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Exposure to toxicants

Methanol use would also reduce pubHc exposure to toxic hydrocarbons associated with gasoline and diesel fuel, including ben2ene, 1,3-butadiene, diesel particulates, and polynuclear aromatic hydrocarbons. Although pubHc formaldehyde exposures might increase from methanol use in garages and tunnels, methanol use is expected to reduce overall pubHc exposure to toxic air contaminants. [Pg.434]

W. Braker, A. L. Mossman, and D. Siegel, Pffects of Exposure To Toxic Gases—First Hid and Medical Treatment, 2nd ed., Matheson Gas Products, East Rutherford, N.J., 1977. [Pg.410]

Toxicology. The toxicity of ethyl ether is low and its greatest hazards in industry are fire and explosion. The vapor is absorbed almost instandy from the lungs and very prompdy from the intestinal tract. It undergoes no chemical change in the body. Prevention and control of health hazards associated with the handling of ethyl ether depend primarily on prevention of exposure to toxic atmospheric concentrations and scmpulous precautions to prevent explosion and fire. [Pg.428]

Operating equipment is opened, cleaned, emptied, or charged frequently. Operator exposure to toxic or flammable materials during normal process operation. [Pg.33]

Operator exposure to toxic vapors during opening and cleaning. [Pg.104]

Many sophisticated models and correlations have been developed for consequence analysis. Millions of dollars have been spent researching the effects of exposure to toxic materials on the health of animals the effects are extrapolated to predict effects on human health. A considerable empirical database exists on the effects of fires and explosions on structures and equipment. And large, sophisticated experiments are sometimes performed to validate computer algorithms for predicting the atmospheric dispersion of toxic materials. All of these resources can be used to help predict the consequences of accidents. But, you should only perform those consequence analysis steps needed to provide the information required for decision making. [Pg.34]

Caution Part B must be conducted in an efficient hood to avoid exposure to toxic nitrosyl chloride. [Pg.95]

Dyspnea Dyspnea is shortness of breath or difficulty in breathing. The victim is usually quite aware of the unusual breathing pattern. Shortness of breath can be an indicator of many physical ailments including simple exertion, a panic attack, a blow to the chest, asthma, cardiac disease, as well as exposure to toxic chemicals. If a person is suffering from shortness of breath, evaluate them for additional symptoms and possible exposures. Keep the victim in a sitting position. Remove the victim to fresh air, if possible, and seek medical attention. [Pg.528]

Edema Edema is an abnormal accumulation of body fluid in tissues. An edema can be as trivial as a blister on your thumb, as life-threatening as a constriction of your airway. As in real estate, the three factors that determine the dangers associated with an edema are location, location, location. Exposure to toxic chemicals can cause a variety of edemas. Pulmonary edema (fluid in the lungs) is particularly dangerous, if not treated. Be sure to avoid inhalation of chemicals whenever possible and to use proper protective measures, as suggested on the MSDS (fume hoods, respirators, etc.). [Pg.528]

A medical surveillance program is designed to protect the workers health. Given the limitations of industrial hygiene monitoring data and the many hazards involved in hazardous waste activities, medical surveillance data may provide the only indication that worker exposure to toxic substances has occurred. [Pg.83]

Congress passed the Occupational and Safety Health Act to ensure worker and workplace safety. Their goal was to make sure employers provide their workers a place of employment free from recognized hazards to safety and health, such as exposure to toxic chemicals, excessive noise levels, mechanical dangers, heat or cold stress, or unsanitary conditions. In order to establish standards for workplace health and safety, the Act also created the National Institute for Occupational Safety and Health (NIOSH) as the research institution for the Occupational Safety and Health Administration (OSHA). OSHA is a division of the U.S. Department of Labor which oversees the administration of the Act and enforces Federal standards in all 50 states. [Pg.25]

Professional society promotes the study and control of environmental factors affecting the health and well-being of factory workers, including procedures for monitoring the exposure to toxic materials in the work place. Offers laboratory accreditation and testing programs and informational pamphlets on various health and safety topics. [Pg.278]

W. Braker et af. Effects of Exposure to Toxic Gases—First Aid and Medical Treatment, " ed., Matlieson, Lindliurst, NJ, 1977. [Pg.282]

