Dariusz SOBKÓW*, Joanna BARTON, Krystyna CZAJA, Marek SUDOŁ, Beata MAZOŃ – Division of Chemical Technology and Polymer Chemistry, Faculty of Chemistry, University of Opole, Opole, Poland Please cite as: CHEMIK 2014, 68, 4, 347–354 Atmospheric ageing Recently manufacturers of products developed on polymer basis put a lot of focus in the safety of their products, including their durability under use conditions, especially outdoors, where due to number of external factors appearance may change (e.g. discolouration, tarnishing or cracking) and/or loss of desired properties e.g. mechanical. This occurs usually as a result of material degradation due to the change of its chemical structure (including oxidation, reduction of molecular weight due to the breaking of macromolecular chains or its increase as a result of their crosslinking and branching) [1, 2]. Change process occurring in materials induced by set of external environmental factors is called atmospheric ageing [3]. Usually it is induced by sunlight (mainly by light from UV range – photodegradation), and its rate might be increased by heat (varying temperature – thermodegradation), precipitation (hydrolytic degradation), air pollution, or even by wind and stress (mechanical degradation) [4÷8]. Atmospheric ageing is a physicochemical process causing gradual destruction of materials [9], usually as a result of change in chemical structure induced by simultaneous and interdependent radical photo- and thermooxidation processes [10]. Thermooxidative degradation occurs in the whole bulk of polymer, while photodegradation occurs mostly in its surface and subsurface layer, due to the limited possibility of UV radation penetration to deeper layers of material [11]. The type and intensity of material property changes during the exploitation of product manufactured from it depends mostly on material’s structure and structural defects, morphology, mainly content of crystalline phase, type and content of other substances (e.g. fillers, modificators, contaminants), as well as product shape and dimensions, type and intensity of factors causing changes in polymer, and finally the exposure time [4]. Polymeric material degradation might be also initiated or assisted by present additives, including catalyst residues, as well as environmental contaminants. Moreover, important role is played by such factors as even low content of hydroperoxide, carbonyl groups as well as content of double bonds that by might generated additionally during material processing and storage. The main light absorbers, responsible for the initiation of photochemical reactions are carbonyl groups. The degradation reaction usually starts from absorbing UV radiation by carbonyl groups and progresses further with assistance of generated radicals, causing cross-linking or breaking of macromolecule chains. Both mentioned processes are main and competitive degradation mechanisms. The physical effect of photodegradation is surface cracking and loss of material rigidity and strength [12]. The intensity of sun radiation that reaches Earth surface is not a constant value. The value of intensity depends on latitude, time of year and day, cloudiness and atmosphere permeability. Due to that, atmospheric ageing of the same composite might progress differently depending on the climate zone or current conditions [10]. In order Corresponding author: Dariusz SOBKÓW – M.Sc., e-mail:dariusz.sobkow@uni.opole.pl nr 4/2014 • tom 68 to evaluate composite materials resistance against external factors it is necessary to carry out ageing tests in natural conditions. Such tests, carried out in testing ground stations equipped with climate factor measurement instruments shall last for at least one year, although due to the variability of natural environmental conditions, the longer, few year period is recommended [2]. Such tests are very time-consuming and thus it was necessary to develop methods for accelerated ageing under laboratory conditions. The time reduction of lab tests is usually possible due to the intensification of UV radiation, usually emitted by xenon lamps equipped with suitable set of filters, imitating sun light spectrum. Lab tests are performed in various climate chambers, that allow programming and constant control of radiation intensity, temperature and humidity inside test chamber, temperature of sample surface, time of water sprinkling (imitating rain) as well as airflow (imitating wind). Lab tests have