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Funktionalisierte Oberflächen sind in vielen Bereichen, z. B. als Haftvermittler in Polymerkompositen, für katalytische Anwendungen oder als Sensoren von Interesse. Für viele solcher Anwendungen ist es ausreichend, den verwendeten Werkstoff mit einem ultradünnen Polymerfilm zu überziehen. Dazu gibt es bislang einige Verfahren, wie z. B. Chemical Vapour Deposition, Layer-by-Layer-Technik, Langmuir-Blodgett-Technik oder Spin-Coating, die alle bestimmte Nachteile haben.
In der vorliegenden Arbeit wurden wenige Nanometer dicke Polymerschichten auf metallischen und nicht-metallischen Substraten mittels Elektrospray Ionisation abgeschieden.
So wurden typischerweise etwa 10 nm dicke Schichten von Polyacrylsäure (PAA) hergestellt. Die analytische Charakterisierung der produzierten Schichten erfolgte mit der Röntgen-Photoelektronenspektroskopie. Die Atomkraft- bzw. Rasterelektronenmikroskopie gaben Auskunft über den Bedeckungsgrad und die Schichtmorphologie. Die Infrarot-Reflexions-Absorptions-Spektroskopie wurde zur Bestimmung des Restlösemittelgehaltes verwendet.
Zur Optimierung der Schichtabscheidung und -struktur wurden verschiedene Parameter variiert, wie z. B. der Kapillaren-Proben-Abstand, die Beschichtungszeit oder die Beschichtungstemperatur, wobei sich herausstellte, dass die Schichtbildungsparameter für jedes Polymer individuell angepasst werden müssen.
Es konnte gezeigt werden, dass Beschichtungen, bei denen sich das Substrat senkrecht zur Kapillare befindet, bei Raumtemperatur mit einem Kapillaren-Proben-Abstand von mindestens 100 mm zu lösemittelfreien PAA-Schichten führen. Dabei war die Ausbildung der Filmtopographie unabhängig sowohl von der Konzentration der Lösung als auch von der Oberflächenenergie des Substrates.
Polymer deposition morphology by electrospray deposition - Modifications through distance variation
(2014)
Electrospray deposition (ESD) of highly diluted polymers was examined with regard to the deposited surface structure. Only the flight distance (flight time) onto the resulting deposited surface was varied from 20 to 200 mm.
An apparatus without any additional heating or gas flows was used. Polyacrylic acid (PAA) and polyallylamine (PAAm) in methanol were deposited on Si wafers. The polymer layers were characterized by scanning electron microscopy, X-ray photoelectron spectroscopy, derivatization reactions and Fourier transform infrared spectroscopy using a grazing incidence unit.
SEM images illustrated the changing structures of PAA and PAAm. For PAA the deposited structure changed from a smooth film (20 mm) to a film with individual droplets on the coated surface (100 mm and 200 mm), while for PAAm individual droplets can be seen at all distances. The ESD process with cascades of splitting droplets slows down for PAA after distances greater than 40 mm. In contrast, the ESD process for PAAm is nearly stopped within the first flight distance of 20 mm. Residual solvent analysis showed that most of the solvent evaporated within the first 20 mm capillary-sample distance.
Die Elektrospray-Ionisations (ESI)-Vernebelung von Polymerlösungen wird analytisch zur massenspektrometrischen Bestimmung der Molmassen von Makromolekülen genutzt. Dabei werden die Polymermoleküle nach einem speziellen Mechanismus im Hochspannungsfeld unter Normaldruckbedingungen vereinzelt und in das Massenspektrometer überführt. Dieser Prozeß kann auch zur flächigen Abscheidung einzelner Polymermoleküle genutzt werden. Die Struktur und Zusammensetzung sowie die Molmassenverteilung der Polymere bleiben dabei erhalten. Schichten polarer oder ionischer Polymere der Dicke einer Quasi-Monolage bis hin zu mehreren 100 Nanometern können abgeschieden werden. Erwähnenswert ist, daß der ESI-Prozeß zu den elektrophoretischen Verfahren gehört, was die Ausbildung lochfreier Schichten auf elektrisch leitenden Substraten nicht nur auf der der Spraydüse zugewandten Seite ermöglicht, sondern auch auf der abgeschatteten Rückseite. Dieses Verhalten wurde zur vollständigen ESI-Umhüllung von dichtgepackten Kohlenstoff-Faser-Bündeln mit haftvermittelnden Polymerschichten ausgenutzt.
