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Wastewater contains a diverse array of organic and inorganic compounds and its complex composition strongly depends on the location and the connected dischargers. However, municipal wastewater as a carrier of feces and urine generally contains considerable amounts of the main nutrients nitrogen and phosphorus. The latter is in the focus of the discussions about the recovery potential of wastewater due to the relatively high mass flows of phosphorus in wastewater and the finite nature and decreasing quality of phosphate rock reserves. But due to the presence of the whole periodic table of elements, wastewater might contain further valuable components of interest for recovery including those defined as critical raw materials by the European Commission. Phosphorus and most of the other critical raw materials are fixed in the sewage sludge and after incineration in the sewage sludge ash (SSA). This is accompanied by high concentration factors from wastewater via sludge to ash. However, the mass fractions of the majority of elements in sewage sludge are comparable to those of the earth crust, indicating no relative enrichment. Nevertheless, enrichment factors of 100 or higher are given for phosphorus, copper, zinc, cadmium, silver, tin, lead and the platinum group elements indicating an anthropogenic input. An economic value of sewage sludge was estimated to $460,-/t calculated on the basis of the respective market prices for high purity elements – a theoretical value. A German survey of sewage sludge ashes showed that the mass fractions and the mass flows of most of the elements present in SSA are probably too low for an economic recovery. In most cases the mass flows are rather small compared to the imports and the chemical forms are not suitable for recovery. An exception is phosphorus that is present in high mass fractions up to 13% and that bears a high substitution potential. If the application of P-recovery technologies lead to a further concentration of valuable elements e.g. as by-products in side streams of the process, it would probably make also the recovery of other elements of economic interest.
This study compares the mercury distribution in the vapor phase, the phosphor powder and the glass matrix of new and spent fluorescent lamps. The spent fluorescent lamps were obtained at the collection yards of a public waste management company in Hamburg, Germany. An innovative systematic sampling method is utilized to collect six spent and eight corresponding new, off-the-shelf fluorescent lamp samples. The efficiency of several acid digestion methods for the determination of the elemental composition was studied and elemental mass fractions of K, Na, Y, Ca, Ba, Eu, Al, Pb, Mg, Hg, and P were measured. The study also finds aqua regia to be the best reagent for acid digestion. However, no significant difference in mercury distribution was found in the different phases of the new and spent fluorescent lamps.
Determination of chromium (VI) in primary and secondary fertilizer and their respective precursors
(2017)
Hexavalent chromium species (Cr(VI)) are often carcinogenic, of high acute toxicity, highly mobile, and thus pose a severe risk to health and environment. Fertilizers usually contain significant amounts of chromium. Therefore, a reliable analysis of chromium and the fraction of Cr(VI) are crucial for safe use of fertilizers. This problem is expected to increase in the future, since more and more recycled fertilizers emerge due to increasing fertilizer demand and respective supply risks. However, existing analytical methods have been developed for conventional fertilizers and have to be tested whether they are suitable for the new materials. Thus, we performed a wet-chemical extraction for Cr(VI) on several matrices as well as respective quality control experiments including spiking with Cr(III) and Cr(VI)compounds. We found the Cr(VI) amounts to be below 2 mg/kg except for a thermally post-treated sewage sludge ash (SSA) that showed 12.3 mg/kg. The presence of organic matter e.g. in sludge or precipitated struvite caused a reduction of spiked Cr(VI) and thus no satisfying recovery for Quality control. Cr(VI) reduction was also observed for SSA, presumably due to the presence of Fe(II) compounds.
Even though the tested procedure can be hampered in some recycled fertilizer matrices, it might be adapted to be applicable also for these complex samples.
The importance of secondary raw materials for phosphorus (P) fertilizer production is expected to increase in the future due to resource depletion, supply risks, and heavy metal contamination of fossil phosphate resources. Municipal wastewater is a promising source for P recovery. In Germany for instance, it contains almost 50% of the total amount of P that is currently applied as mineral fertilizer. Several procedures have been developed to recover and re-use P resulting in a growing number of recycling fertilizers that are currently not regulated in terms of fertilizer efficiency. We tested various materials and matrices for their total P content, solubility of P in neutral ammonium citrate (Pnac) and water, and performed robustness tests to check if existing analytical methods are suitable for those new materials. Digestion with inverse aqua regia was best suited to determine the total P content. Pnac sample preparation and analyses were feasible for all matrices. However, we found significant time and temperature dependencies, especially for materials containing organic matter. Furthermore, several materials didn’t reach equilibrium during the extractions. Thus, strict compliance of the test conditions is strongly recommended to achieve comparable results.
