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397. Generation and Recovery of Selected Materials in Municipal Solid Waste
[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 and
industrial processing, demolition and construction wastes, sewage sludge
and 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 |
1960 |
1965 |
1970 |
1975 |
1980 |
1985 |
1986 |
1987 |
1988 |
1989 |
1990 |
1991 |
1992 |
1993 |
1994 |
1995 |
1996 |
1997 |
1998 |
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| Waste generated, total. |
87.8 |
103.4 |
121.9 |
128.1 |
151.5 |
164.4 |
170.7 |
178.1 |
184.2 |
191.4 |
205.2 |
204.6 |
208.9 |
211.8 |
214.2 |
211.4 |
209.2 |
216.4 |
220.2 |
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| Paper and paperboard . |
29.9 |
38.0 |
44.2 |
43.0 |
54.7 |
61.5 |
65.6 |
69.6 |
71.7 |
71.9 |
72.7 |
71.0 |
74.3 |
77.4 |
80.8 |
81.7 |
79.7 |
83.3 |
84.1 |
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| Ferrous metals . |
9.9 |
10.1 |
12.6 |
12.3 |
11.6 |
10.9 |
11.1 |
11.3 |
11.6 |
12.0 |
12.6 |
12.7 |
12.1 |
11.9 |
11.8 |
11.6 |
11.8 |
12.3 |
12.4 |
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| Aluminum . |
0.4 |
0.5 |
0.8 |
1.1 |
1.8 |
2.3 |
2.4 |
2.4 |
2.5 |
2.5 |
2.8 |
2.8 |
2.9 |
2.9 |
3.0 |
3.0 |
3.0 |
3.0 |
3.1 |
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| Other nonferrous metals. |
0.2 |
0.5 |
0.7 |
0.9 |
1.1 |
1.0 |
1.0 |
1.1 |
1.1 |
1.2 |
1.1 |
1.1 |
1.1 |
1.1 |
1.4 |
1.3 |
1.3 |
1.3 |
1.4 |
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| Glass . |
6.7 |
8.7 |
12.7 |
13.5 |
15.0 |
13.2 |
13.0 |
12.3 |
12.5 |
12.9 |
13.1 |
12.6 |
13.1 |
13.6 |
13.4 |
12.8 |
12.3 |
12.0 |
12.5 |
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| Plastics . |
0.4 |
1.4 |
3.1 |
4.5 |
7.9 |
11.6 |
12.2 |
13.4 |
14.4 |
15.4 |
17.1 |
17.7 |
18.4 |
19.0 |
19.3 |
18.9 |
19.8 |
21.5 |
22.4 |
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| Yard waste. |
20.0 |
21.6 |
23.2 |
25.2 |
27.5 |
30.0 |
30.2 |
31.0 |
31.6 |
34.7 |
35.0 |
35.0 |
35.0 |
33.3 |
31.5 |
29.7 |
27.9 |
27.7 |
27.7 |
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| Other wastes. |
20.3 |
22.6 |
24.6 |
27.6 |
31.9 |
33.9 |
35.2 |
37.0 |
38.8 |
40.8 |
50.7 |
51.7 |
52.1 |
52.5 |
53.1 |
52.4 |
53.5 |
55.3 |
56.7 |
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| PERCENT CHANGE FROM |
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| PRIOR YEAR |
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| Waste generated, total. |
(NA) |
15.1 |
15.2 |
4.8 |
15.4 |
7.8 |
3.7 |
4.2 |
3.3 |
3.8 |
6.7 |
-0.3 |
2.1 |
1.3 |
1.1 |
-1.3 |
-1.0 |
3.3 |
1.7 |