The electrospray ionization (ESI) method was used for deposition of thin films of poly(acrylic acid) (PAA) onto ZSM-5, Cu/ZSM-5 and Ag-Cu/ZSM-5 zeolites. This method allowed the formation of uniform polymer films of controlled thickness on conductive substrates.
The zeolites were prepared home-made. The effect of incorporation of Cu (5 wt.%) and Ag-Cu (1+4 wt.%) onto ZSM-5 on its particle size, unit cell parameters and crystallinity was investigated.
The deposited PAA layer acts as a common dispersing agent with its ionic COOH (COO-) groups. The antibacterial activity towards the bacterial strains such as Staphylococcus pneumonia (S. Pneumonia), Bacillus subtilis (B. subtilis), Escherichia coli (E. coli) and Pseudomonas aeruginosa (P. aeruginosa) as Gram positive and Gram negative bacteria, respectively, and Aspergillus fumigatus (A. fumigatus), Candida albicans (C. albicans) as Fungi was evaluated. The chemical and physical modifications of ZSM-5, Cu/ZSM-5 and Ag-Cu/ZSM-5 surfaces were characterized by X-ray photoelectron spectroscopy, Fourier-transform infrared spectroscopy, atomic force microscopy and X-ray diffraction.
The Cu/ZSM-5 and Ag-Cu/ZSM-5 nanocomposites coated with a 10 nm thick PAA layer exhibit significant antibacterial activity. The carboxyl (¬-COOH) or the corresponding carboxylate groups (¬-COO-) interact with Cu2+ and Ag+ ions by formation of ionic bonds (¬-COO-Ag+ or 2 ¬-COO->Cu2+). Moreover, short exposure to light and temperature has reduced Cu2+ and Ag+ to Cu0 and Ag0.
Plasma polymers and electrospray-ionization (ESI) polymer layers are compared for most efficient adhesion promotion in carbon fiber-epoxy resin composites. The ultra-thin ESI layers (2–30 nm) of commercial poly(acrylic acid) and poly-(hydroxyethylmethacrylate) produce an significant increase of adhesion measured by single-fiber pull out tests.
However, plasma Treatment has also advantages, such as simultaneous activation of the fiber substrate. Chemical structure and composition are rather far from the regular structure of commercial polymers as deposited by ESI processing.
Discussions in science, politics and public media about microplastic in the Environment and its unclear effects for animals and humans are common these days.
Although microplastic findings in water, soil and even air are well known, no general estimations about the quality or quantity of microplastic particles in environment exit. Research is necessary to develop reliable and traceable, harmonized protocols for sampling, sample preparation and fast, but accurate analysis for qualitative and quantitative measurement of microplastic in various environmental matrices. For development of such reliable and traceable methods, the use of microplastic reference materials is necessary to assess various concepts. These microplastic reference particles should be an appropriate reflection of the microplastic particles found in environment.
Due to the high use in industrial products six polymers seem to be relevant in environment as microplastic particles: polyethylene (PE), polypropylene (PP), polystyrene (PS), polyethylene terephthalate (PET), polyamide (PA) and polyvinylchloride (PVC). The raw source of These thermoplastic materials are pellets or granulate with dimensions of 1 to 5 mm in diameter. Most common they own a regular cylindrical shape or are prolate sphericals. These can be bought cost-efficient by various polymer producers. But discussions in microplastic research topic lead to particle sizes down to 1 μm. Furthermore, various unregular shapes and geometries of the particles have to be considered as well as an oxidized surface. In the present work we engage the acquisition and production of
realistic reference material. Different aspects should demonstrate the complex and difficult task of generating approriate, cost-efficient and well-defined reference materials. The particle size distribution by using
different particle sizing methods as well as individual particle shapes are documented. Different material properties were addressed. PE, PS and PA were chosen as typical and relevant microplastic with opposite individual material characteristics in density and glass Transition temperature. The easiest possibility for acquisition of small microplastic particles is the purchase of polymer emulsion particles (20 to 150 μm).
