LESSON 2: CHARACTERISTICS AND QUANTITY OF MSW
Goals Determine why quantification is important Understand the methodology used to quantify MSW Become aware of differences among global production rates Understand factors affecting waste generation rates Become familiar with per capita generation rates
Goals, Cont’d Explain why it is important to characterize MSW. Become familiar with MSW descriptors. Understand the methods used to characterize MSW Describe the physical, chemical, and biological properties associated with MSW. Perform calculations using waste composition and properties.
RCRA Subtitle D Wastes MSW Household hazardous wastes Municipal sludge Non-hazardous industrial wastes Combustion ash SQG hazardous waste Construction and Demolition debris Agricultural wastes Oil and gas wastes Mining wastes
MSW - RCRA Definition Durable goods Non-durable goods Containers/Packaging Food wastes Yard wastes Miscellaneous inorganics
MSW - Textbook Definition Mixed household waste recyclables household hazardous waste commercial waste yard waste litter bulky items construction & demolitions waste
What are the sources of RCRA Subtitle-D Wastes? Residential Commercial Institutional Industrial Agricultural Treatment Plants Open Areas (streets, parks, etc.)
What is the Nature of RCRA Subtitle-D Wastes? Organic Inorganic Putrescible Combustible Recyclable Hazardous Infectious
Terminology Generated Waste = Disposed (Collected) Waste + Diverted Waste
Importance of Generation Rates Compliance with Federal/state diversion requirements Equipment selection, Collection and management decisions Facilities design
Florida MSW Per Capita Generation Rate
Landfills Recycle Incineration
Factors affecting generation Rates Source reduction/recycling Geographic location Season Home food waste grinders Collection Frequency GNP trend Population increase Legislation Public attitudes Per capita income Size of households Population density Pay As You Throw Programs
Waste Composition Studies
Methodology Development Study Planning Sample Plan Sampling Procedure Data Interpretation
Sample Plan Load Selection Number of Samples
Sampling Procedure Vehicle Unloading Sample Selection and Retrieval Container Preparation Sample Placement Sorting
Waste contents are unloaded for sorting
Appropriate mass of material is selected randomly
Each load is separated manually by component example - Wood, concrete, plastic, metal, etc.
Each component is weighed and weights recorded
Components are separated
Data Interpretation Weighted Average based on Generator Source Composition/Distribution Contamination Adjustment
Specific Weight Values lb/yd 3 as delivered Function of location, season, storage time, equipment used, processing (compaction, shredding, etc.)
Moisture content (MC) Weight or volume based –Weight: wt. of water/sample wt. MC wet = water/(water+solids) MC dry = water/solids –Volume: vol. of water/sample volume
Chemical Composition Used primarily for combustion and waste to energy (WTE) calculations but can also be used to estimate biological and chemical behaviors Waste consists of combustible (i.e. paper) and non-combustible materials (i.e. glass)
Proximate Analysis Loss of moisture (temp held at 105 C) Volatile Combustible Matter (VCM) (temp increased to 950 C, closed crucible) Fixed Carbon (residue from VCM) Ash (temp = 950 C, open crucible)
Ultimate Analysis Molecular composition (C, H, N, O, P, etc.) Table in notes
Typical Data on the Ultimate Analysis - Example Food Wastes –Carbon: 48% –Hydrogen: 6.5% –Oxygen: 37.6% –Nitrogen: 2.6% –Sulfur: 0.4% –Ash: 5%
Energy Content Models are derived from physical composition and from ultimate analysis Determined through lab calculations using calorimeters Individual waste component energy contents
Empirical Equations Modified Dulong formula (wet basis): BTU/lb = 145C +610(H2-02/8)+40S + 10N Model based on proximate analysis Kcal/kg = 45B - 6W B = Combustible volatile matter in MSW (%) W = Water, percent weight on dry basis