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Disposal by incineration

Small quantities of spilled form amide can be washed away with plenty of water. Larger amounts should be absorbed appropriately or pumped into containers for proper disposal by incineration or biological degradation in a sewage water treatment plant. [Pg.510]

Used oil disposal trends include waste minimisation such as by reclaiming used fluid on site, as well as recycling of mineral oil lubricants instead of disposing by incineration. The recycling effort involves a system where spent mineral oils are collected then shipped to specialty refineries where the materials are distilled, hydrofinished, and re-refined into fresh base stocks. These re-refined materials are virtually identical to virgin feedstocks. [Pg.267]

Responsible disposal of chemicals, samples and consumables is likewise an important aspect of good operating procedures in the laboratory. Regulations are fairly strict in terms of what may be disposed of into the drainage system. It may be permissible to dispose of some chemicals directly down the drain, flushed down with copious volumes of water. For other chemicals, specific disposal instructions, where available, must be followed. These will include collection of specific types of chemical waste in containers for disposal by incineration, landfill, etc. [Pg.135]

To be effective, it is essential that the impregnant is nonleachable in service conditions. However, it is not a primary requirement that the impregnant be chemically bonded to the cell wall polymeric constituents, although this may occur in some circumstances. It is essential that the frxed impregnant is nontoxic whilst in the cell wall and under any circumstances in which it is released from the cell waU, such as disposal by incineration or composting, or due to any recycling process. [Pg.149]

Small Quantities. Wear goggles and protective gloves and clothing. Work in the fume hood. To 0.25 g of 2-acetylaminofluorene in a 50-mL round-bottom flask add 10 mL of concentrated hydrochloric acid. Fit the flask with a condenser and heat under reflux for at least 10 hours when all trace of yellow should have disappeared. Cool the contents of the flask to 0°C in an ice-salt bath and, over a period of 5 minutes, add dropwise a solution of 0.13 g of sodium nitrite in 0.3 mL of water. Stir the mixture for 30 minutes, then slowly add 2.7 mL of ice-cold 50% hypophosphorus acid. After stirring at room temperature for 16 hours, filter the mixture, wash the filtrate into the drain with water, and discard the solid (fluorene) with normal refuse or package and label for disposal by incineration.4-6... [Pg.10]

Wearing butyl rubber gloves, fireproof clothing, face shield, and goggles cover spill with sand.8 Transfer mixture into a dry plastic bag filled in advance with an inert gas. Package and label for disposal by incineration.2 Alternatively, in the fume hood, add butanol slowly to the solid mixture until the reaction ceases. Then carefully add water until all the... [Pg.331]

Package Lots. Place in a separate labeled container for burning. Dissolve or mix the material into a combustible solvent and package and label for disposal by incineration.2... [Pg.370]

Dioxins are produced naturally when wood burns, for example. They are a group of chemicals, about seventy-five in number, known chemically as dibenzodioxins. Only a few of these are regarded as particularly toxic, with TCDD (tetrachlorodibenzodioxin) being the most potent (see box, p. 122). A variety of human activities can produce dioxins, ranging from chemical synthesis to disposal by incineration of plastics such as PVC and the industrial bleaching of paper with chlorine. Burning waste of any description probably produces dioxins, as do car engines. The major sources of dioxins are ... [Pg.121]

Normally all kinds of organic waste or combustible materials are potential candidates for incineration. Even contaminated water and soils are currently disposed by incineration. [Pg.78]

Potentially infectious waste, such as material from tissue cultures, should be autoclaved and prepared for disposal by incineration. [Pg.298]

The disposal of municipal and industrial wastes has become an important problem because the traditional means of disposal, landfill, has become environmentally much less acceptable than previously. In addition, special incinerator systems are required to meet environmental standards for disposal by incineration. Disposal of wastes by landfill or incineration also includes a potential loss of energy sources and, in some cases, valuable mineral resources. New, much stricter regulation of these disposal methods will make the economics of waste processing for resource recovery much more favorable. [Pg.222]

Emissions to land the CER identifies the quantities and disposal routes for both hazardous and non-hazardous waste in 1997 and 1998. The figures include disposal by incineration. There is also a group target to reduce total waste to less than 255000 tonnes by 2000. [Pg.132]