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| Paper and paperboard . |
(NA) |
21.3 |
14.0 |
-2.8 |
21.4 |
11.1 |
6.2 |
5.7 |
2.9 |
0.3 |
1.1 |
-2.5 |
4.4 |
4.1 |
4.2 |
1.0 |
-2.5 |
4.3 |
1.0 |
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| Ferrous metals . |
(NA) |
2.0 |
19.8 |
-2.4 |
-6.0 |
-6.4 |
1.8 |
1.8 |
2.6 |
3.3 |
5.1 |
0.1 |
-4.8 |
-1.4 |
-1.2 |
-1.2 |
1.6 |
4.1 |
0.3 |
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| Aluminum . |
(NA) |
20.0 |
37.5 |
27.3 |
38.9 |
21.7 |
4.2 |
0.0 |
4.0 |
0.0 |
11.0 |
1.2 |
0.9 |
2.1 |
3.5 |
-2.7 |
-0.3 |
2.0 |
2.3 |
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| Other nonferrous metals. |
(NA) |
60.0 |
28.6 |
22.2 |
18.2 |
-10.0 |
0.0 |
9.1 |
0.0 |
8.3 |
-9.1 |
2.6 |
-0.8 |
-0.9 |
17.8 |
-7.1 |
0.0 |
0.8 |
8.0 |
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| Glass . |
(NA) |
23.0 |
31.5 |
5.9 |
10.0 |
-13.6 |
-1.5 |
-5.7 |
1.6 |
3.1 |
1.6 |
-4.1 |
4.1 |
3.6 |
-2.0 |
-4.1 |
-4.4 |
-2.3 |
3.5 |
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| Plastics . |
(NA) |
71.4 |
54.8 |
31.1 |
43.0 |
31.9 |
4.9 |
9.0 |
6.9 |
6.5 |
10.1 |
3.3 |
3.8 |
3.0 |
1.5 |
-1.9 |
4.4 |
8.0 |
4.0 |
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| Yard waste. |
(NA) |
7.4 |
6.9 |
7.9 |
8.4 |
8.3 |
0.7 |
2.6 |
1.9 |
8.9 |
0.9 |
0.0 |
0.0 |
-5.3 |
-5.6 |
-6.1 |
-6.3 |
-0.7 |
0.0 |
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| Other wastes. |
(NA) |
10.2 |
8.1 |
10.9 |
13.5 |
5.9 |
3.7 |
4.9 |
4.6 |
4.9 |
19.5 |
2.0 |
0.6 |
0.9 |
1.0 |
-1.2 |
2.1 |
3.3 |
2.5 |
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| Materials recovered, total . |
5.9 |
6.8 |
8.6 |
9.9 |
14.5 |
16.4 |
18.3 |
20.1 |
23.5 |
29.9 |
33.6 |
37.0 |
40.6 |
43.8 |
50.8 |
54.9 |
57.3 |
59.4 |
62.2 |
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| Paper and paperboard . |
5.4 |
5.7 |
7.4 |
8.2 |
11.9 |
13.1 |
14.8 |
16.3 |
18.4 |
19.1 |
20.2 |
22.5 |
24.5 |
25.5 |
29.5 |
32.7 |
33.2 |
33.6 |
35.0 |
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| Ferrous metals . |
0.1 |
0.1 |
0.1 |
0.2 |
0.4 |
0.4 |
0.4 |
0.4 |
0.7 |
1.5 |
2.6 |
3.1 |
3.4 |
3.9 |
4.0 |
4.1 |
4.4 |
4.7 |
4.3 |
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| Aluminum . |
0 |
0 |
0 |
0.1 |
0.3 |
0.6 |
0.6 |
0.7 |
0.8 |
0.9 |
1.0 |
1.0 |
1.1 |
1.0 |
1.2 |
0.9 |
0.9 |
1.0 |
0.9 |
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| Other nonferrous metals. |
0 |
0.3 |
0.3 |
0.4 |
0.5 |
0.5 |
0.6 |
0.6 |
0.7 |
0.8 |
0.7 |
0.7 |
0.7 |
0.7 |
1.0 |
0.8 |
0.8 |
0.8 |
0.9 |
|
| Glass . |
0.1 |
0.1 |
0.2 |
0.4 |
0.8 |
1.0 |
1.1 |
1.3 |
1.5 |
2.5 |
2.6 |
2.6 |
