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                       Characterization of Solid Waste                                              83
                           ● Fixed carbon, the combustible residue left after volatile matter is removed; ignition at
                             600 to 900°C.
                           ● Ash, the weight of residue after combustion in an open crucible.

                          Moisture content and ash represent the noncombustible component of the MSW. Moisture is
                       undesirable in MSW as it adds weight to the fuel without adding to the heating value. In addition,
                       moisture content will adversely affect heat release from the fuel. Ash similarly adds weight without
                       providing heat energy. Furthermore, ash retains heat when removed from the furnace; as a result,
                       potentially useful heat is lost to the environment.
                          The volatile matter and the fixed carbon content are the preferred indicators of the combustion
                       capability of MSW. The volatile matter is the portion of MSW converted into gas as the tempera-
                       ture increases. Gasification occurs before the onset of combustion. In many incineration systems
                       these carbonaceous gases are drawn away from the heating mass and carried to a secondary com-
                       bustion chamber where combustion of the fuel gas occurs (see Chapter 9). Heat release is rapid and
                       combustion is complete within a short time (Pfeffer, 1992).
                          Fixed carbon is the solid carbon residue that has settled on the furnace grates. Combustion
                       occurs in the solid state, i.e., on the surface of this “char” material. The rate of combustion is
                       affected by the temperature and surface area of the char. A waste fuel with a high percentage of
                       fixed carbon will require a longer retention time in the combustion chamber to achieve complete
                       combustion as compared with a fuel low in fixed carbon (Pfeffer, 1992).
                          The value for fixed carbon from laboratory results is calculated as follows (Liu and Liptak, 2000):

                                 % fixed carbon   100%   % moisture   % ash   % volatile matter   (4.1)

                       A limitation of proximate analysis is that it does not provide an indication of possible pollutants emit-
                       ted during combustion. These data are determined by conducting ultimate analysis. Proximate analysis
                       data for the combustible components of MSW and bulk samples of MSW are presented in Table 4.18.



                              TABLE 4.18
                              Typical Proximate Analysis of MSW and MSW Components
                                                          Proximate analysis (% by wt)
                              Waste Type   Moisture   Volatiles  Fixed Carbon  Noncombustable (ash)
                              Food mixed     70.0      21           3.6              5.0
                              Paper mixed    10.2      76           8.4              5.4
                              Newspapers      6.0      81          11.5              1.4
                              Cardboard       5.2      77           12.3             5.0
                              Plastics mixed  0.2      96           2                2
                              Polyethylene    0.2      98          <0.1              1.2
                              Polystyrene     0.2      99           0.7              0.5
                              PVC             0.2      87           10.8             2.1
                              Textiles       10        66           17.5             6.5
                              Yard wastes    60        30           9.5              0.5
                              Wood mixed     20        68           11.3             0.6
                              Glass           2                                     96–99
                              Metals          2.5                                   94–99
                              Domestic       10–40     30–60        3–15            10–30
                              MSW
                              Source: Kiely, G., Environmental Engineering, McGraw-Hill, New York, 1997. Reproduced with kind
                                   permission of the McGraw-Hill Companies.
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