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For exceptions, permission may be sought for such use through Elsevier’s permissions site at: http://www.elsevier.com/locate/permissionusematerial Polymer Degradation and Stability 92 (2007) 244e252 www.elsevier.com/locate/polydegstab py Degradation of agar films in a humid tropical climate: Thermal, mechanical, morphological and structural changes a co Y. Freile-Pelegrı́n a,*, T. Madera-Santana a, D. Robledo a, L. Veleva b, P. Quintana b, J.A. Azamar b Department of Marine Resources, CINVESTAV-IPN, Carretera Antigua a Progreso Km 6, A.P. 73 Cordemex, 97310 Merida, Yucatan, Mexico Department of Applied Physics, CINVESTAV-IPN, Carretera Antigua a Progreso Km 6, A.P. 73 Cordemex, 97310 Merida, Yucatan, Mexico b al Received 22 August 2006; received in revised form 16 November 2006; accepted 18 November 2006 Available online 26 December 2006 on Abstract pe rs Agar films were subjected to natural weathering exposure in a humid tropical climate for 90 days to determine their biodegradation behavior and functionality. Exposed samples were taken at 15, 30, 45, 60 and 90 days. Mechanical, thermal, structural and morphological properties were determined using tensile test, differential scanning calorimetry (DSC), attenuated reflectance infrared spectroscopy (ATR-FTIR), X-ray diffraction and environmental scanning electron microscopy (ESEM). The photodegradation process and temperatureerelative humidity fluctuations promoted a decrease in agar mechanical properties in early exposure stages (30e45 days) caused by a reduction in agar molecular size and a decrease in the number of sulfate groups. These changes alter agar crystallinity, causing contraction that leads to formation of micro-fractures and embrittlement, and promote microbial attack. Accelerated weathering exposure of agar films showed that outdoor climate parameters play an important role in their degradation. These results will aid in further research to determine the potential use of agar as an environmentally friendly solution to the problem of biodegradable composites disposal. Ó 2006 Elsevier Ltd. All rights reserved. r's Keywords: Agar; Biodegradation; Mechanical properties; Thermal properties; FTIR, DRX; Tropical humid climate 1. Introduction Au th o Biodegradable polymers have been developed recently in response to public concern over the growing environmental problem of plastic wastes. These wastes originate from the use of non-renewable raw materials and accumulation of this non-biodegradable packaging represents an environmental threat. The search for low-cost, environmentally friendly materials has led to the development of different biodegradable plastics incorporating natural polymers (i.e. starch, cellulose) into conventional plastic formulations. When these plastic blends are placed in biologically active environments the natural polymers in them accelerate the degradation rate by microbial attack and/or exposure to atmospheric agents * Corresponding author. Tel.: +52 999 1242159; fax: +52 999 9812917. E-mail address: [email protected] (Y. Freile-Pelegrı́n). 0141-3910/$ - see front matter Ó 2006 Elsevier Ltd. All rights reserved. doi:10.1016/j.polymdegradstab.2006.11.005 such as solar radiation, wind, rain and humid conditions, among others [1]. Chemical degradation may also occur in these blends when molecular bonds break due to the material’s inherent instability. All these processes aid in break-down (degradation) of materials and consequent natural recycling processes. However, one important reason why some natural polymers are not incorporated into consumer products is their degradation times that range from months to several years (3e4). Also, these polymers are not as strong as synthetic polymers. Many studies have focused on the search for biopolymers capable of substituting synthetic polymers or filled polymers in packaging film, food or pharmaceutical coating applications [2]. Several biopolymers (e.g. lipids, protein and polysaccharides) have proved extremely interesting since they meet a number of specific functional requirements (moisture barrier, solute and/or gas barrier, water or lipid solubility, color and appearance, good mechanical and Y. Freile-Pelegrı́n et al. / Polymer Degradation and Stability 92 (2007) 244e252 2. Experimental py The agar used was extracted by AGARMEX (Mexico) from Gelidium robustum, the main agar source in Mexico [12]. The agar films were prepared as follows: 3 g of agar powder were dissolved in 200 mL