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396. Municipal Solid Waste Generation, Recovery, and Disposal
[In millions of tons (87.8 represents 87,800,000), except as indicated. Covers post-consumer residential and commercial solid wastes which comprise the major portion of typical
municipal collections. Excludes mining, agricultural andindustrial processing, demolition and construction wastes, sewage sludgeand junked autos and obsolete equipment wastes. Based
on material-flows estimating procedure and wet weight as generated;for description, see below table]
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Item and material
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1960
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1965
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1970
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1975
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1980
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1985
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1986
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1987
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1988
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1989
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1990
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1991
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1992
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1993
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1994
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1995
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1996
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1997
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1998
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Waste generated
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87.8
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103.4
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121.9
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128.0
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151.5
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164.4
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170.7
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178.1
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184.2
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191.4
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205.2
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204.6
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208.9
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211.8
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214.2
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211.4
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209.2
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216.4
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220.2
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Per person per day (lb.).
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2.7
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3.0
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3.3
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3.3
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3.7
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3.8
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3.9
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4.0
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4.1
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4.2
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4.5
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4.4
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4.5
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4.5
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4.5
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4.4
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4.3
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4.4
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4.5
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Materials recovered
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5.9
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6.8
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8.6
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9.9
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14.5
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16.4
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18.3
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20.1
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23.5
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29.9
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33.6
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37.0
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40.6
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43.8
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50.8
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54.9
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57.3
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59.4
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62.2
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Per person per day (lb.).
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0.18
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0.19
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0.23
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0.25
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0.35
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0.38
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0.42
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0.45
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0.52
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0.7
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0.7
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0.8
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0.9
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0.9
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1.1
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1.1
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1.2
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1.2
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1.3
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Combustion for energy recovery
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(NA)
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0.2
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0.4
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0.7
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2.7
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7.6
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9.6
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16.0
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24.5
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27.1
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29.7
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30.1
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30.5
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30.9
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31.2
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34.5
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36.1
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36.7
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37.0
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Per person per day (lb.).
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(NA)
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0.01
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0.02
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0.02
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0.06
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0.17
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0.22
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0.36
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0.59
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0.6
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0.7
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0.7
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0.7
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0.7
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0.7
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0.7
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0.7
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0.8
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0.8
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Combustion without energy recovery.
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27.0
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26.8
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24.7
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17.8
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11.0
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4.1
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3.0
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2.0
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1.0
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2.0
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2.2
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2.2
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2.2
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1.6
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1.3
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1.0
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(1)
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(1)
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(1)
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Per person per day (lb.).
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0.82
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0.75
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0.66
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0.45
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0.27
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0.10
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0.07
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0.05
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0.02
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0.04
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0.05
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0.05
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0.05
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0.03
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0.03
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0.02
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(1)
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(1)
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(1)
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Landfilled, other disposal.
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54.9
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69.6
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88.2
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99.7
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123.3
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136.4
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139.8
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140.0
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135.1
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132.4
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139.7
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135.3
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135.7
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135.5
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130.9
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120.9
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115.8
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120.4
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121.1
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Per person per day (lb.).
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1.7
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2.1
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2.4
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2.5
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3.0
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3.13
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3.18
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3.15
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3.02
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2.9
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3.1
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2.9
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2.9
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2.9
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2.8
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2.5
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2.4
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2.5
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2.5
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PERCENT CHANGE FROM
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PRIOR YEAR
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Waste generated
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(NA)
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15.1
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15.2
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4.8
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15.5
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7.8
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3.7
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4.2
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3.3
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3.8
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6.4
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-0.3
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2.1
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1.4
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1.1
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-1.3
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-1.0
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3.5
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1.8
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Per person per day .
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(NA)
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11.3
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8.3
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-0.3
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10.7
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3.2
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2.8
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3.2
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2.7
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2.8
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8.1
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-1.4
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1.0
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0.3
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0.2
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-2.2
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-1.9
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2.5
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0.8
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Materials recovered
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(NA)
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13.2
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20.9
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13.1
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31.7
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11.6
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10.4
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9.0
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14.5
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21.4
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8.3
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10.3
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9.5
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8.0
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15.9
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8.2
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4.4
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3.6
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4.7
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Per person per day .
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(NA)
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5.3
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17.4
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8.0
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28.6
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7.9
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9.5
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6.7
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13.5
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21.2
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2.8
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9.1
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8.3
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6.9
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14.8
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7.2
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3.4
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2.6
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3.7
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Combustion for energy recovery
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(NA)
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(NA)
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50.0
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42.9
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74.1
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64.5
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20.8
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40.0
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34.7
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9.6
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2.8
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1.5
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1.4
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1.1
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1.1
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10.7
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4.5
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1.7
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0.8
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Per person per day .
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(NA)
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(NA)
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50.0
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0.0
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66.7
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64.7
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22.7
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38.9
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39.0
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1.7
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6.0
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0.4
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0.3
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0.0
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0.1
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9.7
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3.5
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0.7
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-0.1
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Combustion without energy recovery.
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(NA)
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-0.7
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-8.5
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-38.8
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-61.8
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-168.3
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-36.7
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-50.0
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-100.0
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50.0
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10.1
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-1.8
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-1.8
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-24.5
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-20.2
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-23.1
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(1)
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(1)
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(1)
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Per person per day .
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(NA)
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-9.3
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-13.6
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-46.7
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-66.7
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-170.0
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-42.9
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-40.0
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-150.0
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50.0
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17.1
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-2.9
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-2.9
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-25.3
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-21.0
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-23.8
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(1)
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(1)
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(1)
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Landfilled, other disposal.
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(NA)
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21.1
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21.1
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11.5
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19.1
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9.6
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2.4
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0.1
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-3.6
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-2.0
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3.0
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-3.2
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0.3
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-0.2
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-3.4
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-7.6
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-4.2
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3.9
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0.6
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Per person per day .
