China Gets Plasma Thermal Waste Destruction System

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PEAT International has successfully commissioned a Plasma Thermal Destruction and Recovery (PTDR) systems in Shanghai, China. The system was designed to deconstruct medical waste and oil refinery sludge.

PEAT International, Inc. (PEAT), a plasma-thermal waste destruction company, has installed a PTDR system in Shanghai, China. The 60 kg/hr system was specifically designed for the treatment of medical waste and oil refinery sludge for Abada Plasma Technology Holdings, Ltd.

“This is end-stage technology and sets the standard for clean hazardous waste remediation. Only with plasma can you achieve temperatures high enough for waste destruction in a single-staged process,” said Joseph Rosin, PEAT International chairman. “It’s a 21st century solution that addresses three important needs: significant volume reduction, full pollution control and competitive pricing. We are currently preparing for other projects already under contract.”

PEAT’s PTDR “single stage” plasma-thermal process transforms hazardous waste through molecular dissociation at 1,500°C (2,732°F) into recoverable, non-toxic end-products, synthetic gas and heat (sources for energy recovery), metals, and a vitrified glass matrix. Emissions are below the most stringent environmental standards.

PTDR systems are in operation in California, Taiwan, and China. For more information and to watch a video of operations, please click here.

Comparing Plasma Arc, Plasma Gasification and other Technologies

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As you may know from reading this blog, in plasma arcplasma gasification, waste is broken down at temperatures around 1,500°C. While this form of gasification can be energy intensive, it ensures that the plasma gasification syngas produced is cleaned of residue tar, which makes it a higher value product. Another major benefit of plasma arcplasma gasification is that it creates little to no emissions. This blog entry attempts to take a quick look at some of the other waste to energy technologies available.

Conventional gasification slightly differs from plasma arc, plasma gasification in that the temperatures inside its primary reactor are lower and the fuel source may be natural gas. However conventional gasification is similar to plasma arc, plasma gasification in that both are thermo-chemical processes in which waste is heated in an oxygen deficient environment to produce syngas which contains hydrogen, carbon monoxide and sometimes methane. This gas can be used as fuel for electricity generation or to produce chemicals or biofuels.

Pyrolysis is sometimes linked to plasma arcplasma gasification. Pyrolysis is also a thermo-chemical process, however here the waste is heated in the complete absence of oxygen. The products are olefin liquid, syngas-type product, and char. The liquid fuel can be used as an input to produce gasoline, while the char can be recovered or passed along to a gasification process.

Other waste to energy alternatives include landfill gas recovery that convert methane gas from decomposing trash in to power. Methane is collected through a series of pipes and compressed for electricity generation. There are also waste to biofuels and waste to chemical processes. These are similar to aforementioned waste to energy technologies as they may utilize gasification or other thermo-chemical processes. Appropriate waste feedstocks include soybean straw, wood waste and used oils/fats.

Finally, there is anaerobic digestion (AD). This differs greatly from the other waste to energy technologies mentioned here in that AD uses microorganisms to convert organic waste into a biogas (primarily methane) and digestate. This biogas can be used to generate electricity, while the digestate has applications as a fertilizer. Anaerobic digestion is limited to wet organic wastes (including manure and sewage) or food waste. As such it requires that these materials to be separated from regular waste.

Waste to Energy and Recycling

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Many contest that the primary goals for waste management; to reduce, reuse and recycle, and increasing waste conversion (i.e. waste-to-energy) rates are not compatible. However, in the United States, the states making the most use of waste-to-energy facilities are also those that recycle the most.

In addition, according to a recent study conducted by the EPA, increasing recycling wastes actually improves the efficiency of waste conversion (i.e. waste-to-energy).

Consumers are increasingly recycling more biogenic waste (paper and food) and throwing away more non-biogenic waste (rubber and plastics).

The higher energy content of non-biogenic waste makes it a more productive feedstock for generating electricity through a waste-to-energy technology such as the TVRC. Conversely to previously held views then, recycling is not just compatible with waste conversion, it actually improves the energy content of the leftover waste, boosting the potential of key waste-to-energy technologies, including plasma-arc plasma gasification.

Waste to Energy solution via Plasma Thermal Destruction and Recovery

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The innovative and patented core Plasma Thermal Destruction & Recovery waste to energy solution is a gasification technology. Gasification is a process that converts organic based carbonaceous materials into carbon monoxide (CO), hydrogen (H2) and carbon dioxide (CO2) by reacting the material (i.e. waste) at high temperatures (minimum 700°C) without combustion with a controlled amount of oxygen and/or steam. The resulting gas mixture is called syngas (from synthesis gas) and is itself a fuel.

