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Engineered capping systems are in most cases an indispensable and often the only efficient component required by the long-term safety concept for landfills, mine tailings tips and contaminated land. In Germany the composite liner is the main component of standard landfill cappings for municipal and hazardous waste landfills and the compacted clay liner (CCL) for landfills for inert or low-contamination waste. The composite liner is a technically highly effective but very expensive system. Research and experience has given rise to concern about the proper long-term performance of a conventional single CCL as a landfill capping. Therefore, alternative capping systems are discussed and applied for landfills and for the containment of contaminated sites. This paper gives an overview on various alternative engineered cappings and suitable systems for capping reflecting the state of the art and the expert view in Germany. According to the European Council Directive on the landfill of waste an impermeable mineral layer is recommended for the surface sealing of non-hazardous landfills and a composition of artificial sealing liner and impermeable mineral layer for hazardous landfills. In both cases a drainage layer thickness of at least 0.5 m is suggested. These recommendations should be interpreted flexibly and to some extent modified in the light of the experience and results presented in this paper.
Data are reported from oven aging in air for more than 13 years (!) and from water immersion tests for 6 years at 80 °C on various high-density polyethylene geomembranes (GM) used in landfill lining. The mechanical properties and oxidative induction times (OIT) of the samples were monitored during the long-term testing. Aging behavior in hot air is different from that in hot water. During oven aging a slow, exponential decrease of OIT is observed. Even after 13.6 years there is no indication of an oxidative degradation of the mechanical properties. During immersion in water a strong reduction in OIT occurs within the first year, after which time the curve levels off. Oxidation starts when very low OIT-values are reached after about 5 years at which time the mechanical strength rapidly falls to values below the yield point. We conclude from these data that the service life of HDPE GM's is essentially determined by the slow loss of stabilizers due to migration. The oxidation starts only after the depletion of antioxidants and then quickly leads to brittleness of the sample. However, no complete oxidative deterioration has been observed to date. We estimate by the van't Hoff rule that under normal ambient conditions many centuries will have to pass before the functional mechanical properties of state-of-the-art stabilized HDPE bulk material will be reduced below acceptable limits by oxidative degradation.
Data are reported from oven aging in circulating air and water immersion tests at 80°C on various polyolefin (polyethylene (PE) and polypropylene (PP)) needle-punched nonwoven geotextiles (GTnws) and the results of these long-term tests are compared with the oxidative resistance of high-density PE geomembranes (HDPE GMs) described in a preceding paper (Polym. Degr. Stability 79(1) (2003) 161). Polyolefin fibers used in geotextiles are typically less stabilized, have a very high surface-to-volume ratio and an oriented morphology compared with HDPE GMs. Therefore, significant differences in the oxidation behavior of these products are expected which may affect their durability. Two general results can be obtained from our measurements: Firstly, while the lifetime of the HDPE GM is essentially determined by the slow loss of stabilizers, for all GTnws a rapid reduction in the oxidative induction time (OIT) and, as we conclude, in the amount of stabilizer was observed during water immersion and air aging. Secondly, the mechanical property degradation of the GTnws depended strongly on the oxidation conditions: the induction period prior to the degradation was much longer for immersion in water than for oven aging in circulating air. After antioxidant depletion, an induction time of the oxidation reaction, which depends on the draw ratio of the stretched fibers and the oxygen supply, might substantially contribute to the induction period of the mechanical property degradation of GTnws. For one PP GTnw product, a sudden reduction in the mechanical strength occurred after onset of degradation which continued rapidly until complete deterioration. For other PP samples as well as for all PE GTnws the reduction in mechanical strength proceeded slowly. Best fits were obtained by modeling the degradation process of the PE GTnws by a second-order kinetic. Using an activation energy of 60 kJ/mol (Geotextiles, Geomembranes and Related Products, Balkema, Rotterdam, 1990; Conference Proceedings of the Sixth International Conference on Geosynthetics, Industrial Fabrics Association International (IFAI), Atlanta, USA, 1998, pp. 683690; Clay Geosynthetic Barriers, Balkema, Lisse, The Netherlands, 2002, pp. 8796), lower limits of the half-live of the degradation at worst case field conditions were obtained in the range 3083 years. Some decades have to be added for the overall induction time. However, under field conditions with limited oxygen supply, the expected service lifetime might be at least half an order of magnitude longer.
Composite liners (a geomembrane in intimate contact with a mineral liner) are frequently used to line landfills and contaminated sites. It is therefore very important to characterise the behaviour of these systems even under extreme conditions.
An investigation was undertaken to determine the influence of a mixture of concentrated organic contaminants on composite liner materials taken from test cells that had been dismantled after a 12-year permeation test.
The organic hydrocarbons had permeated the HDPE-geomembrane and had then migrated or had been adsorbed within the mineral liners, depending on their properties. The obtained concentration profiles of the contaminant mixture components indicate that the various mineral layer materials have selective retardation abilities which correspond to the different parameters of the organic compounds as well as of the mineral layer.
In addition, contaminant transport in the composite liners tested was modelled and the results of the model analysis compared with measurement data. An example (acetone) illustrates the calculated spatial and temporal contaminant concentration.
The composite liners investigated exhibit a very good sealing capacity against the concentrated organic contaminants used.
