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Hazardous components

Safety considerations might dictate that a particularly hazardous component be removed from the process as early as possible to minimize the inventory of that material. [Pg.132]

A knowledge of the molecular composition of a petroleum also allows environmentalists to consider the biological impact of environmental exposure. Increasingly, petroleum is being produced in and transported from remote areas of the world to refineries located closer to markets. Although only a minuscule fraction of that oil is released into the environment, the sheer volume involved has the potential for environmental damage. Molecular composition can not only identify the sources of contamination but also aids in understanding the fate and effects of the potentially hazardous components (7). [Pg.164]

The treatment of waste is the third element of the hierarchy and should be utilized only in the absence of feasible source reduction or recychng opportunities. Waste treatment involves the use of chemical, biological, or physical processes to reduce or eliminate waste material. The incineration of wastes is included in this categoiy and is considered preferable to other treatment methods (i.e., chemical, biological, and physical) because incineration can permanently destroy the hazardous components in waste materials (Ref. 4). It can also be employed to reduce the volume of waste to be treated. [Pg.2165]

A hydrated magnesium silicate in fibrous form. The fibres are believed to be the more hazardous component of asbestos dust. [Pg.79]

The primary hazardous components of EAF dust are zinc, lead, and cadmium nickel and chromium are present when stainless steels are manufactured. [Pg.128]

Separatory operations may isolate the more hazardous components from tlie diluent or inert. Screening of solids, in effect, separates tlie more hazardous dusts (small particles and fines) from the less liazardous larger pieces of material. Centrifuges, like all liigh-speed equipment, must be securely positioned to provide protection to all persomiel working in the vicinity. [Pg.493]

The routine monitoring of every hazardous constituent of the effluent gases of operating incinerators is not now possible. EPA has established procedures to characterize incinerator performance in terms of the destruction of selected components of the anticipated waste stream. These compounds, labeled principal organic hazardous components (POHCs), are currently ranked on the basis of their difficulty of incineration and their concentration in the anticipated waste stream. The destraction efficiency is expressed in terms of elimination of the test species, with greater than 99.99 percent removal typically judged acceptable provided that toxic by-products are not generated in the process. [Pg.134]

Sources of land pollution include direct dumping of domestic and industrial solid waste, excessive application of agrochemicals, and indirect contamination resulting from leaks or from leaching of hazardous components from liquid waste disposal sites or from atmospheric fallout. Land may also become contaminated by chemicals processed, stored or dumped at the site, perhaps in the distant past. Such contamination may pose a health risk to workers on the site, those subsequently involved in building, construction or engineering works, or the public (e.g. arising from trespass), and to animals. [Pg.345]

Reuse minimal K062, Spent pickle liquor Hazardous components lead, nickel, chromium Total generation about 6 million t/yr Reuse some recycled... [Pg.63]

Stripping of electrical and electronic waste appliances must be carried out properly. During the processing of waste appliances (e.g., in shredders), it is essential to avoid that components highly contaminated with hazardous substances end up in fractions that are intended for recycling. It is furthermore necessary to ensure that the disposal of treatment residues (e.g., shredder residues) is not impeded by the presence of hazardous substances. As a rule, components containing particularly hazardous substances are to be removed manually. Future disposal processes, such as pyrolysis, may allow recycling of appliances without prior removal of hazardous substances, in which case it will be possible to do without the disassembly of hazardous components.411... [Pg.1216]

Besides the environmentally sound disposal of hazardous components, the recovery of ferrous, nonferrous, and noble metals is the main priority in the disposal of electrical and electronic appliances. Here, it is important to ensure that the requirements relating to scrap quality are met. [Pg.1216]

Stripping of hazardous components In an initial step, the components containing particularly hazardous substances are for the most part removed manually. [Pg.1217]

These large electrical waste appliances consist mainly of iron, copper, aluminum, and insulation materials. The insulation materials are mostly inorganic. The electronic controllers contained in the appliances are classified as electronic scrap. They may contain particularly hazardous components (accumulators, batteries, condensers, mercury switches, etc.). [Pg.1218]

The requirements for management and disposal of large electrical waste appliances are that appliances may be shredded only if the particularly hazardous components have previously been removed. [Pg.1218]

A chemical process uses as raw material hazardous Component A. Component A is fed as liquid under pressure to a continuous stirred tank vessel in which it performs a first-order reaction to useful Product B. The reaction in the vessel is isothermal first order with a rate of reaction given by — ta = k> txp(-E/RT), where rA is the rate of reaction (kmol-min = 1.5 x 106 min-1, E = 67,000 kJ kmol-1,... [Pg.632]

