Publications
260 results found
Donatello S, Freeman-Pask A, Tyrer M, et al., 2010, Effect of milling and acid washing on the pozzolanic activity of incinerator sewage sludge ash, CEMENT & CONCRETE COMPOSITES, Vol: 32, Pages: 54-61, ISSN: 0958-9465
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- Citations: 96
Rani DA, Roether JA, Deegan DE, et al., 2010, CASTABLE GLASS AND GLASS-CERAMICS FROM DC PLASMA TREATMENT OF AIR POLLUTION CONTROL RESIDUES, 8th Pacific Rim Conference on Ceramic and Glass Technology, Publisher: AMER CERAMIC SOC, Pages: 11-+, ISSN: 1042-1122
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- Citations: 1
Kourti I, Rani DA, Deegan D, et al., 2010, DEVELOPMENT OF GEOPOLYMERS FROM PLASMA VITRIFIED AIR POLLUTION CONTROL RESIDUES FROM ENERGY FROM WASTE PLANTS, 8th Pacific Rim Conference on Ceramic and Glass Technology, Publisher: AMER CERAMIC SOC, Pages: 297-+, ISSN: 1042-1122
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- Citations: 1
Chiang K-Y, Chou P-H, Hua C-R, et al., 2009, Lightweight bricks manufactured from water treatment sludge and rice husks, JOURNAL OF HAZARDOUS MATERIALS, Vol: 171, Pages: 76-82, ISSN: 0304-3894
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- Citations: 154
Tudor TL, Townend WK, Cheeseman CR, et al., 2009, An overview of arisings and large-scale treatment technologies for healthcare waste in the United Kingdom, WASTE MANAGEMENT & RESEARCH, Vol: 27, Pages: 374-383, ISSN: 0734-242X
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- Citations: 18
Townend WK, Cheeseman C, Edgar J, et al., 2009, Factors driving the development of healthcare waste management in the United Kingdom over the past 60 years, WASTE MANAGEMENT & RESEARCH, Vol: 27, Pages: 362-373, ISSN: 0734-242X
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- Citations: 11
Donatello S, Tyrer M, Cheeseman CR, 2009, Recent developments in macro-defect-free (MDF) cements, CONSTRUCTION AND BUILDING MATERIALS, Vol: 23, Pages: 1761-1767, ISSN: 0950-0618
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- Citations: 34
Lampris C, Stegemann JA, Cheeseman CR, 2009, Solidification/stabilisation of air pollution control residues using Portland cement: Physical properties and chloride leaching, WASTE MANAGEMENT, Vol: 29, Pages: 1067-1075, ISSN: 0956-053X
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- Citations: 28
Rani DA, Roether JA, Gomez E, et al., 2009, Glass-ceramics from plasma treated air pollution control (APC) residues, GLASS TECHNOLOGY-EUROPEAN JOURNAL OF GLASS SCIENCE AND TECHNOLOGY PART A, Vol: 50, Pages: 57-61, ISSN: 1753-3546
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- Citations: 3
Qiao XC, Cheeseman CR, Poon CS, 2009, Influences of chemical activators on incinerator bottom ash, WASTE MANAGEMENT, Vol: 29, Pages: 544-549, ISSN: 0956-053X
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- Citations: 19
Velis CA, Wilson DC, Cheeseman CR, 2009, 19th century London dust-yards: A case study in closed-loop resource efficiency, Waste Management, Vol: 29, Pages: 1282-1290, ISSN: 0956-053X
The material recovery methods used by dust-yards in early 19th century London, England and the conditions that led to their development, success and decline are reported. The overall system developed in response to the market value of constituents of municipal waste, and particularly the high coal ash content of household ‘dust’. The emergence of lucrative markets for ‘soil’ and ‘breeze’ products encouraged dust-contractors to recover effectively 100% of the residual wastes remaining after readily saleable items and materials had been removed by the thriving informal sector. Contracting dust collection to the private sector allowed parishes to keep the streets relatively clean, without the need to develop institutional capacity, and for a period this also generated useful income. The dust-yard system is, therefore, an early example of organised, municipal-wide solid waste management, and also of public–private sector participation. The dust-yard system had been working successfully for more than 50 years before the Public Health Acts of 1848 and 1875, and was thus important in facilitating a relatively smooth transition to an institutionalised, municipally-run solid waste management system in England. The dust-yards can be seen as early precursors of modern materials recycling facilities (MRFs) and mechanical–biological treatment (MBT) plants; however, it must be emphasised that dust-yards operated without any of the environmental and occupational health considerations that are indispensable today. In addition, there are analogies between dust-yards and informal sector recycling systems currently operating in many developing countries.
