Industry Overview
The electronics industry, compared to other industries, has been viewed as “clean” in terms of its environmental impact. None the less, the chemicals used in the manufacture of electronic parts and components, and the waste generated, create significant environment issues that must be addressed on a global scale due to the size of the electronics industry. The wastes and by-products derived from the manufacture of printed wiring boards (PWBs), printed circuit boards (PCBs) and semiconductors are areas of interest that the electronic industry has vigorously pursued in terms of pollution prevention, treatment technology and recycling/reclamation techniques.
To a large degree, the incentive to control the environmental footprint of electronic processes has migrated from an environmental impetus to a financial domain. Due to the costs and liabilities associated with hazardous waste and emissions, the electronics industry has aggressively implemented and developed environmental controls that have greatly reduced the impact of its by-products and waste. In addition, the electronics industry has taken a proactive approach to incorporate environmental goals, tools and techniques into its environmentally conscious businesses. Examples of this proactive approach are the phase-out of CFCs and perfluorinated compounds and the development of “environmentally friendly” alternatives, as well as the emerging “design for the environment” approach to product development.
The manufacture of PWBs, PCBs and semiconductors requires the use of a variety of chemicals, specialized manufacturing techniques and equipment. Due to the hazards associated with these manufacturing processes, the proper management of chemical by-products, wastes and emissions is essential to assure the safety of the industry’s employees and the protection of the environment in the communities in which they reside.
Table 1, table 2 and table 3 present an outline of the key by-products and wastes that are generated in the manufacturing of PWBs, PCBs and semiconductors. In addition, the tables present the main types of environmental impact and the generally accepted means of mitigation and control of the waste stream. Primarily, the wastes that are generated affect industrial wastewater or the air, or become a solid waste.
Table 1. PWB waste generation and controls
Process steps |
Hazardous |
Environmental |
Controls1 |
Material |
None |
None |
None |
Stack and pin |
Heavy/precious metals |
Solid waste2 |
Recycle/reclaim |
Drilling |
Heavy/precious metals |
Solid waste2 |
Recycle/reclaim |
Deburr |
Heavy/precious metals |
Solid waste2 |
Recycle/reclaim |
Electroless |
Metals |
Wastewater |
Chemical precipitation |
Imaging |
Solvents |
Air |
Adsorption, condensation or |
Pattern plating |
Corrosives |
Wastewater/air |
pH neutralization/air scrubbing |
Strip, etch, strip |
Ammonia |
Air |
Air scrubbing (adsorption) |
Solder mask |
Corrosives |
Air |
Air scrubbing (adsorption) |
Solder coating |
Solvents |
Air |
Adsorption, condensation or |
Gold plating |
Corrosives |
Air |
Air scrubbing (adsorption) |
Component |
Solvents |
Air |
Adsorption condensation or |
1. Use of mitigation controls depends upon discharge limits in the specific location.
2. A solid waste is any discarded material regardless of its state.
Table 2. PCB waste generation and controls
Process steps |
Hazardous |
Environmental |
Controls |
Cleaning |
Metals (lead) |
Wastewater |
pH neutralization, chemical |
Solder paste |
Solder paste (lead/tin) |
Solid waste |
Recycle/reclaim |
Adhesive |
Epoxy glues |
Solid waste |
Incineration |
Component |
Plastic tapes, reels and tubes |
||
Adhesive cure and |
|||
Fluxing |
Solvent (IPA flux) |
Solid waste |
Recycle |
Wave soldering |
Metal (solder dross) |
Solid waste |
Recycle/reclaim |
Inspection and |
Metal |
Solid waste |
Recycle/reclaim |
Testing |
Scrapped populated |
Solid waste |
Recycle/reclaim |
Reworking and |
Metal (solder dross) |
Solid waste |
Recycle/reclaim |
Support |
Metal |
Solid waste |
Recycle/incineration |
Table 3. Semiconductor manufacturing waste generation and controls
Process steps |
Hazardous |
Environmental |
Controls |
Lithography/etching |
Solvents |
Solid waste |
Recycle/reclaim/incineration |
Oxidation |
Solvents |
Solid waste |
Recycle/reclaim/incineration |
Doping |
Poison gas (arsine, |
Air |
Substitution with liquid |
Chemical vapour deposition |
Metals Corrosives |
Solid waste |
Incineration |
Metallization |
Solvents |
Solid waste |
Incineration |
Assembly and testing |
Solvents |
Solid waste |
Recycle/reclaim/incineration |
Cleaning |
Corrosives |
Wastewater |
pH neutralization |
The following are generally accepted means of mitigating emissions in the PWB, PCB and semiconductor industries. The controls of choice will vary according to engineering capabilities, regulatory agency requirements and the specific constituents/concentrations of the waste stream.
Wastewater Control
Chemical precipitation
Chemical precipitation is generally used in the removal of particulate or soluble metals from wastewater effluents. Since metals do not naturally degrade and are toxic at low concentrations, their removal from industrial wastewater is essential. Metals can be removed from wastewater by chemical means since they are not very soluble in water; their solubilities depend upon the pH, metal concentration, type of metal and the presence of other ions. Typically, the waste stream requires pH adjustment to the proper level to precipitate out the metal. The addition of chemicals to wastewater in an effort to alter the physical state of dissolved and suspended solids is required. Lime, caustic and sulphide precipitation agents are commonly used. The precipitating agents facilitate the removal of dissolved and suspended metals by coagulation, sedimentation or entrapment within a precipitate.
