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And toxic effects

Safety. Magnesium oxide (fume) has a permissible exposure limit (PEL) (134) (8 hours, TWA), of 10 mg/m total dust and 5 mg/m respirable fraction. Tumorigenic data (intravenous in hamsters) show a TD q of 480 mg/kg after 30 weeks of intermittent dosing (135), and toxicity effects data show a TC q of 400 mg/m for inhalation in humans (136). Magnesium oxide is compatible with most chemicals exceptions are strong acids, bromine pentafluoride, chlorine trifluoride, interhalogens, strong oxidizers, and phosphorous pentachloride. [Pg.355]

M. Sittig, Hazardous and Toxic Effects of Industrial Chemicals Noyes Data, Park Ridge, N.J., 1979. [Pg.501]

R. E. Gosselin and co-workers. Clinical Toxicology of Commercial Products, Williams Wilkins Co., Baltimore, Md., 1976, p. 86 M. Sittig, Hazardous and Toxic Effects of Industrial Chemicals, Noyes Data Corp., Park Ridge, N.J., 1979, p. 102. [Pg.61]

B. Hunter and co-workers, Coumarin Tumorigenic and Toxic Effects in Prolonged IPietary Administration, Huntingdon Research Centre, personal communication, (1984). [Pg.324]

When adrninistered long-term for the treatment of hypertension, diuretics fulfill the goals of preventing cardiovascular disease and increasing longevity. However, diuretic therapy may produce both side and toxic effects that are significant in certain patient subgroups, eg, diabetics and cardiac patients. [Pg.212]

A detailed study has been made of the pharmacology and toxic effects of Senecio Ridd llii and its alkaloid by Rosenfeld and Beath. ... [Pg.615]

After the critical study and toxic effect have been selected, the USEPA identifies the experimental exposure level representing the highest level tested at which no adverse effects (including the critical toxic effect) were demonstrated. This highest "no-obserx cd-adversc-effcct-lever (NOAEL) is the key datum obtained from the study of the dose-response relationship. A NOAEL obserx ed in an animal study in which the exposure was intermittent (such as five days per week) is adjusted to reflect continuous exposure. [Pg.329]

Antipsychotic medications are indicated in the treatment of acute and chronic psychotic disorders. These include schizophrenia, schizoaffective disorder, and manic states occurring as part of a bipolar disorder or schizoaffective disorder. The co-adminstration of antipsychotic medication with antidepressants has also been shown to increase the remission rate of severe depressive episodes that are accompanied by psychotic symptoms. Antipsychotic medications are frequently used in the management of agitation associated with delirium, dementia, and toxic effects of both prescribed medications (e.g. L-dopa used in Parkinson s disease) and illicit dtugs (e.g. cocaine, amphetamines, andPCP). They are also indicated in the management of tics that result from Gilles de la Tourette s syndrome, and widely used to control the motor and behavioural manifestations of Huntington s disease. [Pg.183]

Huang G, Bai Z, Dai S, Xie Q (1993) Accumulation and toxic effects of organometallic compounds on algae. Applied Organometallic Chemistry, 7 265-271. [Pg.47]

Often, absorption occurs by multiple routes in humans. Dean et al. (1984) reported deaths and toxic effects as well as lowered blood cholinesterase levels and excretion of urinary 4-nitrophenol in several children who were exposed by inhalation, oral, and possibly dermal routes after the spraying of methyl parathion in a house. In the same incident (Dean et al. 1984), absorption was indicated in adults who also excreted 4-nitrophenol in the urine, though at lower levels than some of the children, and in the absence of other evidence of methyl parathion exposure. In this study, the potential for age-related differences in absorption rates could not be assessed because exposure levels were not known and the children may have been more highly exposed than the adults. Health effects from multiple routes are discussed in detail in Section 3.2. [Pg.87]

Most of the toxic effects caused by methyl parathion resulted from exposure by multiple routes, especially for workers in sprayed fields or formulating facilities, or people in homes. Dean et al. (1984) reported deaths and toxic effects in several children as well as lowered blood cholinesterase levels and excretion of urinary 4-nitrophenol (adults showing no adverse effects also excreted 4-nitrophenol). [Pg.95]

Regrettably, all chemotherapeutic agents have the potential to produce adverse reactions with varying degrees of frequency and severity, and these include hypersensitivity reactions and toxic effects. These may be dose-related and predictable in a patient with a history of hypersensitivity or a previous toxic reaction to a drug or its chemical analogues. However, many adverse events are idiosyncratic and therefore unpredictable. [Pg.135]

MYER R o, FROSETH J A, COON 0 N (1982) Protein utilization and toxic effects of raw beans (Phaseolus vulgaris) for young pigs. . 1 Anim Sci. 55 1087-98. [Pg.182]

In this section, two aspects related to Bfx and Fx future use as drugs will be discussed, metabohc behavior and toxic effects. [Pg.299]

Landrigan PJ Mount Sinai School of Medicine of CUNY, New York, NY Lead and organochlorines in New York City study the current urban sources, environmental distribution and toxic effects on human health of lead and persistent chlorinated hydrocarbons—in particular PCBs and DDT National Institute of Environmental Health Sciences... [Pg.362]

Superfund Hazardous Substances Basic Research Program to study the current urban sources, environmental distribution, and toxic effects on human health of lead... [Pg.441]

Landrigan PJ, Froines JR, Mahaffey KR. 1985. Body lead burden Summary of epidemiological data and its relation to environmental sources and toxic effects Chapter 14. In Magaffev KR, ed. Dietary and environmental lead Human health effects. Amsterdam, The Netherlands Elsevier Sci Publisher BV, 421451. [Pg.542]

From the above discussion, it is clear that while phenol is essential for the well being and advancement of the humans, it also brings in innumerable hazards and toxic effects, if the concentration limits are exceeded. Therefore, it is essential that the excess amount of phenol is degraded and brought under the permissible limits before it is discharged into the environment. Several such efforts have already been attempted with partial to complete success, which needs a review, before some new effort of this laboratory is discussed at the end of the chapter. [Pg.289]

Mets B., Winger G., Cabrera C. et al. A catalytic antibody against cocaine prevents cocaine s reinforcing and toxic effects in rats. Proc. Natl. Acad. Sci. U.S.A. 95 10176, 1998. [Pg.99]

Creppy E E (2005), Update of survey, regulation and toxic effects of mycotoxins in Europe , Toxicol. Lett., 127, 19-28. [Pg.383]

Fantin, A.M.B., A. Franchini, E. Ottaviani, and L. Benedetti. 1985. Effect of pollution on some freshwater species. II. Bioaccumulation and toxic effects of experimental lead pollution on the ganglia in Viviparus ater (Mollusca, Gastropoda). Basic Appl. Histochem. 29 377-387. [Pg.330]

Van den Berg, M., B.L.H.J. Craane, T. Sinnige, S. Van Mourik, S. Dirksen, T. Boudewijn, M. Van der Gaag, I.J. Lutke-Schipholt, B. Spenkelink, and A. Brouwer. 1994. Biochemical and toxic effects of polychlorinated biphenyls (PCBs), dihcnzo-p-dioxins (PCDDs) and dibenzofurans (PCDFs) in the cormorant (.Phalacrocorax carbo) after in ovo exposure. Environ, Toxicol. Chem. 13 803-816. [Pg.1067]


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