Relevant bibliographies by topics / Municipal solid waste incinerator residues

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  1. Journal articles
  2. Dissertations / Theses
  3. Books
  4. Book chapters
  5. Conference papers

Academic literature on the topic 'Municipal solid waste incinerator residues'

Author: Grafiati
Published: 4 June 2021
Last updated: 30 January 2023

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Journal articles on the topic "Municipal solid waste incinerator residues"

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Shaub, Walter M. "Municipal solid waste incinerator residues." Resources, Conservation and Recycling 20, no. 4 (1997): 295–96. http://dx.doi.org/10.1016/s0921-3449(97)00026-8.

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VAITKUS, Audrius, Judita GRAŽULYTĖ, Viktoras VOROBJOVAS, Ovidijus ŠERNAS, and Rita KLEIZIENĖ. "POTENTIAL OF MSWI BOTTOM ASH TO BE USED AS AGGREGATE IN ROAD BUILDING MATERIALS." Baltic Journal of Road and Bridge Engineering 13, no. 1 (2018): 77–86. http://dx.doi.org/10.3846/bjrbe.2018.401.

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In the European Union, more than 140 million tonnes of municipal solid waste is incinerated annually. It generates about 30–40 million tonnes of residues known as municipal solid waste incinerator bottom ash, which is typically landfilled. To deal with growing landfills, there is a need to utilize municipal solid waste incinerator bottom ash as a building material. It has been known that municipal solid waste incinerator bottom ash properties strongly depend on waste composition, which is directly influenced by people’s habits, economic policy, and technologies for metals recovery of bottom ash. Thus, municipal solid waste incinerator bottom ash produced in a specific country or region has primarily to be tested to determine its physical and mechanical properties. The main aim of this study is to determine municipal solid waste incinerator bottom ash physical and mechanical properties (aggregate particle size distribution, water content, oven-dried particle density, loose bulk density, Proctor density, optimal water content, California Bearing Ratio after and before soaking, permeability, Flakiness Index, Shape Index, percentage of crushed and broken surfaces, resistance to fragmentation (Los Angeles coefficient), water absorption and resistance to freezing and thawing). Municipal solid waste in-cinerator bottom ash produced in the waste-to-energy plant in Klaipėda (Lithuania) was used in this research. Ferrous and non-ferrous metals were separated after more than three months of municipal solid waste incinerator bottom ash ageing in the atmosphere. The study showed promising results from considering municipal solid waste incinerator bottom ash as possible aggregates for road building materials.
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Li, Min, Jun Xiang, Song Hu, et al. "Characterization of solid residues from municipal solid waste incinerator." Fuel 83, no. 10 (2004): 1397–405. http://dx.doi.org/10.1016/j.fuel.2004.01.005.

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Huang, Yucheng, Ji Chen, Shenjie Shi, Bin Li, Jialin Mo, and Qiang Tang. "Mechanical Properties of Municipal Solid Waste Incinerator (MSWI) Bottom Ash as Alternatives of Subgrade Materials." Advances in Civil Engineering 2020 (January 30, 2020): 1–11. http://dx.doi.org/10.1155/2020/9254516.

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The rapid development of industrialization, urbanization, and population of the society augments the rising amount of municipal solid waste (MSW). With the advantage of considerably reducing mass and volume of solid wastes and generating energy, the incineration is a widely used treatment method for MSW. During the incineration process, the organic substances contained in the wastes are combusted, and the massive residues are remained. Of the incineration residues, bottom ash takes up to 80–90%, and the remainders are fly ash along with air pollution control residues. Dealing with the municipal solid waste incineration (MSWI) bottom ash in a sustainable manner is the primary principle. Significantly, MSWI bottom ash has been successfully utilized in diverse beneficial applications in recent decades, especially in civil engineering applications. This paper investigates the mechanical properties and validity of MSWI bottom ash as applicable substitutes of conventional subgrade materials. For this reason, a series of direct shear and CBR tests are performed on specimens with different water contents and dry densities.
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Redin, L. Aae, M. Hjelt, and S. Marklund. "Co-combustion of shredder residues and municipal solid waste in a Swedish municipal solid waste incinerator." Waste Management & Research 19, no. 6 (2001): 518–25. http://dx.doi.org/10.1177/0734242x0101900607.

