| EP3 - Pollution Prevention Assessment for a Metal Finishing Facility | A Developing Country | - | CP Audit |
MANUFACTURE OF FABRICATED METAL PRODUCTS # 1
Background
This facility is an electroplating unit that performs zinc, nickel, brass, and chrome plating. Seventy percent of production is comprised of brass articles. The facility operates with 23 workers who work in a single 8-hour shift, 300 days a year. Approximately 15 m2 of metal surface is finished per day.
Facility operations can be divided into five main steps:
| polishing, | |
| cleaning, | |
| racking, | |
| metal finishing, and | |
| gilding. |
Polishing paste is applied to stationary belt sanders to provide the necessary abrasion. The parts are then polished with the sanders. Dust generated by the polishing process is collected by vacuums connected to each machine.
Prior to metal finishing, many parts are cleaned in a vapor degreaser that uses trichloroethylene (TCE) to remove grease and other impurities. Parts removed from the degreaser are dried with paper towels.
The facility electroplates many different kinds of parts. Several parts are hung on special racks that are constructed specifically to handle the part. Other pieces are plated in baskets that are placed directly in the solutions.
The metal finishing line consists of washing tanks, rising tanks, and nickel and chrome plating and recuperation baths. A copper cyanide bath is located across from the line and is used to plate zamak before it is plated to nickel and chrome. All plating is manual. Times are not exact, and there considerable variation in soaking times among different parts and different workers.
Before gilding, parts are rinsed in special rinse baths. They are then immersed in gilding solution for less than a minute.
At the time of the assessment, there were a number of pollution problems including,
| polishing debris, | |
| the use of organic solvents for degreasing, | |
| acid dip contamination, | |
| inefficient cyanide metal finishing, | |
| unnecessary chrome and nickel waste, and | |
| excessive water use. |
The objective of cleaner production assessment was to propose a program of pollution prevention that would:
| reduce the quantity of toxics, raw materials, and energy used in the manufacturing process, thereby reducing pollution and worker exposure, | |
| demonstrate the environmental and economic value of pollution prevention methods to the metal finishing industry, and | |
| improve operating efficiency and product quality. |
The assessment was performed by an EP3 team comprised of an expert in metal finishing and a pollution prevention specialist.
Cleaner Production Principle
Process / product modification; Housekeeping; New technology; Recovery, Reuse and Recycle; Material substitution
Cleaner Production Application
Overall, the assessment identified 18 pollution prevention opportunities at this facility. Recommendations for pollution prevention include,
| replacing the solvent degreaser with an alkaline cleaner, | |
| improving process solution monitoring, and | |
| capturing and returning 100 percent of chromium dragout to the process solution. |
Recommended Pollution Prevention Opportunities:
Polishing:
Solvent degreasing:
Alkaline cleaning:
Acid dip (10% sulfuric):
Acid dip depassivation of nickel:
Eliminate this process step, since cleaner is adequate.
Acid dip mixed acid stripper:
Replace with solutions in smaller tanks, and practice segregation and recovery.
Copper cyanide:
Improved process control and solution monitoring
Cyanide brass metal finishing:
Improved process control and solution monitoring
Chrome metal finishing:
Rinsing effectiveness:
Add agitation and sprays; control water use and reduce water use.
Polishing debris:
As currently performed, the polishing process leaves considerable debris (consisting of a mixture of polishing compound and solids from the polishing wheel) inside the pieces. These deposits cannot be removed by scraping or wiping.
To alleviate this problem, the facility can take following steps.
| Reducing the amount of polishing compounds used will reduce the amount of debris. | |
| Removing visible residue will allow less debris to harden on the pieces. | |
| Reducing the time between buffing and cleaning will also allow less debris to harden on the pieces. | |
| Employing a polishing compound that is compatible with alkaline cleansers will improve the efficiency of the cleaning process (along with recommendations outlined in the next section). |
Degreasing:
The facility currently employs the chlorinated solvent TCE to degrease parts. TCE is highly toxic and chemically reactive, and has been linked to liver cancer and ozone depletion. Parts can be cleaned equally well, or better, through the use of aqueous alkaline cleaners. Thus, the facility can greatly reduce its environmental impact and improve product quality by implementing an alkaline cleaning system. Further, the alkaline system cost effective than the TCE system.
