Risks environmental

Lead-based paint (qv) in old stmctures has been identified as an environmental risk because the chemical form of lead in paint is readily available... [Pg.52]

Phenol. Phenol monomer is highly toxic and absorption by the skin can cause severe blistering. Large quantities can cause paralysis of the central nervous system and death. Ingestion of minor amounts may damage kidneys, Hver, and pancreas. Inhalation can cause headaches, dizziness, vomiting, and heart failure. The threshold limit value (TLV) for phenol is 5 ppm. The health and environmental risks of phenol and alkylated phenols, such as cresols and butylphenols, have been reviewed (66). [Pg.302]

Initially, the source of environmental risk from cooling water was assumed to be the pollutant discharged, ie, heat, in the form of the elevated temperature of the water released from the condensers. Heat is now recognized as being only one of several potential risks of power station cooling (Fig. 2). [Pg.472]

An environmental risk in solution mining is surface subsidence. This risk is greatest with embedded salt. No cases of salt subsidence have been reported in mining domes that have been mined according to standard industry approved practice in the United States, but some have been seen in other countries. One side benefit of dome solution mining is use of the cavities later for storage of industrial fluids, chiefly petroleum and natural gas. [Pg.409]

Typical analysis for the neutralization wet process product is given in Table 5. Sodium cyanide is packed in mild steel or fiber dmms and in 1.4 t Flo-bins. Dry sodium cyanide is also shipped in wet-flo tank cars and tmcks of up to 32 t net. At destination, water is circulated through the wet-flo car or trailer to dissolve the dry sodium cyanide at deUvery. This type of shipment reduces freight costs and reduces environmental risks compared with 30% aqueous solution shipment. Safety regulations are imposed by the various shipping lines and by the countries in which cyanide is transported. [Pg.383]

Despite the attractions of economic forces driving environmental protection, some cautions and failures have been noted. Firstly, the export of hazardous waste to countries where costs for treatment are lower enhances environmental risks during transport and has the potential for transboundary export in the event of pollution. At the same time, the loss of raw material may deprive the home market of an adequate supply of feedstock for the home-based industry. Secondly, there is considerable scepticism that self-regulation of TBT-based antifoulants could be achieved in a timely manner by the shipping industry. This is an instance where the cost benehts to one industry are born by another commercial sector, notably aquaculture. Thus, protection of the marine environment is likely to be aided by economic factors but the role of government, via taxation and standard setting, is not likely to be usurped. Public education and, in turn, pressure, can promote and support corporate environmentalism. [Pg.90]

Assessing environmental risk from effluent diseharges or for formal environmental impaet assessment. [Pg.308]

Airborne particulate matter emissions can, to a great extent, be minimized by pollution prevention and emission control measures. Prevention is frequently more cost-effective than control and, therefore, should be emphasized. Special attention should be given to pollution abatement measures in areas where taxies and buses associated with particulate emissions may pose a significant environmental risk. [Pg.19]

A No. As the Chairman said in a recent interview-and I will repeat now-it is our intention to continually improve performance. However, it is unrealistic to believe that we could achieve a zero accident or emission standard tomorrow. Even if it were theoretically achievable, the cost would be so large that we would bankrupt the company. We must maintain a balance between the benefits we achieve and the cost of achieving them. Let me also remind you that as a company we have made a commitment to abandon any business or technology where we consider the safety and environmental risks to be intolerable. [Pg.45]

Material control and traceability This item could have a higher priority if raw material or product losses are high or represent a significant safety or environmental risk. [Pg.93]

This risk is high relative to the widely accepted standard range of environmental risk of I x lO to 1 x 10 . ... [Pg.346]

Environmental risk commmiication is one of the more important problems that industry faces. Since tlie mid 1980s, public concerns about the environment liave grown faster Uian concern about virtually any other national problem. There are two major categories or risk nonfixable and fixable. Nonfixable risks... [Pg.526]