distilled water at 98 C for 0.5 h; the hot agar solution was poured into square plastic moulds, left at room temperature for 24 h to gel and then dried at 60 C in a vacuum oven for 36 h. co 2.1. Test site and sample exposure on al The test site was located in the ruraleurban humid atmosphere of Merida city (21 010 N, 89 370 W), 30 km from the Caribbean coast. The Yucatan Peninsula tropical humid climate is characterized by two seasons: dry (winter) and rainy (summer). Temperatures follow a cycle of warming beginning in February, a peak in May and a gradual decrease during the rainy season until reaching minimum levels in Decembere January due to cooler northerly winds. The agar films were exposed on a stationary rack [10] fixed to the laboratory roof (Fig. 1) at the site latitude angle (22 ). Outdoor conditions were accelerated by covering samples with glass (3 mm thick), with 5 cm of space between the glass and samples, to increase temperature, simulating a greenhouse effect. Triplicate samples were taken at 15, 30, 45, 60 and 90 days during the experimental period (JanuaryeApril 2004). On-site temperature and irradiance were recorded every 30 Au th o r's pe rs rheological characteristics, non-toxic) more effectively than conventional synthetic materials [2]. Red marine seaweeds (Rhodophyta) are the source of some promising biopolymers since they contain considerable amounts of the polysaccharide agar, which has a unique structure. In seaweeds, agar fulfils a function analogous to that of cellulose in terrestrial plants, although it differs because marine seaweeds require a more flexible structure to resist currents and wave motion [3]. It is extracted from the cell matrix of seaweeds of the Gelidiaceae and Gracilariaceae families. Agar is a hydrophilic colloid consisting of polysaccharides that have the ability to form reversible gels simply by cooling a hot aqueous solution. It is composed of alternating 1,3-linked-D-galactose and 1,4-linked 3,6-anhydro-L-galactose units. This disaccharide can be substituted by sulfate esters and methoxyl, and may also carry pyruvic acid residues [4]. The type, amount and location of these substitutes strongly affect the physical properties of the gel and, therefore, its functionality [5,6]. Agar gel melts on heating and resets on cooling. This cycle can be repeated for an indefinite number of times without compromising gel mechanical properties. Cooling causes agar thermal effusivity to increase to a maximum that coincides with gelation [7], which is produced exclusively by hydrogen bonds. Because of its ability to form very hard gels at very low concentrations, agar has been used extensively as a gelling agent in the food industry and in other applications such as microbiology and molecular biology techniques. More recent uses of agar include dental moulds, casting of archaeological pieces and sculpture moulds [8]. Due to its combination of renewability and biodegradability, its enormous gelling power, and the simplicity of the extraction process [3], agar has been singled out as a promising candidate for future use in plastic materials. Despite its promise, however, only one study has been done using agar in combination with synthetic polymers to produce materials with degradable properties [9], and no research has been done on its degradation behavior. The accelerated outdoor weathering test of degradation has been used recently in a standardized form [10], and has been employed increasingly in response to growing industrial demand for decision-making data. In these tests, outdoor weathering is done using the sun as the irradiance source, but other studies have demonstrated that more than one weathering parameter can influence the rate of deterioration under these circumstances. For example, it has been reported that environmental temperature of humid tropical climate seems to be the key factor that impacts the rate of ageing of composites more than the ambient humidity [11]. The present study objective was to determine the biodegradation behavior and functionality of agar, as an innovative biodegradable material, under accelerated outdoor weathering in the humid tropical climate of the Yucatan Peninsula in southeast of Mexico. Morphological changes on agar films, as well as any mechanical, thermal and structural changes were characterized. 