EPA/600/A-92/237 A STUDY OF THE EFFECTS OF ACIDIC POIXUTATSTTS ON AUTOMOTIVE FINISHES Naraporn Rungsimuntaku!, Douglas White, Raymond Fornes, Richard Gilbert, Chunshan Zhang Physical and Mathematical Sciences Research North Carolina State University P.O. Box 8209, Raleigh, N. C. 27695 John Spence Atmospheric Research and Assessment Laboratory United States Environmental Protection Agency Research Triangle Park, N. C. 27711 ABSTRACT Automotive finishes of various compositions on metal substrates were exposed vertically in a smog chamber to UV and acidic atmospheres that were generated from combinations of SC>2, NO, propylene, water and air. Dews of different compositions were generated and collected for spot testing. Spot tests were performed by placing drops (IOOjiL) of dews on the surfaces of the paints and heating in an air-circulating oven at 90 °C for 24 hours. Visual observation, reflection optical microscopy, profilometry, SEM and EDS were used to examine surface damage. Various degrees of damage occurred depending upon the dew composition and surface properties. In general, the damage areas were in the form of rings with diameters smaller than the original drop. After rinsing and buffing, the damage was still visible. Microscopy and SEM revealed that the rings consisted of numerous small areas of damage and that swelling, pitting blistering and cracking had occurred. EDS showed aluminum and sulfur at the damage surface, while the surrounding area did not Since the base coat contained A1 flakes, this suggested that the acidic dew had penetrated through the top coat into the base coat INTRODUCTION Environmentally-related damage to automotive finishes (paint coatings on metal substrates) has been observed. Weather and acid resistance of materials have concerned coatings and automotive manufacturers and government agencies. Paints exposed to acidic pollutant atmospheres are typically subjected to UV light, oxygen/ozone, temperature and humidity. Understanding the damage characteristics and the influencing factors and mechanisms of photodegradation of materials in an acidic environment will provide highly useful information and guidelines, possibly leading to the development of the acid resistant materials. Paint damage can occur at the macroscopic level, such as darkening or fading of the pigments, decrease in gloss, chalking12 pitting, blistering, peeling and cracking2*3- It can also occur at the microscopic level, such as increased crosslinking, adsorption or film component dissolution2. McEwen et al.1 studied accelerated weathering of automotive paint using xenon-arc and quartz filtered ultraviolet light and compared the results with materials exposed to Florida sunlight. They used gloss meter analysis and attenuated total reflectance infrared spectrometry (ATR-IR). The ATR-IR gave useful information about the degradation and indicated that some surface oxidation occurred. However, the paint film had to be peeled away from the metal substrate in order to be characterized using the ATR-IR. Simson and Moran2 discussed the effects of UV radiation and oxygen/ozone on the degradation of the polymer films. They stated that UV excitation of sufficient energy caused excitation of oxidants resulting in free radical formation. Free radical reaction with polymer films could induce crosslinking or chain scission of the polymer. If the backbone of a polymer chain were ------- disrupted, significant degradation could result. They also discussed the effect of the presence of moisture and stated that it could result in some swelling of the polymer film and lead to increased permeation of pollutants. Campbell et al. used six techniques to assess air-pollution damage to three kinds of paint on steel: alkyd industrial maintenance paints, coil coating finishes and automotive refinishes (titanium in nitrocellulose/acrylic).4 The techniques used were: erosion rate, ATR-IR, gloss and sheen, surface roughness, tensile strength and scanning electron microscopy (SEM). They concluded that the combination of the gravimetric erosion rate, ATR-IR and SEM analysis gave the most useful information in assessing the damage. SEM micrographs showed that the automotive refinish exposed for seven months at Chicago, Illinois and Leeds, North Dakota were unaffected, but that the paints exposed to 1 ppm of SO2 had slighdy greater surface roughness. The erosion rate appeared to be linearly related to (SO2 or O3) concentration. White and Rothschild3 found dark spots of several millemeters in diameter on cars exposed in Israel. Some spots were in the form of shallow pits in the paint films. They reproduced the appearance of the spots by leaving drops of strong nitric and sulfuric acid on the paint for some time. Wolff et al.5 