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International Journal of Advanced Research in Engineering and Technology (IJARET), ISSN 0976 –
6480(Print), ISSN 0976 – 6499(Online) Volume 4, Issue 6, September – October (2013), © IAEME
50
STUDY OF DEGRADATION OF SYNTHETIC POLYMER NYLON 6 BY
COMPOSTING METHOD
Chonde Sonal G1
, Pawar Nilambari R1
, Chonde Sachin G2
, Raut P. D1
Department of Environmental Science, Shivaji University, Kolhapur- 416 004. INDIA,
AMGOI, Vathar, Kolhapur
ABSTRACT
Nylon is a generic designation for a family of synthetic polymers known as polyamides. This
tends to give polymers useful properties such as flexibility and elasticity. Because of durability and
visibility of polyamides hazards of discarding polyamides is called as ‘White Pollution’. Present
study has examined the feasibility of composting for actively degrading Synthetic Polymer Nylon 6.
For present experiment, Nylon 6 sheets were submerged in semi natural environment carried in
Borosil glass for specific duration of 3 months to observe degradation. Physiochemical Analysis of
compost was carried out for concentration of organic carbon, Potassium, Phosphorous and Electrical
conductivity. Nylon 6 sheets were analyzed for degradation study which was monitor by weight
reduction, thickness reduction; chemical analysis etc. composting conditions degrade the polymer
which is confirmed by 10% weight loss, 13% thickness reduction and weakening in amide bond in
polymer.
Keywords: biodegradation, composting study, Nylon 6
INTRODUCTION
Plastics are made up of long chain molecules called polymers. Polymers are made when
naturally occurring substances such as coal, natural gas and oil are transformed into other substances
with completely different properties. Polyamide is a polymer, which contains recurring amide groups
(R-CO-NH-R') as integral part of the main polymer chain. Synthetic polyamides are produced by a
condensation reaction between monomers, in which the linkage of the molecules occurs through the
formation of the amide groups [1]. Biodegradation of polyamides is chemical changes by changes in
bands like stretching, weakening etc., by microorganisms. Polymeric materials are not easily
biodegraded. Efforts have been directed to develop mild physicochemical procedures, which
INTERNATIONAL JOURNAL OF ADVANCED RESEARCH IN
ENGINEERING AND TECHNOLOGY (IJARET)
ISSN 0976 - 6480 (Print)
ISSN 0976 - 6499 (Online)
Volume 4, Issue 6, September – October 2013, pp. 50-56
© IAEME: www.iaeme.com/ijaret.asp
Journal Impact Factor (2013): 5.8376 (Calculated by GISI)
www.jifactor.com
IJARET
© I A E M E
International Journal of Advanced Research in Engineering and Technology (IJARET), ISSN 0976 –
6480(Print), ISSN 0976 – 6499(Online) Volume 4, Issue 6, September – October (2013), © IAEME
51
includes thermal and radiation pre-treatments to enhance the biodegradation process [2]. Degradation
is the process in which a product is capable of being chemically degraded, changing its mechanical
and chemical properties. A product is degradable when it can change its properties in a time scale
due to the action of heat, light or mechanical stress. Any physical or chemical change in polymer as a
result of environmental factors, such as light, heat, moisture, chemical conditions or biological
activity is termed as degradation of plastics.
