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Health effects potentiation

Health effects potentially related to exposure to environmental hazards. [Pg.352]

The objective of an EIA Is to document the potential physical, biological, social and health effects of a planned activity. This will enable decision makers to determine whether an activity is acceptable and if not, identify possible alternatives. Typically, ElA s will be carried out for... [Pg.70]

Proceedings of a Symposium on Potential Health Effects of Components ofPlantEoods and Beverages in the Diet, Aug. 14—15, 1992, University of California at Davis, p. 106. [Pg.376]

J. W. HoUeman, Health Effects of Haloalky I Phosphate Flame Retardants and Potential Metabolic Products, Oak Ridge National Laboratory, Term., 1984, DOE/NBM-4006848 (DE84 006848),... [Pg.483]

SolubiHty of the three commercial polysulfones foUows the order PSF > PES > PPSF. At room temperature, all three of these polysulfones as weU as the vast majority of other aromatic sulfone-based polymers can be readily dissolved in a few highly polar solvents to form stable solutions. These solvents include NMP, DMAc, pyridine, and aniline. 1,1,2-Trichloroethane and 1,1,2,2-tetrachloroethane are also suitable solvents but are less desirable because of their potentially harmful health effects. PSF is also readily soluble in a host of less polar solvents by virtue of its lower solubiHty parameter. [Pg.467]

Pyridine Chronic Toxicology. AH mutagenicity tests have been negative and (1) is not considered a carcinogen or potential carcinogen. There have been no reports of adverse health effects on long-term exposure to (1) at low concentrations. [Pg.334]

Human Health Effects. Any assessment of adverse human health effects from PCBs should consider the route(s) of and duration of exposure the composition of the commercial PCB products, ie, degree of chlorination and the levels of potentially toxic PCDF contaminants. As a result of these variables, it would not be surprising to observe significant differences in the effects of PCBs on different groups of occupationally-exposed workers. [Pg.66]

Environmental exposures to PCBs are significantly lower than those reported in the workplace and are therefore unlikely to cause adverse human health effects in adults. However, it is apparent from the results of several recent studies on children that there was a correlation between in utero exposure to PCBs, eg, cord blood levels, and developmental deficits (65—68) including reduced bkth weight, neonatal behavior anomaUes, and poorer recognition memories. At four years of age, there was stiU a correlation between prenatal PCB exposure levels and short-term memory function (verbal and quantitative). In these studies the children were all exposed to relatively low environmental levels of PCBs. Although these effects may be related to other contaminants, it is clear that this is an area of concern regarding the potential adverse human health impacts of PCBs. [Pg.66]

A basic tenet of risk communication is that people have a right to participate in decisions that affect their lives. The goal of risk communication should be to inform the community about the risks and potential health effects of your activities and to involve the public in developing solutions to any related problems. [Pg.60]

Describe the deficiencies of a total suspended particulate measurement for relating ambient concentrations to potential human health effects. [Pg.215]

Microorganisms MCLG (mg/L) MCL or TTi (mg/L) Potential Health Effects from Ingestion of Water Sources of Contaminant in Drmking Water... [Pg.15]

Pick any three chemicals that you are aware are covered by the NPDW Regulations and discuss the potential health effects that could occur from ingesting water contaminated by them. [Pg.60]

Nonemergency medical care should be arranged for hazardous waste site personnel who are experiencing health effects resulting from an exposure to hazardous substances. Off-site medical care should make sure that any potential job-related symptoms or illnesses are evaluated in the context of the employee s exposure. Off-site medical personnel should investigate and treat non-job-related illnesses that may put the employee at risk because of task requirements [1]. [Pg.88]

Hazard identification, step one, means identification of new chemicals or other factors that may cause harmful health effects. Previously, novel hazards were usually observed in case studies or after accidents or other excessive exposures, usually in occupational environments. Today, thorough toxicity studies are required on all pesticides, food additives, and drugs. New chemicals also have to be studied for their potential toxic effects. Thus, earlier hazards were in most cases identified after they had caused harmful effects in humans. Today, most chemical products have been evaluated for their toxicity with experimental animals. Therefore, hazard identification has become a preventive procedure based on safety studies conducted before a chemical compound or product reaches the market, and before individuals are exposed to it. ... [Pg.328]

Provides information on how levels of exposure of hazardous chemicals affect human health. Covers levels of exposure to hazardous chemicals below which no adverse health effects are expected to occur in various segments of the human population. The reference dose and carcinogenicity assessments on IRIS can sen>e as guides in e >aluating potential health hazards and selecting response to alleviate a potential risk to human health. Hours 8 00 a.m. to 4 40 p.m. EST, Monday - Friday. [Pg.302]

Acceptable Daily Intake (ADI) An estimate similar in concept to the RfD, but derived using a less strictly defined methodology. RfDs have replaced ADIs as the USEPA s (Agency) preferred values for use in evaluating potential noiicarcinogenic health effects resulting from exposure to a chemical. [Pg.316]

A risk estimate indicates the likelihood of occurrence of the different types of health or enviromiiental effects in exposed populations. Risk assessment should include both human healtli and environmental evaluations (i.e., impacts on ecosystems). Ecological impacts include actual and potential effects on plants and animal (otlier than domesticated species). The numbers produced from the risk characterization, representing tlie probability of adverse health effects being caused, must be evaluated. [Pg.395]


See other pages where Health effects potentiation is mentioned: [Pg.602]    [Pg.127]    [Pg.602]    [Pg.127]    [Pg.271]    [Pg.180]    [Pg.314]    [Pg.226]    [Pg.335]    [Pg.555]    [Pg.5]    [Pg.32]    [Pg.132]    [Pg.377]    [Pg.440]    [Pg.19]    [Pg.217]    [Pg.228]    [Pg.291]    [Pg.84]    [Pg.291]    [Pg.292]    [Pg.331]   
See also in sourсe #XX -- [ Pg.8 , Pg.12 ]




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