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Ferrari, Stefano, Hasan Belevi, and Peter Baccini. "Chemical speciation of carbon in municipal solid waste incinerator residues." Waste Management 22, no. 3 (2002): 303–14. http://dx.doi.org/10.1016/s0956-053x(01)00049-6.

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Guarienti, Michela, Alessandra Gianoncelli, Elza Bontempi, et al. "Biosafe inertization of municipal solid waste incinerator residues by COSMOS technology." Journal of Hazardous Materials 279 (August 2014): 311–21. http://dx.doi.org/10.1016/j.jhazmat.2014.07.017.

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Bridle, T. R., P. L. Côté, T. W. Constable, and J. L. Fraser. "Evaluation of Heavy Metal Leachability from Solid Wastes." Water Science and Technology 19, no. 5-6 (1987): 1029–36. http://dx.doi.org/10.2166/wst.1987.0280.

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Future management options for residual inorganic solid wastes are likely to include land disposal. While the environmental ramifications of this option are now better understood, additional data is required to permit a thorough assessment of contaminant leachability from solid wastes. As part of this data gathering exercise, Environment Canada's Wastewater Technology Centre has been actively researching and developing test methods designed to measure intrinsic waste properties that affect contaminant leachability, such as metal solubilities and speciation. Based on this approach the leachability of heavy metals from sewage sludge, char and ash, municipal solid waste ashes, hazardous waste incinerator fly ashes, power plant ashes and a solidified synthetic waste were assessed. The results indicate that incineration of sewage sludge produces a benign ash with most of the metals speciated as insoluble oxides or silicates. By contrast, incineration of municipal solid waste or hazardous wastes produces fly ashes exhibiting significant metal leachability. Environmentally sensitive metals such as Cd, Zn, Ni and Cu in these fly ashes were readily leachable and probably speciated as water soluble chloride salts. The intrinsic properties approach appears to be an effective method of assessing waste leachability.
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Sabbas, T., A. Polettini, R. Pomi, et al. "Management of municipal solid waste incineration residues." Waste Management 23, no. 1 (2003): 61–88. http://dx.doi.org/10.1016/s0956-053x(02)00161-7.

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Sakai, Shin-ichi, and Masakatsu Hiraoka. "Municipal solid waste incinerator residue recycling by thermal processes." Waste Management 20, no. 2-3 (2000): 249–58. http://dx.doi.org/10.1016/s0956-053x(99)00315-3.

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Dissertations / Theses on the topic "Municipal solid waste incinerator residues"

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Li, Xiaomin. "Accelerated carbonation of municipal solid waste incineration residues." Thesis, University of Greenwich, 2008. http://gala.gre.ac.uk/8399/.

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Incineration can reduce the mass and volume of municipal waste significantly but produces solid waste in the form of bottom ash and air pollution control (APC) residues. Landfill is currently the most commonly used disposal option for these ash residues, however, the impact of hazardous compounds in these wastes on the environment during landfilling is becoming more widely appreciated and cheaper, alternative, management options need to be explored. In this research, the treatment of these municipal solid waste incinerator (MSWI) residues by accelerated carbonation is investigated and compared with naturally aged ashes. Both bottom ash and APC residues were carbonated in an atmosphere composed of gaseous CO2. It was found that the carbonation of calcium oxides/hydroxides resulted in the rapid formation of calcium carbonate and that silicate compounds were hydrated. The reduction of pH from 12-12.5 to 7-9 observed upon carbonation was associated with a reduction in availability of soluble salts and meals. Carbonated ash had a higher buffering capacity to acid attack when compared to the untreated, non-carbonated, ash. The bottom and APC ashes sequestrated between 6% and 13% CO2 (w/w dry weight), respectively upon carbonation; and this may be important where the reduction of greenhouse emissions to the atmosphere is concerned.
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Xiong, Yiqun. "Study on behavior of heavy metals in semi-aerobic landfill sites of municipal solid waste incinerator residues." Kyoto University, 2020. http://hdl.handle.net/2433/253263.

