Life Cycle Management of Municipal Solid Waste:

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Life Cycle Management of Municipal Solid Waste: Perspectives and Tradeoffs Keith Weitz May 29, 2008 RTI International is a trade name of Research Triangle Institute 3040 Cornwallis Road P.O. Box 12194 Research Triangle Park, North Carolina, USA 27709 Phone 919-541-6973 Fax 919-541-7155 e-mail kaw@rti.org 1

RTI International RTI is an independent, non-profit research organization formed in 1958 and dedicated to improving the human condition. RTI s main areas of research include: Health Sciences Environmental Sciences Education and Training Social and Economic Development Advanced Technology 2

NPR s All Things Considered: May 4, 2007 If I'm concerned about global warming what should I do with my banana peel? Possible options: Landfill Compost backyard dedicated facility Waste-to-energy What if I m concerned about cost, energy conservation, and/or sustainability? 3

Quick Points on Municipal Solid Waste There is a lot generated and disposed even after aggressive recycling. 300 5 It s a mix of different materials, not homogeneous. It has energy value (perhaps 3,000 to 5,000 btu/lb on average). It is a local burden and/or resource. Million Metric Tons 250 200 150 100 50 0 1960 1970 1980 1990 2000 2005 U.S. Waste Generation 4 3 2 1 0 Pounds/Person/Day Total Per Capita It stinks 4

California Organics Waste Stream Characterization About 40 million tons of organics are disposed statewide. Organics breakdown: 70% carbon-based organics 30% is readily compostable 21% is paper 15% is food Regional characterization of organics being developed. Branches Leaves/Grass Food Plastic Other Organics Paper Readily Compostable Organics Other Carbon-based Organics Inorganics Lumber 5

Presentation Outline Introduction of the application of the life cycle concept to waste management. Review of waste management options: Energy producers: Landfill Waste-to-energy Energy savers: Recycling Composting Summary of life cycle tradeoffs. 6

Life Cycle Assessment A systems analysis, not isolated operations. Considers upstream and downstream burdens. Multi-media and multipollutant. Main components: Inventory Analysis Impact Assessment Interpretation 7

Life Cycle of Solid Waste Collection Composting Landfill Recycling Waste-to- Energy Ash Landfill Compost Product End Use Remanufacturing Facility 8

Life Cycle Process Boundaries Energy Materials Solid Waste Waste Management Activity/Operation Products Energy Air Emissions Water Pollution Residual Waste 9

Life Cycle GHG Emission Boundaries for Solid Waste Management 10

Landfill Designed and operated according to Federal regulations. Conventional, bioreactor, and ash landfill design types. Different gas management options: Venting Collection and flaring Collection and utilization for energy recovery 11

US Federal MSW Landfill Standards Location restrictions. Composite liners requirements. Leachate collection and removal system requirements. Operating practices. Groundwater monitoring requirements requires testing. Closure and postclosure care requirements. Corrective action provisions for control and clean up of landfill releases to meet groundwater protection standards. Financial assurance for environmental protection during closure and post-closure care. 12

Landfill Leachate Collection and Treatment: Offsite or Onsite Offsite Treatment Leachate Collection System Onsite Treatment 13

Landfill Gas Collection and Management: Flare or Energy Recovery Flare Energy Recovery Landfill Gas Collection System 14

Landfill Burdens and Benefits Life Cycle Burdens Energy and emissions associated with material inputs (e.g., liner) Energy and emissions associated with landfill operation Life Cycle Benefits Energy recovery and offset of utility sector emissions Revenue from sale of energy Long term carbon storage Landfill gas emissions Energy and emissions associated with leachate collection and treatment 15

Landfill Gas Collection Efficiency Landfill gas contains about 50% methane which is a potent greenhouse gas. Gas collection and control can greatly reduce methane emissions. Assumed gas collection efficiency can significantly impact carbon emissions. Annual Carbon Emissions (MTCE) 70,000 60,000 50,000 40,000 30,000 20,000 10,000 0 Landfill (vent) Landfill (flare) Landfill (energy) 16

Waste-to-Energy Systems Thermal Systems: Mass Burn Gasification Pyrolysis Plasma Arc Non-Thermal Systems: Anaerobic digestion Hydrolysis (fermentation) 17

Mass Burn Technology Well proven technology for MSW. Minimum waste preparation required. Designed to meet Federal, State and Local environmental regulations. Higher capital cost. Reduces waste volume by 90%. Metals can be recovered for recycling. Ash can be reused or landfilled. 18

