The present invention relates to the production of synthetic gas from bio-waste and, more particularly, to a plasma-based apparatus for gasifying bio-waste into synthetic gas.
Fossil fuel is running out. The price for energy is rising. The global warming is getting worse. People around the world are exploring non-fossil energy such as solar energy, wind power, geothermal energy, fuel cells and bio-energy, intending to reduce the burden that we put on the environment and generating sustainable energy.
The bio-energy plays an important part. We can burn wood to generate heat to cook. It is however inconvenient for urban residents to burn wood. Most of the urban residents use gas instead of wood. Wooden waste causes a serious problem for the environment. Moreover, wood drifting near seashores or in ports might cause danger for traffic in the sea.
There are other types of bio-waste in addition to wooden waste. In fact, bio-waste is produced in thousands of tons in Taiwan alone. The bio-waste includes agricultural waste, forest waste, industrial waste and urban garbage. If converting bio-waste into clean fuel, we will solve a problem in handling the waste and provide a sustainable energy source.
Gasification apparatuses are used to produce synthetic gas from bio-waste. They however produce much sticky tar that sticks to devices and/or pipes used therein. The tar interferes with the operation of the gasification apparatuses. Furthermore, the synthetic gas contains tar so that the use and storage thereof are difficult. To solve the problems, water-scrubbing tar-removing apparatuses are used with the gasification apparatuses. The water-scrubbing tar-removing apparatuses use water to wash the tar from the gasification apparatuses, thus preventing the tar from clogging the pipes and reducing the combustion efficiencies. However, the cost of the equipment and the complexity of the operation and maintenance are increased. Moreover, the use of the water causes a demand on the water resource, which is also precious. Furthermore, after removing the tar from the gasification apparatuses, the water-scrubbing tar-removing apparatuses produce much wastewater, which contains the tar. The wastewater causes another problem for the environment.
The present invention is therefore intended to obviate or at least alleviate the problems encountered in prior art.
The primary objective of the present invention is to provide an apparatus for producing fuel-class synthetic gas from bio-waste.
To achieve the foregoing objective of the present invention, the apparatus for producing synthetic gas from bio-waste includes a chamber, a feeder, a plasma torch, a steam-providing and water-circulating system and a synthetic gas cleaner. The feeder is in communication with the chamber. The feeder feeds the bio-waste into the chamber. The plasma torch is in communication with the chamber. The plasma torch provides plasma into the chamber for gasifying the bio-waste into the fuel-class synthetic gas. The steam-providing and water-circulating system circulates water for cooling the chamber and the plasma torch. Furthermore, the steam-providing and water-circulating system provides steam into the plasma torch for the generation of the plasma. The synthetic gas cleaner is in communication with the chamber. The synthetic gas cleaner receives the produced synthetic gas and polishes it into fuel-class gas.
Other objectives, advantages and features of the present invention will become apparent from the following description referring to the attached drawing.
The present invention will be described via the detailed illustration of the preferred embodiment referring to the attached drawing.
Referring to
The chamber 11 includes an upper portion joined to a lower portion. Each of the upper and lower portions of the chamber 11 is formed with a flange 119. Threaded bolts and nuts may be used to secure the flange 119 of the upper portion of the chamber 11 to the flange 119 of the lower portion of the chamber 11.
A heat-isolating lining 111 is disposed in the chamber 11. The heat-isolating lining 111 is made of a refractory material that stands a high temperature of 1800 degrees Celsius. A water jacket 112 is located between the heat-isolating lining 111 and the chamber 11. The chamber 11 includes a water inlet 113 via which water flows into the water jacket 112 and a water outlet 114 via which the water flows out of the water jacket 112. The water flows past and cools the apparatus 1. A thermometer 115 is inserted through the chamber 11, the water jacket 112 and the heat-isolating lining 111 to measure the temperature inside the heat-isolating lining 111.
A gas inlet pipe 116 and a gas outlet pipe 118 are inserted through the chamber 11, the water jacket 112 and the heat-isolating lining 111. A mixture of reactive gasses is sent into the heat-isolating lining 111 through the gas inlet pipe 116. The types of the reactive gasses and their ratio are dependent on conditions under which the gasification is conducted. The synthetic gas is sent out of the chamber 11 through the gas outlet pipe 118. A crucible 117 is disposed in the heat-isolating lining 111 to receive ash produced after the gasification of the bio-waste. The threaded bolts and nuts can be removed from the flanges 119 so that the upper and lower portions of the chamber 11 can be detached from each other. Thus, the crucible 11 can be taken out of the chamber 11, and the ash disposed of.
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The central control unit 21 controls the operation of the steam-providing and water-circulating system.
Under the control of the central control unit 21, the water reservoir 22 detects the level of water contained therein and takes in more water if necessary to keep the level in a predetermined range. The water reservoir 22 is in communication with the steam reservoir 23 through a pipe so that the former can provide water into the latter that can turn the water into steam. The water reservoir 22 is in communication with the steam plasma torch 12 through a pipe so that the former can send water into the latter. The water reservoir 22 is in communication with the chamber 11 through a pipe so that the water reservoir 22 can provide water into the water jacket 112 of the chamber 11.
Under the control of the central control unit 21, the steam reservoir 23 detects the level of water contained therein and takes in more water if necessary to keep the level in a predetermined range. That is, the space for containing steam is retained in a predetermined range. The steam reservoir 23 is in communication with the steam re-heater 24 via a pipe so that the former sends steam into the latter.
Under the control of the central control unit 21, the steam re-heater 24 heats the steam from the steam reservoir 23 again so that the steam reaches a pre-determined temperature and is super-heated.
The steam flow controller 25 is provided between the steam re-heater and the steam plasma torch 12. The steam re-heater 24 sends the steam into the steam plasma torch 12 at a predetermined flow rate under the control of the steam flow controller 25.
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The plasma torch 12 raises the temperature in the chamber 11 to 800 to 1600 degrees Celsius. The feeder feeds the bio-waste into the chamber 11. The bio-waste is gasified in the chamber 11 so that the organic substances thereof are decomposed into methane, ethane, carbon monoxide and hydrogen. The mixture of the methane, ethane, carbon monoxide and hydrogen with one another is the synthetic gas.
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Tar and char are temporarily produced during the gasification. The tar and char react with the highly active atoms and free radicals of the plasma such as hydrogen atoms, oxygen atoms and hydroxyls.
Moreover, ash is temporarily produced during the gasification. However, the plasma torch 12 provides the plasma at 10,000 degrees Celsius to raise the temperature in the chamber to 1600 degrees Celsius to cause the ash to fuse into lava.
As discussed above, the apparatus exhibits several advantages. Firstly, it turns the organic substances of the bio-waste into the synthetic gas of the high energy density. Secondly, it eliminates tar and char without having to use an additional tar-removing device. Thirdly, it turns the inorganic substances of the bio-waste into quality lava for reuse.
The present invention has been described via the detailed illustration of the preferred embodiment. Those skilled in the art can derive variations from the preferred embodiment without departing from the scope of the present invention. Therefore, the preferred embodiment shall not limit the scope of the present invention defined in the claims.