This conventional design is suitable for the pyrolysis treatment of wastes such as waste water
sludge,
waste tires, and scrapped printed circuit boards. It is just in the concentrated
distillation area of low-boiling organic matter, so the pasty waste has enough time to transform into a viscous phase due to
slow heating, and gradually forms on the surface of the rake teeth (
bare metal parts, which belong to the "hot area" in the
drying area) Agglomeration of slagging, and further adhesion of new
viscous material, so that the gap between the rake teeth is completely filled with material and loses the function of stirring and pushing the material to move on the hearth. The tines "
climb" above the rake arms and form a hard slagging "shell" that completely disables the
moving parts of the furnace, causing
downtime[0013] A simple solution to increase the
furnace temperature in the
drying area by adding fuel to the first or second furnace has been taken, but due to the local extreme high temperature caused by the
flame of the burner in the furnace, the
recovery rate of organic matter is significantly reduced (occurrence complex reaction processes such as high-temperature
polymerization,
cracking,
partial oxidation, and
nitration, which increase the yield of non-condensable gases and reduce the yield of organic matter recovered by condensation), and the hard slagging blocks formed near the
nozzle of the burner will quickly Causing the
combustion unit to
shut down[0014] Attempts were also made to install a double-layer steel cooling plate with a labyrinth channel on the upper hearth, using
heat transfer oil, high-temperature
flue gas from a single incinerator, and high-temperature hot air from a single
hot blast stove as heat sources to improve the operation of the
drying area Although the temperature can alleviate the formation speed of the viscous phase to a certain extent, due to the sharp increase in the area of the "
hot zone", and the
heat resistance of the steel and the heat exchange efficiency of the components
restrict the allowable upper limit of the
furnace temperature (the
maximum temperature in the drying zone can be maintained at about 280°C), and the high-temperature
corrosion of the material on the steel is greatly accelerated (there are potential safety hazards in production), resulting in unsatisfactory application results
[0015] It has also been attempted to introduce the high-temperature
flue gas produced by a separate
coal-fired or oil-fired incinerator, or to introduce the pyrolysis
tail gas (containing a certain concentration of
combustible gas components) of a multi-hearth furnace after recovering organic matter into a post-type post-
combustion chamber for complete
incineration. The high-temperature
flue gas is directly diverted to the drying area of the multi-hearth furnace as a heating medium, but due to the
high heat dissipation of the pipeline, the high-temperature
flue gas conveying device is difficult to operate without failure for a long time, and the
flue gas dust seriously affects the quality and application performance of the recovered organic matter. Problems such as
impact, investment and operating costs have risen sharply, and are not accepted by users
[0016] (2) The problem of
excessive energy consumption of the overall pyrolysis device
[0021] If no process air is fed into the pyrolysis functional area of the multi-hearth furnace for special paste / slurry waste, or the amount of process air introduced is much smaller than the
chemical reaction formula volume ratio (for example: ≤25% formula volume ratio air consumption), then In the pyrolysis
reaction zone, only the gasification and
cracking reactions of organic matter in the
solid phase composition can occur. These two reactions are endothermic reaction processes, which are the main reasons why the overall
energy consumption of the furnace exceeds expectations.