Mass Burn WTE Plant: Water and Air Pollution Control Systems Wastewater Modern Mass Burn WTE Plant Baghouse 19

New Emerging Waste Management Technologies Many new and emerging waste technologies are being developed and marketed to communities. Cost and environmental performance of new and emerging waste treatment technologies is uncertain. Better understanding of all issues associated with adopting new waste treatment technologies is needed. Schematic of Waste Gasification 20

Waste-to-Energy Burdens and Benefits Life Cycle Burdens Energy and emissions associated with facility operation Energy and emissions associated with transport of recovered metals to remanufacturing plants Energy and emissions associated with transport of ash to landfill Energy and emissions associated with ash disposal Life Cycle Benefits Diversion of MSW from landfills Energy production and offset of utility sector emissions Metals recovery and recycling Revenue from sale of energy and recyclables 21

Net Total Energy Consumption for WTE and Landfill Options 1,000,000 Annual Energy Consumption (MBTU 0-1,000,000-2,000,000-3,000,000-4,000,000-5,000,000 WTE Landfill (vent) Landfill (flare) Landfill (energy) -6,000,000 22

Net Total Life Cycle Carbon Emissions for WTE and Landfill Options 500,000 Annual Carbon Emissions (MTCE) 400,000 300,000 200,000 100,000 0-100,000 Landfill - Vent Landfill - Flare Landfill - Energy WTE -200,000 23

Components of WTE Carbon Balance 30,000 20,000 10,000 MTCE 0-10,000 Net Total WTE Plant Electricity Offset Ash Landfill Ferrous Offset -20,000-30,000-40,000 24

WTE Electricity Production and Assumed Utility Offset The mix of fuels used to produce electricity varies throughout the U.S. The fuel(s) displaced by WTE can significantly impact results of an environmental analysis. 25

Recycling Designed to accepted different types of material: Mixed MSW Commingled recyclables Presorted recyclables Automated or manual Market for recycled materials are regional and fluctuate. 26

Recycling Burdens and Benefits Life Cycle Burdens Energy and emissions associated with separate collection Energy and emissions associated with MRF operation Energy and emissions associated with transportation of materials to remanufacturing Life Cycle Benefits Diversion of MSW from landfills Conservation of energy and virgin resources Revenue from sale of recyclables Forest carbon storage associated with paper recycling 27

Composting Designed to accepted different types of material: Organics only Mixed MSW Highly automated in-vessel to less automated windrow and aerated static pile designs. Markets for compost product are regional and dependant on product quality. 28

Composting Burdens and Benefits Life Cycle Burdens Energy and emissions associated with separate collection Energy and emissions associated with compost operation Energy and emissions associated with for transportation of compost product and residuals Life Cycle Benefits Diversion of MSW (organics) from landfills Potential for offset of other products (fertilizer, etc.) Revenue from sale of compost product Soil carbon storage 29

Summary of Life Cycle Tradeoffs Landfills and WTE are well established and tested, accept unprocessed waste, have pollution control requirements, and can recover significant amounts of energy from waste. Recycling and composting typically require separate collection and can save significant energy by offsetting upstream production activities. Landfill has generally been the cheapest option while WTE typically the most expensive option, and recycling and composting typically fall inbetween. WTE most efficient at producing energy while recycling most efficient at saving energy. WTE, recycling, and composting all avoid landfill methane generation. Materials and energy recovery create significant (upstream) benefits. 30

Back to the NPR Question: What should I do with my banana peel? Backyard composting perhaps the best, but all options are pretty good Answers are typically site-specific and depend on values: waste management facility design and operation cost versus GHG emission reductions local versus global impacts What about other organic and inorganic materials in the waste? glass plastics metals paper yard waste 31

Take Home Thoughts Municipal solid waste can provide feedstock for bioenergy production but perhaps challenging to use. All waste management options cost money, consume energy, and create environmental burdens. Waste management options can create significant energy related benefits: Energy savings (recycling, composting) Energy production (LFG to energy, WTE) Where is the tipping point between energy consumption and energy savings/production? Energy savings/production from waste can also produce significant savings of GHG emissions. Source reduction is perhaps a win-win option. 32

Thank You Keith A. Weitz RTI International 3040 Cornwallis Road RTP, NC 27709 Ph: 919-541-6973 Fax: 919-541-7155 Email: kaw@rti.org Visit our web site: https://webdstmsw.rti.org 33