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Lampris, Christos. "Solidification/stabilisation of air pollution control residues from municipal solid waste incineration." Thesis, Imperial College London, 2013. http://hdl.handle.net/10044/1/18973.

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Air pollution control (APC) residues are by-products of the flue gas cleaning process in energy-from-waste (EfW) plants treating municipal solid waste. They are classified as a hazardous waste in the EU Waste Catalogue and are a priority hazardous waste stream in the UK due to high alkalinity, concentrations of volatile heavy metals and soluble salts. Plans currently exist to increase the number of EfW plants in the UK, with the potential to increase future arisings of APC residues. Stabilisation/solidification (S/S) is an inexpensive treatment technology, involving mixing of the waste with cementitious binders. The main objective of this research is to assess the effectiveness of CEM I and ground granulated blast furnace slag (GGBS) as S/S binders for the treatment of APC residues. The ultimate goal is to expand existing knowledge on S/S systems and assist development of more sustainable treatment methods for APC residues. S/S APC residue specimens were prepared varying the waste-to-binder and water-to-solids ratios and subsequently tested for physical properties and contaminant leaching according to international standards. Geochemical modelling was used to assess contaminant release-controlling processes and contribute to more efficient mix and treatment design. Results from this study indicate that mechanical properties of 50 wt.% CEM I and GGBS mixes exceed UK landfill disposal criteria (1.0 MPa), achieving unconfined compressive strength (UCS) values of up to 21 MPa. CEM I mixes with 10 and 20 wt.% binder addition also met the criterion of 1.0 MPa, achieving UCS values of up to 10 MPa. In contrast, 10 and 20 wt.% GGBS mixes exhibited inferior mechanical properties (UCS < 1.0 MPa). S/S is hampered predominantly by high concentrations of chloride in APC residues. All monolithic S/S samples exceeded relevant UK waste acceptance criteria (monWAC) for chloride (20,000 mg/m2) within the first two days of the 64-day monolithic leaching test. Altough partial immobilisation occurs through the formation of chloro-complexes, S/S of APC residues would require binder additions greater than 50 wt.% to meet UK requirements for landfill disposal. Leaching of Pb also becomes problematic for mixes with 10 and 20 wt.% binder addition, exceeding UK monWAC (20 mg/m2). Nevetheless, the amphoteric nature of heavy metals and the high solubility of chloride salts could favour extraction of potentially valuable elements through washing procedures. Modelling results indicate that a simple washing step may be able to extract 650 mg of Pb and 120 mg of Zn per kg of APC residues treated, while removing approximately 90% of available chloride.
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Maldonado, Alameda Alex. "Alkali-activated binders based on municipal solid waste incineration bottom ash." Doctoral thesis, Universitat de Barcelona, 2021. http://hdl.handle.net/10803/672107.

