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Relevant bibliographies by topics / Hazardous wastes Victoria Incineration

Academic literature on the topic 'Hazardous wastes Victoria Incineration'

Author: Grafiati

Published: 10 December 2022

Last updated: 28 January 2023

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Journal articles on the topic "Hazardous wastes Victoria Incineration"

1

Gannon, T., A. R. Ansbro, and R. P. Burns. "Incineration of hazardous wastes." Environmental Monitoring and Assessment 19, no. 1-3 (1991): 105–25. http://dx.doi.org/10.1007/bf00401302.

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ZURER, PAMELA S. "Incineration of Hazardous Wastes at Sea." Chemical & Engineering News 63, no. 49 (December 9, 1985): 24–42. http://dx.doi.org/10.1021/cen-v063n049.p024.

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Dempsey, C. R., and R. C. Thurnau. "Pilot-Scale Evaluation of Incinerating Listed Wastes from Specific Sources." Water Science and Technology 24, no. 12 (December 1, 1991): 255–65. http://dx.doi.org/10.2166/wst.1991.0392.

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Pilot-scale incineration testing was conducted at the United States Environmental Protection Agency's Incineration Research Facility to support the development of best demonstrated available technology standards for the treatment of several hazardous wastes from specific sources. This paper summarizes the results of this testing for four of these wastes. The objective was to determine if these four wastes could be incinerated by a well designed, well operated incinerator based on compliance with the hazardous waste incinerator regulations and to characterize the incineration residuals for hazardous constituents. It was found that these wastes could generally be incinerated in compliance with these regulations. However, the mist carryover from the air pollution control device would have to be more effectively controlled to meet the particulate standard for some of these wastes.

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4

Kamens, Richard. "Incineration of Municipal and Hazardous Solid Wastes." Journal of Environmental Quality 19, no. 1 (January 1990): 157. http://dx.doi.org/10.2134/jeq1990.00472425001900010025x.

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5

Lodge, James P. "Incineration of municipal and hazardous solid wastes." Atmospheric Environment (1967) 23, no. 11 (January 1989): 2636. http://dx.doi.org/10.1016/0004-6981(89)90292-8.

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6

Bennett, GaryF. "Incineration of municipal and hazardous solid wastes." Journal of Hazardous Materials 26, no. 1 (January 1991): 97–98. http://dx.doi.org/10.1016/0304-3894(91)85016-g.

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7

Harris, Robert, and Stephen Washburn. "The Qualitative and Quantitative Risks of Incinerating Hazardous Wastes." Journal of the American College of Toxicology 7, no. 4 (July 1988): 551–58. http://dx.doi.org/10.3109/10915818809019531.

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Incineration is becoming an increasingly popular method of treatment and disposal for both hazardous and municipal solid waste. Concerns about potential health risks associated with the operation of incineration facilities, however, have led to public opposition to their siting in several communities. The process of risk assessment is a useful tool for providing a quantitative basis for decision makers evaluating such siting concerns.

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Al-kaabi, Falah Kareem Hadi. "Supercritical water oxidation for the treatment of various organic wastes: A review." International Journal of Rural Development, Environment and Health Research 6, no. 4 (2022): 1–14. http://dx.doi.org/10.22161/ijreh.6.4.1.

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The removal of complex organic and chemical industrial wastes is not accessible using conventional treatment methods. Incineration and hydrothermal oxidation under supercritical conditions are two options for dealing with a wide range of hazardous wastes. Incineration is an effective treatment for removing hazardous waste. The main disadvantages of incineration are a source of unwanted emissions and high operating costs. Supercritical water oxidation (SCWO) is considered a green technology for destroying organic waste with friendly environmental emissions. The removal efficiency reached 99.99% within a short residence time. In this review, the treatment of organic waste by SCWO is shown using co-fuel and catalysts to enhance the performance of SCWO.

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9

Shin, I. K. C. "The Situation and the Problems of Hazardous Waste Treatment in Germany." Water Science and Technology 26, no. 1-2 (July 1, 1992): 31–40. http://dx.doi.org/10.2166/wst.1992.0383.

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Yearly 4 900 000 tons of hazardous waste are generated in West Germany. The Germany Waste Disposal Act regulates not only the import and the export, but also the transit of wastes. Also avoidance of waste generation and recycling of wastes are emphasized by the act. To reduce waste amounts the collected wastes are treated preliminarily by chemical, physical and biological methods. 740 000 tons of hazardous waste are combusted annually in 27 incineration plants. 18 additional incineration plants are planned. Disposal of diluted acids in the North Sea was completely stopped by the end of 1989. Chlorinated hydrocarbons were burned on a German incineration ship. This was stopped in 1989. The most usual disposal process is the sanitary landfill. Rainfall results in water and soil pollution caused by leachates. A roof above the landfill could eliminate the generation of leachates. The safest disposal is the deep underground deposition in salt domes.