245 Fig. 1. Stationary rack for accelerated weathering test (for details see Ref. [10]). Y. Freile-Pelegrı́n et al. / Polymer Degradation and Stability 92 (2007) 244e252 246 minutes by a data logger (HOBOÒ Onset Computer Corp., Pocasset, MA, USA) placed under the glass and close to the samples (Fig. 2A,B). Location air temperature and relative humidity data during the experimental period were obtained from the National Water Commission (Consejo Nacional de Agua e CAN; http://www.cna.gob.mx) (data for days 7 and 80 are shown in Fig. 3A,B). and 100 scans. The technique applied was attenuated total reflectance (ATR) with an Avantar multibounce HATR accessory with ZnSe crystal at 45 . 2.4. X-ray diffraction analysis py Powder X-ray diffraction (XRD) patterns were recorded with a Siemens D-5000 diffractometer (Cu Ka wavelength of 1.5418 Å) operated at 35 kV and 25 mA. Agar films were placed in a zero background rotary (15 rpm) Si sample holder to avoid any background interference. Measurements were made over the 5e60 (2q) angular range, at a step time of 8 s and at a step size of 0.02 (2q). 2.2. Molecular weight determination co Molecular weight of the tested agar films was calculated from their intrinsic viscosity values [h]. Intrinsic viscosity of the agar samples in an aqueous 0.75 M NaSCN solution was measured using a capillary viscometer (CannoneUbbelohde, State College, PA) at 35 0.5 C. The weight-average molecular weight ðMwÞ was calculated with the MarkeHouwink equation [13]: 2.5. Mechanical properties’ characterization Tensile strength, strain at break and elastic modulus of the agar films were tested using an Instron (model 4442) universal tensile machine. The tensile procedure was done according to ASTM method D882-00 [14], and each tensile testing was calculated with the Series IX ver. 5.1 program (Instron Engineering Corp., Canton, MA, USA). 2.3. Spectroscopic characterization A 40 35 30 r's Temperature (ºC) 45 Enthalpy (DH) and melting temperature (Tm) were measured with a differential scanning calorimeter (DSC, Perkin pe 55 50 2.6. Thermal characterization rs The agar films’ FTIR spectra were determined using an infrared spectrometer with Fourier transformation (Nicolet model Nexus 870). Measurement range was 4000e 650 cm1, with a 4 cm1 resolution, 0.475 cm1/s scan speed on al h ¼ 0:07Mw0:72 25 20 th o 15 10 Irradiance (W m-2) Au 50 B 40 30 20 10 0 0 15 30 45 60 75 90 Days Fig. 2. In situ daily average (A) temperature and (B) irradiance of agar films during accelerated weathering exposure on stationary rack. Bars represent standard deviation. Y. Freile-Pelegrı́n et al. / Polymer Degradation and Stability 92 (2007) 244e252 A 100 30 80 20 70 60 100 B 90 80 50 py 90 70 40 60 50 30 40 al 30 20 2 4 6 8 10 12 14 16 18 20 22 24 Hours rs Fig. 3. Daily changes in air temperature (-), relative humidity () and in situ agar film temperature (,) after 7 days (A) and 80 days (B) of accelerated weathering exposure. on 20 0 (p < 0.01). The AMW decreased drastically from 105,000 g/mol to w25,000 g/mol after 30 days of weathering exposure (Fig. 4). Beginning at 45 days, AMW showed a slight but continuous decrease, reaching a minimum of w8000 g/mol at 90 days. Depending on the agar source, chain molecular weight varies from 80,000 g/mol to 140,000 g/mol [13]. After exposure, agar film functional groups exhibited changes in the FTIR spectra (4000e2500 cm1, Fig. 5A; 1800e800 cm1, Fig. 5B) in comparison to the typical spectrum of pristine agar film (0 day). Absorption bands between 3400 and 3200 cm1 (associated with OeH stretching [15]), decreased notably, indicating water loss. At 60 and 90 days, the peaks at 2850e2820 cm1 (associated with methoxyl groups [5]) and 1640 cm1 (caused by stretching of the conjugated peptide bond formed by amine (NH) and acetone (CO) groups [16]) decreased in intensity. Similar behavior was observed for the peak at 1370 cm1, which is associated with ester sulfate [5]. In contrast, the characteristics agar bands at 1070 and 930 cm1 (associated with the 3,6-anhydro-galactose bridges [17]), and at 890 cm1 (attributed to the CeH of residual carbons of b-galactose [18]) showed no changes in intensity with increased exposure time. These results suggest that the agar photodegrades in sunlight. Photodegradation is the chemical transformation of a compound into smaller compounds caused by absorption of UV, visible, or infrared radiation, including irreversible alterations such as changes in molecules, protein denaturing, and bonding with or cleavage from other atoms or molecules [19]. The agar spectra observed here showed no significant changes in galactose structure during exposure and bands characteristics of this structure