]    [Pg.111]    [Pg.100]    [Pg.102]    [Pg.107]    [Pg.166]    [Pg.162]    [Pg.202]    [Pg.72]    [Pg.74]    [Pg.74]    [Pg.217]    [Pg.82]    [Pg.296]    [Pg.327]    [Pg.333]    [Pg.360]    [Pg.172]    [Pg.320]    [Pg.326]    [Pg.35]    [Pg.161]    [Pg.159]    [Pg.1207]    [Pg.162]    [Pg.145]   
See also in sourсe #XX -- [ Pg.166 , Pg.199 ]




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