MICROALGAE ECOPHYSIOLOGY AND APPLICATIONS IN METAL IONS RECOVERY
Metal Recovery
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Transcript of Metal Recovery
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MATERIALS RECYCLING
AND RECOVERY
Derek FrayDepartment of Materials Science
and Metallurgy
University of Cambridge
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TOPICS TO BE COVERED
Physical separation of materials
Treatment of Electronic Scrap to recovercomponents and valuable constituents
Use of scrap PVC to treat metallic residues
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SORTING
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MAGNETIC SEPARATION
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Eddy Current Sorting
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Melting of Aluminium Scrap
STEELMAKING
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STEELMAKING
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MELTING OF LEAD SCRAP
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TREATMENT OF
ELECTRONIC SCRAP
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KEY POINTS
Exponential demand for electronicequipment
Short life of computers
Small percentage of computers find re-use
Most electronic scrap is either land-filled or
melted Legislation is likely to require
manufacturers to take back equipment
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QUANTITIES OF AVAILABLESCRAP
50,000 tonnes of PCB scrap generated in
the UK 300,000 tonnes of PCB scrap generated in
Europe
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PERCENTAGE RECYCLED
Only 15% of the 50,000 tonnes per annumis subjected to any form of recycling, theremainder being consigned to landfill
Approximately 60% of the 42,500 tonnesper annum is landfilled within the total
redundant equipment package A significant proportion is exported
illegally
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APPROXIMATE COMPOSITION OF
PCB ASSEMBLIES
Glass-reinforced polymer 70% Copper 16%
Solder 5%
Iron, ferrite (from transformer coils) 5%
Nickel 1%
Silver 0.1% Gold 0.025%
Palladium 0.01%
Other (bismuth, antimony, tantalum, etc)
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Component Wt.
(by%)
Value ()
(by kg)
Intrinsic Value
( per kg)
Gold 0.025 12509 3.13
Palladium 0.01 26961 2.70
Silver 0.1 253 0.252
Copper 16 4.093 0.655
Tin 3 5.101 0.153
Lead 2 0.669 0.014
Nickel 1 10.815 0.108
Aluminium 5 1.538 0.077
Iron 5 0.208 0.01
Zinc 1 1.793 0.02
Total 7.12/kg
Value of components ~ 1.5 /kg
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OVERALL AIM
1. Recover value of components
2. Minimise chance of loss of precious metal
3. Recover solder
4. Recover copper
5. Recover bromine
6. Predominantly low temperature process- high energyefficiency
7. Low waste volume
8. Environmentally friendly
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80
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0
10
20
30
40
50
60
70
80
0 100 200 300 400
Time (min)
a
.me
tal
/L
Solder
Cu
Dissolution of solder and copper with
HBF4/ 0.3 M Ti(IV) at 60 deg. C usingoxygen sparge.
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LEACHING RESULTS
Lead and tin dissolved in the same ratio as in the
solder
About 70 g/l of metal was obtained in the
fluoroboric acid Temperature of dissolution was 20 30oC
Dissolution of copper was negligible
After dissolution of the solder, the components
were simply removed and electronically tested
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Divided electrowinning cell (flow cell, laboratory scale)
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Variation of concentrations of Sn and Pb in electrolyte asa function of electrolysis time.
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ELECTRODEPOSITED SOLDER
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ELECTRODEPOSITED COPPER
LEACHING AND
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LEACHING AND
ELECTROWINNING OFPRECIOUS METALS
Precious metals were leached with
hydrochloric acid and nitric acid and thenelectrowon
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RELEASE OF BROMINE
Boards after leaching were simplycombusted in air at 600oC
The bromine and hydrogen bromide were
collected in caustic soda
About 3.5% of the boards were bromine
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P r in ted c i rc u i t boa r d s
S o ld er
rem ov a l
S o ld er( r e - u s e )
Co m pon ents
S tr ipp ed
c i r c u it b oa r d s
R e -use or pre c ious
m eta l s reco very
C o p p e rC o p p e r
r e c o v e r y
B rom iner e c o v e r y
I n e r t r e s id ue s
B r o m i n e
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ECONOMIC ASSESSMENT
Cost of plant to process 10000
tonnes/annum of PCBs is 3m
Profit per tonne of material treated 90
Value of recovered components has not be
included as the value of components
fluctuates considerably. It could be as highas 1500/tonne
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COMBINATION OF PVC ANDSTEEL SCRAP AND RESIDUES
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GENERAL CONCLUSIONS
Conventional and novel metallurgicalextraction techniques can be applied to therecycling of a variety of wastes
In some cases it is possible to combine twowaste materials together to give useful
products
There are many other opportunities whichcan be investigated