A result of chemical precipitation of wastewater is the accumulation of sludge. Therefore, dewatering processes have been developed to reduce the weight of the sludge by means of centrifuges, filter presses, filters or drying beds. The resultant dewatered sludge can then be sent off for incineration or landfill.
pH neutralization
pH (the hydrogen-ion concentration or acidity) is an important quality parameter in industrial wastewater. Due to the adverse effects of pH extremes in natural waters and on sewage treatment operations, the pH of industrial wastewater must be adjusted prior to discharge from the manufacturing facility. Treatment occurs in a series of tanks that are monitored for the hydrogen-ion concentration of the wastewater effluent. Typically, hydrochloric or sulphuric acid is used as neutralizing corrosives, and sodium hydroxide is used as a neutralizing caustic. The neutralizing agent is metered into the wastewater effluent to adjust the pH of the discharge to its desired level.
Adjustment of pH is often required prior to the application of other wastewater treatment processes. Such processes include chemical precipitation, oxidation/reduction, activated carbon sorption, stripping and ion exchange.
Solid Waste Control
Materials are a solid waste if they are abandoned or discarded by being disposed of; burned or incinerated; or accumulated, stored or treated before or in lieu of being abandoned (US Code of Federal Regulation 40, Section 261.2). Hazardous waste generally exhibits one or more of the following characteristics: ignitability, corrosivity, reactivity, toxicity. Depending upon the characteristic of the hazardous material/waste, various means are used to control the substance. Incineration is a common treatment alternative for solvent and metal wastes generated during PWB, PCB and semiconductor manufacturing.
Incineration
Incineration (afterburner) or thermal destruction has become a popular option in handling ignitable and toxic wastes. In many instances, ignitable wastes (solvents) are used as a fuel source (fuel blending) for thermal and catalytic incinerators. Proper incineration of solvents and toxic wastes provides complete oxidation of the fuel and converts combustible material to carbon dioxide, water and ash, thereby leaving no liabilities associated with residual hazardous waste. The common types of incineration are thermal and catalytic incinerators. The selection of the type of incineration method is dependent upon the combustion temperature, fuel characteristics and residence time. Thermal incinerators operate at high temperatures and are widely used with halogenated compounds. Types of thermal incinerators include rotary kiln, liquid injection, fixed-hearth, fluidized bed and other advanced design incinerators.
Catalytic incinerators oxidize combustible materials (e.g., VOCs) by injecting a heated gas stream through a catalyst bed. The catalyst bed maximizes surface area, and by injecting a heated gas stream into the catalyst bed combustion can occur at a lower temperature than thermal incineration.
Air Emissions
Incineration is also used in control of air emissions. Absorption and adsorption are used as well.
Absorption
Air absorption is typically used in the scrubbing of corrosive air emissions, by passing the contaminant through and dissolving it in a non-volatile liquid (e.g., water). The effluent from the absorption process is typically discharged to a wastewater treatment system, where it undergoes pH adjustment.
Adsorption
Adsorption is the adherence (by means of physical or chemical forces) of a gas molecule to the surface of another substance, called an adsorbent. Typically, adsorption is used to extract solvents from an air emission source. Activated carbon, activated alumina or silica gel are commonly used adsorbents.
Recycling
Recyclable materials are used, reused or reclaimed as ingredients in an industrial process to make a product. Recycling of materials and waste provides environmental and economic means of effectively addressing specific types of waste streams, such as metals and solvents. Materials and wastes can be recycled in-house, or secondary markets may accept recyclable materials. The selection of recycling as an alternative for wastes must be evaluated against financial considerations, the regulatory framework and available technology to recycle the materials.
Future Direction
As the demand for pollution prevention increases and industry seeks cost-effective means to address chemical use and waste, the electronics industry must evaluate new techniques and technologies to improve the methods for hazardous-materials handling and waste generation. The end-of-pipe approach has been replaced by design for the environment techniques, where environmental issues are addressed over the full life cycle of a product, including: material conservation; efficient manufacturing operations; the use of more environmentally friendly materials; recycling, regeneration and reclamation of waste products; and a host of other techniques that will assure a smaller environmental impact for the electronics manufacturing industry. One example is the large amount of water that is used in the many rinsing and other processing steps in the microelectronics industry. In water-poor areas, this is forcing the industry to find alternatives. However, it is essential to make sure that the alternative (e.g., solvents) does not create additional environmental problems.
As an example of future directions in the PWB and PCB process, table 4 presents various alternatives for creating more environmentally sound practices and preventing pollution. Priority needs and approaches have been identified.
Table 4. Matrix of priority needs
Priority need (decreasing |
Approach |
Selected tasks |
More efficient use, |
Extend life of electrolytic and |
Research to extend baths. |
Reduce solid waste generated |
Develop and promote |
Develop infrastructure to |
Establish better supplier |
Promote supplier, |
Develop a model hazardous |
Minimize the impact of |
Reduce lead solder use when |
Change specifications to accept |
Use additive processes that |
Develop simplified, |
Collaborate on projects to |
Eliminate hole smear in PWB |
Develop no-smear resins or |
Investigate alternative |
Reduce water consumption |
Develop water use |
Modify specifications to reduce |
Source: MCC 1994.