studied the damage to automotive finishes exposed outdoors in Florida (subjected to heat, UV radiation, wind, rain, dew and air pollution) for five weeks. The damage occurred as circular, elliptical or irregular spots that appeared as deposits or precipitates. They summarized that wetting events such as rain and dew were a prerequisite for damage to occur. The damage was enhanced without exposure to additional wetting events when the deposits remained on the test panels for several days while exposed to daytime heating, sunshine and cooling. Their electron dispersive spectroscopy (EDS) data showed that the precipitate associated with the ringlet shaped spots was composed mainly of calcium sulfate (CaSC^). When the surface was washed, most of the CaSC>4 was removed but the surface remained scarred. Simson and Moran reviewed Edney's work (EPA report 1988) on an oil-based maintenance paint, which they exposed in a smog chamber containing mixtures of C3H^/NOx/SO2, under wet and dry conditions for 21 h.2 The pollutant concentrations used were: 722ppb of SO2, 230 ppb of O3 , 180 ppb of NO* , 380 ppb of HCHO and 7ppb of HNO3 . The results indicated that this paint was fairly inert at this exposure condition. The extent of damage to polymer films caused by acidic pollutants depends on many factors such as the type and concentration of pollutants, the exposure temperature and time and the presence of UV radiation, ozone and humidity. Jellinek et al. reported that chain scission took place in poly(methyl methacrylate) when the polymer was exposed to UV/O2 and UV/O2/SO2.6 Sankar et al.7 reported the results of elemental analysis, x-ray photoelectron spectroscopy (XPS) and 13C magic angle spinning nuclear magnetic resonance (13C MAS NMR) studies of a UV/SO2/H2O exposed acrylate copolymer and a terpolymer of n-butyl acrylate, vinyl acetate and vinyl chloride films. There was clear evidence of the incorporation of sulfur into the polymers and there was significant loss of the acetate group in the terpolymer. The results suggested a synergistic interaction between SO2 and UV leading to rapid degradation. EXPERIMENTAL We developed our spot test to simulate the outdoor damage process of automobile paint exposed to precipitation followed by heating from the sun. In this study we exposed automotive finishes in a smog chamber for one week, followed by dew exposure in the form of a spot test at 90 °C for 24 h. (Note that the outdoor temperature of the automobile body can surpass 90 °C6.) The spot test was performed by placing 100 |iL drops of the dews onto the surface of the paints, followed by heating the samples in an air circulating oven at 90 °C for 24 h. The samples were analyzed using reflection light microscopy, profilometry, SEM and EDS. Samples 2 ------- The paint samples' dimensions were 10 cm x 15 cm x 0.058 cm. They were prepared in a manner that is consistent with the method of the preparation of automobile paint coatings. Two kinds of paints, white and metallic grey, were studied. The white sample consisted of a layer of titanium dioxide in an acrylate blend topcoat on a metal substrate. The metallic grey sample consisted of layers of an acrylate blend topcoat and aluminum flakes on an acrylate blend base coat on a metal substrate. The samples were rinsed with deionized water and lightly buffed with a chamois before each exposure to remove dust Chamber Exposure Samples were positioned vertically and exposed to UV light and pollutants in a smog chamber at North Carolina State University. Pollutants such as SO2, NO and propylene were introduced into the chamber and mixed with dry clean air and deionized water. The chamber was surrounded by banks of UV light which simulated the UV component of the sunlight spectrum. The chamber was operated as a continuously stirred reactor in which NOx, ozone and various acids were formed Each sample holder was placed on a chiller plate so that sample could be chilled below the dew point temperature to generate a wet surface, i.e., dew. The samples were exposed at approximate average pollutant concentrations of 300 ppb of NO*, 460 ppb of C3H6,90 ppb of SO2 and 120 ppb of O3 for one week, under the cycle of 5 h wet -2 h dry - 5 h wet - 12 h dry surface conditions. The sample temperatures under dry deposition and wet deposition were about 30 °C and 5 °C, respectively. The samples were removed from the chamber, observed for surface change and stored in a desiccator. For the spot tests, dews were generated on teflon films placed on the chiller plates and the run-off s were collected twice a day and kept in amber glass botdes under refrigeration. The pH and composition of the dew were measured by using a Fisher pH meter and a Dionex Ion Chromatograph model 2010i, equipped