Polymeric materials are not easily biodegraded. Efforts have been directed to develop mild
physico-chemical procedures which include thermal and radiation pretreatments to enhance the
biodegradation process (Albertson et al., 1987). The degradation of plastics in nature is a very slow
process which is first initiated by environmental factors followed by wild micro-organisms. The
environmental factors include temperature, humidity, pH and UV. Biodegradation is the ability of
micro-organism to influence abiotic degradation through physical, chemical or enzymatic action [2]
[3] [4] [5]. Interplay between biodegradation and different factors in the biotic and abiotic
environments are very important. The micro-organism reported for the biodegradation of the
polyethylene include fungi (Aspergillus niger, Aspergillus flavus, Aspergillus oryzae, Chaetomium
globusum, Penicillium funiculosum, Pullularia pullulan), bacteria (Pseudomonas aeruginosa,
Bacillus cereus, Coryneformes bacterium, Bacillus sp., Mycobacterium, Nocardia, Corynebacterium,
Candida and Pseudomonas) and Actinomycetales, Streptomycetaceae. Their activity on the polymer
was studied by growth tests on solid agar medium for a definite period of time. The changes in
molecular weight, structure, crystalinity, density, weight loss, mechanical, optical or dielectric
properties, etc., were also measured [6] [7] [8] [9] [10]. Unlike polypropylene, more research articles
are published on studies relating to biodegradation of polyethylene. Fungi that include A. niger,
Penicillium funiculosum, Fusarium redolens and A. vesicolor, and soil microorganisms (mixed
culture as well as Rhodococcus rhodochorus, Cladosporium cladosporoides) have been reported to
degrade polyethylene [2].
Plastics are biodegraded aerobically in wild nature, anaerobically in sediments and landfills
and partly aerobically and partly anaerobically in compost and soil. Carbon dioxide and water are
produced during aerobic biodegradation and carbon dioxide, water and methane are produced during
anaerobic biodegradation. Some basic composting methods which have been developed for
degradation of plastic.
MATERIALS AND METHODS
Materials
Polymer Nylon 6 was purchased from Sigma Aldrich Company. Sheets of Nylon 6 are
exposed for composting conditions. For Compost preparation kitchen waste, cow dung, are used.
Disinfection of the sample
The sample sheets were sterilized before they were inoculated into the composting condition.
The nylon 6 sheets were dipped in 1 % hypochlorite for a few hours. Washed with distilled water
thoroughly in order to remove all the hypochlorite and later dried. No physical or chemical changes
were observed in the sample after hypochlorite treatment.
Biodegradation of Nylon 6 sheet under Semi-Natural Environment Composting
Biodegradation of Nylon 6 was carried out by keeping the sheets under semi- natural
conditions of environment that is composting. Semi- natural is word used to describe the laboratory
conditions. Its in-vitro composting method for degradation of polyamides. But in this semi-natural
method composting was carried in Borosil glass tray. Composition of composting in which
International Journal of Advanced Research in Engineering and Technology (IJARET), ISSN 0976 –
6480(Print), ISSN 0976 – 6499(Online) Volume 4, Issue 6, September – October (2013), © IAEME
52
concentration of manure and soil as 1:3 ratios. Green and brown leaves, waste as carbon source,
moisture condition moderately maintained. In semi-natural composting, special type of tray is used
which is made up of Borosil (glass) named as “Square Cake Dish” (small). Usually, for composting,
plastic large trays are used but in semi-natural composting, glass trays are used which is kept in
laboratory under aerobic conditions. Sheets of polyamide under composting condition were kept for
about 3 months for completion of compost. Different composting parameters are checked as pH,
organic carbon, Phosphorous, potassium, electrical conductivity etc. nylon 6 sheets are observed for
biodegradation for weight reduction, thickness reduction, chemical analysis by I. R. Spectroscopy.
Morphological changes were monitor by inverted microscope. Also thermal analysis of plastic was
checked by TGA analysis.
RESULTS AND DISCUSSION
Degradation of Nylon 6 sheets in semi natural composting condition was observed for 90
days. Results presented in the following sections were obtained from two independent sets of
degradation experiments.
Table no.1 Compost parameters observed during 90 days for Nylon 6.
Sr.
No.
Inoculated
with Nylon
6
pH
Temperature organic
carbon
phosphorus
oxide
potassium electrical
conductivity
(µm/cm)
1 Before
composting
7.7 250
C 0.678 256.655 1572.48 0.92
2 After
composting
8.2 290
C 1.002 211.876 1451.52 1.08
Table no. 2Percentage (%) Weight loss observed in Nylon 6 sheets during composting study
Sr.