also another advantage – they might be repeated in identical conditions, what is practically impossible in the case of ground testing. In order to evaluate the degradation progress of the material subjected to ageing process, it is usually necessary to determine the change in its functional properties, i.a. mechanical ones (tensile strength, impact strength or hardness). In this case, it is understood that deterioration of measured property by more than 50% disqualifies the material for further use. By using the additional set of complementary analyses regarding morphology and structure changes preceding the change of functional properties, it is possible to predict more precisely the duration of safe material use. The group of researchers from the Division of Chemical Technology and Polymer Chemistry of the University of Opole for several years has been carrying out evaluation of durability of various, mainly polymeric materials of varying structure and composition (in case of composites and other multi-component compositions) and their field of application. The tests are performed on their own testing ground station equipped with set of measurement sensors registering sun radiation intensity in whole spectral range and in most destructive UV range, ambient and sample surface temperature and air humidity. The aforementioned climate data have been archived since 2002. The lab tests are performed using apparatuses Xenotest Alpha HE and Wezerometr Ci4000, according to standards or in other, set conditions. The most frequent tests concern reproduction of environmental conditions in lab tests for materials used outdoors or simulation of sun light spectra passing through the window for materials used indoors. At the same time, we have number of apparatuses for morphology and structure tests and for evaluation of functional properties of studied polymeric materials. Authors’ works involve ageing tests for various materials, including workpieces made of various plastics used in automotive industry, polyurethane and polystyrene foams, paints and varnishes, packaging foils, labels and stickers, composite materials, including numerous wooden-polymer composites (WPC) of varying composition. The example of spectrum cascade (Fig. 1) for selected WPC presents increasing intensity of carbonyl and ether bands that correspond to various oxidation products that form in the material. • 351 50 Years of Chemistry in Opole Studies of material resistance against natural environmental factors 50 Years of Chemistry in Opole Fig. 1. Set of spectra for WPC produced on base of PEHD and wood flour Lignocel 9 with marked characteristic bands generated during ageing process under natural conditions (ageing time – from 3 to 61 months) Micrographs (Fig.2) confirm surface cracking for similar composite with ageing progress, while visible cracks are systemically deepening and widening creating wide-spread mesh of cracks, that with time forms separates fragments of structure. Changes of wood flour morphology in WPC were also observed – the flour swelling is visible in form of formed clusters. Fig. 2. SEM micrographs of WPCs based on PEHD matrix with wood flour Lignocel C120 (ageing under natural conditions) Properly developed accelerated ageing tests in ageing chambers allow to accelerate ageing process of materials and obtain definitely faster answer to a question how given material will behave during the exposure to natural conditions. These methods are also applicable to comparative studies of various materials (Fig. 3) Fig. 3. Changes of carbonyl band of WPCs on polyolefin matrix subjected to ageing under ground (HDL, LDL, PPL) and lab conditions (xHDL, xLDL, xPPL) Biodegradation Degradation of plastics and composites occurring in the environment due to microorganisms is called biodegradation [13, 14]. This type of degradation might be caused both by bacteria and by fungi that grow in favorable growth conditions [15]. The correct growth of fungi is ensured by the access to sufficient amount of nutrients. The optimum environmental conditions are: approx. 70% humidity, suitable temperature and pH in range 5.6–6.5 [16]. The growth of particular species of fungi is determined also by type and properties of base, on which they grow (contents of various minerals, salinity) [17]. 