The measure used to describe the potential for noncarcinogenic toxicity to occur in an individual is not expressed as tlie probability of an individual suffering an adverse effect. The EPA does not at tlie present time use a probabilistic approach to estimate tlie potential for noncarcinogenic healtli effects. Instead, tlie potential for non carcinogenic effects is evaluated by comparing an exposure level over a specified time period (e.g., lifetime) witli a reference dose derived for a similar exposure period. Tliis ratio of exposure to toxicity is called a liazard quotient and is described below. (The reader is referred to Chapter 11 for additional details on tlie material tliat follows). The noncancer liazard quotient assumes tliat tliere is a level of exposure (i.e., RfD) below which it is unlikely for even sensitive populations to experience adverse healtli effects. [Pg.398]

The potential for noncarcinogcnic health effects is evaluated by comparing iui exposure level over a specified lime period (c.g., lifetime) with a reference dose derived for a similar exposure period. The ratio of exposure to toxicity in called a liazard quotient and, when it is greater tlien unity tlierc is a higher level of concern for potential noncancer effects. [Pg.419]

Caution To avoid exposure to toxic phenylphosphonous dichloride vapors, the Grignard reaction should he conducted in a hood. [Pg.127]

Heterogeneous catalysts are often located at the top of a reactor and manipulated with temporary handling equipment. To avoid exposure to toxic dust, local ventilation should be installed if this is impracticable, scrupulous use of personal protective equipment and rigid compliance with systems-of-work are essential. Respiratory equipment may include self-contained or line-fed breathing apparatus. [Pg.148]

One shortcoming in many field studies is a failure to address adequately exposure to toxic transformation products. In efforts to manage time and cost constraints, the concentrations of parent materials and transformation products are often added together to produce a total toxic residue amount. However, it is more appropriate to evaluate individual transformation products as their toxicity may be significantly increased (e.g. active oxons) or decreased (e.g. dehalogenation or dealkylation products) relative to the parent compound. [Pg.940]

Chemical characteristics and environmental conditions will influence the design of fleld studies to assess distributions of occurrence and exposure." Important chemical characteristics of the test substance include water solubility. Aloe, vapor pressure, degradation rate and potentially labile functional groups. These characteristics also need to be known for toxicologically important fiansformation products. One shortcoming in many fleld studies is a failure to address adequately exposure to toxic transformation products. [Pg.941]

The acceptable limits for toxic exposure depend on whether the exposure is brief or prolonged. Lethal concentration for airborne materials and lethal dose for non-airbome materials are measured by tests on animals. The limits for brief exposure to toxic materials that are airborne are usually measured by the concentration of toxicant that is lethal to 50% of the test group over a given... [Pg.627]

Kavanaugh TJ University of Washington, Seattle, WA Glutathione regulation as a biomarker of exposure to toxicants and of susceptibility to such exposures National Institute of Environmental Health Sciences... [Pg.362]

Muir T, Zegarac M (2001) Societal costs of exposure to toxic substances economic and health costs of four case studies that are candidates for environmental causation. Environ Health Perspect 109(Suppl 6) 885-903... [Pg.134]

House, W.B. 1964. Tolerance criteria for continuous exposure inhalation exposure to toxic materials. III. Effects on animals of 90-d exposure to hydrazine, unsymmetrical dimethylhydrazine (UMDH), decaborane, and nitrogen dioxide. ASD-TR-61-519 (iii). Wright-Patterson AFB, OH. 84 pp. [Pg.158]

The ACGIH clearly points out that the TLVs should not be used as a relative index of toxicity (see Figure 2-8), should not be used for air pollution work, and cannot be used to assess the impact of continuous exposures to toxicants. The TLV assumes that workers are exposed only during a normal eight-hour workday. [Pg.59]

Every effort must be made to reduce worker exposures to toxicants to below the PEL and lower if possible. [Pg.59]


See other pages where Exposure to toxicants is mentioned: [Pg.259]    [Pg.136]    [Pg.370]    [Pg.134]    [Pg.92]    [Pg.96]    [Pg.101]    [Pg.229]    [Pg.72]    [Pg.2]    [Pg.250]    [Pg.108]    [Pg.1461]    [Pg.185]    [Pg.256]    [Pg.38]    [Pg.281]    [Pg.300]    [Pg.313]    [Pg.222]    [Pg.80]    [Pg.251]   
See also in sourсe #XX -- [ Pg.145 ]




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