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- 25 - <br /> <br />program costs while'receiving the benefits in terms of waste <br />reduction. It is also important to keep in mind the net, long- <br />term consumer savings derived from more efficient and less <br />wasteful packaging systems and products. <br /> <br />Waste Reduction Methods Requiring Establishment of Municipal <br />or County Policies <br /> <br />Two waste reduction techniques are more easily implemented at <br />the county or municipal level: office paper reduction and <br />extended tire warranties. Both of these programs involve only <br />minimal planning with implementation through resolution. Each <br />county or city procurement administrator would then restrict <br />purchases to follow the adapted waste reduction guidelines and <br />assist with employee education. Both programs have the <br />potential for net savings, especially when implemented in <br />conjunction with post-generation recycling programs (see <br />"Waste Separation" in this section) <br /> <br />A more controversial waste ~eduction strategy that could po- <br />tentially be instituted by county or city governments is the <br />waste charge.. With the enactment of the new 1980 Waste Manage- <br />ment Act, cities or counties may place reasonable conditions <br />on waste processing and disposal facilities. One such condi- <br />tion could be a per ton waste charge to help defray any <br />planning and management costs of monitoring the facility or <br />any waste recovery program instituted at the local level. In <br />addition to funding recovery, this would increase the genera- <br />tor's incentive to reduce waste output. <br /> <br />2. WASTE SEPARATION <br /> <br />Waste separation program costs will vary according to the system <br />type (that is, recycling centers, source separation with curb-side <br />pickup, picking or mechanical separation), materials handled, <br />population densities andd quality ofprogram administration. <br /> <br />Results from recycling centers, where data is available, indicate <br />that a range of net savings from $10 per ton to a net cost'6f $10 <br />per ton is possible (MPCA, unpub, data). These data assume that <br />all the recycling centers analyzed were operated as a profit- <br />making business. In other words, volunteer labor was calculated <br />at.minimum-wage labor costs. When calculated without this <br />assumption, considering only paid labor and not including <br />volunteers, the program costs range from no net cost to $25 per <br />ton savings from revenues. <br /> <br />Curb-side source separation programs have a wider range of costs, <br />from $10 per ton costs to $77 per ton savings (Boca Raton <br />newspaper collection program). The Boca Raton program may not be <br />representative because of its near ideal market conditions. (A <br />high-capacity newsprint mill is located in Georgia.) Nonetheless, <br />most curb-side programs do break even in terms of materials <br />revenues and transportation and disposal cost savings, at least <br />for meeting the program costs. <br /> <br /> <br />