remained permanent. Galactose chain length, however, was modified, as manifest in the agar film AMW behavior at different exposure times. Changes in AMW were attributed to chain scission, which produces a drastic reduction in AMW at 15e30 days exposure. Molecular chain scission, however, does not open the galactose ring, suggesting that no major functional group transformation co 40 Relative humidity (%) Temperature (ºC) 50 247 2.8. Statistical analysis Au Film mechanical and thermal variables were tested for normality (KolmogoroveSmirnov) and homogeneity of variances (Bartlett test). Weathering effects on mechanical properties were determined with an ANOVA (p < 0.05). All statistical calculations were run with the Statistica ver.6 (Statsoft, Inc.) program. 105000 90000 Average Mw (g th o r's Morphological changes were described based on images of the agar films. Differences in surface film morphology were observed by environmental scanning electron microscopy (ESEM, Phillips XL 30). Average film thickness was determined by measuring 10 different zones with an electronic gauge (Mitutoyo, Japan) with a precision range between 0.1 and 1% as a function of thickness value (0e100 mm). mol-1) 2.7. Morphological characterization pe Elmer model DSC-6). Samples of 10 mg agar film were heated to 200 C at a rate of 10 C/min and then cooled to room temperature. 75000 60000 45000 30000 15000 3. Results and discussion 0 3.1. Structural changes 0 15 30 45 60 75 90 Days Significant changes in average molecular weight (AMW) as a function of exposure time were observed in the agar films Fig. 4. Agar film average molecular weight after 0, 15, 30, 45, 60 and 90 days of accelerated weathering exposure. Y. Freile-Pelegrı́n et al. / Polymer Degradation and Stability 92 (2007) 244e252 248 1400 A 90 1200 60 1000 Counts 30 15 0 800 60 600 py 45 45 0 400 30 15 co 200 90 4000 3500 3000 2500 10 Wavenumber (cm-1) B 20 30 40 50 60 Fig. 6. XRD analysis of agar films at 0, 15, 30, 45, 60 and 90 days of accelerated weathering exposure. al 90 60 high-angle reflections recorded at this exposure time suggests a lower molecular state order that may be related to the agar chain scission apparent in the AMW decrease. The reason there being only minor changes in the diffractogram at 15 days exposure remain unclear. on 45 30 15 rs 0 1600 1400 1200 1000 Wavenumber (cm-1) 800 r's Fig. 5. ATR infrared spectra of agar films in the wavelength ranges of 4000e 2500 cm1 (A) and 1800e800 cm1 (B) at 0, 15, 30, 45, 60 and 90 days of accelerated weathering exposure. Au th o occurred during exposure and that only free radical chain scission may have taken place. Dehydration and depolymerization are generally considered as two main processes in the polysaccharides degradation mechanism [20]. The decrease in the methoxyl and sulfate groups observed in the longest exposure period (60 and 90 days) was mainly due to depolymerization of the agar. Similar results have been reported during degradation of carrageenan, another sulfated anionic polymer from red seaweeds [21]. The XRD pattern for pristine agar film (0 day) showed an orderly structure and a high degree of crystallinity indicated by a peak at 19.9 2q and a slight shoulder at 13.83 2q (Fig. 6). This peak was only slightly affected at 15 days exposure, but its diffraction intensity decreased drastically at longer exposure times, reaching a minimum at 90 days. The XRD pattern behaved similarly at 30, 45 and 60 days, and the low 2q reflection becomes progressively more evident in the diffractograms. At 90 days the peak at 19.9 2q had narrowed, indicating that crystalline order in the agar molecules had been altered. The lower number of The stressestrain curve pattern indicated that agar mechanical properties changed as exposure time increased (Fig. 7). At 45 and 60 days, the agar films had become brittle, exhibiting 25e30% reduction in their strain values. By 90 days the samples could not be tested due to their extreme brittleness. The films also experienced a progressive decay in tensile strength (Fig. 8A) and strain at break (Fig. 8B), with a 50% overall reduction in both properties and minimum values recorded beginning on day 45. No significant difference (p > 0.05) was observed between values for 45 and 60 days. Elastic modulus 3 Stress (MPa) 1800 pe 3.2. Mechanical changes 2 Exposure time, days: 0 15 30 45 60 1 0 0 1 2 3 4 5 6 Strain (%) Fig. 7. Stressestrain curves of agar films at 0, 15, 30, 45, 60 and 90 days of accelerated weathering exposure. Y. Freile-Pelegrı́n et al. / Polymer Degradation and Stability 92 (2007) 244e252 115 A 110 300 2.0 1.5 B 250 95 200 90 85 80 75 6 70 0 15 30 45 150 100 50 60 75 90 Days Fig. 9. Changes in agar film melting temperature and heat of fusion at 0, 15, 30, 45, 60 and 90 days of accelerated weathering exposure. 