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Trial Purpose:
To evaluate cleaning at different levels of contamination.
Date Run:
08/31/1999Experiment Procedure:
One cleaning solutions and DI Water were selected for testing based on their performance from the previous trials. A 2% solution was made of the cleaner using DI water in 600 mL beakers. three concentrations of the contaminant were added to different beakers of the cleaner and DI water, based on volume percent (5, 10 and 15). Each were heated to 100 F on a hot plate. Thirty coupons were wiped with Isopropyl Alcohol and air dried. The coupons were weighed to establish a baseline level of cleanliness. All 30 coupons were observed for particulate matter using an UVP Inc. Black light, Model UVL-56 longwave UV-366nm.
The coupons were dipped into the Evanol and dried overnight at room temperature. Five coupons were cleaned in each solution for five minutes using stir-bar agitation. Parts were rinsed for two minutes in DI water also with stir-bar agitation. Rinsing was performed for two minutes with heated DI water at the same temperature. The parts were dried in a convection oven at 212 F for 15 minutes. After allowing parts to cool to room temperature, final weights were recorded. All coupons were observed again under black light for particulate matter and any remaining Evanol. Visual observations were made on all the coupons for any visible signs of contamination.
Samples were measured for chlorine concentration using LaMotteās Smart Colorimeter. Readings were made before and after cleaning.
SUBSTRATE MATERIAL: Ceramic-Alumina coupons
CONTAMINANTS: DuPont Evanol Concentrated (Vinyl Alcohol Polymers & Copolymers CAS#s: 9002-89-5, 25213-24-5, 54626-91-4; Methanol Bulk/Packaged CAS #: 67-56-1; Sodium Acetate CAS#: 127-09-3)
CONTAMINATING PROCESS USED: Dip coupons into contaminant solution and dry overnight at room temperature
Trial Results:
Micro 90 was successful in removing nearly all of the contamination from the coupons at all three levels of soil loading. At 15% Evanol concentration, the Micro 90 removed approximately 97% of the Evanol on the coupons. The DI water was not as effective at the higher soil loading, cleaning nearly 91% of the contaminant.
Black light fluorescence was inconclusive for the coupons cleaned with the Micro 90. For the DI samples, many fluoresced excessively, revealing that there was still contamination present in larger amounts. Visual inspection was showed that most of the coupons had some of the contaminant still on them. Table 1 lists efficiencies for each coupon and the visual observations at each level of soil loading.
Table 1. Effectiveness of Cleaning
Cleaner | Evanol | Contaminant Location | Evanol | Contaminant Location | Evanol | Contaminant Location |
Micro 90 | 5% | 10% | 15% | |||
98.68 | lower section | 99.77 | 96.8 | on corner | ||
96.16 | lower section | 97.65 | lower section | 99.83 | ||
100 | 99.04 | lower section | 92.16 | on corner | ||
98.9 | upper section | 99.53 | on corner | 98.87 | across middle | |
99.66 | some on back | 98.82 | on corner | 97.72 | ||
Average | 98.68 | 98.96 | 97.08 | |||
Cleaner | Evanol | Contaminant | Evanol | Contaminant | Evanol | Contaminant |
DI Water | 5% | Location | 10% | Location | 15% | Location |
99.83 | lower section | 96.48 | on corner | 92.41 | side & middle | |
99.43 | on corner | 96.82 | on corner | 82.07 | all over | |
93.15 | on corner | 89.37 | lower section | 87.39 | all over | |
97.47 | lower section | 98.76 | on corner | 94.49 | all over | |
97.65 | on corner | 97.16 | side | 98.24 | ||
Average | 97.51 | 95.72 | 90.92 |
Using the colorimeter data, formulas were calculated for each cleaning solution based on baseline readings made from the three levels of soil loading. From the graphs, the readings made after cleaning were measured and approximate soil loading percents were determined. Tables 2 and 3 list the values used for determining the relationships between soil loading and chlorine levels. Figures 1 and 2 can be used to find the unknown soil loading levels.
Table 2. Micro 90 Colorimeter Data
Baseline | After Cleaning | Soil Loading | ||
Standard Reading | Calculated | Readings | Vol% from graph | |
0 | 0 | 0.005 | ||
5 | 0.05 | 0.04 | 0.05 | 6.5 |
10 | 0.07 | 0.075 | 0.1 | 13.5 |
15 | 0.11 | 0.11 | 0.14 | 19 |
25 | 0.18 | |||
Slope | 0.007 | y-int | 0.005 | r = 0.9879 |
Table 3. DI Water Colorimeter Data
Baseline | After Cleaning | Soil Loading | ||
Standard Reading | Calculated | Readings | Vol% from graph | |
0 | 0 | 0.006 | 0 | 0 |
5 | 0.06 | 0.052 | 0.07 | 7 |
10 | 0.1 | 0.098 | 0.12 | 12.5 |
15 | 0.14 | 0.144 | 0.17 | 18 |
20 | 0.19 | |||
slope | 0.0092 | y-int | 0.006 | r = 0.99438 |
Success Rating:
A follow up test, usually based on company input.Conclusion:
Having determined that the Micro 90 was still very effective in removing a majority of the contamination at the 15% soil loading, additional testing could be performed at higher levels of soil loading (25-50%).