Bis Mitte 2005 müssen schätzungsweise 250 alte Hausmülldeponien geschlossen werden, die nicht dem Stand der Technik entsprechen. Danach muß irgendwann eine Sicherung erfolgen. Wo dies im Einzelfall kontrollierbar möglich ist, kann man versuchen, den Deponiekörper anaerob ausreagieren zu lassen oder aerob zu stabilisieren. An einer zusätzlichen technischen Barriere wird jedoch auch dann kaum ein Weg vorbeiführen. Einfache, aber hochwirksame technische Abdichtungen können auch auf der Oberfläche einer Deponie errichtet werden. Für die dort wirksamen Beanspruchungen sind Abdichtungen mit ausgewählten PE-HD-Dichtungsbahnen besonders geeignet. Eine Zulassung der Produkte für diesen Anwendungszweck ist erforderlich, da PE-HD-Werkstoffe, aber auch Dichtungsbahnen, die aus dem gleichen PE-HD-Werkstoff unterschiedlich gefertigt wurden, sich in ihren Eigenschaften drastisch unterscheiden können.
Mit PE-HD-Dichtungsbahnen kann eine sehr wirksame, endgültige Oberflächenabdichtung auf einer Deponie gebaut werden. Dies setzt zwei Dinge voraus: die Dichtungsbahnen müssen fehlerfrei eingebaut werden und sie müssen lange genug halten. Die Lebensdauern von PE-HD-Dichtungsbahnen können sich jedoch je nach Werkstoff, Verarbeitung und Installation um Größenordnungen unterscheiden. Für die Auswahl sind daher spezielle Untersuchungen zur Alterung entscheidend und die Herstellungs-, Schweiß- und Verlegetechnik müssen bestimmte technische Standards erfüllen.
Results are reported from a pilot study under the Consultative Committee for Amount of Substance (CCQM) to compare measurements of and resolve any relevant measurement issues in, the amount of thermal SiO2 oxide on (100) and (111) orientation Si wafer substrates in the thickness range 1.5 - 8 nm. As a result of the invitation to participate in this activity, 45 sets of measurements have been made in different laboratories using 10 analytical methods: medium-energy ion scattering spectrometry (MEIS), nuclear reaction analysis (NRA), RBS, elastic backscattering spectrometry (EBS), XPS, SIMS, ellipsometry, grazing-incidence x-ray reflectrometry (GIXRR), neutron reflectometry and transmission electron microscopy (TEM). The measurements are made on separate sets of 10 carefully prepared samples, all of which have been characterised by a combination of ellipsometry and XPS using carefully established reference conditions and reference parameters.
The results have been assessed against the National Physical Laboratory (NPL) data and all show excellent linearity. The remaining data sets correlate with the NPL data with average root-mean-square scatters of 0.15 nm, half being better than 0.1 nm and a few at or better than 0.05 nm. Each set of data allows a relative scaling constant and a zero thickness offset to be determined. Each method has an inherent zero thickness offset between 0 nm and 1 nm and it is these offsets, measured here for the first time, that have caused many problems in the past. There are three basic classes of offset: water and carbonadeous contamination equivalent to ~1 nm as seen by ellipsometry; adsorbed oxygen mainly from water at an equivalent thickness of 0.5 nm as seen by MEIS, NRA, RBS and possibly GIXRR; and no offset as seen by XPS using the Si 2p peaks. Each technique has a different uncertainty for the scaling constant and consistent results have been achieved. X-Ray photoelectron spectroscopy has large uncertainties for the scaling constant but a high precision and, critically, if used correctly, has zero offset. Thus, a combination of XPS and the other methods allows the XPS scaling constant to be determined with low uncertainty, traceable via the other methods. XPS laboratories returning results early were invited to test a new reference procedure. All showed very significant improvements. The reference attenuation lengths thus need scaling by 0.986 ± 0.009 (at an expansion factor of 2) deduced from the data for the other methods. Several other methods have small offsets and, to the extent that these can be shown to be constant or measurable, then these methods will also show low uncertainty. Recommendations are provided for parameters for XPS, MEIS, RBS and NRA to improve their accuracy.
Durch die hydrolytische Alterung ändert sich die Zugfestigkeit eines Polyester-Bewehrungsgitters im Laufe der Zeit. Nach den Empfehlungen für den Entwurf und die Berechnung von Erdkörpern mit Bewehrung aus Geokunststoffen (EBGEO) der DGGT wird dieser Effekt durch einen Abminderungsfaktor bei der Bemessung berücksichtigt. Es ist zwar im Prinzip festgelegt, wie man bei der Bestimmung eines solchen Faktors für eine chemisch bedingte Materialveränderung vorgehen soll (ISO/TR 20432), es bleiben jedoch große Freiheiten bei der Umsetzung. Die Fragen, die sich daraus bei Bewehrungsgittern aus Polyester ergeben, werden diskutiert. Es werden Bausteine eines einheitlichen Verfahrens vorgeschlagen, das sich nicht nur auf den Festigkeitsverlust, sondern auch auf die molekulare Veränderung konzentriert.