Since the implementation of the RoHS Directive, many problems have already been addressed and hazardous components have been limited or banned. The outcome of the RISKCYCLE project and further research initiatives could be a reason to extend the scope of the directive either by a broader scope (not only electrical and electronic equipment) or by extending the catalogue of restricted substances (Annex II of the Directive). [Pg.471]

Hazardous Components (Specific Chemical identity Common Name(s)) Other limits OSHA PEL ACGlH TlV Recommended o-o (optionan... [Pg.76]

Safety aspects are considered in two phases (Fig. 11). In the rule based synthesis some safety related rules are applied in process concept selections. These include rules such as separate corrosive or hazardous components first or avoid using chemically incompatible substances in the same process. ... [Pg.107]

For a given release scenario, estimate the state of the released contaminant after it has depressurized and become airborne (including any initial dilution). The initial mole fraction of hazardous components will be applied to the final reported concentrations and hazardous endpoint concentrations throughout the process. If source momentum is important (as in a jet release or for plume rise), other models are available that can address these considerations. Disregarding the dilution due to source momentum will likely result in higher concentrations downwind, but not always. [Pg.66]

Removing hazardous components early in the process rather than spreading them throughout the process... [Pg.179]

Asbestos was a relatively economieal produet for a mass market of commercial customers. In other markets better quality also achieves a better market price. This quality may also mean for customers being free of hazardous components (textiles, cosmetics, children s toys). [Pg.26]

Perma-Fix Environmental Services, Inc. (Perma-Fix), has developed the Perma-Fix Process for the neutralization and stabilization of hazardons, radioactive, and mixed wastes. The Perma-Fix Process is a two-step treatment involving proprietary chemical treatment of wastes followed by the addition of stabilization chemicals to create a final waste form with the hazardous component of the wastes neutrahzed. The technology has been used commercially for several years. [Pg.859]

The hazardous component of the treated wastes is eliminated treated wastes contaminated with metals may be disposed of as nonhazardous wastes, and mixed wastes may be disposed of as radioactive wastes, reducing disposal costs and liability concerns. [Pg.859]

According to the vendor, only particles from about 2 mm to 50 p,m in size can be processed by magnetic barrier separation. Some bench-scale studies suggest that high feed rates decrease separation efficiency. Materials undergoing magnetic barrier separation must then be processed by some treatment technology before the hazardous component of the waste can be disposed. [Pg.940]

The hazardous components of MSW, ie, household chemicals, oily wastes, and lead and other metals in batteries, can leach from landfills and contaminate both surface water and groundwater or enter the atmosphere. Increased regulation to improve landfill integrity has led to impermeable liners and drainage and water quality monitoring systems. As a result, in many urban areas, land is either no longer readily available for new landfills or is available only at high cost. [Pg.108]

Through functional-use analysis, toxicological and environmental fate data on structurally similar chemicals can be applied to each member of a functional-use class. A focus on functional use not only offers commonality in perspective for chemical innovators, but also simplifies the risk assessment process. Within a given product dass, the use and exposure patterns are generally the same, with minor variability therefore, the hazard component of the risk equation becomes a... [Pg.113]

ID S is synthesized by the reaction of ammonia with maleic anhydride in water. The synthesis of EDDS and IDS is also in accordance with the 3rd Principle of Green Chemistry Design Less Hazardous Chemical Synthesis, although they are still not perfectly green as there still some hazardous components. This can be a difficult principle to achieve completely as many reactive chemicals in the chemist s toolbox are often hazardous. [Pg.293]

The Safety Data Sheet contains information, such as the identity of the dye, possible hazardous components and physicochemical, toxicological, and ecological data, first aid and emergency measures, occupational exposure limits, and information on personal protective equipment [45],... [Pg.638]


See other pages where Hazardous components is mentioned: [Pg.171]    [Pg.540]    [Pg.192]    [Pg.132]    [Pg.508]    [Pg.146]    [Pg.1222]    [Pg.162]    [Pg.387]    [Pg.798]    [Pg.1067]    [Pg.451]    [Pg.4]    [Pg.78]    [Pg.671]    [Pg.36]    [Pg.231]   
See also in sourсe #XX -- [ Pg.1405 ]

See also in sourсe #XX -- [ Pg.29 ]




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Hazard components

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