2 3.3. Thermal changes on C Agar melting temperature (Tm) ranged from 74 to 97 C, with no significant differences (p > 0.05) during the first 45 days of exposure (Fig. 9). It then increased and remained relatively constant, with no significant differences (p > 0.05) between longer exposure times. Heat of fusion DHmelt ranged from 177 to 306 J/g, decreasing at 15 days and reaching a minimum at 30 days. This parameter then reached higher values at 45 and 60 days exposure, with no significant differences between values during the last 30 days of exposure. These increases in Tm and DHmelt of the exposed agar films may be due to changes in molecular structure associated with ageing behavior, such as greater crosslinking and chain scission. In polymers exposed to solar radiation, side chain bonds break and become crosslinking sites. This increased crosslinking inhibits relative chain motion, strengthens the polymer and makes it more brittle [27]. These changes in crystallinity with greater exposure time were confirmed by the melting enthalpy values shown in the DSC curves and the X-ray analysis. Similar results have been reported in a study of starch, another biopolymer widely used as biodegradable additive, in which the authors state that biodegradation tends to increase thermal stability of this polysaccharide [28]. rs 0 100 al 4 80 60 pe Strain at break (%) 100 py 2.5 105 co Melting temperature (ºC) 3.0 1.0 Elastic modulus (MPa) 350 Heat of fusion (J g-1) Tensile strength (MPa) 3.5 249 40 20 15 30 45 r's 0 60 Days th o Fig. 8. Agar film changes in tensile strength (A), strain at break (B) and elastic modulus (C) at 0, 15, 30, 45 and 60 days of accelerated weathering exposure. Au (Fig. 9C), however, showed an increase at 15 days and reached a maximum at 30 days. It then decreased at 45 and 60 days, but still had values significantly higher (p < 0.05) than those observed at 0 and 15 days. This increase may be explained by crosslinking after the chain scission reactions [22], which could increase film rigidity. The overall decay in agar film mechanical properties during exposure observed here may be associated with a reduction in molecular weight produced by chain scission which is promoted in turn by photodegradation. Studies on the effect of molecular weight on the characteristics of agar [23,24] and other polymers [25,26] have shown that the mechanical properties decrease as molecular weight decreases. Therefore, the decay in agar film mechanical properties observed here indicates a decrease in plastic characteristics, which coincide with results reported for other polymers [27]. 3.4. Morphological changes As exposure time increased, agar surface morphology changed from translucent and smooth to irregular and rough with bent edges. The ESEM images before degradation (Fig. 10B1) and after weathering exposure show small spots at 30 days (Fig. 10B2) followed by randomly distributed fungus growth and micro-fractures, and large unaltered areas (Fig. 10B3,B4). At 90 days, fungal and bacterial colonizations are much more evident on the film surface and a network of micro-fractures and holes in different patterns has clearly degraded the surface (Fig. 10B5). Y. Freile-Pelegrı́n et al. / Polymer Degradation and Stability 92 (2007) 244e252 Au th o r's pe rs on al co py 250 Fig. 10. Surface morphology changes in agar film during accelerated weathering exposure. (A) Macro-morphological observations; (B) Micro-morphological observations; numbers indicate exposure time: 1 ¼ 0 day; 2 ¼ 30 days; 3 ¼ 45 days; 4 ¼ 60 days; and 5 ¼ 90 days. Y. Freile-Pelegrı́n et al. / Polymer Degradation and Stability 92 (2007) 244e252 3.5. Agar degradation behavior co py daily temperature and humidity led to deterioration in agar film morphological, structural and mechanical properties during the early stages (30e45 days) of weather exposure as a result of decreases in molecular size and the number of sulfate groups. These changes alter agar crystallinity, cause it to contract and lead to consequent formation of micro-fractures and polymer embrittlement. These chemical and morphological conditions promote microbial and fungal attacks. The agar degradation process data reported here will be important in further