Use of some biomass feedstocks can increase potential environmental risks. Municipal solid waste can contain toxic materials that can produce dioxins and other poisons in the flue gas, and these should not be burned without special emission controls. Demolition wood can contain lead from paint, other heavy metals, creosote, and halides used in presen a-tive treatments. Sewage sludge has a high amount of sulfur, and sulfur dioxide emission can increase if sewage sludge is used as a feedstock. [Pg.159]

Cadmium presents an environmental risk. Since small nickel-cadmium cells are often not separately disposed of, they may enter municipal garbage incinerators. The search for alternative materials for the negative electrode led to metal hydrides, which not only are regarded as environmentally less critical, but also allow higher energy density than cadmium. This is especially important for use in portable equipment, such as cellular phones or lap-... [Pg.284]

Lithium hexafluoroarsenate is thermally stable [54, 55] but shows environmental risks due to possible degradation products [56-58], even though it is itself not very toxic. Its LD 50 value is similar to that of lithium perchlorate [55]. Just like lithium hexafluorophosphate, it can initiate the polymerization of cyclic ethers. Polymerization may be inhibited by tertiary amines [59], or 2-methylfuran [60], yielding highly stable electrolytes. [Pg.462]

NRMMC-EPHC (2006) Australian guidelines for water recycling Managing health and environmental risks. Natural Resource Management Ministerial Council and Environment Protection and Heritage Council - Australia. ISBN 1 921173 07 6... [Pg.106]

Ferrari B, Mons R, Vollat B, Fraysse B, Paxeus N, Lo Giudice R, Pollio A, Garric J (2004) Environmental risk assessment of six human pharmaceuticals are the current enviommental risk assessment procedures sufficient for the protection of the aquatic environment Environ Toxicol Chem 23 1344-1354... [Pg.225]

Goldman LR. 1995. Case studies of environmental risks to children. Critical Issues for Children and Youths 5 27-33. [Pg.210]

A biomarker is here defined as a biological response to an environmental chemical at the individual level or below, which demonstrates a departure from normality. Responses at higher levels of biological organization are not, according to this definition, termed biomarkers. Where such biological responses can be readily measnred, they may provide the basis for biomarker assays, which can be nsed to stndy the effects of chemicals in the laboratory or, most importantly, in the field. There is also interest in their employment as tools for the environmental risk assessment of chemicals. [Pg.60]

In environmental risk assessment, the objective is to establish the likelihood of a chemical (or chemicals) expressing toxicity in the natural environment. Assessment is based on a comparison of ecotoxicity data from laboratory tests with estimated or measured exposure in the field. The question of effects at the level of population that may be the consequence of such toxicity is not addressed. This issue will now be discussed. [Pg.90]

The development of models incorporating biomarker assays to predict the effects of chemicals upon parameters related to r has obvious attractions from a scientific point of view and is preferable, in theory, to the crude use of ecotoxicity data currently employed in procedures for environmental risk assessment. However, the development of this approach would involve considerable investment in research, and might prove too complex and costly to be widely employed in environmental risk assessment. [Pg.93]

Another issue is the development and refinement of the testing protocols used in mesocosms. Mesocosms could have a more important role in environmental risk assessment if the data coming from them could be better interpreted. The use of biomarker assays to establish toxic effects and, where necessary, relate them to effects produced by chemicals in the field, might be a way forward. The issues raised in this section will be returned to in Chapter 17, after consideration of the individual examples given in Part 2. [Pg.97]

See also in sourсe #XX -- [ Pg.3 , Pg.75 , Pg.76 , Pg.141 , Pg.143 , Pg.146 , Pg.153 , Pg.154 , Pg.171 , Pg.198 , Pg.214 , Pg.226 , Pg.251 , Pg.259 , Pg.272 , Pg.294 , Pg.323 , Pg.329 , Pg.343 , Pg.344 , Pg.349 , Pg.359 , Pg.371 , Pg.395 , Pg.400 , Pg.415 , Pg.419 ]

See also in sourсe #XX -- [ Pg.191 ]

See also in sourсe #XX -- [ Pg.232 ]

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