To
convert the waste components into benign or useful materials, one of suitable
solutions is using the thermal processing methods. These kinds of methods are
implemented by elevating the temperature in designed equipment. Both pyrolysis
and incineration are included in the thermal processing measures. However, the process
occurred when the temperature increased in these two processes is totally
different. Incineration requires the presence of substantial quantities of oxygen
in the process, while pyrolysis requires the absence of oxygen.
Table
1. Calculation of volume reduction by various solid waste disposal systems
|
Original Volume as Fractions
|
Reduction Factor
|
Final Landfill Volume as Fraction as
Original Volume
|
Sanitary Landfill
|
|
|
|
Combustible Waste
Bulky and
Noncombustible Waste
Total
Waste
|
0.8
0.2
1.0
|
0.166
0.5
|
0.133
0.100
0.233
|
Sanitary Landfill with Shredding and Resource Recovery
|
|
|
|
Total
Waste
|
1.0
|
(0.1252)
|
(0.125)
|
Conventional Incineration
|
|
|
|
Combustible Waste
Bulky and
Noncombustible Waste
Total
Waste
|
0.8
0.2
1.0
|
0.0145
0.5
|
0.012
0.100
0.112
|
Incineration with Shredding and Resource Recovery
|
|
|
|
Total
Waste
|
1.0
|
(0.0082)
|
(0008)
|
Pyrolysis Processes with/without Resource Recovery
|
|
|
|
Total
Waste
|
1.0
|
(0.004-0.03)
|
(0.004-0.03)
|
In
the past, incineration was popular in where the landfill capacity is
insufficient. In practice, incineration converts the waste into flue gas, and
heat with adequate quantities of air. A well-designed incinerator can
significantly reduces both the weight and volume of the waste and produce
residue that can be used as a fill material in construction business. As shown
in the table 1, the pyrolysis process is the most efficient method to reduce
the volume of the waste. Incineration shows less performance than pyrolysis,
but still have a high efficiency on size reduction of waste.
In
theory, the combustion gases should be comprised by carbon dioxide, water,
nitrogen and oxygen entirely. All of these gases are normal constituents in the
air. However, other constituents usually exist in the flue gas as well, including
carbon monoxide and some other hazard gases. These gases are mostly generated
due to the inefficient combustion. Thus, air pollution control equipment is
necessary in the incineration plant. Then, gases discharged to the atmosphere
can be treated to reach governmental standards for emission of chemical
constituents as well as particulates. Moreover, the residue after the process should
low heating values.
Before
initiate the incineration process, it is important to consider several factors
firstly. Air supply is always the most crucial factor in incineration design. Only
fully circulating surplus airflow can introduce complete combustion and
minimize the generation of pollution and hazard like carbon monoxide. The
second factor is that different incinerator has different requirements to the
refuse. Therefore, refuse preparation is sometimes necessary for some kinds of
incinerators. After the incineration process is finished, the gas cleaning
process is important to deal with the flue gases. Removing the pollutants like
dioxin, furans and other emissions in the gases is compulsory for industries
according to relevant legislation codes. Otherwise, these pollutants can cause harmful impacts on local and regional
environment. Finally, the residue from the grate usually contains metal and it
should be separated from the residue and be stored. Remaining ash may be used
as an aggregate replacement or be disposed to landfill.