Common E-Waste Materials Reference
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Electronic waste contains hundreds of different materials in complex assemblies. Understanding the composition, hazardous constituents, and typical Basel classifications of common e-waste materials helps with proper characterization, waste code selection, and facility matching. This reference provides technical details on the most frequently encountered e-waste materials in international trade.
Printed Circuit Boards (PCBs)
COMPOSITION:
- Base material: Fiberglass-reinforced epoxy resin (FR-4 most common)
- Copper traces and pads (12-20% by weight)
- Electronic components: Integrated circuits, resistors, capacitors, transistors
- Lead-based solder (pre-RoHS boards) or lead-free solder (post-RoHS)
- Gold, silver, palladium in connector pins and bond wires
- Tin, nickel plating on components and traces
- Brominated flame retardants in resin
HAZARDOUS CONSTITUENTS:
- Lead: 1-4% in solder joints (pre-RoHS);
- Brominated flame retardants: PBDEs, TBBPA in substrate
- Heavy metals: Cadmium in SMD resistors, mercury in older components
- Beryllium: In some connector pins and thermal pads
- Antimony trioxide: Flame retardant synergist
BASEL CLASSIFICATION:
- Y49 if intact boards without testing for hazardous characteristics
- A1181 if boards contain hazardous constituents exhibiting Annex III characteristics
- Y31 (lead) if lead solder present
- H-codes: H6.1 (acute poisonous), H11 (toxic delayed), H12 (ecotoxic)
- UN 3077 for transport if classified as environmentally hazardous
RECOVERY METHODS:
- Pyrometallurgical: Smelting in copper or precious metal refineries
- Hydrometallurgical: Chemical leaching to extract metals
- Mechanical: Shredding and separation (copper, precious metals, plastics)
- Direct refining: High-grade boards to precious metal refiners
- Typical destination facilities: Umicore (Belgium), Aurubis (Germany), Boliden (Sweden)
TYPICAL VALUES:
- Gold: 200-300 ppm (0.02-0.03%) in motherboards, higher in high-grade telecom boards
- Silver: 1,000-2,000 ppm (0.1-0.2%)
- Palladium: 100-150 ppm
- Copper: 12-20% by weight
- Economic value often justifies export costs
Cathode Ray Tube (CRT) Glass
COMPOSITION:
- Panel glass (screen): Lower lead content (1-3% PbO)
- Funnel glass (cone): Medium lead (18-25% PbO)
- Neck glass: Highest lead (25-30% PbO)
- Barium, strontium in panel glass (X-ray shielding)
- Phosphor coating on inner panel surface
HAZARDOUS CONSTITUENTS:
- Lead oxide: Average 3-4 kg per CRT monitor, 2-3 kg per CRT TV
- Barium compounds
- Cadmium in some phosphors
- Zinc, copper in phosphor materials
BASEL CLASSIFICATION:
- A2010: Glass waste from cathode-ray tubes (specific Annex VIII code)
- Y31: Lead; lead compounds
- H-codes: H6.1, H11, H12 (lead toxicity)
- Always classified as hazardous waste
- UN 3077 for transport
RECOVERY CHALLENGES:
- Limited markets due to CRT manufacturing decline
- Panel and funnel glass must be separated (different lead content)
- Lead smelters can process if properly prepared
- Glass-to-glass recycling nearly extinct (no new CRT production)
- Often ends up in hazardous waste landfill
- Exporters struggle to find accepting facilities
PROCESSING OPTIONS:
- Lead smelters: Recover lead, use silica in slag
- Stabilization/encapsulation: Immobilize lead for landfill
- Glass aggregate: Very limited applications due to leaching concerns
- Declining acceptance globally—many countries now refuse CRT imports
LCD and LED Displays
COMPOSITION:
- Liquid crystal display panel
- Backlight: CCFL (mercury) in older LCDs, LED in modern displays
- Glass substrates with indium tin oxide (ITO) coating
- Polarizing films
- Plastic housing and frame
- Driver circuit boards (contain precious metals)
HAZARDOUS CONSTITUENTS:
- Mercury: In CCFL backlights (3-5 mg per lamp, multiple lamps per display)
- Liquid crystals: Some formulations contain hazardous chemicals
- Indium: Rare earth element in ITO coating (not hazardous but valuable)
- Brominated flame retardants in plastic components
BASEL CLASSIFICATION:
- LCD with mercury backlights: Y29 (mercury), A1181
- LED displays (no mercury): Y49 if no other hazardous characteristics