PEAT uses the heat generated by plasma-arcs to first pull apart (dissociate) the molecules that make-up the organic portions of the waste, then, depending on the composition of the waste stream, oxygen is added to reform the dissociated elements of the waste into the syngas The syngas can then be used in a variety of ways: as a fuel for thermal and/or electricity production or as a feedstock for the production of liquid fuels, such as ethanol.

Waste, when heated to a very high temperature in the controlled atmosphere of the reducing plasma reactor undergoes predictable physical and chemical changes. This high temperature, over 1,250°C (2,280°F) prevents the formation of complex organic molecules and breaks down organics into a gas. Our operations reflect that the formation of dioxins or furans is practically impossible inside the plasma reactor due to the unique process features, including high uniform temperatures and a lack of excess oxygen within the system.

This hot gas is then fed through a gas cleaning and conditioning system (The gas that comes out of a plasma reactor has a trace of contaminants compared to huge quantities in the stand-alone incinerator), where it is rapidly cooled and cleaned to remove any entrained particulate and/or acid gases prior to potential re-use.

Any inorganic constituents of the waste are melted (vitrified) into an environmentally safe, leach resistant, glass matrix. Plasma Thermal Destruction & Recovery waste to energy plasma reactors are designed to collect the molten metal and glass. The glass and metal layers are removed through controllable tap ports into a slag/metal collection system. Removal of the molten glass or metals presents no hazards of any kind to personnel, requires no special tools and does not disrupt the operating process. The metal layer settles on the bottom of the basin in the processing reactor below the molten glass. Both layers are tapped as necessary, depending on the metal/inorganic content of the waste stream.

The vitrified product can be used in a variety of commercial applications including concrete aggregate, insulation, roadbed construction, and even in decorative tiles. The metal layer can contain relatively pure amounts of iron, copper and aluminum.

It is important to note that the composition of end-products varies with the waste being processed. For example, processing medical waste, with a relatively high percentage of paper and plastic or pharmaceutical manufacturing waste with high levels of carbon-based constituents would produce meaningful levels of syngas, and a lesser amount of glass product. Conversely, processing fly ash from the high temperature boiler in a TVRC would produce lower amounts of syngas and relatively more vitrified product.

Plasma Thermal Destruction & Recovery waste to energy systems are driven by proprietary, state-of-the-art instrumentation and computerized control systems. The Plasma Thermal Destruction & Recovery waste to energy process is a unique, cost-effective and environmentally effective technology that is superior to other mainstream methods of waste treatment:

  • The Plasma Thermal Destruction & Recovery waste to energy process can utilize virtually any type of feedstock containing combinations of organic, inorganic and/or heavy-metal constituents thus the pre-processing, staging and management costs are minimized thereby reducing processing costs and enhancing recycling designations.
  • Unlike incineration or metal-bearing waste stabilization, the Plasma Thermal Destruction & Recovery waste to energy process is designed to not create any secondary solid wastes that will require further treatment or land filling. As indicated, stand-alone incinerators produce large quantities of bottom and fly ash which are toxic in nature, require further treatment (with stabilization agents) and the resulting post-treated materials (often time whose volume has been doubled) will require final disposal, sometimes in specially designed hazardous waste landfills.

It is also important to note however that through a previous partnership with the Russian Academy of Science, PEAT utilized an AC plasma torch into earlier Plasma Thermal Destruction & Recovery waste to energy systems. The AC plasma torch, which generates the plasma field by utilizing AC electric current directly from the grid without the need for rectifiers (a device, such as a diode, that converts alternating current to direct current). Patents behind the Plasma Thermal Destruction & Recovery waste to energy technology would allow for usage of an AC plasma torch, giving PEAT some additional flexibility. Like electrodes, the AC plasma torch can be more tolerant of a wide range of waste streams (organic and inorganic) and is less expensive to build and to operate than a DC plasma torch. The NCKU facility represented the first applications where an AC plasma torch was utilized in a commercial plant anywhere in the world.

Medical Waste Treatment

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The EPA first issued new performance standards for medical waste incineration in 1986 and then again in 1997 to curb pollutants, which prompted many hospitals to shut down their incinerators. Hospitals turned to autoclaving and steam sterilization, which can only treat limited aspects of medical waste and do not provide any volume reductions.

Over 2,300 medical waste incinerators have closed since 1997 and currently 57 (31 are operated by hospitals) are still online. EPA officials estimate that the new rules passed recently will cost roughly $15.5 million. If that was divided evenly over the 57 locations, that’s over $270,000 per location.

Reducing medical waste incineration is just one side; waste still needs to be thermally treated. At least 14 states have statues requiring incineration of trace-chemotherapy agents and pathological waste – both waste streams can be treated by Plasma Thermal Destruction and Recovery (PTDR).

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