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(NA)
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18.5
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13.5
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6.7
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14.5
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5.1
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1.6
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-1.0
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-4.3
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-3.1
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4.6
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-4.2
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-0.8
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-1.2
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-4.3
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-8.5
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-5.1
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2.9
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-0.4
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Percent distribution of generation:
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Paper and paperboard..
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34.1
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36.8
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36.3
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33.6
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36.1
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37.4
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38.4
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39.1
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38.9
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37.6
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35.4
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34.7
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35.5
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36.6
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37.7
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38.6
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38.1
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38.5
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38.2
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Glass..
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7.6
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8.4
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10.4
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10.5
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9.9
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8.0
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7.6
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6.9
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6.8
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6.7
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6.4
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6.2
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6.3
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6.4
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6.2
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6.1
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5.9
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5.5
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5.7
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Metals.
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12.0
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10.7
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11.6
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11.2
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9.6
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8.6
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8.5
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8.3
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8.3
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8.2
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8.1
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8.1
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7.7
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7.5
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7.6
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7.5
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7.7
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7.7
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7.6
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Plastics..
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0.5
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1.4
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2.5
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3.5
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5.2
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7.1
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7.2
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7.5
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7.8
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8.0
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8.3
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8.7
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8.8
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9.0
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9.0
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8.9
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9.4
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9.9
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10.2
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Rubber and leather..
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2.3
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2.5
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2.6
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3.0
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2.8
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2.3
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2.5
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2.5
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2.5
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2.4
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2.8
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2.9
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2.8
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2.7
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2.9
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2.9
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3.0
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3.0
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3.1
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Textiles
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1.9
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1.8
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1.6
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1.7
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1.7
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1.7
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1.6
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2.1
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2.1
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2.9
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2.8
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3.0
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3.2
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3.2
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3.4
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3.5
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3.7
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3.8
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3.9
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Wood.
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3.4
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3.4
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3.3
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3.4
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4.4
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5.0
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5.3
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5.5
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6.1
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6.1
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6.0
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6.2
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5.9
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5.8
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5.3
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4.9
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5.2
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5.3
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5.4
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Food wastes..
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13.9
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12.3
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10.5
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10.5
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8.7
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8.0
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7.7
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7.4
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7.2
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6.9
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10.1
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10.2
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10.1
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10.0
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10.0
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10.3
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10.4
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10.1
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10.0
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Yard wastes..
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22.8
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20.9
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19.0
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19.7
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18.2
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18.2
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17.7
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17.4
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17.2
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18.1
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17.1
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17.1
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16.8
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15.7
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14.7
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14.0
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13.3
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12.8
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12.6
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Other wastes
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1.6
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1.8
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2.2
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2.9
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3.4
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3.6
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3.4
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3.3
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3.1
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3.1
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3.0
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3.1
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2.9
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3.0
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3.2
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3.3
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3.3
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3.4
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3.3
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1 Combustion without energy recovery is no longer available separately.
Source: Franklin Associates, Ltd., Prairie Village, KS, Characterization of Municipal Solid Waste in the United States: 1998.Prepared for the U.S. Environmental Protection Agency.
http://www.epa.gov/epaoswer/non-hw/muncpl/
*MATERIAL FLOWS METHODOLOGY
The material flows methodology is utilized to generate the estimates above. Thecrucial first step is making estimates of the generation of the materials andproducts in MSW.
DOMESTIC PRODUCTIONData on domestic production of materials and products were compiledusing published data series. U.S. Department of Commerce sources were usedwhere available, but in
several instances more detailed information onproduction of goods by end use is available from trade associations. The goal is toobtain a consistent historical data series for each
product and/or material.
CONVERTING SCRAPThe domestic production numbers were then adjusted for converting orfabrication scrap generated in the production processes. Examples of these kindsof scrap would be
clippings from plants that make boxes from paperboard, glassscrap (cullet) generated in a glass bottle plant, or plastic scrap from a fabricator ofplastic consumer products. This scrap
typically has a high value because it isclean and readily identifiable, and it is almost always recovered and recycledwithin the industry that generated it. Thus, converting/fabrication
scrap is notcounted as part of the postconsumer recovery of waste.
ADJUSTMENTS FOR IMPORTS/EXPORTSIn some instances imports and exports of products are a significant part ofMSW, and adjustments were made to account for this.
DIVERSIONVarious adjustments were made to account for diversions from MSW.Some consumer products are permanently diverted from the municipal wastestream because of the way they are
used. For example, some paperboard is usedin building materials, which are not counted as MSW. Another example ofdiversion is toilet tissue, which is disposed in sewer systems rather
thanbecoming MSW.
In other instances, products are temporarily diverted from the municipalwaste stream. For example, textiles reused as rags are assumed to enter the wastestream the same year the
textiles are initially discarded.
ADJUSTMENTS FOR PRODUCT LIFETIMESome products (e.g., newspapers and packaging) normally have a veryshort lifetime; these products are assumed to be discarded in the same year theyare
produced. In other instances (e.g., furniture and appliances), products haverelatively long lifetimes. Data on average product lifetimes are used to adjust thedata series to account for
this.
MUNICIPAL SOLID WASTE GENERATION AND DISCARDSThe result of these estimates and calculations is a material-by-material andproduct-by-product estimate of MSW generation, recovery, and
discards.
https://allcountries.org/uscensus/396_municipal_solid_waste_generation_recovery_and.html
These tables are based on figures supplied by the United States Census Bureau, U.S. Department of Commerce and are subject to revision by the Census Bureau.
Copyright © 2019 Photius Coutsoukis and Information Technology Associates, all rights reserved.
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