Mobile incinerator

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The role of incineration of waste and equipment used for it has changed radically in the recent years. While they were formerly notorious as pollutant spewing technical monsters in the eyes of citizens' groups, nowadays, thermal waste treatment facilities are considered to be the essential pillars of sustainable, forward-looking recycling and raw material sectors.

One benefit of thermal waste treatment facilities is to avoid the yield of methane gas that is a by-product of decay that damages the climate strongly. Another is the production of energy during incineration which helps protection of the environment. Valuable resources will also be conserved by means of separation and exploitation of the recyclables in the waste before incineration.

Trigger of development[edit]

Since 2005, in the European Union, waste can be disposed of, only if it was subject to a treatment before, so that the substances contained in it will become inert, thus to a large extent no more harmful reactions with the environment will occur in the landfill body. The incineration process takes a key role in the waste management by fulfilling this requirement of the Waste Storage Regulation and the Landfill Regulation.

Main purpose[edit]

The main purpose of incineration is to reduce the waste volume and destruction of potentially dangerous substances.

The incineration of waste is classified as an act of exploitation in the Waste Framework Directive adopted in May 2008. The waste that can be used for energy production is subject to the free trade policy and may be moved in the EU trans-boundary. The waste that is to be eliminated entirely, for example hazardous and toxic waste, must be disposed in the vicinity of their origin.

Since the volume of waste is growing continuously, landfilling does not seem to be a long-term solution for waste disposal.

To eliminate this volume, currently, only two approaches remain:

The first approach is waste incineration and the second one, which is probably the best solution, is waste avoidance in addition to re-utilization by means of recycling. That means, the reintroduction of valuable materials into the production cycle. This is possible only if economically feasible and environmentally acceptable methods are available.

Forecast of future developments[edit]

The interest of new design of incinerators and incineration process focus on further improvements in energy efficiency and the further savings of CO2. Engineers are working on several aspects of it, from the optimization of the fuel consumption of the plants, to increasing the efficiency of the equipment. Similarly, they work for better techniques for utilization of rest materials and utilization of slag and flying ash. Today more than 80 percent of slag and flying ash are already being used, mainly in earth filling or in road construction.

Role of mobile incineration in the cycle of waste management[edit]

Mobile incinerators provide a useful addition to the available standards in waste management.

The elimination of hazardous and toxic waste on site is one of the major uses of mobile incinerators.

A mobile incinerator unit is the most suitable product for countries that are starting to tackle waste management, because in such cases, there are no previous statistics about the amount of waste and its composition. Therefore all initial data is based on assumptions only. Until more accurate data can be collected, mobile incinerator units help make the transition, with their mobility and flexibility.

Description of mobile incinerators[edit]

A mobile incinerator is an incineration system mounted on a semi-trailer. Modern incinerators enable complete and sterile incineration of waste. They can be operated virtually anywhere.

A modern mobile incinerator unit (MIU) is capable of incinerating waste at a temperature of up to 1,200 °C (2,192 °F). This means, it is designed to incinerate all kinds of waste as well as infected hazardous waste. This satisfies the requirement that, waste of hospitals and health facilities must be burnt at a minimum temperature of 1,100 °C (2,012 °F) acc. to the rules of environmental protection. It can also be used to dispose of household waste, as a measure of environment protection.

Applications of mobile incineration units[edit]

Arguments for mobile incineration[edit]

An important argument for the mobile incineration is, due to its mobility, it can go to the place of origin of the waste.

This behavior makes it unique, and allows it to be used for waste disposal of several cities and/or hospitals at the same time.

Fighting against epidemics is a serious issue for authorities responsible for the health of their citizens in every country.

In case of an epidemic it is required to dispose the infected hazardous waste of the diseased, hospitals and health facilities as soon as possible.

Latest burner and control technology, together with a flue gas cleaning system is the basis of a modern mobile incinerator unit that meets the highest environmental standards. (See section Emissions)

Process description of a mobile incinerator unit (state of the art)[edit]

Fuel[edit]

Natural gas, diesel or biodiesel (so called green fuel) is usable as fuel for the mobile incinerators.

Furnace[edit]

Charging of a unit

The furnace of a modern mobile incinerator plant consists of a main combustion chamber (primary chamber) and a post combustion chamber (secondary chamber). Charging is carried out mostly from the front of the main combustion chamber through a feed opening system, which is closed by a gate valve. A check valve behind the feed opening prevents direct contact with the combustion chamber. Feeding is automatically controlled by a furnace control system. An automated burner serves for the heating of the combustion chamber subject to the calorific value of the waste charged. The feed opening is released as soon as the necessary flue gas temperature is reached. Two types of design are normally in use; a) an incinerator without grate and b) a rotary-kiln (pyrolysis). In the post combustion chamber the gas is heated to minimum of 850 °C (1,560 °F) in order to ensure an environmentally friendly emission based on the European Union Directive (85/337/EEC) on Environmental Impact Assessments (known as the EIA Directive). The normal combustion temperature is minimum 850 °C (1,560 °F) and up to 1,200 °C (2,190 °F), depending on the process settings. At the end of the thermal process, ash extraction is done through an ash door.

