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Environmental Guidelines for Electroplating Industry
Industry Description and Practices
 

Electroplating involves the deposition of a thin protective layer (usually metallic) onto a prepared surface of metal, using electrochemical processes. The process involves pre-treatment (cleaning, degreasing, and other preparation steps), plating, rinsing, passivating, and drying. The cleaning and pre-treatment stages involve a variety of solvents (often chlorinated hydrocarbons, whose use is discouraged) and surface stripping agents including caustic soda and a range of strong acids, depending on the metal surface to be plated. The use of halogenated hydrocarbons for degreasing is not necessary as water based systems are available. In the plating process, the object to be plated is usually used as the cathode in an electrolytic bath. There are three main types of plating solutions: are acid or alkaline solutions and may contain complexing agents such as cyanides.


Waste Characteristics
Any or all of the substances used in electroplating (such as acidic solutions, toxic metals, solvents, and cyanides) can be found in the wastewater, either via rinsing of the product or due to spillage and dumping of process baths. The solvents and vapours from hot plating baths result in elevated levels of volatile organic compounds (VOCs) and in some cases, volatile metal compounds (when may contain chromates). Approximately 30 percent of the solvents and degreasing agents used can be released as VOCs when baths are not regenerated.

The mixing of cyanide and acidic wastewaters can generate lethal hydrogen cyanide gas and this must be avoided. The overall wastewater stream is typically extremely variable (1 liter to 500 liters per square meter of surface plated) but usually high in heavy metals (including cadmium, chrome, lead, copper, zinc, and nickel), cyanides, fluorides, and oil and grease, all of which are process dependent. Air emissions may contain toxic organics (such as trichloroethylene and trichloroethane).
Cleaning or changing of process tanks and the treatment of wastewaters can generate substantial quantities of wet sludges containing high levels of toxic organics and/or metals.


Pollution Prevention and Control
Plating involves different combinations of a wide variety of processes and there are many opportunities to improve upon the traditional practices in the industry. The following improvements should be implemented where possible:

Changes in Process
• Replace cadmium with high quality corrosion resistant zinc plating. Use cyanide-free systems for zinc plating where appropriate. In those cases where cadmium plating is necessary, use bright chloride, high alkaline baths or other alternatives. However, alternate complexing agents to cyanides may cause problems in wastewater treatment for they may result in the release of heavy metals.
• Use trivalent chrome instead of hexavalent chrome: acceptance of the change in finish needs to be promoted.

373 374 Electroplating Industry
• Give preference to water-based surface cleaning agents, where feasible, instead of organic cleaning agents, some of which are considered toxic.
• Regenerate acids and other process ingredients, whenever feasible.

Reduction in Drag-out and Wastage
• Minimize drag-out by effective draining of bath solutions from the plated part by measures such as making drain holes in bucket type pieces, if necessary.
• Allow dripping time of at least 10 to 20 seconds before rinsing.
• Use fog spraying of parts while dripping.
• Maintain the density, viscosity, and temperature of the baths to minimize dragouts.
• Place recovery tanks before the rinse tanks (which then provide make-up for the process tanks). The recovery tank provides for static rinsing with high dragout recovery.

Minimizing Water Consumption in Rinsing Systems
It is possible to design rinsing systems to achieve 50-99% reduction of traditional water usage. Testing is required to determine the optimum method for any specific process but proven approaches include:
• Agitation of rinse water or work pieces to increase rinsing efficiency.
• Multiple counter current rinses.
• Spray rinses (especially for barrel loads).

Management of Process Solutions
• Recycle process baths after concentration and filtration. Spent bath solutions should be sent for recovery and regeneration of plating chemicals, not discharged into wastewater treatment units.
• Recycle rinse waters (after filtration).
• Regularly analyze and regenerate process solutions to maximize useful life.
• Clean racks between baths to minimize contamination.
• Cover degreasing baths containing chlorinated solvents when not in operation to reduce losses. Spent solvents should be sent to solvent recyclers and the residue from solvent recovery properly managed (e.g., blending with fuel and burning in a combustion unit with proper controls for toxic metals).