352 • The biodegradation processes can be divided into aerobic and anaerobic. In former case, the main products of decomposition occurring in the presence of oxygen are CO2, water and biomass. In anaerobic conditions methane is also generated [14]. Activity of microorganisms to a great extent affects functional value of materials (wood, paper products, plastics, ceramic construction materials, paints and varnishes) exposed to contact with microbes [18,19] Currently used materials show varying resistance against destructive action of biofactors. Meanwhile this is the quality that determines their potential application range. Susceptibility of polymer material to biodegradation processes results, among others form chemical structure and polymer molecular weight, its physicochemical properties, as well as type and intensity of impact of microorganisms [20, 21]. The matrix of polymeric composites is usually made of synthetic polymers showing none or negligible susceptibility to biodegradation processes [22]. It is a result of i.a. chemical structure and hydrophobic nature of their surface. However, the number of factor effecting acceleration of biocorrosion processes, i.e. presence of easily hydrolysing functional groups (ester, amide), low degree of crystallinity and large content of amorphous phase, hygroscopy (easy transport of of enzymes produced by microorganisms) or low molecular weight [23÷25]. Biodegradation of polymeric materials include number of processes of chemical and biological nature. As a result of interaction between material and enzymes produced by microorganisms, the polymer chains are shortened, what causes the reduction of molecular weight as well as change of physicochemical and mechanical properties. This results in increased susceptibility of material to other degradation processes [26]. Depending on the application field of polymeric materials, it is desirable that it shows particular resistance against biodegradation. On one hand there are efforts aiming at development of new materials showing increased susceptibility to biodegradation processes (e.g. packagings and other materials short-living), while on the other hand there is an ongoing research on improvement of construction materials durability (construction, automotive industry). While it is obvious that seeking to increase biodegradation rate for different types of materials is intended to i.a. improve waste management systems, the desire to protect materials from microorganisms is mostly a result of two different factors. Firstly, material corrosion caused by biodegradation might pose a threat to life and health of materials’ users [27]. What’s more, the toxic impact of fungi might turn out to be even more dangerous [28, 29]. Many of fungi species produces mycotoxins (e.g. aflatoxins) that even in a single dose might lead to irreversible, precancerous and cancerous lesions. Other diseases include: allergic rhinitis, bronchial asthma, fungal dermatitis, allergic pulmonary alveolitis and food allergies [16]. Current tendency in material engineering is related to the search for materials that could be an alternative for synthetic polymeric materials. Performing various modifications that give materials new, unique properties or developing materials containing renewable plant materials. However, it is believed that content of plant materials reduces lifetime of these materials making them susceptible to biocorrosion caused by hyphal fungi. For this reason, the research aiming to evaluate factors causing deterioration of material properties under conditions of their potential application is an attractive scientific field determining future application field of developed composites. The subject of research in scope of evaluation of biological resistance performed by group from the Division of Chemical Technology and Polymer Chemistry in collaboration with employees of the Division of Analytical and Ecological Chemistry of UO are all types of materials: composites and polymer coatings, foils or nr 4/2014 • tom 68 3. 4. 5. 6. 7. 8. 9. Fig. 4. a) an example of culture grown on liquid mineral medium Czapek-Dox, b) an example of culture grown on solid medium – observation of colonization effect Presented in Figure 5 representative test results regarding composite biodegradation have proven that both environment of culture growth, as well as different composition of composite material (type, content of filler, presence of compatibiliser) are of importance to course of mycelium growth. 10. 11. 12. 13. 14. 15. 16. 