No.
Time Duration % Weigh reduction of sheets
of nylon 6 in composting
condition
1 0 Days 0
2 1 month 2
3 2 month 6
4 3 month 10
International Journal of Advanced Research in Engineering and Technology (IJARET), ISSN 0976 –
6480(Print), ISSN 0976 – 6499(Online) Volume 4, Issue 6, September – October (2013), © IAEME
53
Graph no. 2Percentage (%) Weight loss observed in Nylon 6 sheets during composting study
0
2
4
6
8
10
12
0 Days 1 month 2 month 3 month
% Weigh reduction of sheets of
nylon 6 in composting condition
% Weigh reduction of
sheets of nylon 6 in
composting condition
Table No. 3 Percentage (%) thickness reduction observed in Nylon 6 sheets during composting
study
Graph No. 3 Percentage (%) thickness reduction observed in Nylon 6 sheets during composting
study
0
2
4
6
8
10
12
14
0 Days 1 month 2 month 3 month
% thickness reduction of Nylon 6
sheets in composting condition
% thickness reduction of
Nylon 6 sheets in
composting condition
Sr.
No.
Time Duration % thickness reduction of
Nylon 6 sheets in
composting condition
1 0 Days 0
2 1 month 6
3 2 month 10
4 3 month 13
International Journal of Advanced Research in Engineering and Technology (IJARET), ISSN 0976 –
6480(Print), ISSN 0976 – 6499(Online) Volume 4, Issue 6, September – October (2013), © IAEME
54
Chemical study of Nylon 6 sheet
Fourier Transformed Spectroscopy Study of Nylon 6
FTIR Spectra of Nylon 6 sheet (Control)
FTIR Spectra of Nylon 6 sheet (expose to composting conditions)
Table No. 4 Thermo gravimetric study of Nylon 6 sheet treated with composting
Sample Temperature o
C Corresponding to weight loss
10% 20% 30% 40% 50% 60% 70% 80% 90%
Nylon 6 (Control) 413 437 448 457 461 469 476 482 -
Nylon 6 treated with
composting condition
412 435 445 456 459 467 474 480 -
International Journal of Advanced Research in Engineering and Technology (IJARET), ISSN 0976 –
6480(Print), ISSN 0976 – 6499(Online) Volume 4, Issue 6, September – October (2013), © IAEME
55
Morphological changes observed in Nylon 6 Sheet
Nylon 6 (Control)
Nylon 6 sheet treated with composting condition
RESULTS AND DISCUSSION
Composting parameters observed
The compost which was prepared from kitchen waste material shows increase in some
parameters as Temperature, pH, organic carbon, electrical conductivity etc. the compost prepared
was show high nutrient content due to organic carbon. As the carbon content was increase up to 1.02
mg/l. the conductivity was also found to be increased up to 1.08 µm/cm. (Table no 1).
Degradation of nylon 6 sheets
Present study was related with the study of biodegradation of nylon 6 under composting
conditions. The study was carried out under composting conditions. In case of nylon 6, the physical
parameter such as weight and thickness was observed to be reduced to some extent. It was observed
that the weight loss was observed up to 10% (Graph 1) and thickness of sheets was reduced up to
13%.(Graph 2). Chemical analysis by using FTIR shows the weakening in the amide bonds. The
strength of characteristic bands of C (O) NH occurring around 3300, 1640, 1550 and 1018 cm-1
decreased after composting. There may be formation of new groups like CH3, CONH2, CHO and
COOH, may be formed due to hydrolysis and oxidation [11]. The thermo gravimetric results explain
the thermal stability of nylon polymer. At control condition the polymer was found to be stable and
show 80% degradation at 482o
C, while the nylon 6 sheets treated at composting condition shows
30% weight loss at 445o
C, 60% weight loss at 467o
C and 80% weight loss at 480o
C temperature.