Emissions to land figures are presented for production and other waste , and the volumes sent to each destination (on- and off-site disposal by incineration or landfill) are identified. During 1998 approximately 700000 tonnes of wastes were disposed of by landfill (34%) or energy recovery/ incineration (66%). [Pg.148]

Coupled with these facilities and analytical procedures are programs for routine weekly decontamination waste disposal by incineration and burial personnel protection and safety training. [Pg.456]

Recent concern about environmental issues regarding cutting fluids has raised the problem of using lubricants containing chlorinated chemical compounds because chlorine causes serious air pollution in connection with dioxin emission when they are disposed by incineration. At the moment, the most practicable replacement... [Pg.313]

Figure 8.30 Energy consumption (a) and carbon dioxide equivalent amount (b) for PLLA production. In Case (1), used PLLA is disposed by reclamation and equivalent amount of PLLA is produced from corn. In Case (2), used PLLA is disposed by incineration, the energy is utilized for power generation, and equivalent amount of PLLA is produced from com. In Case (3), used PLLA is recycled by hydrolytic degradation, lactide production and polymerization, and PLLA with equivalent amount of which is lost during recycling is produced from com [433]. (Reproduced from [433] with permission from Society of Environmental Science, Japan 2009.)... Figure 8.30 Energy consumption (a) and carbon dioxide equivalent amount (b) for PLLA production. In Case (1), used PLLA is disposed by reclamation and equivalent amount of PLLA is produced from corn. In Case (2), used PLLA is disposed by incineration, the energy is utilized for power generation, and equivalent amount of PLLA is produced from com. In Case (3), used PLLA is recycled by hydrolytic degradation, lactide production and polymerization, and PLLA with equivalent amount of which is lost during recycling is produced from com [433]. (Reproduced from [433] with permission from Society of Environmental Science, Japan 2009.)...
PVC has been under attack from environmental groups on a variety of grounds for a number of years. Because PVC contains chlorine, it may lead to the formation of chlorinated dioxins if it is disposed by incineration. While evidence suggests that the presence or absence of PVC is not very significant in dioxin emissions from well-controlled incineration, less important than combustion conditions, there is reason for concern about its presence in poorly controlled incineration systems. PVC has also been attacked because of concerns related to the carcinogenicity of its vinyl chloride monomer. Increasingly, lead and cadmium stabilizers used in some PVC resins are being restricted or banned, due to concerns about toxic effects of these heavy metals. [Pg.157]

As no hazardous waste arises in the production of secondary raw materials or products made of virgin materials, the scenarios for mechanical recycling substituting plastics show no effect at all (Fig. 13.30). The increased quantities of hazardous waste in the case of processes that substitute wood or concrete result largely from the final disposal by incineration (filter dust). [Pg.548]

One method to address this issue was implemented by a company that supplied T-Shirts to a large mass merchant more than a dozen years ago. It encapsulated the batteries, circuits, and LEDs in hard, clear epoxy shells that were placed in sealed pockets. These units were capable of flashing up to 100,000 times before shutting down. When these shirts were disposed of, the electronics, batteries, and electrical leads were therefore sealed and were suitable for landfill disposal, but they were not suitable for disposal by incineration. Recycling is a far more environmentally friendly... [Pg.203]

Precaution Disposal by incineration recommended Amadol WE [Akzo Nobel Surf. Chem. AB]... [Pg.95]

F recaution Wear eye/face protection disposal by incineration recommended Storage Store in closed containers preferably 10-20 C Elfiacos ST 9 [Akzo Nobel / kzo Nobel bv]... [Pg.394]


See other pages where Disposal by incineration is mentioned: [Pg.950]    [Pg.113]    [Pg.214]    [Pg.398]    [Pg.277]    [Pg.69]    [Pg.234]    [Pg.204]    [Pg.49]    [Pg.77]    [Pg.704]    [Pg.598]    [Pg.163]    [Pg.115]    [Pg.369]    [Pg.537]    [Pg.153]    [Pg.979]    [Pg.77]    [Pg.562]    [Pg.368]    [Pg.141]    [Pg.109]    [Pg.442]    [Pg.290]   
See also in sourсe #XX -- [ Pg.154 ]




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