2.9 |
3.0 |
3.1 |
3.1 |
3.2 |
2.9 |
3.2 |
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| Plastics . |
0 |
0 |
0 |
0 |
0 |
0.1 |
0.1 |
0.1 |
0.2 |
0.3 |
0.4 |
0.5 |
0.6 |
0.7 |
0.9 |
1.0 |
1.1 |
1.1 |
1.2 |
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| Yard waste. |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0.5 |
3.5 |
4.2 |
4.8 |
5.4 |
6.9 |
8.0 |
9.0 |
10.4 |
11.5 |
12.6 |
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| Other wastes. |
0.3 |
0.6 |
0.6 |
0.6 |
0.6 |
0.7 |
0.7 |
0.7 |
0.7 |
1.3 |
1.8 |
1.9 |
2.0 |
2.1 |
3.1 |
3.2 |
3.3 |
3.8 |
4.1 |
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| Percent of generation recovered, total. |
6.7 |
6.6 |
7.1 |
7.7 |
9.6 |
10.0 |
10.7 |
11.2 |
12.8 |
15.6 |
16.4 |
18.1 |
19.4 |
20.7 |
23.7 |
26.0 |
27.4 |
27.4 |
28.2 |
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| Paper and paperboard . |
18.1 |
15.0 |
16.7 |
19.1 |
21.8 |
21.3 |
22.6 |
23.4 |
25.6 |
26.6 |
27.8 |
31.7 |
33.0 |
32.9 |
36.5 |
40.0 |
41.6 |
40.3 |
41.6 |
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| Ferrous metals . |
1.0 |
1.0 |
0.8 |
1.6 |
3.4 |
3.7 |
3.6 |
3.5 |
5.8 |
12.6 |
20.4 |
24.1 |
27.7 |
32.8 |
33.9 |
35.5 |
37.2 |
38.4 |
35.1 |
|
| Aluminum . |
0 |
0 |
0 |
9.1 |
16.7 |
26.1 |
25.0 |
29.2 |
31.7 |
35.5 |
35.9 |
35.5 |
38.7 |
35.7 |
37.8 |
31.4 |
31.5 |
31.6 |
27.9 |
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| Other nonferrous metals. |
0 |
60.0 |
42.9 |
44.4 |
45.5 |
50.0 |
60.0 |
54.5 |
65.1 |
68.3 |
66.4 |
65.5 |
63.4 |
63.1 |
73.3 |
64.3 |
66.7 |
65.4 |
67.4 |
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| Glass . |
1.5 |
1.1 |
1.6 |
3.0 |
5.3 |
7.6 |
8.5 |
10.6 |
12.0 |
19.5 |
20.0 |
20.3 |
22.0 |
22.1 |
23.3 |
24.5 |
25.8 |
24.3 |
25.5 |
|
| Plastics . |
0 |
0 |
0 |
0 |
0 |
0.9 |
0.8 |
0.7 |
1.1 |
1.7 |
2.2 |
2.5 |
3.3 |
3.5 |
4.9 |
5.2 |
5.4 |
5.2 |
5.4 |
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| Yard waste. |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
1.6 |
10.0 |
12.0 |
13.7 |
15.4 |
20.8 |
25.4 |
30.3 |
37.2 |
41.4 |
45.3 |
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| Other wastes. |
1.5 |
2.7 |
2.4 |
2.2 |
1.9 |
2.1 |
2.0 |
1.9 |
1.8 |
3.2 |
3.6 |
3.7 |
3.9 |
4.0 |
5.9 |
6.1 |
6.2 |
6.8 |
7.3 |
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Source: Franklin Associates, Ltd., Prairie Village, KS,
Characterization of Municipal Solid Waste in the United States: 1998; and earlier reports.
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. The
crucial first step is making estimates of the generation of the materials and
products in MSW.
