How can I recover the silver from my photo
processing waste?
The Center for Environmental Health and Safety (CEHS) does not
recover silver from photo processing waste. Use Tables 2 and 3 and
the following discussion to help you choose the best method for
your situation. (The information was taken from “Need For &
Efficiency of Silver Recovery, or Silver Sampling Faux Pas &
Fundamental Conclusions” presented at the 16th College and
University Hazardous Waste Conference on July 20, 1998 in New
Orleans, LA. The authors are
Susan M. Morgan
(Assistant Professor of Civil Engineering, SIUE), Erik A. Talley
(former Associate Director of the Center for Environmental Health
and Safety, SIUC), Mohammed Z. Rahman (former Graduate Assistant
in Civil Engineering, SIUE), and Keith E. Morgan (former Hazardous
Waste Technician in the Office of Environmental Health and Safety,
SIUE).)
Electrolysis, or electrolytic recovery, and metallic replacement
are the most common methods used for silver recovery from photo
processing wastewaters. During electrolysis, an electric current
reduces the silver-thiosulfate complex and plates almost pure
silver metal onto an electrode. If the unit is placed in-line and
closed-loop fixers are used, chemical use can be reduced by up to
50%. Efficiencies above 90% are easily obtainable when recovering
silver from black and white processing fixers. However, while
efficiencies approaching 90% are possible when recovering
bleach-fix and fixer solutions from color processing, higher
current densities, longer times, and pH adjustments are necessary
due to iron complexes present. In addition, over-extending the
electrolysis time or raising the current density can result in
lower efficiencies due to sulfide precipitation on the cathode. To
reduce concentrations below 5 mg/L, electrolysis must be followed
by another recovery method, such as metallic replacement or ion
exchange.
Metallic replacement makes use of the fact that iron is more
active than silver. Silver in solution will exchange with solid
iron through an oxidation-reduction reaction. Steel wool, iron
particles, or iron-impregnated resin are used as the iron source.
The iron is placed in a container referred to as a metallic
replacement cartridge (MRC), chemical recovery cartridge (CRC), or
silver recovery cartridge (SRC). One cartridge can recover more
than 95% of the silver from silver-rich solutions (such as fixer
and bleach-fix) while a series of two cartridges can recover more
than 99%. A series arrangement will also prevent breakthrough,
which occurs as small channels develop in the iron. However, for
flows less than 0.5 gallons of fixer per day, one canister is
adequate. Although low silver concentrations are removed with
metallic replacement, the iron catalyst will be consumed more
quickly due to the reduced protection from corrosion.
While precipitation, evaporation/distillation, ion exchange, and
reverse osmosis are potential recovery methods that would meet
many low discharge requirements, capital and operating costs
preclude them from use by most small generators. Precipitation can
be very efficient, generating a sludge with 99.9% or more of the
silver from silver-rich solutions, but it is not a common method
utilized to recover silver due to the chemicals and skilled
personnel required. Evaporation/distillation can concentrate
silver-rich solutions to between 8 and 30% of the original volume.
However, the residue is unusable for mixing fresh developer
solution, although it may be usable for making secondary
replenishers (such as bleach, fixer, and stabilizers). Ion
exchange works by attracting the negatively-charged silver
thiosulfate complex to positively-charged sites on the resin. The
resin can be regenerated with a concentrated solution or replaced.
However, ion exchange only works on dilute solutions, such as wash
waters (although wash baths can have concentrations as high as 200
mg/L), since high concentrations quickly saturate the resin.
Reverse osmosis uses pressure and a membrane to filter solutions,
removing up to 95% of salts from fixers. It results in a
concentrated silver stream that could be sent to a refiner. This
technology also works best on dilute solutions, achieving up to
90% efficiency. Electrowinning (used in the plating industry) is
also not used for silver recovery from photographic solutions
because it can decompose processing chemicals, resulting in fouled
equipment and hazardous odors.
How can I reduce the amount of silver waste I have to manage?
One option to eliminate silver waste in the photographic process
is to convert to electronic, or digital, technology. The SIUC
Department of Cinema and Photography eliminated approximately 5%
of their waste stream by using digital cameras, and the SIUC
Office of Printing and Duplicating reduced approximately 25% of
their waste. The SIUE University Graphics and Photographic Service
also does some digital work while the SIUE Print Shop changed 100%
to digital the summer of 1997.
Silver waste can also be reduced by using silver-free film, such
as diazo, vesicular, photopolymer, electrostatic, and
selenium-based.
Other recommendations made by the EPA include to:
-
follow manufacturers’ recommendations for pH
levels and stop bath use
-
replenish the fixer strength by adding ammonium
thiosulfate when necessary
-
keep the fixer covered when not being used to
prevent oxidation and minimize emissions
-
use floating covers on solution tanks
-
add ammonium thiosulfate to silver-contaminated
baths to extend the allowable buildup of silver
-
improve the efficiency of the wash bath by
keeping the water at 80 0F, adding ammonia to keep the pH above
4.9, and adding washing aids (salts)
-
recirculate the effluent from ion exchange units
-
use countercurrent rinsing
-
collect and reuse wash water
-
use squeegees to minimize chemical carryover
from stabilization
-
collect and reuse cleaners
-
control inventory to avoid disposal of
off-specification film and chemicals
-
store unused chemicals and paper away from heat
and light.
Who do I contact if I have questions or have hazardous waste
for off-site shipment?
Contact a member of
the CEHS
Laboratory and
Hazardous Waste Section at 618-453-7180 or
chemical@cehs.siu.edu if you have questions or
hazardous waste requiring collection for
off-site shipment.
|
Table 3. Comparison of silver recovery
methods. |
|
Recovery Method |
Advantages |
Disadvantages |
|
Electrolysis (In-line) |
- Obtain >90% pure silver
- Recirculate fixer
- Reduce chemical use£50%
- 70% and mixing labor
|
- Minimum of 5 gal/wk
- Used for fixers and high-silver
solutions only
- Can damage fixer if not properly
maintained
|
|
Electrolysis (Terminal) |
- Low refining costs
- Moderate capital costs
- Able to determine silver recovered
|
|
Evaporation
Distillation |
- Up to 90% waste reduction
|
- Moderate to high capital costs
-
Messy
sludges
|
|
Ion Exchange |
- 98 – 99.99% removal efficiency from
dilute solutions
|
|
|
Metallic Replacement |
- Available for all silver-rich
solutions
- Low capital costs
- Low maintenance
- 99% removal possible with 2 units
|
|
|
Precipitation |
- >99% consistent removal possible
- Moderate capital costs
-
Little
maintenance
|
- Higher smelting cost than
electrolytic
- Ongoing chemical usage
- Moderate to high operation costs
|
|
Reverse Osmosis |
- Up to 90% efficiency on dilute
streams
- No treatment chemicals required
|
- High capital costs
- Frequent maintenance required
- Works best on dilute solutions
- Large installations noisy
|