Kunststoff-Dränelemente werden auch in Böschungen eingebaut. Da sie in der Regel aus mehreren Komponenten, nämlich mindestens aus einem Dränkern und einem Filtervliesstoff bestehen, hängt die Standsicherheit u. a. von der inneren Scherfestigkeit der Produkte ab. Diese kann entweder durch die reine Reibung der Komponenten untereinander oder durch die mechanische Festigkeit von Fügestellen zwischen den Komponenten bedingt sein, die schon bei der Produktion hergestellt werden. Im letzteren Fall ist nicht klar, wie Ergebnisse von Reibungsversuchen im Rahmenschergerät zu interpretieren sind. Vor diesem Hintergrund wird gezeigt, wie die Druck- und Scherkräfte, die ein Produkt langfristig aushalten kann, aus einem Reibungsversuch im Zusammenhang mit Kriechversuchen abgeleitet werden können. Dieses Vorgehen wird bei der Zulassung nach der Deponieverordnung für den Einsatz in Deponieabdichtungen angewendet.-----------------------------------------------------------------------------------------------------
Geocomposite drains (GCD) are used on long and steep slopes. Since they are usually composed of different components, at least a drain core in connection with a nonwoven filter geotextile, the internal shear strength is of significant relevance for the slope stability. The internal shear strength may be due to pure friction forces between the different components or due to the mechanical strength of the bonding between the components achieved in a special production process. In the latter case the interpretation of the results of friction shear box tests is quite unclear. Against this background it is shown how the pressure and shear forces, which are acceptable for a product in the long run, may be derived from such a shear box test in combination with long-term creep tests. The procedure is used within the framework of the certification of the products for landfill cover systems according to the German landfill ordinance.
Mit Dichtungskontrollsystemen (DKS) werden Konvektionssperren in Oberflächenabdichtungssystemen von Deponien kontrolliert. Die Funktionsfähigkeit eines eingebauten DKS muss in jedem Projekt zuvor überprüft werden. Diese projektspezifische Funktionsprüfung des DKS selbst wird am Beispiel der Verwendung mit einer Kunststoffdichtungsbahn (KDB) diskutiert. Der grundsätzliche Aufbau, die zugrunde liegenden Messprinzipien und das Ziel der Prüfung werden vorgestellt. Die Anforderungen an die nach der Deponieverordnung (DepV) zugelassenen Systeme hinsichtlich Betrieb, Leitungsfähigkeit und Konstruktion werden beschrieben. Dabei wird auf die Vorgaben der Richtlinie, die einer Zulassung zugrunde liegt, eingegangen. Das mögliche Vorgehen bei der projektspezifischen Kontrollprüfung im Hinblick auf Aspekte wie Vorgehensweise, Zeitpunkt und Randbedingungen sowie äußere Einflussfaktoren werden diskutiert.--------------------------------------------------------------------------------------------------------------------------------------------------------------
Leak detection systems (LDS) are used to control tight barriers in landfill cover systems. However, the efficiency of the installed LDS itself has to be verified in every landfill construction project. As an example the efficiency test for LDS used in connection with geomembranes is discussed in detail. The basic principles, the measuring techniques and objectives of the efficiency testing are described. The requirements for a certification of LDS under the terms of the new German landfill ordinance with regard to operation, capability and design are listed. The conditions necessary for a certification of LDS are introduced. Possible project related efficiency testing procedures with respect to the scope, time of convenience, general conditions as well as external influencing factors are discussed.
Die neue Deponieverordnung regelt im Anhang 1 auch den Einsatz von Geokunststoffen im Deponiebau. Deren Eignung muss der zuständigen Behörde gegenüber nachgewiesen werden. Auf die entsprechenden Regelungen wurde im ersten Teil dieses Aufsatzes eingegangen. Zumindest in den nächsten Jahren kommt nur ein Nachweis durch Vorlage einer Zulassung der BAM Bundesanstalt für Materialforschung und -prüfung in Betracht. Das Zulassungsverfahren wird in der Deponieverordnung geregelt. Die Zulassungsbehörde soll u.a. nicht nur ein bestimmtes Produkt auf der Grundlage von Zulassungsrichtlinien überprüfen, sondern auch in Zusammenarbeit mit einem Fachbeirat Anforderungen an den fachgerechten Einbau und das Qualitätsmanagement festlegen. Das Zulassungsverfahren und einige wesentliche technische Zulassungsanforderung, die für Kunststoffdichtungsbahnen, Schutzschichten, Geotextilien, Kunststoff-Dränelement, Bewehrungsgitter aus Kunststoff und Dichtungskontrollsysteme inzwischen erarbeitet und in Zulassungsrichtlinien beschrieben wurden, werden erläutert.
Hydrolytic degradation and functional stability of a segmented shape memory poly(ester urethane)
(2009)
In order to understand the effects of water and hydrolytic ageing on semi-crystalline poly(ester urethane) and its shape memory functionality, water immersion experiments at elevated temperature have been performed on a model substance and various parameters were monitored: change of the melting/crystallisation temperatures, substantial increase in crystallinity, temperature dependence of the water diffusion coefficient and solubility, hydrogen-bonding index and phase mixing by peak deconvolution of the FT-IR carbonyl region and day-to-day tensile and thermo-mechanical cyclic tensile tests. A rising fraction of freezable water agglomerates in the polymer was found for specimens cooled from the immersion temperature. The degradation process could be divided into three phases: an induction phase, a phase of continuous degradation and a phase of accelerated degradation. Shape recovery remains fairly constant during phase one and decreases slowly during phase two. The increase in crystallinity in phase two is accompanied by an increase in shape fixing ability.
In two hydrolytic degradation studies the tensile (mechanical) and functional (thermo-mechanical) properties of a hydrolysis-stabilized shape memory poly(ester urethane) and its non-stabilized analog were investigated. Hydrolytic degradation was enforced by specimen immersion in de-ionized water at 80 °C. Significant differences in the fundamental shape memory parameters were monitored as function of aging time for the stabilized and non-stabilized polymer. This included the ability to recover strain (shape recoverability) and stress (stress recoverability) on heating after shape programming. Hydrolysis-related mechanical and functional changes were correlated with morphological ones, detected by differential scanning calorimetry (DSC). The shape memory poly(ester urethane), which was protected by a carbodiimide-based hydrolysis stabilizer, revealed significantly improved resistance towards hydrolysis with respect to various mechanical and shape memory parameters.
