Lab tests can yield predictions of durability in outdoor environments.
Building the model
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| Table. 1. Trial matrix for xenon arc, Weather-Ometer exposures. |
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The first step was to perform a simple DOE in Ci4000 and Ci5000 xenon arc Weather-Ometers. For this DOE, all exposure trials utilized quartz inner, borosilicate outer filters with no spray or dark cycles. The ultraviolet (UV) light irradiance settings, black-panel temperature (BPT) settings and relative humidity (RH percent) settings were adjusted to a variety of levels for seven trials as shown in
Table 1. In each trial, the amount of exposure required to cause a change in yellowness index(1) (delta Y.I.) of 6 units was determined for each exposure condition. For example, the irradiance, BPT and RH percent conditions of trial 1 required 1,427 KJ/m2 at 340 nm exposure to reach a delta Y.I. of 6 while the conditions of trial 6 only required 829 KJ/m2 at 340 nm to produce the same yellowing.
The second step to build the SLP model was to use multi-linear regression analysis(2) to obtain a predictive equation. To do this, the duration, irradiance, BPT and RH percent variables had to be converted into the appropriate form for the Arrhenius relationship; Ln (life estimate in KJ/m2 at 340 nm), UV irradiance intensity in W/m2-nm, 1/DegK BPT, and RH percent. Once in Arrhenius form, the 73 data points from the DOE were used in the regression analysis to calculate the predictive function shown in
Table 2. Thus, the xenon arc Weather-Ometer DOE data and regression analysis produced a predictive model describing the polycarbonate yellowing as a function of the UV intensity, BPT and RH percent variables.
Fig. 1 shows the model function for two of the three variables.
Using the model
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| Fig. 2. Example of single-day, black-panel temperature and irradiance values in Florida. |
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The first step in using the SLP model was to obtain the variable levels that occur in the outdoor weathering environment where the polycarbonate was to be exposed. Atlas researchers obtained environmental variable measurements in South Florida and Central Arizona for UV irradiance, BPT and RH percent. This environmental data was in 30-min. time increments, yielding 48 data points per day for a year. An example of a single day’s outdoor data for irradiance and BPT is shown in
Fig. 2.
The second step to use the predictive model was to enter each 30-min. combination of outdoor environmental variable observations into the predictive function. This gave a prediction of the polycarbonate yellowing for each 30-min. duration of outdoor exposure. All contributions for which the light intensity was zero (night time) were disregarded. Researchers continued to sum the degradation from each 30-min. exposure interval throughout the year until the degree of yellowing reached failure (delta Y.I. of 6). This sum represented the service life prediction for this study. The calculations predicted a service life of 332 MJ/m2 Total Ultra Violet Radiation (TUVR) in South Florida and a service life of 408 MJ/m2 TUVR in Central Arizona with service life being defined as the amount of UV-radiant exposure before the polycarbonate yellowed to 6 delta Y.I. units.
Important considerations
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| Table. 2. Regression data for xenon arc exposures. |
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One important consideration discovered in this case study was that significant differences existed in weathering variable measurements in the xenon arc laboratory instruments and the outdoor variable measurements. In xenon arc exposures, the light intensity variable is measured in W/m2 at 340 nm, while outdoors, light intensity is measured in W/m2 from 295 nm to 385 nm or TUVR. BPT measurement devices used in outdoor exposures also differ significantly from the BPTs used in xenon arc exposures. Ideally, both the model measured variables and the outdoor measured variables should be measured in the same way with devices of identical response. In order to obtain comparable irradiance data, the outdoor TUVR irradiance data was simply multiplied by ten in order to obtain a proportional approximation for the 340 nm xenon intensity data. The outdoor BPT data was used directly as measured with the outdoor style sensors.
Another important consideration is that weathering is highly material dependent. Different formulations, and even different batches of a single formulation, may weather differently. The information presented in this case study is not meant to address service-life prediction of polycarbonate, but only to study the methodologies for applying SLP to exposure data. Use of this information for any other purpose is not recommended.
Comparing Data
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| Fig. 3. Observed reference exposure results compared to model predictions. |
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Actual outdoor exposure of the polycarbonate were performed at Atlas’s outdoor exposure laboratories in South Florida and Central Arizona in order to confirm the utility of the SLP model. Five independent exposures of the polycarbonate material were performed in Miami and Phoenix at outdoor reference laboratory exposure facilities. All exposures were conducted at an angle of 5 Deg facing south in an un-backed configuration. The five exposures started on different years and at different seasons of the year at the different locations. Changes in Y.I. as a function of total UV exposure for the different tests are shown in
Fig. 3. One observes the service life of the polycarbonate as approximately 380 MJ/m2 TUVR and 450 MJ/m2 TUVR in Miami and Phoenix, respectively for these exposures.
The model predicted estimates for service life are compared to the actual observed values in
Fig. 3. In both exposure environments, the model predicted service life estimate differed from the observed outdoor service life by less than 15 percent. Given the differences in variable measurement and the crude approximations undertaken in the calculation, this level of agreement was unexpected for a first approximation.
This case study on polycarbonate offered researchers a good opportunity to gain experience and insights in SLP methodologies. The model developed showed reasonable agreement between predicted and observed service life. One way researchers may improve the methodology is to use the same type environmental variable measurements outdoors as used in the laboratory. Building SLP models with xenon arc Weather-Ometers in the laboratory and using the models by inputting outdoor environmental variable data appears to offer a powerful tool for the weathering researcher’s toolbox.
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