(Table no.4) This indicates the decrease in temperature for the degradation, which indicates the
degradation of polymer. The morphological study shows change in colour of nylon 6 sheet as it
changes to brown color and smoothness of sheets are changes to rough surface area of sheet.
International Journal of Advanced Research in Engineering and Technology (IJARET), ISSN 0976 –
6480(Print), ISSN 0976 – 6499(Online) Volume 4, Issue 6, September – October (2013), © IAEME
56
CONCLUSION
Present study was related with the biodegradation of nylon 6 polymers at composting
condition. The study concludes that the polymer nylon 6 which is found to be hard for degradation
degraded partially in composting process. The microorganisms which are present in compost play
important role in degradation of polymer.as the degradation was observed by 10% weight loss and
13% thickness reduction. Chemical characterization also explains the weakening in amide bond
while the TGA study shows that the polymer has lost thermal stability due to degradation.
Composting is found to be very good method for biodegradation of polymer. It takes more time to
degrade the polymer as it is combined action of microorganisms.
ACKNOWLEDGMENT
Authors are thankful to authorities of Shivaji University, Kolhapur and Department of
Environmental Science, Shivaji University, Kolhapur and Department of CFC Shivaji University,
Kolhapur for providing facilities to carry out work. Authors are also thankful to Sigma Aldrich for
providing Nylon 6 polymer.
REFERENCES
1. Rutkowska1 M., Heimowska1 A., Krasowska1 K., Janik H., 2002, Biodegradability of
Polyethylene Starch Blends in Sea Water. Polish Journal of Environmental Studies, Vol.
11(3), pp. 267-274.
2. Albertsson A.C. and Karlsson S., 1990, The influence of biotic and abiotic environments on
the degradation of polyethylene. Prog Polym Sci, Vol 15, pp. 77–92.
3. Eberiel J. D., D. T., Mac Carthy S. P. and Gross R. A., 1993, J. Environ. Polym. Degrad.,
Vol.1, pp. 143.
4. Solaro R., Chiellini E.E., Giannasi D., Morganti F. and Chiellini E.1997, Multifunctional
polymeric materials for biomedical applications. Macromol Symp, Vol.118: pp.603
5. Chiellini E. and Solaro R., 1995, Multifunctional bio erodible/biodegradable polymeric
materials. Macromol Symp, Vol. 98, pp. 803.
6. Weiland M, Daro A, David C. 1995, Biodegradation of thermally oxidized polyethylene.
Polymer Degradation Stability, vol., 48 (2) pp. 275–89.
7. Hashimoto K., Hamano T. and Okada M., 1994, Degradation of several polyamides in soils. J.
Appl Polym. Sci., Vol. 54, pp. 1579.
8. Yamano Naoko E., Atsuyoshi Nakayama E., N orioki Kawasaki , Noboru Yamamoto E, and
Seiichi Aiba, 2008, Mechanism and Characterization of Polyamide 4 Degradation by
Pseudomonas sp. J Polym Environ, pp. 1-6.
9. Orhan Y. and Buyukgungor H., 2000, Enhancement of biodegradability of disposable
polyethylene in controlled biological soil. International Biodeterioration and Biodegradation,
Vol.45, pp.49-55.
10. Barry E. Digregorio, 2009, Biobased Performance Bioplastic: Mirel. Chemistry & Biology
Innovations, pp. 10-19.
11. Deguchi T., Kitoka Y., Kakezawa, M. and Nishida T., 1998, Purification and characterization
of a nylon degrading enzyme, Applied Environmental Microbiology, Vol. 64, pp. 1366-1371.
12. S.Selvaraj and Dr.P.Venkataramaiah, “Production of Nylon-6 Fr Lever using an Injection
Moulding Tool and Identification of Optimum Process Parameter Combination”, International
Journal of Mechanical Engineering & Technology (IJMET), Volume 3, Issue 3, 2012,
pp. 270 - 284, ISSN Print: 0976 – 6340, ISSN Online: 0976 – 6359.

