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Metal-stamping scrap Oily wastewater Diesel and water* Paper, uncontaminated Steam booth sludge Gasoline and water OCC Used oil Parts washer Pallets Empty drums Sump/dike water* Waste paint Ethylene glycol Aerosols Lamp ballasts Surfactants CFC (R-11) * Alkaline/lithium Lead acid batteries HID lamps Medical waste Cylinder lab pack* NiCd batteries* Chlorinated solvent lab pack* Total
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13.23 17.88 4.92 5.53 8.64 5.42 5.48 5.46 4.17
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52,191
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CASE STUDY
recycled materials. The plant recycled over 107 million pounds of solid waste each year. Of the total, metal-stamping scrap comprises over 90 percent. Table 34.3 displays the major solid wastes not currently recycled by the plant, segmented by the percentage of total waste (in pounds). As shown in the table, the plant disposed of an estimated 1,463,280 lb (732 tons) of solid waste at the land ll each year. The table also shows that general trash (including food waste), which is nonrecyclable, comprises about 52 percent of the total land lled waste. Floor block (15 percent) and polypropylene (11 percent) were the next two largest nonrecycled waste components. Table 34.4 displays the major annual waste streams at the plant that are potentially recyclable in terms of annual weight (pounds). This information is useful because recycling vendors usually pay for recyclables based on weight. If these materials can
TABLE 34.3 ANNUAL WASTE STREAM NONRECYCLED MATERIALS FOR AUTOMOTIVE CASE STUDY YEAR 2000 (TONS) YEAR 2001 (TONS) AVERAGE (TONS/YEAR) AVERAGE (LB/YEAR)
MATERIAL
TOTAL (%)
Trash (including food waste) Floor block Polypropylene Yard trash* Debris* Diesel soil and absorbents* Oily rags Oily basement sump sludge* Grease Oil lters Crushed lamps Other/special waste Total
449.44 155.96 82.03
318.64 66.39 82.47 59.26 42.99 28.05
384.04 111.18 82.25 59.26 42.99 28.05 13.86 7.00 1.51
768,080 222,350 164,500 118,520 85,980 56,100 27,720 14,000 3,020 1,710 900 400 1,463,280
52.490 15.195 11.242 8.100 5.876 3.834 1.894 0.957 0.206 0.117 0.062 0.027 100
3.76 7.00
1.51 0.88 0.30 0.20 0.83 0.60
0.86 0.45 0.20
*Handled by specialized waste hauler
Hazardous waste
INDUSTRIAL AND COMMERCIAL MACHINERY INCLUDING AUTOMOTIVE MANUFACTURING
TABLE 34.4 REVENUE FROM THE SALE OF RECYCLABLES (AUTOMOTIVE CASE STUDY) POUNDS PER YEAR CURRENT MARKET VALUE PER TON REVENUE (FROM SALE OF RECYCLABLES)
COMPONENT
Polypropylene White ledger Newspaper Mixed of ce paper Total
164,500 9,884 4,942 9,884 189,210
$100 $127 $36 $14
$8,225 $6,276 $89 $69 $14,659
be removed from the waste stream and sent to a recycler instead of the land ll, revenue could be generated and waste hauling costs could be reduced. The waste assessment team found the national average price paid for polypropylene plastic scrap was $0.07 per pound. The waste minimization team used $0.05 per pound to be conservative. Local recyclers contacted by the waste assessment team would pay between $0.03 and $0.08 per pound depending on the type, grade, form, and contamination of the polypropylene plastic scrap. Based on the 24,710 lb of commingled paper (white ledger, newspaper, and mixed of ce paper) collected each year and estimates from the on-site survey, a total of over $6400 could be generated from the sale of these materials. These materials are currently collected but are not separated. The plant received no revenue from these materials because they are commingled. The audit indicated that the plant could potentially generate a total of $14,659 annually from the sale of recyclables if a local vendor could be found to purchase and recondition the material. The amounts paid per ton of recyclables were gathered from current market prices. Additional cost savings could also be realized from a reduction in hauling costs of polypropylene plastic. Waste hauling charges can be reduced by approximately 10 percent by reducing the volume of polypropylene plastic waste taken by the hauler. The plant could potentially save approximately $2508 annually (calculated from a 10 percent reduction of the annual waste hauling cost of $25,080) by removing polypropylene plastic from the wastes. The cost savings will be achieved by reducing the frequency of pickup by waste management at the plant. Should a plastic-washing system be purchased, additional savings could be realized if the polypropylene plastic could be used in place of virgin material after the washing process. The plant could potentially save a total of $17,167 annually ($14,659 from additional recycling and $2508 from waste hauling reduction). Speci c information regarding procedures to achieve these cost reductions is in Table 34.5.
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