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10

Bond, Desmond. "ES Views: Ocean incineration of hazardous wastes: An update." Environmental Science & Technology 19, no. 6 (June 1985): 486–87. http://dx.doi.org/10.1021/es00136a601.

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Dissertations / Theses on the topic "Hazardous wastes Victoria Incineration"

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Coward, Harriet Michelle. "Health risk assessment of the radioactive emissions from the consolidated incineration facility at Savannah river site." Thesis, Georgia Institute of Technology, 1995. http://hdl.handle.net/1853/17948.

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Mayer, Kate A. "Laboratory chamber experiments simulating in-situ plasma vitrification for geoenvironmental concerns." Thesis, Georgia Institute of Technology, 1996. http://hdl.handle.net/1853/18990.

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Akki, Umesh. "Gas phase formation pathways and mechanisms of polychlorinated dibenzo-p-dioxins and dibenzofurans." Diss., Georgia Institute of Technology, 1998. http://hdl.handle.net/1853/23157.

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Calcagno, James A. "Data analysis and correlations : for the particulate matter continuous emisions monitoring system test program at the TSCA incinerator /." 2001. http://etd.utk.edu/2001/CalcagnoJames.pdf.

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Lu, Yan. "A study of lead devolatilization using a laminar entrained-flow." Thesis, 1995. http://hdl.handle.net/1957/35213.

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Books on the topic "Hazardous wastes Victoria Incineration"

1

Brunner, Calvin R. Handbook of hazardous waste incineration., ed. Hazardous waste incineration. 2nd ed. New York: McGraw-Hill, 1993.

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2

1943-, Freeman Harry, ed. Incinerating hazardous wastes. Lancaster, Pa: Technomic Pub. Co., 1988.

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3

Handbook of hazardous waste incineration. Blue Ridge Summit, PA: TAB Professional and Reference Books, 1989.

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4

Buren, D. Van. Characterization of hazardous waste incineration residuals. Cincinnati, OH: U.S. Environmental Protection Agency, Hazardous Waste Engineering Research Laboratory, 1987.

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5

J, Rossi Amadeo, and Vick Katherine M, eds. Incineration of municipal and hazardous solid wastes. San Diego: Academic Press, 1989.

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6

S, Rickman William, ed. CRC handbook of incineration of hazardous wastes. Boca Raton: CRC Press, 1991.

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7

Chrystal, Cook S., ed. Hazardous waste incineration and human health. Boca Raton, Fla: CRC Press, 1989.

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8

Theodore, Louis. Introduction to hazardous waste incineration. New York: Wiley, 1987.

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9

Agency, Illinois Environmental Protection. The Illinois mobile incineration program. Springfield, Ill: Illinois Environmental Protection Agency, Office of Government & Community Affairs, 1988.

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10

Agency, Illinois Environmental Protection. The Illinois mobile incineration program. Springfield, Ill: Illinois Environmental Protection Agency, Office of Government & Community Affairs, 1987.

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Book chapters on the topic "Hazardous wastes Victoria Incineration"

1

Gannon, T., A. R. Ansbro, and R. P. Burns. "Incineration of Hazardous Wastes." In Fourth Symposium on our Environment, 105–25. Dordrecht: Springer Netherlands, 1991. http://dx.doi.org/10.1007/978-94-011-2664-9_11.

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2

Huguenin, Michael T., and Jeffrey A. Kolb. "Comparison of Risks from Ocean-Based and Land-Based Incineration of Hazardous Wastes." In New Risks: Issues and Management, 693–700. Boston, MA: Springer US, 1990. http://dx.doi.org/10.1007/978-1-4899-0759-2_74.

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3

"Incineration of Hazardous Wastes." In Waste Management Practices, 471–504. CRC Press, 2005. http://dx.doi.org/10.1201/9781420037517.ch15.

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4

"Incineration of Hazardous Wastes." In Waste Management Practices, 451–78. CRC Press, 2014. http://dx.doi.org/10.1201/b16576-19.

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"Incineration of Hazardous Wastes." In Waste Management Practices, 505–32. CRC Press, 2005. http://dx.doi.org/10.1201/9781420037517-19.

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6

"Incineration Systems for Hazardous Wastes." In Combustion and Incineration Processes, 479–510. CRC Press, 2010. http://dx.doi.org/10.1201/ebk1439805039-17.