with an IonPac column AS-10. Dew Exposure Three drops of filtered chamber dews (100 p.1 each) were pipetted onto the surface of the samples. The samples were kept at room temperature for 1 h and then placed in an air-circulating oven at 90 °C for 24 h. Finally, the samples were rinsed with deionized water and lightly buffed with a chamois before surface analyses were performed. Surface Analysis of the Painted Samples A reflection light microscope (Zeiss model AXIOMAT) was used to examine the damaged surface areas. An Alpha Step 200 profilometer manufactured by Tencor Instruments Co., with a stylus in the shape of a 60° cone rounded at the end to a spherical tip of 12.5 |im radius was used to measure the depth or height of the damage by dragging it across the surface. An SEM, (JEOL 840) equipped with an EDS (Kevex model 8000) was used to examine the details of the damage and the elemental composition of the surface. RESULTS AND DISCUSSION From visual observations, there was no significant change of the surface appearance on either of the chamber exposed samples. The samples were then subjected to spot testing using two chamber dews with pH 3.35 and 3.50, respectively. The composition of the dews are shown in Table 1. Table 1 dH and composition of the chamher dews. Chamber. pH Ion Concentration (mg/L) DeW# F- CI" S04= NO3- CH3COO- HCOO 91-3 91-6 3.35 1.21 0.54 20.51 10.14 20.49 3.50 1.59 0.99 14.91 7.99 23.07 1.83 32.81 ------- The samples with dew drops placed on their surfaces were placed into an oven and heated at 90 °C. The behavior of the drops was essentially the same as reported by White8. From the damage size and shape, it appears that at a critical concentration the acidic chamber dew attacks the painted surfaces. Previously, the damage was found to be more pronounced when the exposure temperature was increased from 54 to 90 °C, and when the exposure time was increased from 1 to 24 h8. This also suggests that the extent of the attack directly depends on the exposure temperature and that the attack continues with the exposure time. Various degrees of damage occur depending upon the dew composition and the surface properties. For the white paint (#7), reflection light microscopy reveals that the damage is in the form of a ring with some damage in the middle. Some surface cracking also occurs (Figure la). The corresponding surface profile of this damage (Figure lb) shows that the damage is a blister with a height of 0.8 mm. (Note that the 4.5 |im value in the figure represents the height of the deposits or reaction products.) The white paint (#7B), which was exposed to pollutants in the smog chamber for one week prior to the spot test, has a larger damage area and a slighdy higher blister (0.9 mm) than #7, as shown in Figures 2a and 2b, respectively. When drops of acidic dew containing various acids such as H2SO4, HNC^ HCOOH, CH3COOH, were dried, deposits were left on the paint surface. It appears that they penetrated the top coat and caused swelling and cracking of the paint The chamber exposed (#1B) and unexposed metallic grey paint samples (#1) were subjected to spot tests using chamber dews #91-3 and #91-6. The height and depth of the damage area are reported in Table 2. The damage on the chamber exposed samples is greater than on the unexposed sample. The chamber dew #91-3, pH 3.35, causes more damage than the chamber dew #91-6, pH 3.50. Table 2 Maximum height (H) and depth (D) of the damage on the paint samples exposed to chamber dews at 90 °C for 24 h, measured by profllometry scans Chamber pH "PaTnt #T- ~ "PaTnt"#2~ ~Paint~#3 Paint #4 ~ Dew# H D H PHD HP #91-3 3.35 0.90, -0.1 2.60 -- 0.86, -0.90 0.90 -0.80 #91-6. 2JQ CL22 11 L52 - NA NA 0,60 -0,94 Microscopy and SEM reveal that the ring shaped damages on paint #1 and #1B consist of many small areas of damage and that swelling, pitting, blistering and cracking occurred. The EPS spectrum of the damage surface on paint #1B shows aluminum and sulfur (Figure 3a), while the surrounding area does not (Figure 3b). This suggests that the chamber dew has attacked the top coat and penetrated through cracks into the base coat, exposing the aluminum in the base coat. It also suggests that the sulfuric acid in the dew may have reacted with the acrylate polymer. SUMMARY This preliminary study of the effects of acidic pollutants on acid resistant automotive finishes showed that one week of exposure to moderately high concentration of pollutants in a smog chamber does not visually damage the paints. However, the spot test at 90 °C for 24 h using a chamber dew containing various organic and inorganic acids causes blistering and cracking of the top coat. EDS data provide evidence that the acidic dew can penetrate through the top coat into the base coat. Further studies are underway in an attempt to understand the mechanism of the attack. REFERENCES 1. D. J. McEwen, M.H. Verma and R.O. Turner, "Accelerated Weathering of Automotive Paints Measured by Gloss and Infrared Spectroscopy", J. Coat. Tech.. 52(755): 123 (1987). 