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Toxicology techniques

Industrial toxicology—Technique—Congresses. 2. Instrumental analysis—Congresses. 3. Air—Pollution Measurement—Congresses. 4. Work environment— Congresses. [Pg.332]

If we come down to normally encountered low concentrations of SO2 in air, we see rapidly tliat classical or elaborate toxicological techniques do not help very mucli we liave thus to turn to more sensitive tecimiques, for example epidemiology or to more sensitive reagents (vegetal, tissue culture, or any organism or part of an organism witli reduced adaptability). [Pg.18]

Stoeppler. M. (1984). Cadmium. In Vercruysse, A. (ed.) Hazardous metals in human toxicology, techniques and instrumentation in analytical chemistry-Volume 4. Zeeuw,... [Pg.337]

We have worked out the techniques for measuring lead at these low levels. We know little about toxicological techniques. [Pg.401]

Grandjean, P., Olsen, N. B., Lead, in Vercruysse, A., Hazardous Metals in Human Toxicology, Techniques and Instrumentation in Analytical Chemistry, Vol. 4, Elsevier, Amsterdam 1984, pp. 153/69. [Pg.26]

From a toxicological and physiological point of view, the determination of very small amounts of tellurium is becoming increasingly important. Interest is environmental and human health has promoted development in analytical techniques and methods for the trace and ultra trace levels (see Trace AND RESIDUE ANALYSIS). [Pg.388]

An overview of some basic mathematical techniques for data correlation is to be found herein together with background on several types of physical property correlating techniques and a road map for the use of selected methods. Methods are presented for the correlation of observed experimental data to physical properties such as critical properties, normal boiling point, molar volume, vapor pressure, heats of vaporization and fusion, heat capacity, surface tension, viscosity, thermal conductivity, acentric factor, flammability limits, enthalpy of formation, Gibbs energy, entropy, activity coefficients, Henry s constant, octanol—water partition coefficients, diffusion coefficients, virial coefficients, chemical reactivity, and toxicological parameters. [Pg.232]

Indicators of toxicity hazards include LD50, LC50, plus a wide range of in vitro and in vivo techniques for assessment of skin and eye indtation, skin sensitization, mutagenicity, acute and chronic dermal and inhalation toxicity, reproductive toxicology, carcinogenicity etc. [Pg.81]

In this present chapter, the applications of multidimensional chromatography to forensic and toxicological analysis are described in detail, being organized by technique. While multidimensional chromatography has not been as widely applied in... [Pg.407]

Section 104(i)(5) of CERCLA, as amended, directs the Administrator of ATSDR (in consultation with the Administrator of EPA and agencies and programs of the Public Health Service) to assess whether adequate information on the health effects of methyl parathion is available. Where adequate information is not available, ATSDR, in conjunction with the National Toxicology Program (NTP), is required to assure the initiation of a program of research designed to determine the health effects (and techniques for developing methods to determine such health effects) of methyl parathion. [Pg.120]

GC/MS has been employed by Demeter et al. (1978) to quantitatively detect low-ppb levels of a- and P-endosulfan in human serum, urine, and liver. This technique could not separate a- and P-isomers, and limited sensitivity confined its use to toxicological analysis following exposures to high levels of endosulfan. More recently, Le Bel and Williams (1986) and Williams et al. (1988) employed GC/MS to confirm qualitatively the presence of a-endosulfan in adipose tissue previously analyzed quantitatively by GC/ECD. These studies indicate that GC/MS is not as sensitive as GC/ECD. Mariani et al. (1995) have used GC in conjunction with negative ion chemical ionization mass spectrometry to determine alpha- and beta-endosulfan in plasma and brain samples with limits of detection reported to be 5 ppb in each matrix. Details of commonly used analytical methods for several types of biological media are presented in Table 6-1. [Pg.249]

Burczynski, M. (Ed.) (2003). An Introduction to Toxicogenomics—Describes, with examples, the use of genomic techniques in toxicology. [Pg.98]

Although there is considerable activity in developing computational toxicology for regulatory applications, the reality for the foreseeable future is that QSARs and related techniques are not yet sophisticated enough to replace whole animal testing. [Pg.476]

In the area of predictive toxicology the applicability domain is taken to express the scope and limitations of a model, that is, the range of chemical structures for which the model is considered to be applicable [106]. Although this issue has been fundamental to the use of QSAR (and indeed any predictive technique) since its conception, there remain few reliable methods to define and apply an applicability domain in predictive toxicology. The current status of methods to define the applicability domain for use in (Q)SAR has been assessed recently by Netzeva et al. [106]. [Pg.487]

Screening Techniques for Detecting Toxicity. Simple toxicity screening techniques are necessary to identify toxic species and to monitor the efficacy of isolation and purification procedures used to purify toxins. Atterwill and Steele 108) have recently comprehensively reviewed in vitro methods for toxicology and so much of the following is in the nature of a general overview. [Pg.326]

COMMENT Let me make something clear. We don t need any new techniques. The experiments are very simple they just have to be done at 2 weeks rather than at 18 hours. And it may be that you are entirely correct. But until those experiments are performed at longer timcpoints, I don t think we know if we are dealing with pharmacology or toxicology. [Pg.175]


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