- H-codes for mercury LCDs: H6.1, H11, H12
- Modern LED displays may qualify as non-hazardous if properly characterized
RECOVERY METHODS:
- Manual dismantling: Remove mercury lamps for separate processing
- Mechanical shredding: Plastic, metal, and glass separation
- Indium recovery: Specialized facilities extract indium from ITO
- Mercury lamp recycling: Separate specialized processors
MARKET TRENDS:
- Mercury LCD imports increasingly restricted
- LED displays more acceptable (no mercury)
- Indium recovery economically viable at scale
- Driver boards processed like PCBs for precious metals
Batteries
LEAD-ACID BATTERIES (MOST COMMON IN UPS, EQUIPMENT):
Composition:
- Lead plates (60-70% of weight)
- Sulfuric acid electrolyte (15-20%)
- Polypropylene case (5-10%)
- Lead alloys with antimony or calcium
Basel Classification:
- Y31: Lead; lead compounds
- Y34: Acidic solutions or acids in solid form
- A1160: Waste lead-acid batteries, whole or crushed
- H6.1, H8 (corrosive), H11, H12
- UN 2794 (wet filled) or UN 2800 (non-spillable) for transport
Recovery:
- Highly recyclable (>95% recycling rate)
- Lead smelters worldwide accept
- Plastic casings recovered and recycled
- Sulfuric acid neutralized or reprocessed
- Strong economic value—often paid for rather than charged disposal fee
LITHIUM-ION BATTERIES:
Composition:
- Cathode: Lithium cobalt oxide (LiCoO2), lithium manganese oxide, lithium iron phosphate
- Anode: Graphite
- Electrolyte: Lithium salts in organic solvents (flammable)
- Separator: Polymer membrane
- Steel or aluminum casing
Basel Classification:
- Y49 if installed in equipment
- May be A1180/A1181 if separated and damaged
- H3 (flammable liquid—electrolyte), H4.1 (flammable solid—lithium)
- UN 3480 (batteries alone) or UN 3481 (batteries in equipment) for transport
- Class 9 dangerous goods
Recovery:
- Pyrometallurgy: High-temperature smelting recovers cobalt, nickel, copper
- Hydrometallurgy: Chemical processing for lithium, cobalt recovery
- Direct recycling: Cathode material regeneration (emerging technology)
- Safety critical: Discharge required before processing, fire/explosion risk
NICKEL-CADMIUM (NiCd) BATTERIES:
Composition:
- Nickel oxide hydroxide cathode
- Cadmium anode
- Potassium hydroxide electrolyte
- Steel casing
Basel Classification:
- Y26: Cadmium; cadmium compounds
- A1170: Waste batteries containing cadmium
- H6.1, H11, H12 (cadmium highly toxic)
- Strictly regulated, import bans common
Recovery:
- Cadmium recovery in specialized facilities
- Nickel recovered for steel production
- Declining volumes as NiCd phased out in many applications
Plastics from E-Waste
COMPOSITION:
- ABS (acrylonitrile butadiene styrene): Most common in casings
- HIPS (high-impact polystyrene): Monitor and TV cases
- PC (polycarbonate): Clear components, optical media
- PC/ABS blends: Laptop cases, housings
- PP (polypropylene): Internal components, battery cases
- PVC (polyvinyl chloride): Cable insulation, some casings
HAZARDOUS CONSTITUENTS:
- Brominated flame retardants: PBDE, TBBPA (5-10% by weight in some plastics)
- Heavy metal pigments: Lead, cadmium in colored plastics
- PVC plasticizers: Phthalates (some toxic)
- Antimony trioxide: Flame retardant synergist
BASEL CLASSIFICATION:
- Clean sorted plastics: B3011 (Annex IX—non-hazardous)
- Mixed or contaminated plastics: Y49 or A1181 depending on characteristics
- Plastics with high brominated flame retardants: May be hazardous
- Growing restrictions under Basel plastic waste amendments
RECOVERY CHALLENGES:
- Mixed polymer types difficult to separate economically
- Brominated flame retardants complicate recycling
- Color sorting required for high-quality recycling
- Markets declining due to contamination concerns
- Often sent to energy recovery (incineration) rather than material recycling
PROCESSING OPTIONS:
- Mechanical recycling: Grinding, washing, pelletizing for reuse
- Chemical recycling: Depolymerization to monomers
- Energy recovery: Incineration with energy capture (R1)
- Pyrolysis: Thermal decomposition to oils and gases
- Many facilities avoid e-waste plastics due to flame retardant issues
Cables and Wiring
COMPOSITION:
- Copper conductors (40-60% by weight in power cables)
- Aluminum in some larger cables
- PVC insulation (most common)
- Polyethylene, rubber insulation (specialty cables)
- Steel armor in some power cables
HAZARDOUS CONSTITUENTS:
- PVC contains chlorine (releases HCl when burned)
- Lead in some cable sheathing (older cables)
- Brominated flame retardants in some insulation
- Generally low hazard if properly processed
BASEL CLASSIFICATION:
- B1115: Waste metal cables coated or insulated with plastics (Annex IX)
- Non-hazardous if free of lead and other hazardous materials
- Simplified procedures often available
- Good candidate for green list (OECD countries)
RECOVERY METHODS:
- Granulation: Shredding and density separation (copper from plastic)
- Wire stripping: Manual or mechanical removal of insulation
- Copper recovery: High purity copper for smelting or direct reuse
- Plastic insulation: Energy recovery or landfill
- High copper content makes cables economically attractive
Metal Components
FERROUS METALS (IRON, STEEL):
Sources: Casings, frames, shields, screws, springs
Classification:
- B1010: Metal wastes in metallic non-dispersible form (Annex IX)
- Non-hazardous if segregated and clean
- Simplified procedures
Recovery:
- Magnetic separation from shredded e-waste
- Direct to steel mills or scrap processors
- High recyclability, universal acceptance
- Low value per ton but high volumes
ALUMINUM:
Sources: Heat sinks, housings, connector shells, hard drive frames
Classification:
- B1010: Non-hazardous metal waste
- Often mixed with magnesium alloys
Recovery:
- Eddy current separation from e-waste streams
- Smelting to remove coatings and alloys
- Moderate value, readily recycled
COPPER:
Sources: Wiring, transformers, coils, heat pipes
Classification:
- B1010: Non-hazardous
- High value material
Recovery:
- Dense media separation, eddy current
- Direct to copper smelters or refineries
- High purity achievable
- Strong economic driver for recycling
Mercury-Containing Components
SOURCES:
- LCD backlights (CCFL tubes): 3-5 mg mercury per tube
- Mercury switches and relays: 1-3 grams per switch
- Mercury thermostats: Up to 3 grams
- Fluorescent tubes in scanners/copiers
BASEL CLASSIFICATION:
- Y29: Mercury; mercury compounds
- A1030: Wastes from production of mercury
- H6.1 (acute toxicity), H11 (chronic toxicity), H12 (ecotoxic)
- Strictly controlled—import restrictions common
PROCESSING:
- Manual removal before shredding critical
- Mercury distillation/recovery in specialized facilities
- Stabilization for disposal if recovery not viable
- Never shred equipment with mercury components intact
Practical Guidance
FOR WASTE CHARACTERIZATION:
- Know your material composition before classification
- PCBs with lead solder → A1181, Y31, H6.1/H11/H12
- CRT glass → Always A2010, Y31
- Modern LED displays without mercury → May be Y49 non-hazardous
- Lead-acid batteries → A1160, high value
- Clean sorted metals → B1010, simplified procedures
FOR FACILITY MATCHING:
- PCBs: Precious metal refiners, integrated smelters
- CRT glass: Lead smelters (declining acceptance)
- Batteries: Specialized battery recyclers
- Plastics: Energy recovery more likely than material recycling
- Cables: Granulators, copper processors
FOR MAXIMIZING VALUE:
- Segregation pays: Separate high-value from low-value materials
- PCB grading: High-grade (telecom, servers) vs. low-grade (consumer)
- Remove mercury components before export
- Clean sorted materials get better prices and easier approvals
- Mixed contaminated waste → lowest value, hardest to place
Common Errors
- Not identifying mercury in LCD backlights (leads to classification errors)
- Assuming all plastics are non-hazardous (brominated flame retardants make some hazardous)
- Mixing CRT glass with other glass (leads to rejection)
- Not testing lead content in solder (pre-RoHS assumption may be wrong)
- Claiming cables as non-hazardous without checking for lead sheathing
- Not segregating battery types (NiCd, Li-ion, lead-acid have different requirements)
- Underestimating precious metal content in high-grade PCBs
- Not considering plastic waste amendments when classifying plastic fractions