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Health effects, chemicals

Nordic steering group for assessment of health effects of chemicals Health effects of selected chemicals 4-5. B-butyl acetate, rec-butyl acetate, tert-butyl acetate, iso-butyl acetate. Nord 15 63-82, 1999... [Pg.98]

NSF, NSF Product and Service Listings, NSF/ANSI Standard 60 Drinking Water Treatment Chemicals-Health Effects, NSF International, www.nsf.org/Cerfified/PwsChemicals/ Listings.asp , June 10, 2004. [Pg.316]

NSF/ANSI Standard 60 Drinking Water Treatment Chemicals - Health Effects Standard 60 addresses the potential for adverse health effects to occur because of the use of drinking water treatment chemicals and related impurities. The standard includes a procedure for developing... [Pg.912]

Most studies on the action of phosgene oxime have utilized animal studies. Human information has been obtained from accidental exposure to the chemical. Health effects following phosgene oxime exposure are dependent on the route of exposure. [Pg.1994]

NSF/ANSl (National Sanitation Foundation/ American National Standards Institute) Standard 60-2003 e (Ol-Oct-2003). Drinking Water Treatment Chemicals - Health Effects. NSE International, Ann Arbor, Ml, USA. [Pg.929]

Chemical profiles including a description of the chemical, health effects, pre-hospital management, emergency department management and a patient information sheet hOpJAmm. atsdr.cdc.gov/mmg56.pdf. [Pg.359]

Although thermal performance is a principal property of thermal insulation (13—15), suitabiHty for temperature and environmental conditions compressive, flexure, shear, and tensile strengths resistance to moisture absorption dimensional stabiHty shock and vibration resistance chemical, environmental, and erosion resistance space limitations fire resistance health effects availabiHty and ease of appHcation and economics are also considerations. [Pg.331]

In the United States, the largest concentration of atmospheric vanadium occurs over Eastern seaboard cities where residual fuels of high vanadium content from Venezuela are burned ia utility boilers. Coal ash ia the atmosphere also coataias vanadium (36). Ambient air samples from New York and Boston contain as much as 600—1300 ng V/m, whereas air samples from Los Angeles and Honolulu contained 1—12 ng V/m. Adverse pubHc health effects attributable to vanadium ia the ambieat air have aot beea deteroiiaed. lacreased emphasis by iadustry oa controlling all plant emissions may have resulted ia more internal reclamation and recycle of vanadium catalysts. An apparent drop ia consumption of vanadium chemicals ia the United States since 1974 may be attributed, in part, to such reclamation activities. [Pg.393]

R. M. Harrington, D. Gates, and R. R. Romano, "A Review of the Uses, Chemistry and Health Effects of Chlorine Dioxide and the Chlorite Ion, Chlorine Dioxide Panel of the Chemical Manufacturers Association, Washington, D.C., Api. 1989. [Pg.492]

Another way to evaluate risks is to calculate the sensitivity of the total risk estimates to changes in assumptions, frequencies, or consequences. Risk analysts tend to be conservative in their assumptions and calculations, and the cumulative effect of this conservatism may be a substantial overestimation of risk. For example, always assuming that short-term exposure to chemical concentrations above some threshold limit value will cause serious injury may severely skew the calculated risks of health effects. If you do not understand the sensitivity of the risk results to this conservative assumption, you may misallocate your loss prevention resources or misinform your company or the public about the actual risk. [Pg.45]

ACUTE TOXICITY Advcfse health effects occumng within a short time period of exposure to a single dose of a chemical or as a result of multiple exposures over a short time period, e.g. 24 hours. [Pg.10]

CHRONIC TOXICITY Advcfsc health effects resulting from repeated daily exposures to a chemical for a significant period. [Pg.12]

Whilst the causative agent(s) have not been established it is thought to be multifunctional and possibilities include physical factors (humidity, temperature, lighting), static electricity, electromagnetic radiation, air ion concentrations, fungi, noise, psychological stress, and chemicals. Chemicals which are not those involved in the normal work processes can become trapped within the building, albeit at concentrations below those known to cause ill-health effects, if ... [Pg.142]