Flue gas cleaning system[edit]

Not all available devices in the market have a flue gas treatment plant. But there are devices available with a dry flue gas cleaning system according to the rigorous European standards. Such a flue gas system mainly consists of a dry sorption system for SO2, HCI, HF, dust reduction, heavy metals, dioxins, etc. To protect the whole system, an automatic emergency water injection facility at the combustion chamber serves for the cooling of flue gas in case, too much waste or waste with too high calorific value is charged. Mobile incinerator units with such a system are environmental friendly.

Fuel and water tank[edit]

A fuel and a water tank are mostly installed on or under the semi-trailer.

Fan and stack[edit]

Mostly a fan transports the flue gas to the stack.

Electrical, instrumentation and control equipment and its standards[edit]

The electrical, instrumentation and control equipment of such a modern incinerator unit includes a main switch, an emergency switch as well as all necessary safety catches, contactors, relays and clamps, key switches for the start up and so on. All measuring, controlling and adjusting functions are realized in a modern mobile incineration plant. There are some safety limits which are processed by the hardware of such a plant. For start-up and operation of the mobile units, most have their own electrical generator on board for power supply. The whole equipment has to comply with European (e.g. DIN 41494, DIN 41488) and/or international (e.g. IEC Publication 297) standards.

Emissions of a modern mobile incinerator with a flue gas cleaning system[edit]

Under normal operation conditions, mobile incinerators are consistently able to keep emissions well below respective limits, for example in accordance to the German TA-Luft regulation. Often, emissions are well below the limits. This applies especially to the polychlorinated dibenzodioxins and furans (dioxins and furans). In spite of sophisticated technology, it may happen that higher emission values are reached due to inhomogeneous fuel (waste composition), especially in the phases of start up, shut down and malfunction of a plant.

Legally permitted emission levels[edit]

The legally permitted emission levels usually are far above the actual emissions of pollutants if the emissions over a period of one year is considered.

It should be emphasized however that these isolated instances of exceeding the limits has no effect on public health since even these higher values are usually still within the limits permitted for other technical or chemical plants.

The impact of waste composition on emissions[edit]

Domestic waste has a calorific value of approx. from 5,000 kJ/kg (12,000 BTU/lb) to approx 12,500 kJ/kg (29,000 BTU/lb). Industrial waste shows much higher fluctuation. This inhomogeneity pose a problem during the thermal treatment of waste. The exact composition of waste that is subject to fluctuation can not usually be estimated initially but it shows its potential energy as well as its pollutants during combustion. sorting the waste, recycling and composting has significant influence on the composition of waste which in turn affects its heating value. The large possible variation in calorific value and composition of the waste require a highly complex automatic control during the thermal treatment that must take into account both the reliability of the process and the requirements of environmental protection. Since the requirements of environmental protection and the reliability are contradictory to each other, there must be compromising solutions that are mutually acceptable for both sides. The parameters of O2 and CO concentration and fire room temperature are the main basic variables to be controlled when designing the process.

Summaries of EU legislation[edit]

EUROPA > Summaries of EU legislation > Environment > Waste management

General framework[edit]

  • Council Directive 1999/31/EC of 26 April 1999 on the landfill of waste
  • Directive 2000/76/EC of the European Parliament and of the Council of 4 December 2000 on the incineration of waste
  • Regulation (EC) No 2150/2002 of the European Parliament and of the Council of 25 November 2002 on waste statistics
  • Directive 2006/12/EC of the European Parliament and of the Council of 5 April 2006 on waste. (From 11.12.2010 replaced by Directive 2008/98/EC)
  • Regulation (EC) No 1013/2006 of the European Parliament and of the Council of 14 June 2006 on shipments of waste
  • Directive 2008/1/EC of the European Parliament and of the Council of 15 January 2008 concerning integrated pollution prevention and control
  • Directive 2008/98/EC of the European Parliament and of the Council of 19 November 2008 on waste and repealing certain Directives

Hazardous waste[edit]

  • Council Directive 91/689/EEC of 12 December 1991 on hazardous waste. (From 11.12.2010 replaced by Directive 2008/98/EC)
  • Council Decision 93/98/EEC of 1 February 1993 on the conclusion, on behalf of the Community, of the Convention on the control of transboundary movements of hazardous wastes and their disposal (Basel Convention)
  • Council Decision 97/640/EC of 22 September 1997 on the approval, on behalf of the Community, of the amendment to the Convention on the control of transboundary movements of hazardous wastes and their disposal (Basel Convention), as laid down in Decision III/1 of the Conference of the Parties

Waste from consumer goods[edit]

  • Council Directive 75/439/EEC of 16 June 1975 on the disposal of waste oils. (From 11.12.2010 replaced by Directive 2008/98/EC)
  • European Parliament and Council Directive 94/62/EC of 20 December 1994 on packaging and packaging waste
  • Council Directive 96/59/EC of 16 September 1996 on the disposal of polychlorinated biphenyls and polychlorinated terphenyls (PCB/PCT).
  • Directive 2006/66/EC of the European Parliament and of the Council of 6 September 2006 on batteries and accumulators and waste batteries and accumulators and repealing Directive 91/157/EEC

See also[edit]

External links[edit]