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Disposal methods incineration

Disposal of exhausted soHds can be easily overlooked at the plant design stage, particularly when these have no intrinsic value alternative disposal methods might include landfiU of inert material or incineration, hydrolysis, or pyrolysis of organic materials. Liquid, soHd, and gaseous emissions are aU subject to the usual environmental considerations. [Pg.93]

SpiHs should be confined and prevented from entering water sources. Smother with foam and take up residue with an absorbent and put into dmms for disposal. The suggested method of disposal is incineration at an approved waste handling facHity in a system equipped with a combustion gas scmbber system (23). [Pg.35]

For those waste streams that can impact public health or the environment (if mismanaged), provide a summary of the treatment and disposal methods (for example, solvents are incinerated or recycled, lab wastes are incinerated) used to manage them and identify the on-site or off-site facilities used. Is the disposal of the waste adequately documented (for example, retention of manifests, bills of lading or transfer notes) ... [Pg.168]

This article reports on a full-scale study of the incineration of plasties with ordinary municipal waste, conducted in Germany by APME. The results, which indicate that burning waste plastics does less damage to the environment than other waste disposal methods, are commented upon by the plastics industry, and environmentalists. [Pg.97]

The recommended method of trichloroethylene disposal is incineration after mixing with a combustible fuel (Sittig 1985). Care should be taken to carry out combustion to completion in order to prevent the formation of phosgene (Sjoberg 1952). Other toxic byproducts of incomplete combustion include polycyclic aromatic hydrocarbons and perchloroaromatics (Blankenship et al. 1994 Mulholland et al. 1992). An acid scrubber also must be used to remove the haloacids produced. [Pg.201]

Some mills will combust the biosolids for heat recovery in a specialized biosolids incinerator, or a hogged or fossil fuel power boiler. Currently, this disposal method is less common than landfilling.64... [Pg.896]

Because acrylonitrile is listed as a hazardous substance, disposal of waste acrylonitrile is controlled by number of federal regulations (see Chapter 7). Rotary kiln, fluidized bed and liquid injection incineration are acceptable methods of acrylonitrile disposal (HSDB 1988). Underground injection is another disposal method. The most recent quantitative information on amount of acrylonitrile disposed in waste sites is for 1987. Emissions were 0.9 metric tons in surface water, 152 metric tons disposed through Publicly Owned Treatment Works (POTW), 92 metric tons disposed of on land 1,912 metric tons by underground injection (TR11988). Because acrylonitrile is relatively volatile and is also readily soluble in water, release to the environment from waste sites is of concern. [Pg.81]

Hexachloroethane and waste containing hexachloroethane are classified as hazardous wastes by EPA. Generators of waste containing this contaminant must conform to EPA regulations for treatment, storage, and disposal (see Chapter 7). Rotary kiln or fluidized bed incineration methods are acceptable disposal methods for these wastes. Underground injection may also be used (HSDB 1995). [Pg.121]

Waste Disposal Method Open pit burning or burying of VX or items containing or contaminated with VX in any quantity is prohibited. The detoxified VX(using procedures above) can be thermally destroyed by in a EPA approved incinerator according to appropriate provisions of Federal, State, or local Resource Conservation and Recovery Act (RCRA) regulations. [Pg.344]

WASTE DISPOSAL METHOD All decontaminated material should be collected, contained and chemically decontaminated or thermally decomposed in an EPA approved incinerator, which will filter or scrub toxic by-products from effluent air before discharge to the atmosphere. Any contaminated protective clothing should be decontaminated using HTH or bleach and analyzed to assure it is free of detectable contamination (3X) level. The clothing should then be sealed in plastic bags inside properly labeled drums and held for shipment back to the DA issue point. Decontamination of waste or excess material shall be accomplished in accordance with the procedures outlined above with the following exception ... [Pg.432]

Because endrin and endrin aldehyde are listed as hazardous substances, disposal of wastes containing these compounds is controlled by a number of federal regulations (see Chapter 7). Land disposal restrictions apply to wastes containing endrin or endrin aldehyde (EPA 1986d, 1987b). Chemical treatment (reductive dechlorination) or incineration are possible disposal methods (HSDB 1995 IRPTC 1985). Past disposal... [Pg.105]

Production, Import/Export, Use, Release, and Disposal. Data on the production and uses of 1,4-dichlorobenzene in the United States are available (C EN 1995 Chemical Marketing Reporter 1990 HSDB 1998 IRPTC 1985 SRI 1996 TRI96 1998). Production has increased over the past decade and is projected to increase for the next several years due to an increased demand for 1,4-dichlorobenzene to be used in the production of polyphenylene sulfide (PPS) resins. Incineration is the recommended disposal method for 1,4-dichlorobenzene (HSDB 1998 IRPTC 1985). Disposal of this compound is controlled by... [Pg.208]

Potential treatment and disposal methods for drilling fluids include (1) fluid ejection, (2) pit and solids encapsulation, (3) injection into safe formations, (4) removal to disposal sites off location, (5) incineration, (6) microorganism processing, and (7) distillation, liquid extraction, and chemical fixation [13]. [Pg.274]

The pesticide industry generates many concentrated wastes that are considered hazardous wastes. These wastes must be detoxified, pretreated, or disposed of safely in approved facilities. Incineration is a common waste destruction method. Deep well injection is a common disposal method. Other technologies such as wet air oxidation, solvent extraction, molten-salt combustion, and microwave plasma destmction have been investigated for pesticide waste applications. [Pg.536]

Figure 23 shows the result of comparisons of life cycle CO2 emission of Bionolle, starch-Bionolle compound, LDPE, and polystyrene. Data for producing LDPE and polystyrene are taken from a report of the Plastic Waste Management Institute [17]. The disposal method assumed is incineration. CO2 emissions from both Bionolle and starch-Bionolle compound are lower than those of LDPE or polystyrene. [Pg.310]

Off-site waste disposal methods involve the transfer of solvent wastes to an alternative location before their treatment, reuse, or release into the environment. One such method commonly used both on- and offsite is incineration. Solvent wastes are often incinerated, especially when they contain toxic substances and pose long-term EHS risks if directly released. The process of waste incineration releases a large amount of CO2 into the environment, but often the heat generated from this process may be recovered for use within a plant. When contaminated... [Pg.62]


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