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Municipal solid waste incineration (MSWI) is the most widely used solution in those countries where landfilling areas are limited. Incineration allows reducing the total volume of waste (up to 90%) and generating energy resulting from combustion. The main by-product generated in waste-to-energy plants is known as incineration bottom ash (IBA), which is a heterogeneous mixture of ferrous and non-ferrous metals, ceramics, and glass. IBA is classified as a non- hazardous material due to its composition rich in calcium oxide, silica, and iron. IBA composition and morphology are very similar to natural siliceous aggregates after an ageing treatment where the weathered bottom ash (WBA) is obtained. This maturation process makes feasible the WBA valorisation as a secondary aggregate in the field of construction and civil engineering. Moreover, the high percentage of glass and aluminium found in the WBA would allow its valorisation as a precursor in the alkali-activated binders (AABs) formulation. The main goal of this PhD thesis was the scientific and technological development of new AABs based on the alkali activation of WBA (AA-WBA binders), to reduce the use of ordinary Portland cement (OPC) in building and civil engineering fields. In this sense, this aim is related to the use of more sustainable cement-based materials, which promote the circular economy and zero-waste principle through the valorisation of WBA. The potential of WBA as a precursor in the AA-WBA binders’ formulation was evaluated along with the PhD thesis through different studies that can be classified into four blocks. The first block was based on the evaluation of the WBA potential as a precursor in AABs based on its particle size. This study demonstrated the variability in the reactive SiO2 and Al2O3 availability as a function of the particle size. The potential of the entire fraction (EF) and the 8-30-mm fraction highlighted the possible use of them as precursors in the AABs formulation. The second block of this thesis was focused on the study of AA-WBA binders using the WBA as a sole precursor. Mixtures of sodium silicate (WG) and NaOH (2M, 4M, 6M, and 8M) were used as alkaline activator solutions to assess the effect of the NaOH concentration on the final properties. It was demonstrated the possibility of developing AA-WBA. The influence of alkaline activator solution concentration on the final properties of the AA-WBA was evidenced, obtaining better mechanical performance with the use of the WG/NaOH 6M solution. The results revealed the enhancement in the mechanical properties when the 8-30-mm fraction was used. However, the environmental results revealed arsenic and antimony leaching values that require further research to validate the environmental feasibility of AA-WBA. In the third block, the 8-30-mm fraction was mixed with other precursors with greater availability of Al2O3 (metakaolin and PAVAL®). The main purpose was to improve the mechanical properties and the heavy metal stabilisation effect of the AA- WBA obtained in the second block. In both cases, mechanical performance was improved due to the inclusion of Al2O3. However, the environmental properties continued to show leaching values that did not ensure the environmental viability of the AA-WBA binders. Finally, the fourth block of the thesis was focused on carrying out an environmental and ecotoxicological assessment to validate the use of AA-WBA binders as construction material. The results showed a medium-low level of ecotoxicity in the AA-WBA formulated with the 8-30-mm fraction, similar to the binders activated with MK (AA-MK).<br>El principal subproducte generat durant la incineració de residus sòlids urbans es coneix com a cendra de fons. La seva composició és molt similars als agregats silícics naturals després d’un tractament d’envelliment on s’obté la cendra de fons madurada (weathered bottom ash; WBA segons les sigles angleses). El seu alt contingut en vidre i alumini el converteixen en un potencial candidat com a precursor en la fabricació d’aglutinants activats alcalinament (alkali-activated binders, AABs segons les sigles angleses). L’objectiu principal d’aquesta tesi doctoral va consistir en el desenvolupament de AABs mitjançant l’activació alcalina de WBA (aglutinants AA-WBA). El potencial de la WBA i els aglutinants AA-WBA es va avaluar mitjançant diferents estudis que es poden classificar en quatre blocs. Al primer bloc es va avaluar el potencial de WBA com a precursor en funció de la seva mida de partícula. Aquest estudi va demostrar el potencial de la fracció sencera i de la fracció 8-30 mm. El segon bloc es va centrar en l’estudi d’aglutinants AA-WBA que utilitzaven el WBA com a únic precursor. Es va evidenciar la influència de la concentració de la solució activadora alcalina en les propietats finals dels aglutinants AA-WBA. Els resultats van revelar la millora de les propietats mecàniques quan es va utilitzar la fracció 8-30 mm. No obstant, els resultats ambientals van revelar valors de lixiviació d'arsènic i antimoni que requerien la validació a nivell ambiental dels aglutinants. Al tercer bloc, la fracció 8-30 mm es va barrejar amb altres precursors rics en d’Al2O3 (metakaolin i PAVAL®) per millorar les propietats mecàniques i l’estabilització de metalls pesants dels aglutinants obtinguts al segon bloc. En ambdós casos, es va millorar el rendiment mecànic, tot i que les propietats ambientals van continuar mostrant valors de lixiviació que no asseguraven la viabilitat ambiental dels aglutinants AA-WBA. Finalment, al quart bloc es va realitzar una avaluació ambiental i ecotoxicològica per validar l’ús d’aglutinants AA-WBA com a material de construcció. Els resultats van mostrar un nivell mitjà-baix d’ecotoxicitat a l’AA-WBA formulat amb la fracció de 8 a 30 mm, similar als aglutinants activats amb MK (AA-MK).
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Olsson, Susanna. "Environmental assessment of municipal solid waste incinerator bottom ash in road constructions." Licentiate thesis, Stockholm : KTH Land and Water Resource Engineering, 2005. http://urn.kb.se/resolve?urn=urn:nbn:se:kth:diva-435.