The shape memory functionality of a segmented poly(ester urethane) and its hydrolytically aged specimens has been studied by cyclic thermo-mechanical measurements with an imposed strain of 100%. The shape memory effect was triggered by a melting transition in the soft segment phase. Aging was enforced by immersion in hot de-ionized water. In the course of the immersion the tensile properties (secant moduli, stress and strain at yield and break) were impaired by hydrolysis. Advanced specimen embrittlement finally led to rupture during the first thermo-mechanical cycle. This happened after 68 days of aging at 55 °C and correspondingly after 8 days at 80 °C. The residual strain after the first cycle, which was about 25%, increased significantly with aging time. Therefore, the total strain recoverability became ever smaller: aged specimens needed conditioning by at least two cycles for a full development of shape recoverability. Likewise the recovery force decreased continuously. Despite these degradation effects, it was observed that the shape fixity and the cycle-related shape recovery of appropriately conditioned specimens (number of cycles N > 2) remained on a constant high level (at round 100% and between 90% and 100%, respectively) throughout the whole aging period. These observations are discussed within the framework of a simplified model of the behavior of crystallizable shape memory polymers. The amorphous state of the polymer is described by the equation of the linear visco-elastic solid. As for the semi-crystalline state the material is assumed to react elastically with respect to deviations from the configuration, which was frozen up under constraint conditions. The curves of the dependence of the material behavior on aging time at 55 °C match perfectly those at 80 °C when the time axis is adjusted by a factor of 8.5, from which the apparent activation energy for hydrolytic aging in the amorphous state of 82 kJ mol-1 could be deduced.
The fluorolytic sol–gel synthesis is applied with the intention to obtain two different types of core–shell nanoparticles, namely, SrF2–CaF2 and CaF2–SrF2. In two separate fluorination steps for core and shell formation, the corresponding metal lactates are reacted with anhydrous HF in ethylene glycol. Scanning transmission electron microscopy (STEM) and dynamic light scattering (DLS) confirm the formation of particles with mean dimensions between 6.4 and 11.5 nm. The overall chemical composition of the particles during the different reaction steps is monitored by quantitative Al Kα excitation X-ray photoelectron spectroscopy (XPS). Here, the formation of stoichiometric metal fluorides (MF2) is confirmed, both for the core and the final core–shell particles. Furthermore, an in-depth analysis by synchrotron radiation XPS (SR-XPS) with tunable excitation energy is performed to confirm the core–Shell character of the nanoparticles. Additionally, Ca2p/Sr3d XPS intensity ratio in-Depth profiles are simulated using the software Simulation of Electron Spectra for Surface Analysis (SESSA). In principle, core–shell like particle morphologies are formed but without a sharp interface between calcium and strontium containing phases.
Surprisingly, the in-depth chemical distribution of the two types of nanoparticles is equal within the error of the experiment. Both comprise a SrF2-rich core domain and CaF2-rich shell domain with an intermixing zone between them. Consequently, the internal morphology of the final nanoparticles seems to be independent from the synthesis chronology.
Data from four samples of commercially available PET geogrids (made either of yarns or bars), which were measured by BAM or other institute, are analyzed to discuss the procedure and problems of determining the chemical reduction factor RFCH associated with a certain service life. Estimates from Arrhenius extrapolation usually have very large statistical errors. The level of confidence must therefore be specified. A reliable estimate requires data from immersion tests below the glass transition temperature of PET. To extrapolate the time of reductions for each reduction factor at such low temperatures, one has to know the functional form of the mechanical degradation curve. It is shown how the degradation curve of the tensile strength may be obtained by determining the relation between increase in concentration of carboxyl end group (CEG) and decrease in tensile strength. Therefore, experimental studies to determine the chemical reduction factor should be accompanied by the measurements of the CEG concentration and the intrinsic viscosity. Furthermore, such measurements allow a non-ambiguous determination of the molecular mass. Hydrolytic molecular degradation will proceed continuously even at 20 °C with half-life of the inverse of the CEG concentration of 40–100 y. Nevertheless, small chemical reduction factors at a lifetime of 100 y are obtained with high level of confidence for materials with low initial CEG concentration and high molecular mass. This is shown by pooling data from samples with comparable CEG concentration, molecular mass and above all comparable intrinsic relation between increase in CEG concentration and decrease in strength. Therefore, the recommendation of ISO TR 20432, Table 2, for chemical reduction factors seems to be applicable to PET geogrids with index properties well below the one specified by the technical report. Whether these index properties are actually a sufficient condition to have small chemical reduction factors even at a very long service life is still an open question. The determination of chemical reduction factor should be based on aging experiments, at least for products with index properties close to the limiting values for the following reasons. (1) Even so standards are available, results of different laboratories on absolute values of CEG concentration and number averaged molecular mass differ to a certain extent. (2) Other factors, like crystallization, affect the mechanical degradation significantly. (3) There is no universally applicable form of the mechanical degradation curve.