Acid Dips:
In this facility's plating process, an acid dip (usually 10 percent sulfuric acid) is used to remove any oxides that may have developed on the brass or steel surface. With time, copper and organic contamination accumulates in the acid bath. If more than 300 mg/l of copper is present in the acid dip, the bath can cause adhesion problems for the steel substrate. Further, copper contamination also impacts the nickel metal finishing solution. While the facility utilises nickel depassivation to remove the copper contamination, it is not efficient, wasting nickel, brightener, and energy.
Separate acid dips for steel and brass substrates will improve the quality of both the steel substrate cleaning, and the nickel metal finishing solution, and, hence, reduce the number of rejects the facility produces.
Cyanide Metal finishing:
Cyanide metal finishing cannot be eliminated at this facility because the known non-cyanide alkaline alternatives do not function well in this application. However, improved process control and solution monitoring could enhance product quality, and, hence, reduce the number of rejects the facility produces.
Nickel and Chrome Waste:
Currently, the facility purifies the nickel bath six times per year.
Water Use:
Wastewater is generated in significant volumes from the facility's rinse steps. Some fairly simple changes can be made that will reduce water use by 25 percent. The use of air or solution agitation would increase the efficiency of the rinses, and reduce the frequency of changes. Spray rinses would also be more efficient than the current practice. Lastly, water inputs should be installed with switches that turn off the inputs after a set period of inactivity.
Environmental and Economic Benefits
| Costs | Financial Benefits | Payback period | |||||||
| Polishing: Reduction of compound and heel use through proper operating practice |
$150-$300 (US) per year | Immediate | |||||||
| Solvent degreasing: Replacement of this process step with aqueous alkaline cleaner |
$5000 (US) | $11,134 (US) per year | less than 6 months | ||||||
Alkaline cleaning
|
Nil
Less than $100 (US) |
$895 (US) per year
$930 (US) per year |
Immediate
Immediate |
||||||
Acid dip (10% sulfuric)
|
Nil Nil |
Improves quality of the product $144 (US) |
Immediate |
||||||
| Elimination of acid dip - Depassivation of nickel | Nil | $672 (US) | Immediate | ||||||
| Replace acid dip mixed acid stripper with solutions in smaller tanks, and practice segregation and recovery | Reduced treatment cost | ||||||||
| Copper cyanide - Improved process control and solution monitoring | Less than $ 100 (US) | Improved product quality | |||||||
| Cyanide brass metal finishing - Improved process control and solution monitoring | Improved product quality | ||||||||
|
$100 (US)
No extra cost |
Improved product quality with less solution loss
$4,130 (US) to $5875 (US) per year |
Immediate |
||||||
Chrome metal finishing |
Nil
$500 to $1000 (US) |
Reduces need for treatment.
Elimination of treatment |
1-2 years. |
||||||
|
less that $100 (US) | $19,783 (US) per year | less than three months | ||||||
| $5,500 to $6,500 (US) | $19,783 per year. | ||||||||
| Degreasing- use of aqueous alkaline cleaners instead of TCE | $ 5,000 | $ 12,000 (US) per year | |||||||
| Separate acid dips for steel and brass substrates | Reduced number of rejects the facility produces, additionally a saving of $ 816 (US) per year | ||||||||
| Improved process control and solution monitoring for cyanide metal finishing | Enhanced product quality | ||||||||
| Improved process control to avoid Nickel and Chrome wastes | $ 500 - $ 1,000 (US) | $ 4,100 - $ 5,900 (US) per year | |||||||
| Use of air or solution agitation/ Use of spray rinses | $ 100 | $ 1,728 (US) per year |
Constraints
None reported.
Contacts
Review Status
This case study was carried out in a developing country in which EP3 has an established Program. It was submitted to UNEP IE and edited for the ICPIC diskette in August 1995.
Subsequently the case study has undergone a technical review by Dr Prasad Modak at Environmental Management Centre, Mumbai, India, in September 1998.