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Wasantakorn, Aran. "Efficient power generation by integrating a MSW incinerator with a combined cycle gas turbine plant." Thesis, University of Sheffield, 2001. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.369938.

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Rhea, Lisa R. "Mineral Solubilization from Municipal Solid Waste Combustion Residues: Implications for Landfill Leachate Collection Systems." [Tampa, Fla.] : University of South Florida, 2004. http://purl.fcla.edu/fcla/etd/SFE0000534.

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Wilkes, Timothy. "The treatment of municipal solid waste air pollution control (MSW APC) residues with sodium silicate." Thesis, University of Surrey, 2005. http://epubs.surrey.ac.uk/773426/.

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Waste materials are hazardous if they display toxic, corrosive or other characteristics which have the potential to cause danger to health or the environment. New regulations to meet the requirements of the Landfill Directive contain controls on hazardous waste including the requirement to pre-treat hazardous waste prior to disposal and to ensure these wastes meet stringent waste acceptance criteria (WAC) on leachability. Waste from the cleaning of combustion gases produced from municipal solid waste (MSW) incineration is classed as hazardous by virtue of their corrosive properties. The majority of these air pollution control (APC) residues which contain dioxins, heavy metals and high levels of chloride are currently sent to landfill. To meet the new controls, pretreatment will be required to improve the handling properties and reduce the release of chloride ions into the environment. Ordinary Portland cement (OPC) is used to treat hazardous wastes. The solid form produced with the addition of OPC is however susceptible to degradation from aggressive leaching fluids and may release contaminants over time. Additives with high silica content can be used to interact with free lime produced during OPC hydration to improve the physical and chemical properties of the solid waste form. The treatment of MSW APC residues with sodium silicate and cement produces a solid waste form with a reduced structural integrity and a tendency to breakdown under attack from aggressive fluids. Silica 'gels' are formed during initial setting reactions which 'depolymerise' with fluid ingress to form new calcium rich silica 'gels' within cracks and voids of the solid waste form. Expansion due to water absorption and continual 'gel' formation causes structural failure. The addition of sodium silicate to sludges produced from a current treatment by mixing MSW APC residues with other mixed hazardous waste improves strength development by 'encapsulating' the waste sludge inside a calcium/silica 'gel'. This stops components of the sludge from interfering with normal OPC hydration. The treatment of MSW APC residues with sodium silicate will not produce a solid form to meet the new waste acceptance criteria. However, sodium silicate has the potential to improve handling and structural integrity of the sludge produced from the current treatment process.
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Zhu, Fenfen. "Technological Development of an Effective Recycling System for Fly Ash from Municipal Solid Waste Incinerator to be Raw Material in Cement Industry." 京都大学 (Kyoto University), 2008. http://hdl.handle.net/2433/66206.