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20120130406006

  • 1. International Journal of Advanced Research in Engineering and Technology (IJARET), ISSN 0976 – 6480(Print), ISSN 0976 – 6499(Online) Volume 4, Issue 6, September – October (2013), © IAEME 50 STUDY OF DEGRADATION OF SYNTHETIC POLYMER NYLON 6 BY COMPOSTING METHOD Chonde Sonal G1 , Pawar Nilambari R1 , Chonde Sachin G2 , Raut P. D1 Department of Environmental Science, Shivaji University, Kolhapur- 416 004. INDIA, AMGOI, Vathar, Kolhapur ABSTRACT Nylon is a generic designation for a family of synthetic polymers known as polyamides. This tends to give polymers useful properties such as flexibility and elasticity. Because of durability and visibility of polyamides hazards of discarding polyamides is called as ‘White Pollution’. Present study has examined the feasibility of composting for actively degrading Synthetic Polymer Nylon 6. For present experiment, Nylon 6 sheets were submerged in semi natural environment carried in Borosil glass for specific duration of 3 months to observe degradation. Physiochemical Analysis of compost was carried out for concentration of organic carbon, Potassium, Phosphorous and Electrical conductivity. Nylon 6 sheets were analyzed for degradation study which was monitor by weight reduction, thickness reduction; chemical analysis etc. composting conditions degrade the polymer which is confirmed by 10% weight loss, 13% thickness reduction and weakening in amide bond in polymer. Keywords: biodegradation, composting study, Nylon 6 INTRODUCTION Plastics are made up of long chain molecules called polymers. Polymers are made when naturally occurring substances such as coal, natural gas and oil are transformed into other substances with completely different properties. Polyamide is a polymer, which contains recurring amide groups (R-CO-NH-R') as integral part of the main polymer chain. Synthetic polyamides are produced by a condensation reaction between monomers, in which the linkage of the molecules occurs through the formation of the amide groups [1]. Biodegradation of polyamides is chemical changes by changes in bands like stretching, weakening etc., by microorganisms. Polymeric materials are not easily biodegraded. Efforts have been directed to develop mild physicochemical procedures, which INTERNATIONAL JOURNAL OF ADVANCED RESEARCH IN ENGINEERING AND TECHNOLOGY (IJARET) ISSN 0976 - 6480 (Print) ISSN 0976 - 6499 (Online) Volume 4, Issue 6, September – October 2013, pp. 50-56 © IAEME: www.iaeme.com/ijaret.asp Journal Impact Factor (2013): 5.8376 (Calculated by GISI) www.jifactor.com IJARET © I A E M E
  • 2. International Journal of Advanced Research in Engineering and Technology (IJARET), ISSN 0976 – 6480(Print), ISSN 0976 – 6499(Online) Volume 4, Issue 6, September – October (2013), © IAEME 51 includes thermal and radiation pre-treatments to enhance the biodegradation process [2]. Degradation is the process in which a product is capable of being chemically degraded, changing its mechanical and chemical properties. A product is degradable when it can change its properties in a time scale due to the action of heat, light or mechanical stress. Any physical or chemical change in polymer as a result of environmental factors, such as light, heat, moisture, chemical conditions or biological activity is termed as degradation of plastics. Polymeric materials are not easily biodegraded. Efforts have been directed to develop mild physico-chemical procedures which include thermal and radiation pretreatments to enhance the biodegradation process (Albertson et al., 1987). The degradation of plastics in nature is a very slow process which is first initiated by environmental factors followed by wild micro-organisms. The environmental factors include temperature, humidity, pH and UV. Biodegradation is the ability of micro-organism to influence abiotic degradation through physical, chemical or enzymatic action [2] [3] [4] [5]. Interplay between biodegradation and different factors in the biotic and