SOLID WASTE SORTING LINE

Revision Date: 5/00
Process Code: Navy/Marines: SR-04-00; Air Force: FA01; Army: N/A
Usage: Navy: Medium; Marines: Medium;Army: Medium; Air Force: Medium
Compliance Impact: Low
Alternative for: Landfilling or Incineration
Applicable EPCRA Targeted Constituents: N/A

Overview: A solid waste sorting line (SWSL), also known as a dirty material recovery facility (dirty MRF), processes recyclables from a stream of raw solid waste and is typically used in rural areas with no curbside programs and communities that are not actively promoting recycling. A properly designed SWSL will process and recover between five and 45 percent of the incoming material as recyclables. The remainder of the material is used in a waste-to-energy facility, landfilled or otherwise disposed. Materials processed as recyclables include newspaper; steel and aluminum cans; brown, green and clear glass; polyethylene terephthalate (PET) and high-density polyethylene (HDPE) plastic containers. A SWSL serving a small community is typically designed to process less than 200 tons per day of solid waste. A SWSL serving a municipality can process 700 tons per day of solid waste. In many cases, independent private contractors who haul commercial waste operate SWSLs. Rather than hauling the waste directly to the landfill, the trucks stop at an SWSL and recyclable material is extracted. Only the material for which there is no market goes to the landfill.

SWSL designs can vary significantly. SWSL sorting systems can be fully automated, partially automated or consist solely of manual sorting systems. A combined system of automated and manual sorting usually begins with automated sizing and sorting and ends with manual sorting. The type of recyclables processed, and anticipated current and future processing rates need to be considered when designing an SWSL. SWSLs typically include a customer vehicle weigh scale and areas for queuing and maneuvering; recyclable shipping areas; vehicle parking; and outdoor storage of recyclables. The main building housing the SWSL will typically include a tipping floor for dumping mixed solid waste, areas for sorting materials and processing recyclables, interim storage of recyclable materials, and warehouse storage for processed recyclables awaiting shipment.

At the tipping floor, a rubber-tired loader spreads the waste out for inspection. At this stage, hazardous items and appliances are recovered. The loader then transports the solid waste onto incline conveyors. These conveyors transport the solid waste to a sorting area, usually located 10 to 20 feet above the ground level. Sorting is conducted at the designated sorting area, and recovered recyclables are dropped into the appropriate segregated collection bins.

In an automated system, the initial sorting operation usually removes bulky or dangerous items followed by waste screening to remove both small grit and aluminum and tin cans. An air classifier, the most common density sorting system used at a SWSL, is used to split the solid waste stream into heavy and light fractions, which allows the other sorting operations to specialize in the most common materials found in the respective fraction. The light fraction includes paper, aluminum cans and plastic, while the heavy fraction includes glass and ferrous materials. Equipment that sorts by chemical composition such as magnets and eddy current separators are commonly used in automated SWSLs.

Manual sorting follows automated sorting. The waste travels down a flat conveyor belt and workers remove the recyclables as they pass by. The conveyor belt for sorting may be as long as 50 to 100 feet to accommodate between five and 20 sorters. The length of the belt depends on the number of types of recyclables and the total amount of each type of recyclable being sorted.

Once the recyclables are separated, they must be processed into materials for sale. Processing typically includes baling for paper, steel cans, and plastic bottles, flattening or densifying for aluminum cans; granulating or perforating for plastic bottles; and crushing for glass bottles. Once processed, the materials are sold directly to specialty recyclers for reuse.

If the residual solid waste can be used in a waste-to-energy facility, additional processing is required. In addition to balers, SWSLs employ other processing equipment including shredders, pelletizers and compactors. A shredder reduces the volume and increases the uniformity of the residual solid waste for use at a waste-to-energy facility. Pelletizers receive shredded waste and extrude it under high pressure to form small pellets. The pellets may then be used as fuel for a furnace or power plant.

Compactors are typically used to process residual solid waste bound for landfills. Compactors are large balers that compress either shredded or un-shredded waste into large bales weighing up to 29 tons. The compactor loads the bales into trailers for transport to a disposal site, which ensures the maximum legal load to reduce hauling costs.

SWSLs operated by municipalities have had a dramatic effect on reducing the reliance on landfills. The use of SWSLs has in many states, been mandated by legislation requiring a significant reduction in landfill disposal. California Assembly Bill 939 requires every city and county in California to reduce its landfill waste stream 25% by 1995 and 50% by the year 2000. Similar mandates are now law in many other states. The employment of SWSLs has greatly assisted municipalities in achieving these goals.


Compliance Benefit: Solid waste sorting lines remove recyclables from a raw solid waste stream and therefore, help facilities to meet the requirements under Executive Order 13101 requiring executive agencies (e.g. DOD) to incorporate waste prevention and recycling in their daily operations.

Use of a loader may increase fuels on site which may increase a facility’s need to comply with SARA (40 CFR 355 and EO 12856) reporting requirements and SPCC (40 CFR 112) issues. In addition, conveyor liners, automated sorting systems, balers, crushers, shredders and pelletizers will increase electricity consumption. Under EO 12902, federal facilities are required to reduce energy consumption.

The compliance benefits listed here are only meant to be used as a general guideline and are not meant to be strictly interpreted. Actual compliance benefits will vary depending on the factors involved, e.g. the amount of workload involved.


Materials Compatibility:
Material compatibility issues are specific to the design of the SWSL. Most notably, materials must be inspected when received at the tipping floor to ensure that materials not compatible to the operation of the SWSL are not processed. The proper removal and treatment of hazardous materials or wastes is a necessity.