17. Fig. 5. Mass balance obtained for culture grown on full Czapek-Dox medium and glucose-free Czapek-Dox medium (polymer materials based on PE-HD with 40% content of floud Lignocel C-120 and/or possible 5% content of compaitibiliser) expressed in grams of dried mycelium Summary Carrying out complex studies on photo-, thermo- and biodegradation allows to determine lifetime of products manufactured from studied materials under conditions corresponding to their potential area of application. Moreover, the research is also of cognitive nature in the scope of understanding the ageing processes nature and mechanisms and are essential part of works on development and implementation to exploitation new materials or their variations modified chemically or physically. Joanna Barton is a recipient of the scholarship under project “Ph.D. scholarships - investment in scientific staff of Opole voivodeship” co-funded by the European Union, within the European Social Found. Literature 1. 2. Andrady A. L. (Ed.): Plastic and the environment, John Wiley & Sons, Inc. 2003. Wypych G.: Handbook of material weathering, 4th edition, ChemTec Publishing, Toronto 2008, 99–115. nr 4/2014 • tom 68 18. 19. 20. 21. 22. 23. 24. ATLAS Material Testing Solutions, Weathering Testing Guidebook 2001. Sobków D., Czaja K.: Wpływ warunków przyspieszonego starzenia na proces degradacji poliolefin. Polimery 2003, 9, 627–632. 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Acemoglu, M.: Chemistry of polymer biodegradation and implications on parenteral drug delivery, International Journal of Pharmaceutics 2004, 277 (1–2), 133–139. Mohee, R., Unmar, G.: Determining biodegradability of plastic materials under controlled and natural composting environments. Waste Management 2007, 27 (11), 1486–1493. Szlezyngier W.: Tworzywa sztuczne. Tom 3. Wydawnictwo Oświatowe FOSZE 2000, 215–216. Mucha M.: Polimery a ekologia. Wydawnictwo Politechniki Łódzkiej 2002, 193–205. • 353 50 Years of Chemistry in Opole construction materials. The experiments testing susceptibility to biocorrosion are carried out for selected hyphal fungi. The cultures are grown on different type of mineral media (Fig. 4a) or in composting conditions. The result of the research is determination of material susceptibility to colonization (Fig. 4b), biodeterioration or biodegradation. The evaluation is performed based on macroscopic observations (evaluation of mycelium growth in comparison with control group), mass balance of mycelium or analysis of structural (ATR-FTIR) and surface changes (SEM). 50 Years of Chemistry in Opole 25. Łabużek S., Pająk J., Nowak B.: Biodegradacja tworzyw sztucznych. Ekologia 2005, 32–35. 26. Razza, F., Innocenti, F.D.: Bioplastics from renewable resources: The benefits of biodegradability. Asia-Pacific Journal of Chemical Engineering 2012, 7 (3), S301-S309. 27. Janińska B.: Foundations of Civil and Environmental Engineering 3, Wydawnictwo Politechniki Poznańskiej 2002, 47–64. 28. Andersson M.A., Nikulin M., Koljalg U., Andersson M.C., Rainey F., Reijula K., Hintikka E.L., Salkinoja-Salonen M.: Bacteria, molds, and toxins in waterdamaged building materials. Applied and Environmental Microbiology 1997, 63 (2), 387–393. 29. Fisher, M.C., Henk, D.A., Briggs, C.J.,Brownstein, J.S., Madoff, L.C., McCraw, S.L., Gurr, S.J.: Emerging fungal threats to animal, plant and ecosystem health. Nature 2012, 484 (7393), 186–194. * Dariusz SOBKÓW – M.Sc., is a graduate of the University of Opole in the field of chemistry in 2000, as well as in the field of economics (2003). He works at the Division of Chemical Technology and Polymer Chemistry, Faculty of Chemistry, University of Opole. Specialization: studies of material ageing under natural conditions and in accelerated laboratory tests, modification of polyolefins for their stabilization or degradation acceleration. e-mail:dariusz.sobkow@uni.opole.pl; phone: +48 77 452 71 07 Joanna BARTON – M.Sc., is a graduate of the Faculty of Chemistry of the University of Opole (2011). Currently, she a student of Environmental Doctoral Studies organized at the Faculty of Chemistry, Wroclaw University of Technology and the Faculty of Chemistry, University of Opole. Specialization: production and characterization of composites with renewable plant fillers and study on biodegradation processes of materials including evaluation of fungistatic properties. e-mail:jbarton@uni.opole.pl; phone: +48 77 452 71 35 Professor Krystyna CZAJA – (Ph.D., Eng.) is a graduate of the Faculty of Chemical Technology and Engineering of the Silesian