An alternative possibility to produce small microplastic particles is milling under liquid nitrogen conditions in cryo mills. Particles purchased or self-made differ strongly in shape and size depending on production method.
SETAC
Nebulizing of polymer solutions, in a high-voltage field under atmospheric conditions by electrospray ionization (ESI), is a comfortable way to deposit ultra-thin layers of polar or ionic polymers onto any conductive substrate materials. The substrate is grounded and the polymer solution is sprayed through a powered capillary. The formed charged droplets shrink by solvent evaporation during their way to the grounded substrate, the charges close ranks and the droplets collapse consecutively by charge repulsion, thus forming finally charged single macromolecules. After their discharging at the grounded substrate, an ultrathin ‘quasi-monomolecular’ polymer layer is formed. It could be shown by imaging of scratches through the polymer layer by atomic force microscopy that the deposited polymer layers are dense at a thickness of about 10 nm. Carbon fibre bundles were coated with poly (allylamine) (PAAm) or poly(acrylic acid) (PAA) as potential adhesion-promoting layers in fibre–polymer composites. The polymer deposition is self-inhibiting after formation of a continuous coverage of about 200 nm for PAAm and 30 nm for PAA as result of surface charging. Continuous deposition onto such isolating layers or polymers without charging can be achieved by using current of alternating polarity. The film formation is self-healing because of the electrophoretic effect, i.e. the ion discharging occurs preferentially at noncoated areas. This electrophoretic effect of ESI was demonstrated by completely enwrapping all the carbon fibres of the roving within a distance of about 100 μm far from its outside and also at the backside of the fibre bundle with about 80% of the topside coverage, as measured by X-ray photoelectron spectroscopy and visualized using scanning electron microscopy.
The occurrence of small particles consisting of organic polymers, so-called microplastic (MP), in aquatic Environments attracts increasing interest in both public and science. Recent sampling campaigns in surface Waters revealed substantial numbers of particles in the size range from a few micrometers to a few millimeters. In order to validate sample preparation, identification and quantification and to investigate the behavior of MP particles and potential toxic effects on organisms, defined MP model particles are needed. Many studies use spherical compounds that probably behave differently compared to irregularly shaped MP found in environmental samples.
However, preparation and handling of MP particles are challenging tasks and have been systematically investigated in the present study. Polystyrene (PS) as a commonly found polymer with a density slightly above that of water was selected as polymer type for milling and fractionation studies. A cryogenic ball mill proved to be practical and effective to produce particles in the size range from 1 to 200 μm. The yield of small particles increased with increasing pre-cooling and milling durations. Depending on the concentration and the size, PS particles do not completely disperse in water and particles partly creep vertically up along glass walls. Stabilized MP suspensions without use of surfactants that might harm organisms are needed for toxicological studies. The stabilization of PS particle suspensions with ozone treatment reduced the wall effect and increased the number of dispersed PS particles but increased the dissolved organic carbon concentration and changed the size Distribution of the particles.
A harmonization of sampling, sample preparation and detection is pivotal in order to obtain comparable data on microplastics (MP) in the environment. This paper develops and proposes a suitable sampling concept for waterbodies that considers different plastic specific properties and influencing factors in the environment.
Both artificial water including defined MP fractions and the discharge of a wastewater treatment plant were used to verify the derived sampling procedure, sample preparation and the subsequent analysis of MP using thermal extraction-desorption gas chromatography - mass spectrometry (TED-GC-MS).
A major finding of this paper is that an application of various particle size classes greatly improves the practical handling of the sampling equipment. Size classes also enable the TED-GC-MS to provide any data on the MP size distribution, a substantial sampling property affecting both the necessary sampling volume and the optimal sampling depth.
In the artificial water with defined MP fractions, the recovery rates ranged from 80 to 110%, depending on the different MP types and MP size classes. In the treated wastewater, we found both Polyethylene and polystyrene in different size classes and quantities.