abiotic environments are very important. The micro-organism reported for the biodegradation of the polyethylene include fungi (Aspergillus niger, Aspergillus flavus, Aspergillus oryzae, Chaetomium globusum, Penicillium funiculosum, Pullularia pullulan), bacteria (Pseudomonas aeruginosa, Bacillus cereus, Coryneformes bacterium, Bacillus sp., Mycobacterium, Nocardia, Corynebacterium, Candida and Pseudomonas) and Actinomycetales, Streptomycetaceae. Their activity on the polymer was studied by growth tests on solid agar medium for a definite period of time. The changes in molecular weight, structure, crystalinity, density, weight loss, mechanical, optical or dielectric properties, etc., were also measured [6] [7] [8] [9] [10]. Unlike polypropylene, more research articles are published on studies relating to biodegradation of polyethylene. Fungi that include A. niger, Penicillium funiculosum, Fusarium redolens and A. vesicolor, and soil microorganisms (mixed culture as well as Rhodococcus rhodochorus, Cladosporium cladosporoides) have been reported to degrade polyethylene [2]. Plastics are biodegraded aerobically in wild nature, anaerobically in sediments and landfills and partly aerobically and partly anaerobically in compost and soil. Carbon dioxide and water are produced during aerobic biodegradation and carbon dioxide, water and methane are produced during anaerobic biodegradation. Some basic composting methods which have been developed for degradation of plastic. MATERIALS AND METHODS Materials Polymer Nylon 6 was purchased from Sigma Aldrich Company. Sheets of Nylon 6 are exposed for composting conditions. For Compost preparation kitchen waste, cow dung, are used. Disinfection of the sample The sample sheets were sterilized before they were inoculated into the composting condition. The nylon 6 sheets were dipped in 1 % hypochlorite for a few hours. Washed with distilled water thoroughly in order to remove all the hypochlorite and later dried. No physical or chemical changes were observed in the sample after hypochlorite treatment. Biodegradation of Nylon 6 sheet under Semi-Natural Environment Composting Biodegradation of Nylon 6 was carried out by keeping the sheets under semi- natural conditions of environment that is composting. Semi- natural is word used to describe the laboratory conditions. Its in-vitro composting method for degradation of polyamides. But in this semi-natural method composting was carried in Borosil glass tray. Composition of composting in which
  • 3. International Journal of Advanced Research in Engineering and Technology (IJARET), ISSN 0976 – 6480(Print), ISSN 0976 – 6499(Online) Volume 4, Issue 6, September – October (2013), © IAEME 52 concentration of manure and soil as 1:3 ratios. Green and brown leaves, waste as carbon source, moisture condition moderately maintained. In semi-natural composting, special type of tray is used which is made up of Borosil (glass) named as “Square Cake Dish” (small). Usually, for composting, plastic large trays are used but in semi-natural composting, glass trays are used which is kept in laboratory under aerobic conditions. Sheets of polyamide under composting condition were kept for about 3 months for completion of compost. Different composting parameters are checked as pH, organic carbon, Phosphorous, potassium, electrical conductivity etc. nylon 6 sheets are observed for biodegradation for weight reduction, thickness reduction, chemical analysis by I. R. Spectroscopy. Morphological changes were monitor by inverted microscope. Also thermal analysis of plastic was checked by TGA analysis. RESULTS AND DISCUSSION Degradation of Nylon 6 sheets in semi natural composting condition was observed for 90 days. Results presented in the following sections were obtained from two independent sets of degradation experiments. Table no.1 Compost parameters observed during 90 days for Nylon 6. Sr. No. Inoculated with Nylon 6 pH Temperature organic carbon phosphorus oxide potassium electrical conductivity (µm/cm) 1 Before composting 7.7 250 C 0.678 256.655 1572.48 0.92 2 After composting 8.2 290 C 1.002 211.876 1451.52 1.08 Table no. 2Percentage (%) Weight loss observed in Nylon 6 sheets during composting study Sr. No. Time Duration % Weigh reduction of sheets of nylon 6 in composting condition 1 0 Days 0 2 1 month 2 3 2 month 6 4 3 month 10