University of Technology (1970). She has received academic degrees from the Faculty of Chemistry of Warsaw University of Technology in the field of chemical sciences: She obtained Ph.D. degree in 1977 After obtaining a doctorate, he earned habilitation in 1992. The title of full professor of chemical science was conferred on her in 2002 . She has been working at Opole academy since 1973, currently as a full professor at the Faculty of Chemistry of the University of Opole. Specialization: polymer chemistry and technology, mostly polyolefins including synthesis of metalloorganic catalysts and low-pressure (co) polymerization of olefins with the use of such catalysts, physical and chemical modification of polymers, polymer matrix composites and nanocomposites, characterization of molecular structure and polymer functional properties, particularly study of their thermo-, photo- and biodegradation. e-mail: krystyna.czaja@uni.opole.pl; phone: +48 77 452 71 40 Marek SUDOŁ – Ph.D., is a graduate in the field of chemistry of the State Higher Pedagogical College (currently University of Opole). Since his graduation, he has been working at the Faculty of Chemistry (till 2008 Institute of Chemistry) of this University. Scientific field: identification of micro- and macromolecular compounds by means of infrared spectroscopy and chemical and physical modifications of polyolefins for specific practical applications. e-mail:marek.sudol@uni.opole.pl; phone: +48 77 452 71 38 Beata MAZOŃ – M.Sc. in 1991 has graduated from the Institute of Chemistry of the University of Wroclaw. Since her graduation she has been working at the Division of Chemical Technology and Polymer Chemistry, University of Opole. Specialization: molecular characteristic of macromolecular compounds, mostly polyolefins by means of high-temperature gel permeation chromatography. beata.mazon@uni.opole.pl, +48 77 452 7110 Z prasy światowej – innowacje: odkrycia, produkty i technologie From the world press - innovation: discoveries, products and technologies Dokończenie ze strony 350 Przeciwbakteryjne metalopolimery Popularnie stosowane antybiotyki stają się coraz mniej skuteczne, ponieważ bakterie bardzo szybko stają się na nie odporne. Dla przykładu, co roku 2 miliony pacjentów amerykańskich szpitali ulega zakażeniom szpitalnym, a aż 99 000 z nich umiera. Ok. 30% tych zakażeń jest spowodowanych bakteriami Staphylococcus aureus. Obecnie nawet 60% szczepów Staphylococcus aureus znajdowanych w szpitalach jest odporna na penicylinę, metycylinę i wiele innych antybiotyków beta-laktamowych. Dlatego też wankomycyna i amoksycylina/kwas klawulanowy są jednymi z najbardziej powszechnie stosowanych antybiotyków do leczenia infekcji spowodowanych Staphylococcus aureus. Choć antybiotyki te są najsilniejsze w swojej klasie związków, to częste stosowanie spowodowało ich zmniejszoną aktywność przeciwbakteryjną. W celu uniknięcia antybiotykooporności, projektowane są nowe inhibitory β-laktamazy, w tym pochodne kwasu boronowego i fosfoniany. Inną możliwością jest używanie odporna jako środków przeciwbakteryjnych odporna. Związki te działają poprzez przerywanie grubych ścian komórkowych lub błon i wykazują skuteczność w walce z Staphylococcus aureus. 354 • Naukowcy ze Stanów Zjednoczonych, na łamach JACS, przedstawiają klasę naładowanych metalopolimerów, które wykazują nie tylko wysoką skuteczność w zmniejszaniu aktywności β-laktamazy, ale również zwalczają komórki bakteryjne. Wyniki pokazują, że metalopolimery atakują enzymy β-laktamazy i ściany komórek oraz chronią sprzężone z nimi antybiotyki poprzez oddziaływania jonowe pomiędzy polimerami i antybiotykami. Metalopolimery zbudowane są z kationowych polimerów zawierających kobaltocen. Dzięki wyjątkowej zdolności kobaltocenu do kompleksowania anionów karboksylanowym, różne komercyjne antybiotyki β-laktamowe, w tym penicylina-G, amoksycylina, ampicylina i cefazolina, mogą być chronione przez tworzenie stabilnych jonowych par z polimerem. Co więcej, metalopolimery wykazują wysoką skuteczność wobec Staphylococcus aureus, natomiast nie wykazują aktywności hemolitycznej ani toksyczności in vitro i in vivo. (kk) (Jiuyang Zhang, Yung Pin Chen, Kristen P. Miller, Mitra S. Ganewatta, Marpe Bam, Yi Yan, Mitzi Nagarkatti, Alan W. Decho, Chuanbing Tang, Antimicrobial Metallopolymers and Their Bioconjugates with Conventional Antibiotics against Multidrug-Resistant Bacteria, J. Am. Chem. Soc., DOI: 10.1021/ja5011338) nr 4/2014 • tom 68