research on potential uses of agar as an environmentally friendly solution to the problem of biodegradable composite disposal. Acknowledgements on al This research was financed by SAGARPA-CONACYT under project contract no. 2002-C01-1057. The authors thank C. Chávez Quintal and D. Aguilar for technical assistance during the experimental work. Mechanical and thermal properties were determined at the FIQ-UADY and ITM-Merida. References [1] Lemaire J. Control of the weathering of polymers in plasticulture. Plasticulture 1993;97:17e22. [2] Gontard N, Guilbert S. Bio-packing technology and properties of edible and/or biodegradable material of agricultural origin. In: Maathlouth M, editor. Food packing and preservation. Glaskow: Blackie Academic and Professional; 1994. p. 159e81. [3] Stanley NF. Agar. In: Stephen AM, editor. Food polysaccharides and their applications. New York: Marcel Dekker; 1995. p. 187e99. [4] Duckworth M, Yaphe W. The structure of agar. Part I. Fractionation of a complex mixture of polysaccharides. Carbohydr Res 1971;16:189e97. [5] Armisén R, Galatas F. Production, properties and uses of agar. In: McHugh DJ, editor. Production and utilization of products from commercial seaweed. FAO Fish Tech Papers, 288; 1987. p. 1e57. [6] Freile-Pelegrı́n Y, Murano E. Agars from three species of Gracilaria (Rhodophyta) from Yucatan Peninsula. Bioresour Technol 2005;96: 295e302. [7] Freile-Pelegrı́n Y, Bante J, Alvarado-Gil JJ, Yáñez-Limón M. Photothermal characterization of the gelation process in Gelidium robustum agar. J Phys IV 2005;125:821e4. [8] Armisén R, Galatas F. Handbook of hydrocolloids. In: Phillps G, Willians P, editors. USA: Woodhead Publishing UK; 2000. p. 450. [9] Lee JP, Lee KH, Song HK. Manufacture of biodegradable packing materials from agar by freeze-drying. J Mater Sci 1997;321:5825e32. [10] Veleva L, Valadez-González A. Stationary rack and black under glass exposures of mineral filled polyethylene in inland and marine tropical climates. In: Durability 2000: accelerated and outdoor weathering testing, vol. 1385. ASTM International STP; 2000. 61e72. [11] Valadez-González A, Veleva L. Mineral filler influence on the photooxidation mechanism degradation of high density polyethylene. Part II: natural exposure test. Polym Degrad Stab 2004;83:139e48. [12] Robledo D. The seaweed resources of Mexico. In: Critchley AT, Ohno M, editors. Seaweed resources of the world. Japan: JICA; 1998. p. 331e42. [13] Rochas C, Lahaye M. Average molecular weight and molecular weight distribution of agarose and agarose-type polysaccharides. Carbohydr Polym 1989;10:289e98. [14] ASTM D882. Standard test method for tensile properties of thin sheeting. Designation D822-00. In: Annual book of ASTM standards. Philadelphia, PA; 2000. p. 160e68. [15] Tako M, Higa M, Medoruma K, Nakasone Y. A highly methylated agar from red seaweed, Gracilaria arcuata. Bot Mar 1999;42:513e7. Au th o r's pe rs The present results indicate that during accelerated weathering exposure agar films absorb solar energy, mainly inducing photodegradation, consequent chain scission and a decrease in sulfate and methoxyl groups. Diminished mechanical properties caused by a reduction in molecular weight make the material more rigid and lead to the formation of surface cracks. The drastic weather changes recorded in Yucatan during the trial period enhanced the agar film biodegradation rate. As it has been stated, the prevailing weathering process in the tropical humid climate of the Yucatan Peninsula can be extremely complex, and involves a number of weathering factors acting in conjunction to produce polymer degradation [29]. The extreme fluctuations in daily temperature and high humidity recorded during the present accelerated weathering exposure trial promoted agar degradation. Similar results were found by Jakubowicz et al. [30], who reported that moisture can have a strong accelerating effect on polyethylene film degradation. Based on the weather data used here and previously reported data for the Merida ruraleurban environment [29], temperature in the area generally peaks around noon (38e 41 C), when relative humidity reaches about 40%, and falls at night, when relative humidity is about 100%. According to ISO 9223, time of wetness (TOW) is defined as the time during which a layer of moisture appears on a material surface exposed to the environment. This phenomenon occurs when relative humidity 80% at temperatures above 0 C [29]. These extreme daily changes in temperature and humidity cause surface