A list of danger categories is given in Table 14.2. Note that chemicals may possess several hazards, e.g. nitric acid is classed as both an oxidizer and a conosive. If a chemical is not in one of these categories it is not generally considered to be dangerous. If the hazards of a new chemical have not been established it should be labelled Caution - substance not yet fully tested . Mixtures can be classified either from results from tests on the preparation, or by calculation to predict the healtli effects of the product based on the properties of individual components and tlieu concentration in the mixture. Preparations need to be classified for both physico-chemical and health effects but, to date, not for environmental effects. [Pg.443]

Mercury Manufacture of certain chemicals, paper, paint Pesticides Fungicides Adverse health effects... [Pg.504]

A difficulty that should not be overlooked is that airborne particulates are rarely homogeneous. They vary greatly in size and shape, and their chemical composition is determined by factors specific to the source and location of the emissions. The combined effects and interactions of various substances mixed with particulates have not yet been established (except for sulfur dioxide), but they are believed to be significant, especially where long-term exposure occurs. Measurement techniques and their reliability may vary across regions and countries, and so may other factors, such as diet, lifestyle, and physical fitness, that influence the human health effects of exposure to particulates. [Pg.19]

In nonindustrial settings, MCS substances are the cause of indoor air pollution and are the contaminants in air and water. Many of the chemicals which trigger MCS symptoms are known to be irritants or toxic to the nervous system. As an example, volatile organic compounds readily evaporate into the air at room temperature. Permitted airborne levels of such contaminants can still make ordinary people sick. When the human body is assaulted with levels of toxic chemicals that it cannot safely process, it is likely that at some point an individual will become ill. For some, the outcome could be cancer or reproductive damage. Others may become hypersensitive to these chemicals or develop other chronic disorders, while some people may not experience any noticeable health effects. Even where high levels of exposure occur, generally only a small percentage of people become chemically sensitive. [Pg.45]

The threshold for toxic injury is not the same for everyone because sensitivity varies greatly among individuals. Most chemicals in consumer products remain untested for health effects, such as cancer, reproductive problems, and the impacts of long-term, low level exposure. How these substances affect women, children, and people with existing conditions is also little studied. Once a person s defenses have been broken down and he or she has become hypersensitive, a wide variety of common chemical exposures can trigger a reaction. Just what products and other chemicals which cause problems varies greatly among affected individuals. [Pg.45]

Chronic Health Effect A chronic health effect is an adverse health effect resulting from long-term exposure to a substance. The effects could be a skin rash, bronchitis, cancer, or any other medical condition. An example would be liver cancer from inhaling low levels of benzene at your workplace over several years. The term is also applied to a persistent (months, years, or permanent) adverse health effect resulting from a short-term (acute) exposure. Chronic effects from long-term exposure to chemicals are fairly common. Recognize the PEL (permissible exposure level) for each substance in your workplace and minimize your exposure whenever possible. [Pg.524]

Sensitizer A sensitizer is defined by OSHA as "a chemical that causes a substantial proportion of exposed people or animals to develop an allergic reaction in normal tissue after repeated exposure to the chemical." The condition of being sensitized to a chemical is also called chemical hypersensitivity. Certain chemicals have no immediate health effect. But if you are exposed to them several times, they can make you allergic or sensitive to other chemicals. A classic example is formaldehyde (HCHO). Typical reactions to sensitizers can include skin disorders such as eczema. When working with sensitizers, always use proper protective equipment such as gloves, respirators, etc. Once you are sensitized to a particular chemical, even minute amounts will cause symptoms. Sensitization is usually a lifelong effect. [Pg.547]

Access to a 2,700 chemical data base with hazard information, precautions, and health effects. Menu-driven software. [Pg.287]


See other pages where Health effects, chemicals is mentioned: [Pg.4756]    [Pg.55]    [Pg.469]    [Pg.303]    [Pg.177]    [Pg.215]    [Pg.4756]    [Pg.55]    [Pg.469]    [Pg.303]    [Pg.177]    [Pg.215]    [Pg.271]    [Pg.370]    [Pg.114]    [Pg.423]    [Pg.469]    [Pg.79]    [Pg.136]    [Pg.226]    [Pg.335]    [Pg.400]    [Pg.2171]    [Pg.2179]    [Pg.4]    [Pg.5]    [Pg.19]    [Pg.49]    [Pg.44]    [Pg.217]    [Pg.516]    [Pg.541]   
See also in sourсe #XX -- [ Pg.340 ]




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