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Materials hazards toxicity

Clean Air Act and its amendments ia 1970, 1977, and 1990 1967 Air Quahty Standards and National Air Pollution Acts and 1970 National Environmental PoHcy Act) (2) better waste disposal practices (1965 SoHd Waste Disposal Act 1976 Resource Conservation and Recovery Act) (see Wastes, industrial Waste treatment, hazardous wastes) (i) reduced noise levels (1972 Noise Control Act) (4) improved control of the manufacture and use of toxic materials (1976 Toxic Substances Control Act) and (5) assignment of responsibiUty to manufacturers for product safety (1972 Consumer Product Safety Act) (15,16). [Pg.92]

Shipping vitamin D in crystalline or resin form should be done in containers marked appropriately to indicate the material is toxic by DOT standards. Its proper DOT labeling is DOT Hazard Class 6.1, poisonous. Waste material should be burned or placed in an appropriate landfill. [Pg.132]

Low-Pressure Tanks (below 15 psig) Low-pressure storage tanks for highly hazardous toxic materials should meet, as a minimum, the American Petroleum Institute (API) 620 Standard, Recommended Rules for the Design and Construc tion of Large Welded, Low-Pressure Storage Tanks (API Standards). This standard covers... [Pg.2308]

Since discharges of vapors from highly hazardous toxic materials cannot simply be released to the atmosphere, the use of a weak seam roof is not normally acceptable. It is best that tanks be designed and stamped for 15 psig to provide maximum safety, and pressure relief systems must be provided to vent to equipment that can collect, contain, and treat the effluent. [Pg.2308]

While either rupture disks or relief valves are allowed on storage tanks by Code, rupture disks by themselves should not be used on tanks for the storage of highly hazardous toxic materials since they do not close after opening and may lead to continuing release of toxic material to the atmosphere. [Pg.2308]

The discharge of copious quantities of chemicals directly to the atmosphere can give rise to secondary hazards, especially if the materials are toxic and can form a flammable atmosphere (e.g., vapor or mist) in air. In such cases, the provision of a knockout device (scrubber, dump tank) of adequate size to contain the aerated/foaming fluid is required. [Pg.976]

CHEMpendium regularly updated information on the transport of hazardous materials, chemical toxicity, industrial chemicals and environmental contaminants, workplace safety, regulatory compliance, WHMIS and Right-to-Know, Canada s DLS and NDSL, Emergency response. [Pg.313]

The material factor is then modified to allow for the effect of general and special process and material hazards the physical quantity of the material in the process step the plant layout and the toxicity of process materials. [Pg.378]

A variety of other gases are also given off by burning materials In two studies fire fighters went to address actual buildings on fire, equipped with combustion product monitors [40, 41]. Both studies had the same conclusions the overwhelming hazardous toxicant in a fire is carbon monoxide. [Pg.470]

Mond Index Material factor Special material hazards General process hazards Special process hazards Quantity factor Layout hazards Toxicity hazards... [Pg.26]

In snmmary, many of the specific chemicals in petroleum are hazardous because of their chemical reactivity, fire hazard, toxicity, and other properties. In fact, a simple definition of a hazardons chemical (or hazardous waste) is that it is a chemical substance (or chemical waste) that has been inadvertently released, discarded, abandoned, neglected, or designated as a waste material and has the potential to be detrimental to the environment. Alternatively, a hazardons chemical may be a chemical that may interact with other (chemical) snbstances to give a prodnct that is hazardous to the environment. Whatever the case, methods of analysis mnst be available to determine the nnrture of the released chemical (waste) and from the data predict the potential hazard to the environment. [Pg.153]

Flammability properties of materials are clearly important for fire prevention but there are other properties that are also significant. There have been a number of severe fire incidents initiated by a material s reactivity properties that were previously unrecognized or unknown to the user. The development of a Materials Hazard Identification program requires knowledge of a material s toxicity and reactivity, as well as flammability. [Pg.47]

In many states, regulations only require that hospital incinerators not create a public nuisance usually recognized as odors and smoke opacity. Disposal costs for these medical wastes are becoming stiffer, just as surely as they are for infectious and other hazardous/toxic wastes. This adds another incentive to incinerate. It may be possible that a good deal of hospital waste could be separated, reduced, and recycled. While infectious waste is obviously not recyclable, the amount of waste designated infectious can be greatly reduced by separating materials to avoid excess contamination [74]. [Pg.82]

Acetal is dangerous when exposed to heat or flame and it can react vigorously with oxidizing materials. Its toxicity, toxicology and fire hazards are discussed in Ref 7... [Pg.13]

Sai, N. 1., Ed., 1984, Dangerous Properties of Industrial Materials, 6th ed., Reinhold, New York. Physical properties, fire and explosion hazards, toxicity, and incompatibility for about 20,000 chemicals. [Pg.294]

Willard, E.M. and Ruby, M.M., Eds., Environmental Hazards Toxic Waste and Hazardous Material. ABC-CLIO, Inc., 1991. [Pg.102]

Human activities are associated with the use and disposal of a variety of chemicals and chemical products. This is the situation for a householder, a laboratory student, and also the industry worker. Many materials have properties that make them hazardous. They can create physical (fire, explosion) or health hazards (toxicity, chemical bums). However, there are many ways to work with chemicals which can both reduce the probability of an accident and reduce the consequences should an accident occur. Risk minimization depends on safe practices, appropriate engineering controls for chemical containment, the proper use of personnel protective equipment, use of the least amount of material necessary, and substitution of a less-hazardous chemical for a more hazardous one. Before beginning any chemical processing or operation, ask What would happen if. .. The answer to this question requires understanding of the hazards associated with chemicals, the equipment, and the procedure involved. The hazardous properties of the material and its intended use will dictate the precautions to be taken. [Pg.408]

There are a large number of different methods used for bench-scale assessment of combustion toxicity, and the applicability of test data to lire hazard assessment is not always clear. Obviously, toxic potency data should not be used in isolation but should either be a part of a classification scheme or as part of the input to lire risk and lire safety engineering assessments. It is important that uncertainty or confidence limits should be used with toxic potency data, because they are often relatively large. Fire effluent toxic potency does not have a unique value but is a function of the material and the fire conditions, particularly temperature and oxygen availability in the fire zone, and also the fire environment (enclosure, geometry, and ventilation). To assess the fire hazard, toxic potency data must be relevant to the end use fire situation, and the fire condition, which can be defined using the ISO classification of fire stages. [Pg.474]


See other pages where Materials hazards toxicity is mentioned: [Pg.2308]    [Pg.2308]    [Pg.2308]    [Pg.2309]    [Pg.29]    [Pg.380]    [Pg.1232]    [Pg.373]    [Pg.47]    [Pg.92]    [Pg.100]    [Pg.100]    [Pg.12]    [Pg.368]    [Pg.369]    [Pg.5]    [Pg.2]    [Pg.284]    [Pg.100]    [Pg.373]    [Pg.463]    [Pg.427]    [Pg.323]    [Pg.346]    [Pg.10]    [Pg.2063]    [Pg.2063]   
See also in sourсe #XX -- [ Pg.487 ]




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