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Issues Impacting Bridge Painting: an Overview
FHWA/RD/94/098 –August 1995

Abstract | Table of Contents | Executive Summary | Chapter 1 | Chapter 2 | Chapter 3 | Chapter 4 | Chapter 5 | Chapter 6 | Chapter 7 | Appendix A | References | List of Figures | List of Tables

Executive Summary

The bridges of the United States are under constant attack from the environment. Whether it is the sudden yet violent effects of floods or earthquakes or the long term effects associated with sunlight, rain, deicing salts and freeze/thaw cycles. To often, in the design of a bridge, little thought is given to the mitigation of these effects and seldom are provisions made for ease of future rehabilitation.

The quality of the environment has always been of concern to the general populace as well as to the government. Concerns over the potential pollution of the environment, by lead and other heavy metals, during the removal of older paint systems from bridges has resulted in regulations severely limiting the options available for paint removal. Prior to 1985 open air blasting with grit was the standard method of paint removal. While inexpensive it resulted in paint debris scattered over a wide area. Today, open air blasting is illegal and has been replaced with removal in containment. Containment means that the bridge or a portion of the bridge is enclosed thereby containing the paint debris. Since this concept requires engineering analysis and construction and potential movement of the enclosure the costs for paint removal has dramatically increased oftentimes without meeting the regulatory goals.

With the advent of containment the emphasis has shifted to the worker. The use of containment has led to increased concentrations of particulates within the structure. With the increase in particulate concentrations has come regulations as to the attire, respiratory protection, and decontamination of workers within the containment. Increasing regulation has led to decreased productivity which again has resulted in increased cost to the bridge owners and the inability to adequately meet the needs of the infrastructure with the available funding.

Additional regulations have been enacted limiting Volatile Organic Compounds (VOCs) for architectural and maintenance coatings. These regulations have resulted in the application, onto bridges, of modified paint systems with limited available information associated with their durability. The use of these paints to replace or repair existing systems is a gamble that the states must take in order to meet regulatory compliance.

The purpose of this study was to review aspects of the rehabilitation process in light of the above mentioned limitations, assess to the degree possible the state of the art, arrive at conclusions and make recommendations where applicable. To this end five technical and one economic tasks were performed. Below are selected conclusions and recommendations resulting from the various tasks.

  1. TASK A - ECONOMIC ANALYSIS

    A life cycle cost (LCC) model has been developed for the maintenance painting of steel bridges. The model computes the Equivalent Uniform Annual Cost (EUAC) for a given coating system with a particular initial cost and known life expectancy under a given set of financial conditions (interest and inflation rates). The cost data is presented on a dollars per square foot basis. This allows the user to calculate an average yearly cost for controlling corrosion of a steel bridge using a particular coating system based upon the estimated usefull life of the structure. The model shows that the coating life expectancy plays a major role in the determination of life cycle cost of maintaining the paint system and the structure. This is particularly true for coating life expectancies in the lower range. An increase in life expectancy from 6 to 10 years can mean a life cycle cost savings of nearly 60% for ____ economic conditions 7% interest and a 4% inflation rate. The corresponding percentage decrease in life cycle cost with increasing life expectancy diminishes as the coating life expectancy extends outward towards 40 years but still remains significant to 40 years.

    What is quite clear from the economic analysis that a new way of costing the removal of old paint and the application of new paint is necessary. For this or any other model to be an effective tool, costing needs to be made in an itemized manner and more information about the durability of VOC compliant paint systems is necessary. What is also clear is that the cost of material i.e. paint is the least costly element of paint removal and recoating. It is penny wise and pound foolish not to buy the highest quality paint for recoating.

  2. TASK B - WORKER PROTECTION/PAINT REMOVAL

    As discussed above the regulations concerning paint removal and worker safety are complex and under constant revision. The preferred method of removing lead containing paints is containment and total removal. Once the paint is removed it no longer presents a danger. Unfortunately, it is expensive and this study has found that the potential exists for particulates with diameters less than Ü are generated by steel grit blasting and laser ablation. For these particles many HEPA filters have limited capture potential. Additionally, similar results would be expected for any process that pyrolyses the paint. It is recommended that the presence of these particles be determined in an unambiguous manner and technology developed to insure their capture.

  3. TASK C - WASTE TREATMENT AND DISPOSAL

    The purpose of this task was to evaluate the Toxicity Characteristic Leaching Test (TCLP) in the presence of iron to determine whether adequate stabilization occurs in order that the debris can be disposed of in commercial waste sites. This study and others concludes that the TCLP test is indicative of the stabilization of the waste at the time of the test and is not a reliable indicator of future resistance to leaching. Insufficient information is available at this time as to the actual "typical" environment in a commercial dump site to define an improvement or replacement for the TCLP test.

  4. TASK D - ALTERNATE COATINGS

    Many of the alternative coatings, with the exception of metallizing, have sufficient data to make recommendations. In the case of mettalizing the technology can be recommended for use in fabrication shops and as a replacement in the field were appropriate. As part of this task the difficulties faced by fabrication shops and the concept of "overcoating" are discussed. Additionally, problems were identified and future research to affect solutions to those problems was outlined.

  5. TASK E - ACCELERATED TESTING

    One of the difficulties of responding to changing regulations is the lack of time to evaluate new paint systems before they must be used. This task identified modifications to existing tests that, if implemented, might provide better correlation between accelerated tests performed in the laboratory and durability in the field. Additionally, laboratory tests were evaluated to determine their applicability in the field.

  6. TASK F - PRODUCTIVITY IMPROVEMENT

    In this task an evaluation was made to determine where sensors could best influence productivity and result in improvements to coating performance. Since it is commonly acknowledged that over 70% of coating failures are associated with poor surface preparation a series of sensor technologies were evaluated. They included enhanced monochrome CCD techniques to determine the degree of surface rusting, Color CCD techniques to evaluate blast cleaned surfaces, and thermal wave imaging for the quantitative evaluation of painted surfaces prior to paint removal.

While this study has reviewed and evaluated existing and future rehabilitation practices it raises more issues than it answers since the issues are far more complex than they appear.

 

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Last updated: July 12, 2006    © 2005 Infrastructure Technology Institute