 

Target Pollution Loads
A key parameter is the water use in each process and systems should be designed to reduce water use. Where electroplating is routinely performed on objects with known surface area in a production unit, water consumption of no more than 1.3 liters per sequence meter plated (L/m2) for rack plating and 10 L/m2 of surface area plated for drum plating should be achieved. The recommended pollution prevention and control measures can achieve the following target levels:
• Cadmium plating should be avoided. In cases where there are no feasible alternatives, a maximum cadmium load in the waste of 0.3 grams for every kilogram (kg) of cadmium processed is recommended.
• At least 90% of the solvent emissions to air must be recovered by the use of an air pollution control system such as a carbon filter.
• Ozone depleting solvents (such as chlorofluorocarbons and trichloroethane) are not to be used in the process.

 

Treatment Technologies
Segregation of waste streams is essential due to the dangerous reactions which can occur: strong acid/caustic reactions can generate boiling and splashing of corrosive liquids; acids can react with cyanides and generate lethal hydrogen cyanide gas. In addition, segregated streams that are concentrated are easier to treat.


Air Emissions
Exhaust hoods and good ventilation systems protect the working environment but the exhaust streams should be treated to reduce VOCs (using carbon filters which enable the reuse of solvents) and heavy metals to acceptable levels before venting to the atmosphere. Acid mists and vapours should be scrubbed with water before venting. In some cases, VOC levels of the vapours are reduced by 375 Electroplating Industry combustion (and energy recovery) after scrubbing adsorption, or other treatment methods.


Liquid Effluents
Cyanide destruction, flow equalization and neutralization, and metals removal are required, as a minimum, for electroplating plants. Individual design is necessary to address the characteristics of any specific plant but there are a number of common treatment steps. For small facilities, the possibility of sharing a common wastewater treatment plant should be considered. Cyanide destruction must be carried out upstream of the other treatment processes. If hexavalent chrome (Cr+6) occurs in the wastewater, then this is also usually pre-treated to reduce it to a trivalent form using a reducing agent (such as a sulphide) followed by precipitation and sedimentation/filtration.


The main treatment processes are equalization, pH adjustment for precipitation, flocculation, and sedimentation/filtration. The optimum pH for metal precipitation is usually in the range of 8.5-11 but this depends on the mixture of metals present. The presence of significant levels of oil and grease may affect the effectiveness of the metal precipitation process. Hence, the level of oil and grease affects the choice of treatment options and the treatment sequence. It is preferred that the degreasing baths be treated separately. Flocculating agents are sometimes used to facilitate the filtration of suspended solids. Pilot testing and treatability studies may be necessary. Final adjustment of pH and further polishing of the effluent may also be required. Modern wastewater treatment systems use ion exchange, membrane filtration, and evaporation to reduce the release of toxics and the quantity of effluent that needs to be discharged. These can be designed to have a closed system with a minor bleed stream.


Solid and Hazardous Wastes

Treatment sludges contain high levels of metals and these should normally be managed as hazardous waste or sent for metals recovery. Electrolytic methods may be used to recover metals. Sludges are usually thickened, dewatered, and stabilized using chemical agents (such as lime) before disposal which must be in an approved and controlled landfill. High costs of proper sludge disposal are likely to become an increasing incentive for waste minimization.

 

Emission Guidelines
Emission levels for the design and operation of each project must be established through the Environmental Assessment (EA) process, based on country legislation and the Pollution Prevention and Abatement Handbook as applied to local conditions. The emission levels selected must be justified in the EA and acceptable to MIGA.


The following guidelines present emission levels normally acceptable to the World Bank Group in making decisions regarding provision of World Bank Group assistance, including MIGA guarantees; any deviations from these levels must be described in the project documentation.
The guidelines are expressed as concentrations to facilitate monitoring. Dilution of air emissions or effluents to achieve these guidelines is unacceptable.
All of the maximum levels should be achieved for at least 95% of the time that the plant or unit is operating, to be calculated as a proportion of annual operating hours.


Air Emissions
A 90% recovery of the quantity of VOCs released from the process is required. 376 Electroplating Industry


Liquid Effluents
Electroplating plants should use closed systems where feasible or attain the following effluent levels.

Effluents from the Electroplating Industry Parameter

Maximum value milligrams per liter (mg/L)

pH

7 - 10

Total suspended solids

25

Oil and grease

10

Arsenic

0.1

Cadmium

0.1

Chromium (hexavalent)

0.1

Chromium (total)

0.5

Copper

0.5

Lead

0.2

Mercury

0.01

Nickel

0.5

Silver

0.5

Zinc

2

Total metals

10

Cyanides (free)

0.2

Fluorides

20

Trichloroethane

0.05

Trichloroethylene

0.05

Phosphorus

5

 

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