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"Incineration Systems for Hazardous Wastes." In Combustion and Incineration Processes, 449–79. CRC Press, 2010. http://dx.doi.org/10.1201/ebk1439805039-c11.

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"Incineration Systems for Hazardous Wastes." In Combustion and Incineration Processes. CRC Press, 2002. http://dx.doi.org/10.1201/9780203908365.ch11.

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9

Shammas, Nazih, and Lawrence Wang. "Incineration and Combustion of Hazardous Wastes." In Advances in Industrial and Hazardous Wastes Treatment, 955–84. CRC Press, 2009. http://dx.doi.org/10.1201/9781420072228-c23.

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10

Tillman, David A., Amadeo J. Rossi, and Katherine M. Vick. "PERMANENT SOLID HAZARDOUS WASTE INCINERATION SYSTEMS." In Incineration of Municipal and Hazardous Solid Wastes, 201–43. Elsevier, 1989. http://dx.doi.org/10.1016/b978-0-12-691245-6.50010-9.

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Conference papers on the topic "Hazardous wastes Victoria Incineration"

1

Cassidy, Helen. "Oil Immobilization Program at Sellafield: An Innovative Approach." In The 11th International Conference on Environmental Remediation and Radioactive Waste Management. ASMEDC, 2007. http://dx.doi.org/10.1115/icem2007-7065.

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Non-standard wastes — those defined as being both hazardous waste under the United Kingdom Hazardous Waste Regulations 2005 [1] and radioactive under the Radioactive Substances Act 1993 [2] — pose particular, unique challenges for radioactive waste management organizations [3]. Treatment and disposal routes for such wastes are limited, in some cases non existent, and generally not cost effective. A non-standard waste of particular concern in the United Kingdom, and indeed on the Sellafield site, is that of radiologically contaminated waste oil. The optioning process for treatment of bulk contaminated waste oil on the Sellafield site has assessed a range of options including incineration, chemical decontamination, physical decontamination and immobilization. Immobilization has proved to be a potentially useful option for oil wastestreams that fail to meet waste acceptance criteria for incineration facilities. Experimental development work has been undertaken at Sellafield during 2006 to test the suitability of an innovative technology for the solidification of waste oil with a cross section of wastestreams from the site. These trials have demonstrated that this polymer system is able to successfully immobilize a range of aged, chemically and physically diverse contaminated oil wastestreams and thus provide a potential solution to the disposal problem posed by this wastestream.

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2

Deckers, Jan, Rik Vanbrabant, Ronald Womack, and Mark Shuey. "Plasma Treatment of Problematic Waste." In ASME 2001 8th International Conference on Radioactive Waste Management and Environmental Remediation. American Society of Mechanical Engineers, 2001. http://dx.doi.org/10.1115/icem2001-1234.

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Abstract Worldwide a great deal of the low and medium radioactive waste inventory is mixed with hazardous wastes and different non-combustibles. The path to treating these wastes historically has been to sort combustibles from non-combustibles and process them separately through incineration, supercompaction, cementation or other encapsulating technologies. Special attention has to be taken due to the presence of hazardous constituents. The cost and health physics exposure for sorting these types of mixed wastes and treating the separated streams in specialized infrastructure is not optimal and leaves a great potential for further optimization. After several years of development, a commercially available high temperature treatment system has been developed and installed that treats heterogeneous low-level radioactive waste. High temperature plasma processing and unique torch design and operating features make it feasible to achieve a volume reduced, permanent, high integrity waste form while eliminating the personnel exposure and cost associated with sorting, characterizing and handling. Plasma technology can also be used to recondition previous conditioned waste packages that don’t meet any longer the present acceptance criteria for final disposal. Plasma treatment can result in many cases in a substantial volume reduction, lowering the final disposal costs. This paper covers the unique plasma centrifugal treatment principles and history. It also explains the roles of international partners that blend plasma, off gas treatment and nuclear expertise into one “best developed and available technology” (BDAT) for the treatment of problematic wastes.

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3

Robertson, Daniel, Stephen Burnley, and Rod Barratt. "The Immobilisation of Flue Gas Treatment Residues Through the Use of a Single Staged Wash and Crystalline Matrix Encapsulation (CME) Treatment Process." In 11th North American Waste-to-Energy Conference. ASMEDC, 2003. http://dx.doi.org/10.1115/nawtec11-1679.