2. T.C. Simson and P.J. Moran, TTie Johns Hopkins University, Baltimore, MD, personal 4 ------- communication, 1990. 3. J. White and W. Rothschild."Defects in the Finish of Motor Cars," Metal Finishing. 85(5), 15 (1987),. 4. G.G. Campbell, G.G. Schurr and D.E. Slawikowski, "A Study to Evaluate Techniques of Assessing Air Pollution Damage to Paints," EPA-R3-73-040, U.S.Environmental Protection Agency, Research Triangle Park, 1972. 5. G.T Wolff, W.R. Rodgers, D.C. Collins, M.H. Verma and C.A. Wong,"Spotting of Automotive Finishes from the Interactions Between Dry Deposition of Crustal Material and Wet Deposition of Sulfate," J.Air Waste Manage. Assoc.. 40(12), 1638 (1990). 6. HJLG. Jellinek, F. Flajsman and FJ. Krymn,"Reaction of SO2 and NQ2 with Polymers," J.AppI- Polvm. Sci.. 13, 107 (1969). 7. S.S. Sankar, D,Patil, R. Schadt, R.E. Fornes and R.D. Gilbert,"Environmental Effects on Latex Paint Coatings. II: CP/MAS 13C-NMR and XPS Investigations of Structural Changes in the Base Polymer," J. AppI. Polvm. Sci..41.1251 (1990). 8. DJF. White,"Investigations of Techniques to Assess Physical Damage to Polymeric Automotive Coatings on Metals by Acidic Deposition," M.S. Thesis, North Carolina State University, (1992). DISCLAIMER This paper has been reviewed in accordance with the U.S. Environmental Protection Agency's peer and administrative policy for publication. Mention of trade names of commercial products does not constitute endorsement or recommendation for use. T sou tuuu rxro—'—-vS Horizontal Distance (jim) (b) Figure 1. Paint#7, spot tested with chamber dew #91-3,90 °C, 24h. a. Optical micrograph b. Surface profile of the damage ------- (a) J '•/** - - X 1 1000 ' IMU 55 Horizontal Distance (pm) (b) Figure 2. Paint #?B, one week chamber exposed and spot tested with chamber dew #91-3, 90 °C. 24 h. a. Optical micrograph b. Surface profile of the damage. ,, «*» i it ?>• i (a) m,M.| ili,w S ©#• l**i* I J ii.fii M* (b) Figure 3. EDS spectra of Paint # IB, one week chamber exposed and spot test with chamber dew #91-3, 90°C, 24 h a, EDS spectrum of the dew exposed area b. EDS spectrum of the unexposed area ------- TECHNICAL REPORT DATA 1. REPORT *0, EPA/600/A-92/237 2. 3' 4. TITLE AND SUBTITLE A STUDY OF THE EFFECTS OF ACIDIC POLLUTANTS OK AUTOMOTIVE FINISHES 5.REPORT DATE 6.PERFORMING ORGANIZATION CODE 7. AUTHORCSJ Rungsimuntakul, N., White, D,, Fornes, R., Gilbert, R., Zhang, C., and Spence, J. 8.PERFORMING ORGANIZATION REPORT NO. 9. FERFORHING ORGANIZATION KAHE AND ADDRESS North Carolina State University Raleigh, NC 27695 U. S. Environmental Protection Agency/AREAL Research Triangle Park, NC 27711 10.PROGRAM ELEMENT NO. 11. CONTRACT/GRANT NO. CR-814121 12. SPONSORING AGENCY NAME AND ADDRESS Atmospheric Research & Exposure Assess. Laboratory Office of Research and Development U. S. Environmental Protection Agency Research Triangle Park, NC 27711 13.TYPE OF REPORT AND PERIOD COVERED 1*. SPONSORING AGENCY CODE EPA/600/09 15. SUPPLEMENTARY NOTES ,1 '/v ' 16. ABSTRACT ; Automotive finishes of various compositions- on metal substrates were exposed vertically in a smog chamber to UV and acidic atmospheres. The pollutants were generated from combinations of SO^, NO, propylene, water, and air. Dews of different compositions were generate# and collected twice a day. Spot tests were performed by placing drops of (100 juL) of.--dews on the surfaces of the paints and heating in an air-circulating oven at 90*C for 24 hours. Visual observation, reflection optical microscopy, profilometry, SEM, and EDS were used to examine surface damage. Various degrees of damage occurred depending upon the dew composition and surface properties. In general, the damage areas were in the form of rings with diameters smaller than the original drop. After rinsing and buffing, the damage was still visible. Microscopy and SEM revealed that the rings consisted of numerous small areas of damage and that swelling, pitting, blistering, and cracking had occurred. EDS showed aluminum and sulfur at the damage surface, while the surrounding area did not. Since the base coat contained Al flakes, this suggested that the acidic dew had penetrated through the top coat into the base coat./^.-:.---- 17. KEY WORDS AND DOCUMENT ANALYSIS «. DESCRIPTORS b.IDENTIFIERS/ OPEN ENDED TERMS e.COSATI 18. DISTRIBUTION STATEMENT RELEASE TO PUBLIC • 19. SECURITY CLASS (this Recort) UNCLASSIFIED 21.HO. OF FAGES % • 20. SECURITY CLASS (This P*«e) "UNCLASSIFIED 22. PRICE ------- |