The German Federal Institute for Materials Research and Testing (BAM) has established a testing guideline to assess the suitability of geosynthetic or geocomposite drain (GCD) elements for final landfill cover systems. In an earlier paper the uniform procedure according to the BAM guideline for determining long-term water flow capacity was described, and the structural stability of drain cores under creep was investigated. The extrapolation of creep curves is permissible only when it can be shown, over the extrapolated period (at least 100 years), that oxidative aging does not invoke any relevant changes in the polyolefin material. This can be shown by measuring antioxidant depletion and mechanical degradation of the drain cores and filter/protection geotextiles in oven aging and water immersion tests. In this paper the results of such aging studies on three different GCD products are reported. Degradation of the tensile strength of HALS-stabilized polypropylene needle-punched nonwoven geotextiles (PP NWGTs) starts right from the beginning of the oven aging. This has to be taken into account for lifetime predictions based on residual tensile strength. The rate of oxidative degradation of NWGTs decreases significantly with increasing mass per area. Therefore the expected service life sets a limit on acceptable geotextile grammage. Antioxidant depletion in the drain cores, which are made of relatively thick PP strands or HDPE ribs, is about an order of magnitude slower than in filter and protection NWGTs, which are made of thin fibers. Service life values in excess of 100 years may be obtained for the products when the geotextiles and drain cores are properly stabilized and designed.
Bewehrungsgitter aus Kunststoff, die zum Schutz vor hangparallelem Gleiten auf langen und steilen Böschungen eingebaut werden, müssen sicher verankert werden. Für den Entwurf und die Berechnung der Verankerung sind bestimmte Regeln gebräuchlich. An Hand von Modellen für die Wechselwirkung zwischen Füllboden und Bewehrungsgitter wird diskutiert, welche physikalischen Annahmen und Vereinfachungen in diese Bemessungsregeln eingehen. Dabei wird gezeigt, dass das bisher benutzte Bemessungskonzept ohne Einschränkung nur auf eine spezielle Klasse von Bewehrungsgittern anwendbar ist, deren Herausziehwiderstand überwiegend von Effekten der 'Oberflächenreibung' zwischen Bodenpartikeln und Längselementen des Gitters bedingt ist ('Reibungsgitter'). Für die Bemessung muss hier der Verbundbeiwert dieser reinen Oberflächenreibung verwendet werden. Bei Bewehrungsgittern, wo ein Erddruck, der sich vor den Querelementen des Gitters aufbaut, maßgeblich zum Herausziehwiderstand beiträgt, ist die Festigkeit der Verbindungsstellen zwischen Längs- und Querelementen von entscheidender Bedeutung für eine sichere Verankerung ('Erddruckgitter'). Die Zusammenhänge zwischen mechanischem Verhalten der Verbindungsstellen, Dehnbarkeit der Längselemente, Oberflächenreibung und maximaler Herausziehkraft werden beispielhaft aufgezeigt. Die Festlegung eines Bemessungswiderstands der Verbindungsstellen, der grundsätzlich nicht überschritten werden darf, erfordert eine Modifikation des Bemessungskonzepts. Zwei Fälle können unterschieden werden: Bei Böden mit hinreichend geringer innerer Reibung und geringer Auflast, wo der maximal mobilisierbare Erdwiderstand die zulässige Festigkeit der Verbindungsstelle nicht übersteigen kann, können die Bemessungsregeln noch angewendet werden. In allen anderen Fällen nicht mehr: Der Bemessungswiderstand der Verbindungsstelle setzt nämlich der möglichen aktivierbaren Verankerungslänge eine obere Grenze. Es können dann auch nur Zugkräfte bis zu einer bestimmten Stärke verankert werden, völlig unabhängig davon, wie groß die Zugfestigkeit des Bewehrungsgitters ist. Nur bei Beachtung dieser Grenzen ist eine langfristig sichere Verankerung möglich.
Long-term water flow capacity of geosynthetic drains and structural stability of their drain cores
(2008)
Richtlinie für die Zulassung von Geotextilien zum Filtern und Trennen für Deponieabdichtungen
(2010)
Die neue Deponieverordnung fordert Zulassungen für Geokunststoffe, die in Deponiedichtungssystemen eingesetzt werden. Diese gesetzliche Vorgabe führt dazu, dass in nationalen Regelwerken und Empfehlungen neue Vorgehensweisen verankert werden müssen. Zulassungsstelle ist die BAM Bundesanstalt für Materialforschung und -prüfung. Zuständig für die entsprechenden GDA Empfehlungen ist die UAG-Ak 5.1-6.1. Der Beitrag zeigt die Neuerungen, aber auch die Ausnahmeregelungen. Auf der Grundlage der Deponieverordnung hat die BAM einen Fachbeirat zusammengerufen, der verschiedene Arbeitsgruppen eingerichtet hat, um Zulassungsrichtlinie für Kunststoffdichtungsbahnen, Schutzschichten, Geotextilien zum Filtern und Trennen sowie Bewehrungsgitter aus Kunststoff zu erarbeiten oder zu aktualisieren. Die Zulassungsanforderungen lehnen sich wiederum eng an GDA- und EAG-Empfehlungen an. In dem Beitrag wird der Stand der Fachdiskussion in den Arbeitsgruppen erläutert.