  • 4. International Journal of Advanced Research in Engineering and Technology (IJARET), ISSN 0976 – 6480(Print), ISSN 0976 – 6499(Online) Volume 4, Issue 6, September – October (2013), © IAEME 53 Graph no. 2Percentage (%) Weight loss observed in Nylon 6 sheets during composting study 0 2 4 6 8 10 12 0 Days 1 month 2 month 3 month % Weigh reduction of sheets of nylon 6 in composting condition % Weigh reduction of sheets of nylon 6 in composting condition Table No. 3 Percentage (%) thickness reduction observed in Nylon 6 sheets during composting study Graph No. 3 Percentage (%) thickness reduction observed in Nylon 6 sheets during composting study 0 2 4 6 8 10 12 14 0 Days 1 month 2 month 3 month % thickness reduction of Nylon 6 sheets in composting condition % thickness reduction of Nylon 6 sheets in composting condition Sr. No. Time Duration % thickness reduction of Nylon 6 sheets in composting condition 1 0 Days 0 2 1 month 6 3 2 month 10 4 3 month 13
  • 5. International Journal of Advanced Research in Engineering and Technology (IJARET), ISSN 0976 – 6480(Print), ISSN 0976 – 6499(Online) Volume 4, Issue 6, September – October (2013), © IAEME 54 Chemical study of Nylon 6 sheet Fourier Transformed Spectroscopy Study of Nylon 6 FTIR Spectra of Nylon 6 sheet (Control) FTIR Spectra of Nylon 6 sheet (expose to composting conditions) Table No. 4 Thermo gravimetric study of Nylon 6 sheet treated with composting Sample Temperature o C Corresponding to weight loss 10% 20% 30% 40% 50% 60% 70% 80% 90% Nylon 6 (Control) 413 437 448 457 461 469 476 482 - Nylon 6 treated with composting condition 412 435 445 456 459 467 474 480 -
  • 6. International Journal of Advanced Research in Engineering and Technology (IJARET), ISSN 0976 – 6480(Print), ISSN 0976 – 6499(Online) Volume 4, Issue 6, September – October (2013), © IAEME 55 Morphological changes observed in Nylon 6 Sheet Nylon 6 (Control) Nylon 6 sheet treated with composting condition RESULTS AND DISCUSSION Composting parameters observed The compost which was prepared from kitchen waste material shows increase in some parameters as Temperature, pH, organic carbon, electrical conductivity etc. the compost prepared was show high nutrient content due to organic carbon. As the carbon content was increase up to 1.02 mg/l. the conductivity was also found to be increased up to 1.08 µm/cm. (Table no 1). Degradation of nylon 6 sheets Present study was related with the study of biodegradation of nylon 6 under composting conditions. The study was carried out under composting conditions. In case of nylon 6, the physical parameter such as weight and thickness was observed to be reduced to some extent. It was observed that the weight loss was observed up to 10% (Graph 1) and thickness of sheets was reduced up to 13%.(Graph 2). Chemical analysis by using FTIR shows the weakening in the amide bonds. The strength of characteristic bands of C (O) NH occurring around 3300, 1640, 1550 and 1018 cm-1 decreased after composting. There may be formation of new groups like CH3, CONH2, CHO and COOH, may be formed due to hydrolysis and oxidation [11]. The thermo gravimetric results explain the thermal stability of nylon polymer. At control condition the polymer was found to be stable and show 80% degradation at 482o C, while the nylon 6 sheets treated at composting condition shows 30% weight loss at 445o C, 60% weight loss at 467o C and 80% weight loss at 480o C temperature. (Table no.4) This indicates the decrease in temperature for the degradation, which indicates the degradation of polymer. The morphological study shows change in colour of nylon 6 sheet as it changes to brown color and smoothness of sheets are changes to rough surface area of sheet.
