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                       80                        Waste Management Practices: Municipal, Hazardous, and Industrial
                       4.5.1 ULTIMATE ANALYSIS OF SOLID WASTE COMPONENTS
                       The ultimate analysis of a material is defined as its total elemental analysis, i.e., the percentage of
                       each individual element present. The results of the ultimate analysis are typically used to charac-
                       terize the chemical composition of the organic fraction of MSW. Such a determination is essential
                       for assessing the suitability of the waste as a fuel and predicting emissions from combustion. The
                       data are also used to define the proper mix of MSW materials to achieve suitable nutrient ratios
                       (e.g., C/N) for biological conversion processes such as composting.
                          The ultimate analysis involves the determination of the percent values of carbon, hydrogen,
                       oxygen, nitrogen, sulfur, and ash in a sample. Due to concerns over emissions of chlorinated com-
                       pounds during combustion, the determination of halogens is often included in an ultimate analysis
                       (Tchobanoglous et al., 1993; Liu and Liptak, 2000). The percent values of carbon, hydrogen, nitro-
                       gen, sulfur, and chlorine are measured directly by established procedures. The oxygen value is cal-
                       culated by subtracting the other components, including ash and moisture, from 100%.
                          Data on the ultimate analysis of individual combustible materials are presented in Table 4.16.
                       The majority of MSW is composed of carbon, hydrogen, and oxygen. Five materials tend to pre-
                       dominate in the organic portion of MSW: cellulose, lignins, fats, proteins and hydrocarbon poly-
                       mers. Cellulose accounts for the majority of the dry weight of MSW and is the predominant
                       compound in paper, wood, food waste, and yard waste (Masterson et al., 1981, Liu and Liptak
                       2000;). The relatively low sulfur and nitrogen contents are significant, as both are precursors to acid
                       rain. Sulfur is not a component of any solid waste category, except perhaps building materials (gyp-
                       sum panels) or yard waste. Nitrogen occurs mainly in food waste, grass clippings, and textiles (e.g.,
                       wool and nylon)(Liu and Liptak, 2000). Chlorine occurs in the organic form as polyvinyl chloride
                       (PVC) and vinyl, and paper products bleached with chlorine. Chlorine may also occur in the inor-
                       ganic form as sodium chloride and other simple salts.
                          The ash fraction is the residual remaining after combustion and is primarily inorganic although
                       some organics may remain as well. Ash can impart significant environmental and public health
                       effects if improperly managed. Ash may exit an incinerator and enter the atmosphere via the flue,



                                TABLE 4.16
                                Ultimate  Analysis of the Combustible Components in Household
                                MSW
                                                       % by Wt (dry basis)
                                Component    Carbon  Hydrogen  Oxygen  Nitrogen  Sulfur  Ash
                                Organic
                                  Paper        43.5     6.0     44.0     0.3     0.2      6.0
                                  Plastics     60.0     7.2     22.8     —       —       10.0
                                  Food Wastes  48.0     6.4     37.6     2.6     0.4      5.0
                                  Yard Wastes  47.8     6.0     38.0     3.4     0.3      4.5
                                  Textiles     55.0     6.6     31.2     4.6     0.15     2.5
                                  Rubber       78.0    10.0      —       2.0     —       10.0
                                  Wood         49.5     6.0     42.7     0.2     0.1      1.5

                                Inorganic
                                  Glass        0.5      0.1      0.4    0.1      —       98.9
                                  Metals       4.5      0.6      4.3    0.1      —       90.5
                                  Dirt, ash    26.3     3.0      2.0     0.5     0.2     68.0
                                  MSW          15–30    2–5     12–24    0.2–1.0  0.02–0.1  —
                                Adapted from Kaiser, E.R., Proceedings of the National Incinerater Conference, ASME, New
                                York, 1969; U.S. Department of Health, Education, and Welfare, 1969. Data reproduced with
                                kind permission of the American Society of Mechanical Engineers.
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