Bispidines for dual imaging
(2014)
The efficient transformation of the hexadentate bispidinol 1 into carbamate derivatives yields functional bispidines enabling convenient functionalization for targeted imaging. The BODIPY-substituted bispidine 3 combines a coordination site for metal ions, such as radioactive 64CuII, with a fluorescent unit. Product 3 was thoroughly characterized by standard analytical methods, single crystal X-ray diffraction, radiolabeling, and photophysical analysis. The luminescence of ligand 3 was found to be strongly dependent on metal ion coordination: CuII quenches the BODIPY fluorescence, whereas NiII and ZnII ions do not affect it. It follows that, in imaging applications with the positron emitter 64CuII, residues of its origin from enriched 64Ni and the decay products 64NiII and 64ZnII, efficiently restore the fluorescence of the ligand. This allows for monitoring of the emitted radiation as well as the fluorescence signal. The stability of the 64CuII–3 complex is investigated by transmetalation experiments with ZnII and NiII, using fluorescence and radioactivity detection, and the results confirm the high stability of 64CuII–3. In addition, metal complexes of ligand 3 with the lanthanide ions TbIII, EuIII, and NdIII are shown to exhibit emission of the BODIPY ligand and the lanthanide ion, thus enabling dual emission detection.
Geosynthetics are planar polymeric products, which are used in connection with soil, rock or other soil-like materials to fulfill various functions in geoenvironmental engineering. Geosynthetics are of ever-growing importance in the construction industry. Sealing of waste storage facilities to safely prevent the emission of wastewater, landfill gas and contaminated dust as well as the diffusion of pollutants into the environment and coastal protection against storms and floods and reconstruction after natural disaster are important fields of application. We will give an overview of the various geosynthetic products. Two examples of the material problems related to geosynthetics are discussed in detail: the effect of creep on the long-term performance of geocomposite drains and the numerical simulation of the interaction of soil with geogrids. Both issues are of importance for the use of these products in landfill capping systems. The various functions, which geosynthetics may fulfill in the protection of coastal lines, are illustrated by case studies. The geosynthetic market is evaluated and economical and environmental benefits, as well as environmental side effects related to the use of geosynthetics, are discussed.
Im ersten Teil dieses Aufsatzes wurde gezeigt, dass nur ein Teil der für den Deponiebau wesentlichen technischen Eigenschaften in den europäisch harmonisierten Bauproduktnormen DIN EN 13252 und DIN EN 13257, die der CE-Kennzeichnung der Geotextilien (GTX) und geotextilverwandten Produkte (GTP) zugrunde liegen, erfasst werden. Um eine im Wesentlichen vorhandene Gleichwertigkeit der Produkteigenschaften überhaupt abwägen zu können, müssen aber sämtliche relevanten Eigenschaften bekannt sein. Dies erfordert für CE-gekennzeichnete Produkte zusätzliche Prüfungen auf der Grundlage der DepV-Liste der Kriterien und Einwirkmechanismen (Anhang 1, Nummer 2.1.1, DepV). In diesem Teil werden die Tabellen C1 und C2 sowie die Tabelle D aus dem ersten Teil, in denen die Eigenschaften der harmonisierten europäischen Normen (hEN) den Anforderungen der DepV gegenübergestellt wurden, in technischer Hinsicht näher erläutert.
In absehbarer Zeit werden CE-gekennzeichnete Geovliesstoffe, Geogewebe, geosynthetische Dränelemente und Geogitter aus Kunststoff erhältlich sein, bei denen die CE-Leistungserklärung den Hinweis enthält 'dauerhaft für bis zu 100 Jahre' oder sogar 'dauerhaft für mindestens 100 Jahre'. Hersteller, Bauherren, Planer und zuständige Behörden werden sich daher die Frage stellen, ob diese Produkte auf der Grundlage von Anhang 1 Nummer 2.1 Satz 7 Ziffer 1 der Deponieverordnung (DepV) im Deponiebau auch ohne Zulassung verwendet werden dürfen. Ein Vergleich der europäisch harmonisierten Bauproduktnormen DIN EN 13252 und DIN EN 13257, die der CE-Kennzeichnung der Geotextilien und geotextilverwandten Produkte zugrunde liegen, mit den Anforderungen der DepV zeigt nun aber, dass nur ein Teil der für den Deponiebau wesentlichen technischen Eigenschaften in diesen Normen erfasst werden. Daher sind für CE gekennzeichnete Produkte zusätzliche Prüfungen auf der Grundlage der DepV-Liste der Kriterien und Einwirkmechanismen erforderlich. Die in den Produktnormen beschriebene Qualitätssicherung ist nach Anhang 1 Nummer 2 Satz 14 ff der DepV ebenfalls für die Gleichwertigkeit nicht ausreichend. Eine CE-Kennzeichnung ist deshalb noch kein Nachweis, dass die Produkte dem Stand der Technik nach der DepV entsprechen und die Eigenschaften der Produkte den geforderten Eigenschaften im Wesentlichen gleichwertig sind, auch wenn mit Bezug auf den Anhang B der genannten Normen deren Dauerhaftigkeit für 100 Jahre vom Hersteller deklariert wird.----------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------
In the near future, CE-marked woven and nonwoven geotextiles, geocomposite drains and geogrids will be available on the market, whose declaration of performance will contain the qualification 'predicted service life up to 100 years' or even 'predicted service life minimum 100 years'. Manufacturer, principals and their design engineers as well as the responsible authorities will have to deal with the question, whether such products can be used on the basis of Annex 1, no. 2.1, sentence 7, cipher 1 of the German landfill ordinance (DepV) as components of landfill liner and capping systems. A comparison of the harmonized European standards hEN 13252 and 13257, on which the CE-marking of geotextiles and geotextile-related products is based, with the DepV, shows that only a few of the essential technical characteristics actually relevant for landfill constructions are considered in these standards. Therefore, additional tests based on the DepV-list of criteria and mechanisms of action are necessary for CE-marked products. Requirements on quality managements in the hEN are likewise not adequate for essential equivalence with respect to annex 1, No. 2.1, sentence 14 ff, DepV. Therefore, CE-marking is actually no proof of the fulfilment of the state of the techno logy according to the DepV and of the essential equivalence of product properties to the required properties, albeit the declaration of performance indicates a predicted service life of 100 years.