  • 7. International Journal of Advanced Research in Engineering and Technology (IJARET), ISSN 0976 – 6480(Print), ISSN 0976 – 6499(Online) Volume 4, Issue 6, September – October (2013), © IAEME 56 CONCLUSION Present study was related with the biodegradation of nylon 6 polymers at composting condition. The study concludes that the polymer nylon 6 which is found to be hard for degradation degraded partially in composting process. The microorganisms which are present in compost play important role in degradation of polymer.as the degradation was observed by 10% weight loss and 13% thickness reduction. Chemical characterization also explains the weakening in amide bond while the TGA study shows that the polymer has lost thermal stability due to degradation. Composting is found to be very good method for biodegradation of polymer. It takes more time to degrade the polymer as it is combined action of microorganisms. ACKNOWLEDGMENT Authors are thankful to authorities of Shivaji University, Kolhapur and Department of Environmental Science, Shivaji University, Kolhapur and Department of CFC Shivaji University, Kolhapur for providing facilities to carry out work. Authors are also thankful to Sigma Aldrich for providing Nylon 6 polymer. REFERENCES 1. Rutkowska1 M., Heimowska1 A., Krasowska1 K., Janik H., 2002, Biodegradability of Polyethylene Starch Blends in Sea Water. Polish Journal of Environmental Studies, Vol. 11(3), pp. 267-274. 2. Albertsson A.C. and Karlsson S., 1990, The influence of biotic and abiotic environments on the degradation of polyethylene. Prog Polym Sci, Vol 15, pp. 77–92. 3. Eberiel J. D., D. T., Mac Carthy S. P. and Gross R. A., 1993, J. Environ. Polym. Degrad., Vol.1, pp. 143. 4. Solaro R., Chiellini E.E., Giannasi D., Morganti F. and Chiellini E.1997, Multifunctional polymeric materials for biomedical applications. Macromol Symp, Vol.118: pp.603 5. Chiellini E. and Solaro R., 1995, Multifunctional bio erodible/biodegradable polymeric materials. Macromol Symp, Vol. 98, pp. 803. 6. Weiland M, Daro A, David C. 1995, Biodegradation of thermally oxidized polyethylene. Polymer Degradation Stability, vol., 48 (2) pp. 275–89. 7. Hashimoto K., Hamano T. and Okada M., 1994, Degradation of several polyamides in soils. J. Appl Polym. Sci., Vol. 54, pp. 1579. 8. Yamano Naoko E., Atsuyoshi Nakayama E., N orioki Kawasaki , Noboru Yamamoto E, and Seiichi Aiba, 2008, Mechanism and Characterization of Polyamide 4 Degradation by Pseudomonas sp. J Polym Environ, pp. 1-6. 9. Orhan Y. and Buyukgungor H., 2000, Enhancement of biodegradability of disposable polyethylene in controlled biological soil. International Biodeterioration and Biodegradation, Vol.45, pp.49-55. 10. Barry E. Digregorio, 2009, Biobased Performance Bioplastic: Mirel. Chemistry & Biology Innovations, pp. 10-19. 11. Deguchi T., Kitoka Y., Kakezawa, M. and Nishida T., 1998, Purification and characterization of a nylon degrading enzyme, Applied Environmental Microbiology, Vol. 64, pp. 1366-1371. 12. S.Selvaraj and Dr.P.Venkataramaiah, “Production of Nylon-6 Fr Lever using an Injection Moulding Tool and Identification of Optimum Process Parameter Combination”, International Journal of Mechanical Engineering & Technology (IJMET), Volume 3, Issue 3, 2012, pp. 270 - 284, ISSN Print: 0976 – 6340, ISSN Online: 0976 – 6359.