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Nondestructive testing of defects in adhesive joints

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for packag<strong>in</strong>g ow<strong>in</strong>g to their low cost <strong>of</strong> production, higher tensile strength, gloss and versatility [8].<br />

Therefore, <strong>in</strong>crease <strong>in</strong> its consumption leads to litter<strong>in</strong>g and causes environmental problem. So,<br />

polypropylene was taken as the material for <strong>in</strong>vestigation <strong>in</strong> the present study.<br />

The degradation behaviour <strong>of</strong> PE us<strong>in</strong>g various photo<strong>in</strong>itiators under natural weather<strong>in</strong>g<br />

condition was <strong>in</strong>vestigated [9, 10]. The photodegradation behaviour <strong>of</strong> polypropylene under natural<br />

weather<strong>in</strong>g conditions us<strong>in</strong>g non-toxic transition metal carboxylate as prodegradant has not been<br />

pursued earlier. Iron stearate was taken as the prodegradant for polypropylene and the photodegradability<br />

<strong>of</strong> polypropylene under natural weather<strong>in</strong>g situations was <strong>in</strong>vestigated and the results<br />

are discussed.<br />

Experimental<br />

Materials<br />

Stearic acid, potassium hydroxide, ferric sulphate monohydrate were used as received to<br />

synthesize ferric stearate. Iron salt <strong>of</strong> stearic acid (MF01) was synthesized by react<strong>in</strong>g ferric sulphate<br />

monohydrate with the potassium salt <strong>of</strong> the fatty acid. Polypropylene (Repol Grade H100EY)<br />

obta<strong>in</strong>ed from Reliance Industrial Limited, Jamnagar, India was chosen for the present study. The<br />

virg<strong>in</strong> polypropylene (4Kg) was blended with 0.2% <strong>of</strong> prepared prodegradant us<strong>in</strong>g a blender. The<br />

virg<strong>in</strong> PP and the prodegradant blended PP were blown <strong>in</strong>to films us<strong>in</strong>g an extruder (Film width =<br />

36cm and Film thickness = 60μm).<br />

Methods<br />

The films were naturally weathered on a suitably designed and fabricated outdoor exposure<br />

rack, which was located <strong>in</strong> the premises <strong>of</strong> Kamaraj College <strong>of</strong> Eng<strong>in</strong>eer<strong>in</strong>g and Technology, S.P.G.C.<br />

Nagar, K.Vellakulam Post - 625 701, Virudhunagar, India. The natural weather<strong>in</strong>g <strong>of</strong> all PP films was<br />

carried out from December 2006 to March 2007 (w<strong>in</strong>ter season) and May 2007 to July 2007 (summer<br />

season). Dur<strong>in</strong>g the course <strong>of</strong> natural weather<strong>in</strong>g the average temperature, pressure and humidity were<br />

about 34 °C, 748 mmHg and 40 % rel. respectively. The average visible and UV light <strong>in</strong>tensity were<br />

937 x 10 2 LUX and 998 uW/cm 2 respectively. The sampl<strong>in</strong>g was done at regular <strong>in</strong>tervals to assess<br />

the changes occurr<strong>in</strong>g <strong>in</strong> the material dur<strong>in</strong>g the natural weather<strong>in</strong>g. Fourier Transform Infrared<br />

Spectrophotometry (FTIR), Universal Test<strong>in</strong>g Mach<strong>in</strong>e (UTM) and Scann<strong>in</strong>g Electron Microscopy<br />

(SEM) were utilized to follow the chemical and physical changes occurr<strong>in</strong>g <strong>in</strong> the material.<br />

Results and Discussion<br />

FTIR Studies<br />

From the FTIR spectra <strong>of</strong> the weathered PP samples, hydroperoxide, hydroxyl, carbonyl,<br />

lactone, ester, carboxylic acid, v<strong>in</strong>ylidene and crystall<strong>in</strong>ity <strong>in</strong>dices have been calculated. The<br />

characteristic <strong>in</strong>frared absorption frequencies for the different functional groups are listed <strong>in</strong> Table 1.<br />

In the present work, the band at 974 cm -1 (CH3- rock<strong>in</strong>g) was chosen as the reference peak, because it<br />

rema<strong>in</strong>s unchanged dur<strong>in</strong>g photodegradation process.<br />

Carbonyl <strong>in</strong>dex is the most used parameter to monitor the degree <strong>of</strong> degradation <strong>in</strong> polyolef<strong>in</strong>s<br />

[11]. The carbonyl <strong>in</strong>dex was calculated as the ratio <strong>of</strong> the maximum absorbance at 1715 cm -1 to the<br />

absorbance at 974 cm -1 . The carbonyl <strong>in</strong>dex value <strong>in</strong>creases with <strong>in</strong>creas<strong>in</strong>g exposure period only after<br />

certa<strong>in</strong> days <strong>of</strong> exposure, which can be taken as the <strong>in</strong>duction period for degradation. From Fig. 1, it is<br />

clear that PP weathered at w<strong>in</strong>ter season starts to degrade after 50 days <strong>of</strong> exposure whereas for PP<br />

weathered dur<strong>in</strong>g summer season, the <strong>in</strong>duction period for degradation was found to be 40 days.<br />

Incorporation <strong>of</strong> the prodegradant (iron stearate, MF01) <strong>in</strong> PP drastically reduces this <strong>in</strong>duction period.<br />

These results confirm the fact that the added prodegradant plays an important role to <strong>in</strong>duce<br />

photodegradation. Environmental conditions like temperature, UV <strong>in</strong>tensity, visible light <strong>in</strong>tensity,<br />

etc., also play a def<strong>in</strong>ite role <strong>in</strong> the photodegradation behaviour <strong>of</strong> PP. In general, carbonyl groups

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