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Kyoto University (京都大学)<br>0048<br>新制・課程博士<br>博士(工学)<br>甲第14148号<br>工博第2982号<br>新制||工||1443(附属図書館)<br>26454<br>UT51-2008-N465<br>京都大学大学院工学研究科都市環境工学専攻<br>(主査)教授 津野 洋, 教授 森澤 眞輔, 教授 酒井 伸一<br>学位規則第4条第1項該当
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Cardoso, Antonio J. "Relationship of waste characteristics to the formation of mineral deposits in leachate collection systems." [Tampa, Fla.] : University of South Florida, 2005. http://purl.fcla.edu/fcla/etd/SFE0001266.

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Books on the topic "Municipal solid waste incinerator residues"

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Ujihara, Alyce M. Managing ash from municipal waste incinerators: A report. Center for Risk Management, Resources for the Future, 1989.

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Wiles, Carlton C. Beneficial use and recycling of municipal waste combustion residues: A comprehensive resource document. National Renewable Energy Laboratory, 1999.

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Scott, P. The co-disposal of municipal solid waste incineration residues. Department of the Environment, 1993.

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Scott, P. The co-disposal of municipal solid waste incineration residues. Department of the Environment, 1993.

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Doboku Kenkyūjo (Japan). Zairyō Jiban Kenkyū Gurūpu. Shin Zairyō Chīmu. Toshi gomi shōkyakubai o mochiita tekkin konkurīto zairyō no kaihatsu ni kansuru kyōdō kenkyū hōkokusho. Doboku Kenkyūjo Shin Zairyō Chīmu Kōzōbutsu Manejimento Gijutsu Chīmu, 2002.

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K, O'Connor William, and ASME Research Committee on Industrial and Municipal Wastes. Subcommittee on Ash Vitrification., eds. ASME/U.S. Bureau of Mines investigative program report on vitrification of residue (ash) from municipal waste combustion systems. American Society of Mechanical Engineers, 1994.

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Sawell, S. E. The National Incinerator Testing and Evaluation Program (NITEP): A summary of the characterization and treatment studies on residues from municipal solid waste incineration. Environment Canada, 1993.

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Stieglitz, L. Formation and decomposition of polychlorodibenzodioxins and furans in municipal waste incineration. NTIS, 1988.

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United States. Congress. House. Committee on Energy and Commerce. Subcommittee on Transportation, Tourism, and Hazardous Materials. Municipal incinerator ash: Hearing before the Subcommittee on Transportation, Tourism, and Hazardous Materials of the Committee on Energy and Commerce, House of Representatives, One Hundredth Congress, second session, on H.R. 2517, H.R. 4255, and H.R. 4357 ... April 13, 1988. U.S. G.P.O., 1989.

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Materials, United States Congress House Committee on Energy and Commerce Subcommittee on Transportation and Hazardous. Regulation of municipal solid waste incinerators: Hearing before the Subcommittee on Transportation and Hazardous Materials of the Committee on Energy and Commerce, House of Representatives, One Hundred First Congress, first session, on H.R. 2162 ... May 11, 1989. U.S. G.P.O., 1989.

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Book chapters on the topic "Municipal solid waste incinerator residues"

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Chandler, A. J., T. Eighmy, J. Hartlen, et al. "Treatise on Municipal Solid Waste Incinerator Residues." In Contaminated Soil ’90. Springer Netherlands, 1990. http://dx.doi.org/10.1007/978-94-011-3270-1_305.

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Shimaoka, Takayuki, Teppei Komiya, Fumitake Takahashi, and Hirofumi Nakayama. "Dechlorination of Municipal Solid Waste Incineration Residues for Beneficial Reuse as a Resource for Cement." In Testing and Specification of Recycled Materials for Sustainable Geotechnical Construction. ASTM International, 2011. http://dx.doi.org/10.1520/stp49481t.

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Shimaoka, Takayuki, Teppei Komiya, Fumitake Takahashi, and Hirofumi Nakayama. "Dechlorination of Municipal Solid Waste Incineration Residues for Beneficial Reuse as a Resource for Cement." In Testing and Specification of Recycled Materials for Sustainable Geotechnical Construction. ASTM International, 2011. http://dx.doi.org/10.1520/stp154020120020.