Accurate and reproducible measurement of the structure and properties of high-value nanoparticles is extremely important for their commercialization. A significant proportion of engineered nanoparticle systems consist of some form of nominally core-shell structure, whether by design or unintentionally. Often, these do not form an ideal core-shell structure, with typical deviations including polydispersity of the core or shell, uneven or incomplete shells, noncentral cores, and others. Such systems may be created with or without intent, and in either case an understanding of the conditions for formation of such particles is desirable. Precise determination of the structure, composition, size, and shell thickness of such particles can prove challenging without the use of a suitable range of characterization techniques. Here, the authors present two such polymer core-shell nanoparticle systems, consisting of polytetrafluoroethylene cores coated with a range of thicknesses of either polymethylmethacrylate or polystyrene. By consideration of surface energy, it is shown that these particles are expected to possess distinctly differing coating structures, with the polystyrene coating being incomplete. A comprehensive characterization of these systems is demonstrated, using a selection of complementary techniques including scanning electron microscopy, scanning transmission electron microscopy, thermogravimetric analysis, dynamic light scattering, differential centrifugal sedimentation, and X-ray photoelectron spectroscopy. By combining the results provided by these techniques, it is possible to achieve superior characterization and understanding of the particle structure than could be obtained by considering results separately.
Plastic products used in geotechnical engineering, so-called geosynthetics, are often made of polyolefins (polyethylene or polypropylene) and stabilized against oxidative degradation by antioxidants (AO). Three types of AO “packages” are used: (P1) phenols and phosphites/sulfides, (P2) hindered amines (HAS) with a marginal stabilization P1 of the basic resin, (P3) a combination of packages P1 and P2 with comparable amounts of phenol and HAS. We report about long-lasting oven aging and water immersion tests at 80 °C of 29 different polyolefin based products (geomembranes, geonets and geotextiles). Pronounced differences in the degradation behavior were found depending solely on the type of AO package. In case of P1, the oxidative degradation is prevented by the AO. Autocatalytic oxidation only begins after depletion of AO and may lead to catastrophic failure depending on the environmental conditions. In case of P2, degradation starts right from the beginning. However, it is decelerated and proceeds gradually. In case of P3, the degradation behavior seems to be a superposition of the characteristics obtained for P1 and P2. Plotting the fractional loss of the AO in P1 and P2 as function of the square root of aging time, we identified two regimes of AO depletion. We suggest to attribute this observation to the different mechanisms of AO depletion.
An approach to achieve 'zero leakage' is discussed with respect to experience in Germany, where strict regulations for landfill lining and capping Systems have been developed and issued because of large environmental Problems related to landfills that accumulated in the 1970s and 1980s. Using a thick, high-quality high-density Polyethylene (HDPE) geomembrane (GM) that is installed free of residual waves and wrinkles in intimate contact with a compacted clay liner or geosynthetic clay liner of very low permeability, by a qualified, experienced, well-equipped and properly third-party-controlled installer, and which is protected by heavy protection layers designed with respect to the long-term performance of the GM may result in a liner or capping system of practically no leakage. This is demonstrated by analysing results of measurements obtained from permanently installed leak-detection Systems in combination with HDPE GMs. The survey was based on 32 German landfills with 1.276.500 m² of installed GMs.
Core–shell nanoparticles (CSNPs) have become indispensable in various industrial applications. However, their real internal structure usually deviates from an ideal core–shell structure. To control how the particles perform with regard to their specific applications, characterization techniques are required that can distinguish an ideal from a nonideal morphology. In this work, we investigated poly(tetrafluoroethylene)–poly(methyl methacrylate) (PTFE–PMMA) and poly(tetrafluoroethylene)–polystyrene (PTFE–PS) polymer CSNPs with a constant core diameter (45 nm) but varying shell thicknesses (4–50 nm). As confirmed by transmission scanning electron microscopy (T-SEM), the shell completely covers the core for the PTFE–PMMA nanoparticles, while the encapsulation of the core by the shell material is incomplete for the PTFE–PS nanoparticles. X-ray photoelectron spectroscopy (XPS) was applied to determine the shell thickness of the nanoparticles. The software SESSA v2.0 was used to analyze the intensities of the elastic peaks, and the QUASES software package was employed to evaluate the shape of the inelastic background in the XPS survey spectra. For the first time, nanoparticle shell thicknesses are presented, which are exclusively based on the analysis of the XPS inelastic background. Furthermore, principal component analysis (PCA)-assisted time-of-flight secondary-ion mass spectrometry (ToF-SIMS) of the PTFE–PS nanoparticle sample set revealed a systematic variation among the samples and, thus, confirmed the incomplete encapsulation of the core by the shell material. As opposed to that, no variation is observed in the PCA score plots of the PTFE–PMMA nanoparticle sample set. Consequently, the complete coverage of the core by the shell material is proved by ToF-SIMS with a certainty that cannot be achieved by XPS and T-SEM.