Safety and Health: Safety issues for operators working at an SWSL include the operation of power equipment, as well as eye, ear, respiratory and dermal protection. Therefore proper personal protective equipment including gloves, eye protection, respiratory protection, and hearing protection should be used. Operators should be specifically trained in the use of all machinery. Machinery should not be used if workers are intoxicated or on medication.

Consult your local industrial health specialist, your local health and safety personnel, and the appropriate MSDS prior to implementing this technology.


Benefits:
  • Saves landfill space by diverting recyclable materials.
  • Allows municipalities to meet mandated goals for the reduction of landfilled waste.
  • Income is generated from the sale of recyclables.
  • Cost savings in landfill tipping fees.
  • Conserves resources.


Disadvantages:
  • High capital cost.


Economic Analysis: The cost of the equipment and installation of an SWSL varies depending upon the size. A small SWSL non-automated system, including balers will cost on average from $500,000 to $700,000. A large system can cost $1,500,000 or more depending upon the equipment and degree of automation. When conducting an economic analysis for a new SWSL, it is critical that the amounts and types of materials processed, as well as the markets and finished specifications for these materials, be well defined. The market price for recyclables is volatile and as a consequence, predicting the long-term revenue obtained from a SWSL is difficult. Since there are no long-term markets in recyclables, operators of successful SWSLs must research markets on a frequent basis. The volatility of the marketplace makes it necessary for SWSL operators to avoid long-term contracts in order to stay on top of changing commodity prices and to not get locked into a price that has the potential of increasing. The recent high cost of landfill disposal has enhanced the economics of SWSLs.

The economic analysis presented below is for a successful SWSL located in the eastern United States. The facility is processing approximately 1000 tons per month of solid waste

Assumptions:

  • Monthly processing rate: 1,000 tons/month of solid waste
  • Recovered recyclables: 400 tons/month
  • Recovered waste to energy fuel: 200 tons/month
  • SWSL labor cost: $100/ton of solid waste
  • SWSL energy and maintenance cost: $30/ton of solid waste
  • SWSL transportation cost: $20/ton of solid waste
  • Recovered recyclable sale cost: $100/ton
  • Recovered waste to energy fuel sale cost: $40/ton
  • Landfill disposal cost: $25/ton
  • Landfill disposal/waste to energy labor cost: $80/ton
  • Landfill/waste to energy transportation cost: $25/ton

Annual Operating Cost Comparison for Diversion Through Solid Waste Sorting Lines and for Disposal

 
Diversion
Disposal
Operational Costs:    
Labor: $1,200,000 $960,000
Transportation: $240,000 $300,000
Waste Disposal: $120,000 $300,000
Energy/ Maintenance: $360,000 $0
Total Operational Costs: $1,920,000 $1,560,000
Total Recovered Income: $576,000 $0
Net Annual Cost/Benefit: -$1,344,000 -$1,560,000

Economic Analysis Summary

    Annual Savings for New Technology: -$216,000
    Capital Cost for Diversion Equipment/Process: $1,150,000
    Payback Period for Investment in Equipment/Process: N/A

Click Here to view an Active Spreadsheet for this Economic Analysis and Enter Your Own Values.


Approving Authority: Approval is controlled locally and should be implemented only after engineering approval has been granted. Major claimant approval is not required.Approval is controlled locally and should be implemented only after engineering approval has been granted. Major claimant approval is not required.


NSN/MSDS:
Product NSN Unit Size Cost MSDS*
None Identified $  

*There are multiple MSDSs for most NSNs.
The MSDS (if shown above) is only meant to serve as an example.

Points of Contact: Navy:
Mr. Wallace Eakes
Naval Facilities Engineering Service Center
1100 23rd Ave.
ESC 426
Port Hueneme, CA 93043-4370
Phone: (805) 982-4882
DSN: 551-4882
FAX: (805) 982-4832

Mr. Eugene Wang
Naval Facilities Engineering Service Center
1100 23rd Avenue
ESC 423
Port Hueneme, CA 93043-4370
Phone: (805) 982-4291
DSN: 551-4291
FAX: (805) 982-4832

Vendors: Mayfran International
P.O. Box 43038
Cleveland,  OH   44143
Phone: (440) 461-4100 
FAX: (440) 461-5565

  Norton Environmental
6200 Rockside Woods Blvd.
Independence,  OH   44131
Phone: (216) 447-0070 
FAX: (216) 447-5028

  General Kinematics Corporation
777 Lake Zurick Road
Barrington,  IL   60010
Phone: (847) 381-2240 
FAX: (847) 381-1376

  Sierra International Machinery, Inc.
Sierra International Machinery, Inc.
Bakersfield,  CA   93307
Phone: (805) 327-7073 
FAX: (805) 322-8759

  CP Manufacturing, Inc.
1428 McKinely Avenue
National City,  CA   91950
Phone: (619) 477-3175 
FAX: (619) 477-3426

  Duraquip, Inc.
P.O. Box 948
Tualatin,  OR   97062
Phone: (503) 639-9826 
FAX: (503) 684-7296

Sources: Mr. Eugene Wang, Naval Facilities Engineering Service Center, March 1999.
Mr. Bob Clinton, Mayfran International, May 1996.
Ms. Shiela Martin, State of California Department of Conservation, Division of Recycling, May 1996.
"The Medina County, Ohio, Central Processing Facility," Waste Age, August 1994.
"Equipping your MRF," World Wastes, February 1993.
"Equipping MRFs," World Wastes, November 1994.



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