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Environmental threat

Terphenyls in heat-transfer appHcations are used in relatively smaller quantities with negligible release to the environment. They are sufficiently biodegradable so as not to constitute an environmental threat (56,57). Some properties important for environmental considerations are summari2ed in Table 7. [Pg.118]

Interim measures may be separate from the comprehensive Corrective Action plan but should be consistent with, and integrated with, any longer-term Corrective Action (e.g., corrective measure through an order, an op erating permit, a post-closure permit or interim status closure requirements). To the extent possible, interim measures should not seriously complicate the ultimate physical management of hazardous wastes or constituents, nor should they present or exacerbate a health or environmental threat. Interim measures may add additional costs or work to the comprehensive Corrective Action. Such added costs or work do not preclude implementation of an interim measure. [Pg.114]

The Machinery of Protein Synthesis Can Respond to Environmental Threats... [Pg.370]

There are a few situations in which U.S. EPA does not require strict application of the mixture and derived-from rules. U.S. EPA determined that certain mixtures involving listed wastes and certain residues from the treatment of listed wastes typically do not pose enough of a health or environmental threat to deserve regulation as listed wastes. The principal regulatory exclusions from the mixture and derived-from rules are summarized below. [Pg.512]

Building new dams or increasing existing dam water-storage capacities would allow more water storage however, as dams block sediment transport, they could affect the Ebro delta if they further impede sediment accretion. On the other hand, they may act as pollutant traps associated with sediments. If so, removal and disposal of these environmental threats need to be considered. [Pg.324]

The Pew Charitable Trusts, Attack asthma Why America needs a public health defense system to battle environmental threats, 2000, www.pewtrusts.com/pdf/hhs asthma.pdf. [Pg.555]

Octyl- and nonylphenol are well known raw materials used in the surfactant industry since the early 1960s, mainly for the production of their corresponding ethoxylated derivatives (APE). Today, these products have lost considerable importance in this industry as a consequence of substantial environmental threats, resulting from their relatively slow biodegradation, toxicity of their biodegradation metabolites and positive endocrine-disrupting reactions. [Pg.57]

For this industry then, is risk necessary The short answer must be yes, but the flow of that risk is unevenly realized. The hidden costs of chemical hazards are home primarily by those who apply chemicals. Unsurprisingly then, while some (owner-operators) deny personal or environmental threats from these chemicals, others (wage laborers) are more likely to acknowledge ecological and personal peril. [Pg.87]

No doubt the greatest environmental threat to the skin is not chemical, but is rather a physical agent, sunlight most skin cancers are caused by excessive exposure to ultraviolet radiation from the sun. [Pg.112]

Detergent manufacturers have been reluctant to stop using TPP in their syndet formulations, however. For one thing, they are not convinced that TPP is as much of an environmental threat as some scientists have suggested. Also, they point out that many of the alternatives available pose problems of their own. For example, there is some evidence that NTA may be carcinogenic in rats. In response to that information, the U.S. Environmental Protection Agency (EPA) banned the use of NTA in detergents in 1970. A decade later, however, the EPA reversed course and once more permitted its use in 1980. [Pg.108]

Toxic material was placed many years ago in the sediments of a lake. Sedimentation since that time has continued their burial. Now, a harbor authority would like to put in ship piers with pilings that may disturb the toxic compounds in the sediments. You would like to know if the concentrations of the toxic compound have reached a sufficient level that the pilings will create an environmental threat. Which equation would you use for a quick, first estimate (See Figure E2.3.1.)... [Pg.35]

Rodent models have been used successfully to study generalized anxiety, but, unfortunately, their applicability to the study of panic attacks is doubtful [File 1995]. In contrast, nonhuman primate models of both anxiety and panic have been developed in our own group and in other laboratories. These models, which typically involve the administration of a challenge agent to a singly caged animal, have been successful because fear and anxiety occur spontaneously in the primate, typically in response to social or environmental threat, and because monkeys exhibit much the same behavioral repertoire in their natural environment and in captivity [Higley and Suomi 1989 Kalin and Shelton 1989 Sapolsky 1990 Suomi 1982]. [Pg.424]

Thomas, W Methyl Bromide—Pesticide and Environmental Threat, Atmos. Environ., 30, i-iv (1996). [Pg.941]

Perhaps, a more important reason for the little research in this particular area is the slow reaction rate associated with acid catalysis in general. However, the ability of solid acids to catalyze both esterification and transesterification reactions simultaneously and the possibility for employing catalysts that are reusable and green, meaning that they do not pose a great environmental threat, are attractive aspects that make the study of these materials imperative. [Pg.83]

Risk assessment An evaluation of the potential impacts of a chemical or physical hazard on human health or the environment. A risk assessment is the first step in managing and minimizing risks. Risk assessments often include identifying human health or environmental threats, possible exposure routes (e.g. inhalation, digestion, or contact with skin), the likely duration of any exposure, and the individuals that are at risk (e.g. workers, the general public, or both). A risk assessment may also involve defining the probability of an adverse effect and establishing safety limits based on health standards. [Pg.464]

While parenteral exposure is not a route posing a significant environmental threat to human health from the isotopes of radium, data acquired in studies using this route are presented here because thousands of persons did acquire radium via this route, and most of the toxicity and metabolic studies with experimental animals have used this route. It is again important to note that effects observed after parenteral administration of radium may be attributed not only to radium itself, but to the presence of any or all of its daughter products and their radioactive emissions in vivo. [Pg.26]


See other pages where Environmental threat is mentioned: [Pg.199]    [Pg.89]    [Pg.85]    [Pg.711]    [Pg.96]    [Pg.166]    [Pg.174]    [Pg.468]    [Pg.183]    [Pg.347]    [Pg.295]    [Pg.297]    [Pg.183]    [Pg.238]    [Pg.72]    [Pg.306]    [Pg.45]    [Pg.319]    [Pg.709]    [Pg.89]    [Pg.139]    [Pg.347]    [Pg.67]    [Pg.22]    [Pg.87]    [Pg.292]    [Pg.400]    [Pg.126]    [Pg.106]    [Pg.522]    [Pg.10]   
See also in sourсe #XX -- [ Pg.523 ]




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