Bei den von der Bundesanstalt für Materialforschung und ‐prüfung (BAM) zugelassenen Kunststoff‐Dränelementen sind drei verschiedene Varianten von überlappenden Querstößen nach den Einbauanleitungen zulässig. Das Wasserableitvermögen innerhalb dieser Querstöße wurde vom SKZ – Das Kunststoffzentrum und von der KIWA Deutschland GmbH in Abstimmung mit der BAM gemessen. Dabei zeigte sich bei den gewählten Prüfbedingungen (einem hydraulischer Gradienten i = 1, Auflasten von 20 und 50 kPa sowie den Bettungen hart/weich und weich/weich) praktisch keine Verringerung gegenüber dem Wasserableitvermögen im Kunststoff‐Dränelement selbst. Eine solche war insbesondere dann nicht zu beobachten, wenn die Dränkerne im Überlappungsbereich direkt aufeinandergelegt wurden (Variante A). Werden die Kunststoff‐Dränelemente als Ganzes entweder dachschindelartig hinsichtlich der Strömungsrichtung (Variante B) oder in einer gerade umgekehrten Anordnung (Variante C) übereinandergelegt, so genügt dabei eine Überlappungslänge von 20 cm, damit ausreichend Wasser durch die zwischen den Dränkernen liegende Trennschicht aus Filter‐ und Trägergeotextil strömt. Der bisher in der GDA‐Empfehlung E2‐20 für die Bemessung angesetzte Abminderungsfaktor von 1,2 für Querstöße kann daher für die hier untersuchten, zugelassenen Produkte bei einer genügend großen Überlappung entfallen. Entsprechende Hinweise werden zukünftig in den Zulassungsscheinen gegeben.
Vor 30 Jahren wurde die erste BAM-Zulassung für ein Geokunststoffprodukt in der Deponietechnik ausgestellt. Seither wurden immer wieder eigene wissenschaftliche Untersuchungen durchgeführt, neue Forschungsergebnisse herangezogen und die Prüftechnik weiterentwickelt, um die Eignung und Funktionsdauer von Kunststoffdichtungsbahnen, Schutzschichten, Kunststoff-Dränelementen, geotextilen Filtern oder Bewehrungsgittern beurteilen zu können. Einige dieser Entwicklungen werden hier diskutiert.
Der Zugversuch ist ein wichtiges Prüfverfahren für die Qualitätssicherung von Kunststoffdichtungsbahnen, die in der Geotechnik (Deponiebau, Tunnelbau usw.) verwendet werden. Für die Vergleichbarkeit und Beurteilung der Ergebnisse ist ein standardisiertes Verfahren erforderlich. Da sich Kunststoffe durch ihr ausgeprägtes viskoelastisches Verformungsverhalten von anderen Baumaterialien unterscheiden, werden die ermittelten Kennwerte sowie deren Bedeutung und Verwendbarkeit für die Praxis diskutiert. Die Einsatzmöglichkeiten und -grenzen von Extensometern werden erläutert. Am Beispiel des Zugversuchs werden zudem die Schwierigkeiten bei der Normungsarbeit aufgezeigt: Angefangen vom Einfluss unterschiedlicher Normungsorganisationen und -komitees sowie der Hersteller auf den Entstehungsprozess der Normen bis hin zu Übersetzungsfehlern. Dabei zeigt sich, dass es durchaus sinnvoll sein kann, für bestimmte Arten von Produkten, wie z. B. PEHD-Dichtungsbahnen, eine eigene Norm zu erarbeiten.
Geomembranes used in basal liner systems of landfills must not be damaged by the coarse gravel of the standard drainage layer. Therefore, the geomembrane must be protected against mechanical damage and strain by means of a suitable protective layer. The main requirements for this protective layer as well as the long-term durability of the mineral and geotextile components are compiled in the guideline recently released by German authorities. An overview is given on the existing types of protective layer systems with the state-of-the-art testing, the requirements and selected results of related research programs.
Geosynthetic clay liners (GCLs) often have a sandwich-like multilayer structure, e.g. bentonite encased between two geotextile layers connected by fibers or yarns, either by needle-punching or stitch-bonding. Therefore, the internal shear strength of the GCL depends on the strength of reinforcing fiber bundles or yarns and their anchoring strength in the cover and carrier geotextiles. When used on long and steep slopes and covered with thick soil layers, the GCL is permanently exposed to a combined action of compressive and shear stress. Such load conditions are characteristic for landfill covers and the slope stability of the overall cover system in the long run strongly depends on the long-term internal shear strength of the GCL. A new test method was developed to study this long-term shear behavior. The focus was not only on creep, as it is normally done, but on aging effects. The shear test devices allow the measurement of creep curves and times-to-failure at elevated temperatures in different media (tap water and de-ionized water). In this publication, the main findings of the experiments on needle-punched GCLs with and without thermal treatment are summarized. Tap water as a test medium was essential to ensure sodium to calcium ion exchange in the bentonite layer. Under this condition extremely long test durations without failure were achieved. Sliding failure occurred when de-ionized water was used. Two failure modes were observed: brittle failure of the GCLs with thermal treatment and slow disentanglement of fiber bundles for untreated GCLs. Short-term shear strength (e.g. peel strength) is unrelated to the actual long-term shear strength, i.e. to the times-to-failure achieved in long-term shear strength test. Hence, short-term shear strength alone will not provide reliable dimensioning data for product design and choice of resins. Therefore, the often suggested approach, namely, restriction to short-term tests only and application of factors of safety, is challenged by these results.