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All incineration and other thermal treatment technologies produce flue gas treatment residues (FGTR) that require specialised treatment and disposal. In the United Kingdom the FGTR arising from municipal solid waste incineration is classified as a hazardous (special) waste. This is primarily due to the irritant properties of chloride, but also due to the content of heavy metals. These wastes must be handled, transported & disposed of in accordance with the Special Waste Regulations 1996 and are disposed into highly engineered landfill sites, which isolate the material from the environment. The low levels of trace elements in the FGTR mean that the recycling of the metallic elements is not economic. Control through stabilisation and encapsulation in a crystalline matrix converts the FGTR primary form from a powder into solid block form. The use of a novel metal matrix encapsulation (MME) process allows low level engineering processes to be employed, increasing a range of reuse options combined with long-term improved storage.

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4

Farrell, Paul, and Philip R. LeGoy. "Using Plasma Pyrolysis Vitrification (PPV) to Enhance Incineration Waste Ash Reduction in Ireland." In 10th Annual North American Waste-to-Energy Conference. ASMEDC, 2002. http://dx.doi.org/10.1115/nawtec10-1028.

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Ireland has been called the Silicon Valley of Europe. Like the Silicon Valley in the U.S. it has a large amount of waste created by the Microchip Industry. Ireland is also an agricultural country. A large amount of bio-waste has been stockpiled in Ireland. This is the result of recent outbreaks/epidemics of animal diseases in the EU. The current growth industry of Ireland is the chemical and pharmaceutical manufacturing industry. Nine of the top ten pharmaceutical companies are manufacturing in Ireland. Wastes from these industries are often toxic and hazardous. They can contain large amounts of combustible organic compounds depending on their source. Since Ireland is an island it has special problems disposing of waste. Waste comes in as products as packaging and it doesn’t go out. The emerging solution is Incineration. Municipal Solid Waste (MSW) can contain many forms of metal and chemistry under normal conditions. When a large amount of the primary industry of a region is chemistry based and agricultural based there is the probability of more than usual amount of toxic residue in the refuse. The ash from incineration contains items such as dioxins & heavy metals that are environmental toxins. Using a Plasma Pyrolysis Vitrification (PPV) process the volume of the resultant ash from incineration can be further reduced by as much as 30 to 1. A PPV process has an added advantage of giving an incineration facility the capability of rendering ash safe for reuse as construction material and as a side benefit reclaiming many valuable elemental components of the ash. The PPV plant can be used to destroy waste directly and economically as long as the gate fees are high. One byproduct of incinerator ash smelting/destruction using a PPV process is CO gas, a combustible fuel resource for power generation. Precious metals may also be reclaimed as an alloy material by-product.

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El Achkar, Jean H., Abrar Ben Husain, Nadeen Alotaibi, Noor Alhaddad, Taiyeba Alamgir, Husain Alshamali, Yousef Alshammari, et al. "Could Petroleum Sludge be Used to Produce Biomethane as a Renewable Energy Source?" In ADIPEC. SPE, 2022. http://dx.doi.org/10.2118/210953-ms.

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Abstract During the exploration, production, and refining of crude oil, as well as the effluent treatment facilities of refineries, the petroleum sector produces a substantial quantity of sludge. This review offers in-depth insights into the methods used to treat and dispose of petroleum sludge today. It also explores the possibility of valorizing such waste while converting it to a sustainable energy source using anaerobic digestion technology. Aside from health concerns, the random disposal of untreated petroleum sludge causes land pollution, water pollution, and ecosystem devastation. Consequently, the adequate treatment and disposal of this sludge provide a substantial challenge to the oil and gas sector, which has become a worldwide concern. Various methods used, such as incineration, oxidation, ultrasounds, stabilization, and landfarming will be presented. On another note, this review imparts a new insight into the possibility of generating biomethane from petroleum sludge. It also investigates its anaerobic co-digestion with food waste and other byproducts, promoting the transition toward a circular bioeconomy. Most conventional sludge treatment methods are unstainable and insufficient to deal with a large amount of generated sludge. Ultrasonic treatment, solvent extraction, and incineration are all expensive processes. Moreover, incineration contributes to air pollution, whereas landfarming and degradation are inefficient and contribute to heavy metals leaching. Considering those disadvantages, creating a greener and more cost-effective approach to securely disposing of these hazardous materials is vital. The bacterial degradation of any substrate without oxygen is known as anaerobic digestion (AD). It is one of the highly efficient systems for recovering bioenergy from small to large sizes. Sludge treatment in anaerobic digesters yields biomethane, a substitute for natural gas, recovered while microorganisms reduce the organic matter in the sludges. However, the sludges have poor anaerobic degradability, and the presence of heavy metals might interfere with anaerobic microorganisms' ability to function. Suitable pretreatment of sludge and its co-digestion with organic wastes such as food waste can be an option to solve the above problems, tackling at the same time the food waste management issues alongside petroleum sludge management.

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