cracking on agar films. Moreover, agar has a high hygroscopic character, which is important to maintain its structure, meaning its water content increases as humidity rises during the night. Agar is an aqueous gel the entire structure of which consists of polymer molecules linked only by hydrogen bonds; this network can store a large amount of water and allows it to move freely through the macroreticulum. Each molecule maintains its structure independently, so the gelation process in agar is not a polymerization but rather a simple electrostatic attraction [8]. Gelation of agar involves its conversion from a fluctuating disordered coil formation in solution to a rigid, ordered structure (co-axial double helix) which forms the junction zones of the gel network [8]. This pattern may explain why galactose rings in agar do not open and it can therefore maintain its structure, despite molecular chain scission during photodegradation. The decrease in molecule sulfate groups may promote microbial degradation on the damaged agar films. This is based on the fact that sulfation of a hydroxyl group in galactose residues can prevent enzymatic hydrolysis [31], and that reports on agar properties have demonstrated the antimicrobial character of these groups [32,33]. 4. Conclusions Accelerated weathering exposure of agar films suggests that outdoor climate parameters play a significant role in the degradation process. Both photodegradation and fluctuations in 251 252 Y. Freile-Pelegrı́n et al. / Polymer Degradation and Stability 92 (2007) 244e252 [16] Cristiaen D, Bodard M. Spectroscopie infrarouge de films d’agar de Gracilaria verrucosa (Huds) papefuss. Bot Mar 1983;26:425e7. [17] Chirapart A, Ohno M, Ukeda H, Sawamura M, Kusunose H. Chemical composition of agars from a newly reported Japanese agarophyta, Gracilariopsis lemaneiformis. J Appl Phycol 1995;7:359e65. [18] Matsuhiro B. Vibrational spectroscopy of seaweeds galactans. Hydrobiologia 1996;326/327:481e9. [19] Malešic J, Kolar J, Strlic M, Kocar D, Fromageot D, Lemaire J, et al. Photoinduced degradation of cellulose. Polym Degrad Stab 2005;89:64e9. [20] Soares RMD, Lima AMF, Oliveira RVB, Pires ATN, Soldi V. Thermal degradation of biodegradable edible films based on xanthan and starches from different sources. Polym Degrad Stab 2005;90:449e54. [21] Relleve L, Nagasawa N, Luan LQ, Yagi T, Aranilla C, Abad L, et al. Degradation of carrageenan by radiation. Polym Degrad Stab 2005;87:403e10. [22] Bottino FA, Cinquegrani AR, Di Pasquale G, Leonardi L, Pollicino A. Chemical modifications, mechanical properties and surface photo-oxidation of films of polystyrene (PS). Polym Test 2004;23:405e11. [23] Murano E. Chemical structure and quality of agars from Gracilaria. J Appl Phycol 1995;7:245e54. [24] Freile-Pelegrı́n Y, Robledo D. Influence of alkali treatment on agar from Gracilaria cornea from Yucatan, Mexico. J Appl Phycol 1997;9:533e9. [25] O’Donnel B, Whyte JR. Stress-accelerated photo-oxidation of polypropylene and glass-fibre-reinforced polypropylene. Polym Degrad Stab 1994;44:211e22. Au th o r's pe rs on al co py [26] Sousa AR, Amorim KLE, Medeiros ES, Mélo TJA, Rabello MS. The combined effect of photodegradation and stress cracking in polystyrene. Polym Degrad Stab 2006;91:1504e12. [27] Callister WD. Materials science and engineering: an introduction. 6th ed. New York: John Wiley and Sons; 2003. p. 848. [28] Morancho JM, Ramis X, Fernández X, Cadenato A, Salla JM, Vallés A, et al. Calorimetric and thermogravimetric studies of UV-irradiated polypropylene/starch-based materials aged in soil. Polym Degrad Stab 2006; 91:44e51. [29] Veleva L, Pérez G, Acosta M. Statistical analysis of the temperaturee humidity complex and time of wetness of a tropical climate on the Yucatan Peninsula in Mexico. Atmos Environ 1997;31:773e6. [30] Jakubowicz I, Yarahmadi N, Petersen H. Evaluation of the rate of abiotic degradation of biodegradable polyethylene in various environments. Polym Degrad Stab 2006;91:1556e62. [31] Usov AI, Ivanova EG. Polysaccharides of algae. XXXVII. Characterization of hybrid structure of substituted agarose from Polysiphonia morrowii (Rhodophyta, Rhodomelaceae) using b-agarasa and 13C-NMR spectroscopy. Bot Mar 1987;30:365e670. [32] Neushul M. Antiviral carbohydrates from marine red algae. Hydrobiologia 1991;204e205:99e104. [33] Damonte E, Neyts J, Pujol CA, Snoeck R, Andrei G, Ikeda S, et al. Antiviral activity of a sulfated polysaccharide from red seaweed Nothogenia fastigata. Biochem Pharmacol 1994;47:2187e92.