DOMESTIC PRODUCTION
Data on domestic production of materials and products were compiled
using published data series. U.S. Department of Commerce sources were used
where available, but in several instances more detailed information on
production of goods by end use is available from trade associations. The goal is to
obtain a consistent historical data series for each product and/or material.
CONVERTING SCRAP
The domestic production numbers were then adjusted for converting or
fabrication scrap generated in the production processes. Examples of these kinds
of scrap would be clippings from plants that make boxes from paperboard, glass
scrap (cullet) generated in a glass bottle plant, or plastic scrap from a fabricator of
plastic consumer products. This scrap typically has a high value because it is
clean and readily identifiable, and it is almost always recovered and recycled
within the industry that generated it. Thus, converting/fabrication scrap is not
counted as part of the postconsumer recovery of waste.
ADJUSTMENTS FOR IMPORTS/EXPORTS
In some instances imports and exports of products are a significant part of
MSW, and adjustments were made to account for this.
DIVERSION
Various adjustments were made to account for diversions from MSW.
Some consumer products are permanently diverted from the municipal waste
stream because of the way they are used. For example, some paperboard is used
in building materials, which are not counted as MSW. Another example of
diversion is toilet tissue, which is disposed in sewer systems rather than
becoming MSW.
In other instances, products are temporarily diverted from the municipal
waste stream. For example, textiles reused as rags are assumed to enter the waste
stream the same year the textiles are initially discarded.
ADJUSTMENTS FOR PRODUCT LIFETIME
Some products (e.g., newspapers and packaging) normally have a very
short lifetime; these products are assumed to be discarded in the same year they
are produced. In other instances (e.g., furniture and appliances), products have
relatively long lifetimes. Data on average product lifetimes are used to adjust the
data series to account for this.
MUNICIPAL SOLID WASTE GENERATION AND DISCARDS
The result of these estimates and calculations is a material-by-material and
product-by-product estimate of MSW generation, recovery, and discards.
*
TERMS
Municipal solid waste ( MSW) includes wastes such as durable goods, nondurable goods,
containers and packaging, food scraps, yard trimmings, and miscellaneous inorganic wastes from
residential, commercial, institutional, and industrial sources. Examples of waste from these
categories include appliances, automobile tires, newspapers, clothing, boxes, disposable
tableware, office and classroom paper, wood pallets, and cafeteria wastes. MSW does not include
wastes from other sources, such as construction and demolition debris, automobile bodies,
municipal sludges, combustion ash, and industrial process wastes that might also be disposed in
municipal waste landfills or incinerators.
Source reduction activities reduce the amount or toxicity of wastes before they enter the
municipal solid waste management system (see Generation). Reuse is a source reduction activity
involving the recovery or reapplication of a package, used product, or material in a manner that
retains its original form or identity. Reuse of products such as refillable glass bottles, reusable
plastic food storage containers, or refurbished wood pallets are examples of source reduction.
Generation refers to the amount (weight or volume) of materials and products that enter the
waste stream before recycling (including composting), landfilling, or combustion takes place.
Recovery of materials means removing MSW from the waste stream for the purpose of recycling
(including composting). Recovery for recycling as defined for this report includes purchases of
postconsumer recovered materials plus net exports of the materials. Recovery of yard trimmings
includes diverting yard trimmings from disposal to a composting facility. For some materials,
recovery for uses such as highway construction or insulation is considered recovery along with
materials used in remanufacturing processes.
Combustion includes combustion of mixed MSW, fuel prepared from MSW, or a separated
component of MSW (such as rubber tires), with or without energy recovery.
Discards include the municipal solid waste remaining after recycling (including composting).
These discards are usually combusted or disposed of in landfills, although some MSW is littered,
stored, or disposed on site, particularly in rural areas.
*
http://www.allcountries.org/uscensus/397_generation_and_recovery_of_selected_materials.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 © 2006 Photius Coutsoukis and Information Technology Associates, all rights reserved.
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