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Cobb, James T., and Kunal Banerjee. "Mathematical Analysis of a Municipal Solid Waste Rotary Incinerator." In Conversion And Utilization Of Waste Materials. Routledge, 2023. http://dx.doi.org/10.1201/9781315140360-18.

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Cobb, James T., C. P. Mangelsdorf, Jean R. Blachere, et al. "High-Strength Portland Cement Concrete Containing Municipal Solid Waste Incinerator Ash." In Clean Energy from Waste and Coal. American Chemical Society, 1992. http://dx.doi.org/10.1021/bk-1992-0515.ch021.

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Zhu, Fenfen, Masaki Takaoka, Chein-Chi Chang, and Lawrence K. Wang. "Chlorides Removal for Recycling Fly Ash from Municipal Solid Waste Incinerator." In Natural Resources and Control Processes. Springer International Publishing, 2016. http://dx.doi.org/10.1007/978-3-319-26800-2_7.

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Huang, Kang, Xiaohui Fan, Min Gan, and Zhiyun Ji. "Use of Municipal Solid Waste Incinerator (MSWI) Fly Ash in Alkali Activated Slag Cement." In The Minerals, Metals & Materials Series. Springer International Publishing, 2019. http://dx.doi.org/10.1007/978-3-030-05749-7_40.

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Ashworth, Danielle C., Gary W. Fuller, Mireille B. Toledano, et al. "Chapter 4 Comparative Assessment of Particulate Air Pollution Exposure from Municipal Solid Waste Incinerator Emissions." In Air Quality. Apple Academic Press Inc., 2016. http://dx.doi.org/10.1201/9781315366074-5.

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Johnson, C. A., T. Lichtensteiger, H. Belevi, and P. Baccini. "The Long-Term Behaviour of Municipal Solid Waste Incinerator Bottom Ash in Monofills: A Potential Problem?" In Soil & Environment. Springer Netherlands, 1993. http://dx.doi.org/10.1007/978-94-011-2018-0_84.

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Gautam, Kapil Kumar, Ravi Kumar Sharma, and Abhishek Sharma. "Effect of Municipal Solid Waste Incinerator Ash and Lime on Strength Characteristics of Black Cotton Soil." In Lecture Notes in Civil Engineering. Springer Singapore, 2021. http://dx.doi.org/10.1007/978-981-15-9554-7_10.

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Conference papers on the topic "Municipal solid waste incinerator residues"

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Scarfato, P., E. Garofalo, B. Coppola, et al. "Development and characterization of PP eco-composites filled with inertized residues from municipal solid waste incinerator." In 9TH INTERNATIONAL CONFERENCE ON “TIMES OF POLYMERS AND COMPOSITES”: From Aerospace to Nanotechnology. Author(s), 2018. http://dx.doi.org/10.1063/1.5045886.

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Guojian Li and Yanjun Hu. "Comparisons of municipal solid waste incineration residues management in China and Europe." In 2010 International Conference on Mechanic Automation and Control Engineering (MACE). IEEE, 2010. http://dx.doi.org/10.1109/mace.2010.5536410.

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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 &amp; 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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Gražulytė, Judita, Audrius Vaitkus, Alfredas Laurinavičius, and Ovidijus Šernas. "Performance of concrete mixtures containing MSWI bottom ash." In 6th International Conference on Road and Rail Infrastructure. University of Zagreb Faculty of Civil Engineering, 2021. http://dx.doi.org/10.5592/co/cetra.2020.1164.