Lampris C, Lupo R, Cheeseman CR, 2009, Geopolymerisation of silt generated from construction and demolition waste washing plants, WASTE MANAGEMENT, Vol: 29, Pages: 368-373, ISSN: 0956-053X
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- Citations: 69
Bou E, Quereda MF, Lever D, et al., 2009, Production of pulverised fuel ash tiles using conventional ceramic production processes, ADVANCES IN APPLIED CERAMICS, Vol: 108, Pages: 44-49, ISSN: 1743-6753
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- Citations: 11
Velis CA, Wilson DC, Cheeseman CR, 2009, 19th century London dust-yards: A case study in closed-loop resource efficiency, Waste Management, Pages: 1282-1290
The material recovery methods used by dust-yards in early 19th century London, England and the conditions that led to their development, success and decline are reported. The overall system developed in response to the market value of constituents of municipal waste, and particularly the high coal ash contentof household ‘dust’. The emergence of lucrative markets for ‘soil’ and ‘breeze’ products encouraged dust-contractors to recover effectively 100% of the residual wastes remaining after readily saleable itemsand materials had been removed by the thriving informal sector. Contracting dust collection to the private sector allowed parishes to keep the streets relatively clean, without the need to develop institutional capacity, and for a period this also generated useful income. The dust-yard system is, therefore, an early example of organised, municipal-wide solid waste management, and also of public–private sector participation. The dust-yard system had been working successfully for more than 50 years before the Public Health Acts of 1848 and 1875, and was thus important in facilitating a relatively smooth transition to an institutionalised, municipally-run solid waste management system in England. The dust-yards canbe seen as early precursors of modern materials recycling facilities (MRFs) and mechanical–biological treatment (MBT) plants; however, it must be emphasised that dust-yards operated without any of the environmental and occupational health considerations that are indispensable today. In addition, thereare analogies between dust-yards and informal sector recycling systems currently operating in many developing countries.
Amutha Rani D, Boccaccini AR, Deegan DE, et al., 2009, Glass-ceramic tiles prepared by pressing and sintering dc plasma vitrified air pollution control residues, International Journal of Applied Ceramic Technology
Lampris C, Stegemann JA, Cheeseman CR, 2008, Chloride leaching from air pollution control residues solidified using ground granulated blast furnace slag, CHEMOSPHERE, Vol: 73, Pages: 1544-1549, ISSN: 0045-6535
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- Citations: 12
Little MR, Adell V, Boccaccini AR, et al., 2008, Production of novel ceramic materials from coal fly ash and metal finishing wastes, RESOURCES CONSERVATION AND RECYCLING, Vol: 52, Pages: 1329-1335, ISSN: 0921-3449
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- Citations: 59
Wilson DC, Araba AO, Chinwah K, et al., 2008, Building recycling rates through the informal sector, Proceedings of the Eleventh International Waste Management and Landfill Symposium.
Qiao XC, Tyrer M, Poon CS, et al., 2008, Novel cementitious materials produced from incinerator bottom ash., Resources Conservation and Recycling
Amutha Rani D, Gomez E, Boccaccini AR, et al., 2008, Plasma treatment of air pollution control residues., Waste Management
Imam A, Mohammed B, Wilson DC, et al., 2008, Solid waste management in Abuja, Nigeria, 30th Annual Meeting of the Society-of-General-Internal-Medicine, Pages: 468-472
The new city of Abuja provided an opportunity to avoid some of the environmental problems associated with other major cities in Africa. The current status of solid waste management in Abuja has been reviewed and recommendations for improvements are made. The existing solid waste management system is affected by unfavourable economic, institutional, legislative, technical and operational constraints. A reliable waste collection service is needed and waste collection vehicles need to be appropriate to local conditions. More vehicles are required to cope with increasing waste generation. Wastes need to be sorted at source as much as possible, to reduce the amount requiring disposal. Co-operation among communities, the informal sector, the formal waste collectors and the authorities is necessary if recycling rates are to increase. Markets for recycled materials need to be encouraged. Despite recent improvements in the operation of the existing dumpsite, a properly sited engineered landfill should be constructed with operation contracted to the private sector. Wastes dumped along roads, underneath bridges, in culverts and in drainage channels need to be cleared. Small-scale waste composting plants could promote employment, income generation and poverty alleviation. Enforcement of waste management legislation and a proper policy and planning framework for waste management are required. Unauthorized use of land must be controlled by enforcing relevant clauses in development guidelines. Accurate population data is necessary so that waste management systems and infrastructure can be properly planned. Funding and affordability remain major constraints and challenges. (C) 2007 Elsevier Ltd. All rights reserved.
Imam A, Mohammed B, Wilson DC, et al., 2008, Solid waste management in Abuja, Nijeria, Waste Management, Vol: 28, Pages: 468-472
Gomez E, Amutha Rani D, Cheeseman CR, et al., 2008, Thermal plasma technology for the treatment of wastes: A critical review, Journal of Hazardous Materials, ISSN: 0304-3894
Adell V, Cheeseman CR, Doel A, et al., 2008, Comparison of rapid and slow sintered pulverised fuel ash, Fuel, Vol: 87, Pages: 187-195
Lupo R, Tyrer M, Cheeseman CR, et al., 2007, Manufactured aggregate from waste materials, Sustainable construction materials and technologies
Vlasopoulos N, Cheeseman CR, 2007, Use of Magnesium Oxide-Cement binders for the production of blocks with lightweight aggregates., Sustainable construction materials and technologies
Qiao XC, Tyrer M, Poon CS, et al., 2007, Charcterisation of alkali-activated thermally treated incinerator bottom ash, Waste Management
Bouzalakos S, Dudeney AWL, Cheeseman CR, 2007, Controlled low-strength materials containing waste precipitates from mineral processing, Minerals Engineering
Uwe EA, Boccaccini AR, Cook SG, et al., 2007, Effect of borate addition on the sintered properties of pulverised fuel ash, AshTech 2006., International Conference on Coal Fired Power Station Ash
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