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In the European Union, each inhabitant annually generates about 500 kg of municipal waste. About 30 % of this are incinerated in waste-to-energy plants. It results in approximately 20 million tonnes of residues known as municipal solid waste incinerator (MSWI) bottom ash, which is typically landfilled. To address the continuous growth of landfills and to implement zero waste and circular economy policies, researchers are focusing on possibilities to use MSWI bottom ash in civil engineering instead of landfilling. One of them is to replace natural aggregates in concrete mixtures applicable for roads with MSWI bottom ash. Therefore, the subject of this research is the performance of concrete mixtures containing different amount (0–100%) and fraction (0/5–0/16) of MSWI bottom ash. Four specimens with similar aggregate gradations were designed. Each of them was mixed with two different amount (340 kg/m3 and 300 kg/m3) of cement (CEM I 42.5 R). In total eight different concrete mixtures were tested and analysed. The performance of designed concrete mixtures containing different amount of MSWI bottom ash was evaluated according to density and compressive strength after 28 days. The results showed good MSWI bottom ash performance as a substitute for natural aggregates. The compressive strength after 28 days varied from 21 MPa to 29 MPa depending on the aggregate type and amount of MSWI bottom ash and cement. For concrete mixtures made only of MSWI bottom ash at least 340 kg/m3 of cement is required to achieve compressive strength higher than 20 MPa.
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Bergfeldt, B., M. M. Fisher, T. Lehner, et al. "Large Scale Co-combustion Demonstration of Electrical and Electronic Shredder Residue at the Wuerzburg Municipal Solid Waste Incinerator (MHKW)." In Proceedings of the 2006 IEEE International Symposium on Electronics and the Environment, 2006. IEEE, 2006. http://dx.doi.org/10.1109/isee.2006.1650081.

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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 &amp; 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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Chung-Hsing Wu, Kai-Yuan Yang, and Yu-Lian Chen. "Performance Prediction on Municipal Solid Waste Incinerator In Taiwan." In 2004, Ottawa, Canada August 1 - 4, 2004. American Society of Agricultural and Biological Engineers, 2004. http://dx.doi.org/10.13031/2013.16770.

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Venturini, E., I. Vassura, F. Passarini, et al. "The environmental impact of a municipal solid waste incinerator: 15 years of monitoring." In WASTE MANAGEMENT 2014. WIT Press, 2014. http://dx.doi.org/10.2495/wm140261.

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Badami, Marco, Antonio Mittica, and Alberto Poggio. "MSW Incineration Capacity Evaluations for the Province of Turin (Northern Italy)." In 16th Annual North American Waste-to-Energy Conference. ASMEDC, 2008. http://dx.doi.org/10.1115/nawtec16-1926.

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This paper assesses the incineration capacity requirement of the Province of Turin through a detailed analysis of the mass streams and the properties of residual Municipal Solid Waste (MSW). Historical data series were elaborated to study the trend evolution of household generation and separate collection. Residual MSW material compositions were calculated for each year over an observed period and for planned scenarios. A waste properties model was applied to calculate the residual MSW chemical composition and the LHV. The analysis allows conclusions to be drawn about the design of the planned waste-to-energy plant and to estimate the required size and technology to be used. The results show that the use of grate furnace combustor appears to be more suitable than fluidized bed.
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Voišnienė, Violeta, Olga Kizinievič, Viktor Kizinievič, and Jurgita Malaiškienė. "Production of fired clay brick from municipal solid waste incinerator fly ash." In The 13th international scientific conference “Modern Building Materials, Structures and Techniques”. Vilnius Gediminas Technical University, 2019. http://dx.doi.org/10.3846/mbmst.2019.149.

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This paper is a report on the results of a feasibility study on the immobilization of municipal solid waste incinerator fly ash by producing a fired clay brick. The main purpose of this work was to test the clay used in the manufacture of a fired clay brick that could incorporate municipal solid waste incinerator fly ash. The raw materials, municipal solid waste incinerator fly ash and clay, were mixed together in different proportions (100:0, 97.5:2.5, 95:5 and 92.5:7.5). Clay brick samples were heated to 1000 °C temperatures for 1 h. The fired clay brick specimens were characterised with respect to compressive strength, porosity, linear shrinkage (after drying, after firing) and density. Leaching tests, in accord with the European Union regulation, was done on fired clay brick made with different additions of municipal solid waste incinerator fly ash.
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