Phosphor ist ein für alle Lebewesen essentielles Element und in seinen Funktionen nicht zu ersetzen. Der Bedarf wird aus der Nahrung gedeckt, daher wird Phosphor letztendlich durch Ackerbau den Böden entzogen. Der Nährstoff muss ersetzt werden, um dauerhafte Landwirtschaft zu ermöglichen. Das geschieht zum einen durch den Einsatz von Wirtschaftsdüngern, aber zu einem großen Teil auch durch Mineraldünger. Das hierfür benötigte Rohphosphat wird bergmännisch aus fossilen Lagerstätten gewonnen. Die entsprechende Reichweite wird auf über 300 Jahre geschätzt. Daher besteht zwar keine unmittelbare Gefahr, dass dieser lebenswichtige Nährstoff zu Neige geht, es bestehen jedoch erhebliche Versorgungsrisiken. Zum einen ist Europa nahezu vollständig von Importen abhängig und damit auch Schwankungen der Weltmarktpreise ausgesetzt. Darüber hinaus liegen Förderung und Reserven von Rohphosphaten entweder in Ländern mit hohem Eigenbedarf (USA, China) oder in politisch instabilen Regionen (Marokko, West Sahara). Außerdem sind viele Rohphosphate mit Schwermetallen wie Uran, Thorium und Cadmium belastet. Das Umweltbundesamt schätzt, dass jährlich mehr als 160 t Uran durch Mineraldünger auf deutsche Ackerflächen ausgebracht werden. Rückgewinnung von Phosphor könnte helfen, diese Probleme zu reduzieren. Ein bedeutendes Potential dafür stellt der Abwasserstrom dar. Die Menge an Phosphor darin wird deutschlandweit auf etwa 70.000 t jährlich geschätzt. Das entspricht etwa der Hälfte der Menge an Phosphor, die derzeit für Mineraldünger benötigt wird. Der Vortrag würde sich mit möglichen Prozessen der Rückgewinnung, deren Wirtschaftlichkeit und Herausforderungen der Analytik befassen:
- in den letzten Jahren wurden zahlreiche Verfahren zur Rückgewinnung von Phosphor aus verschiedensten Phasen der Abwasserreinigung entwickelt (wässrige Phase, Klärschlamm, Klärschlammasche). Ausgewählte Verfahren würden vorgestellt und bewertet.
- für einen Einsatz der so gewonnenen Recyclingphosphate als Düngemittel muss die Schadstofffreiheit und Pflanzenverfügbarkeit der Nährstoffe sichergestellt werden. Dazu ist zu prüfen, ob die zurzeit gängigen Verfahren der Probenvorbereitung und Analytik auch auf Recyclingphosphate anwendbar sind. Das gilt neben der Bioverfügbarkeit von Phosphor besonders für Schadstoffe, da die Recyclingdünger aus Abfallmaterialien gewonnen werden, die stark belastet sein können. Das gilt besonders für die speziesspezifische Analytik von Chrom (Chrom (VI) vs. Chrom (III)) in verschiedenen Matrices.
The annual demand of phosphorus (P) for fertilizer use is more than 550,000 t in Germany. Several of the input streams like mineral fertilizer produced from phosphate rock or sewage sludge are problematic due to contamination with heavy metals and organic pollutants and/or supply risks. Phosphorus recovery from the wastewater stream might help to diminish these problems. Several procedures have been developed to recover P from either sewage sludge ash (SSA) or wastewater via precipitation or crystallization as struvite. This study determined the elemental composition and trace metal mass fractions of 252 SSA samples and 17 struvite samples from wastewater treatment plants (WWTP) to see whether there are differences related to the source of the sludge (municipal/industrial) or the stage of the WWTP where the struvite is produced. Results indicated that there is no clear trend of the elemental mass fractions related to the source of the sludge. All struvite samples show very low heavy metal contents, even though the struvite precipitated from the sludge shows slightly elevated heavy metal mass fractions compared to struvite crystallized from sludge liquor. Struvite is a clean and plant available material for fertilizer production from wastewater streams and has some advantages for the wastewater treatment plant. However, since the P recovery rate of struvite processes is low (7–11%) compared to that from SSA processes (90%), recovery from SSA is necessary for a substantial P recovery from the wastewater stream.
Recovery of rare earth elements - optimized elemental analysis of fluorescent lamp shredder waste
(2016)
Rare earth elements (REE) are a crucial component of fluorescence lamps. Several procedures have been developed to recovery these technological important elements. Nevertheless, actual REE recycling from fluorescence lamps is scarce so far (recovery rate of less than 1 %), with current recycling approaches concentrating on glass recovery. Since most recycling processes include several, also wet-chemical steps, a complete knowledge of the actual elemental composition of the respective mass flows is necessary for an efficient REE recovery. We tested seven different reagent mixtures for microwave-assisted digestion of fluorescent lamp shredder, including HF, HClO4, and H2O2. We determined the concentrations of 25 of the most relevant rare earth and other trace elements in the respective dilutions. Two independent digestions, one a mixture of perchlorid/nitric/hydrofluoric acid and the other aqua regia, showed the highest concentrations of 23 of these elements, excluding only Sn and Tb. The REE concentrations in the tested lamp shredder sample (stated in g/kg) were 10.2 (Y), 12.1 (La), 7.77 (Ce), 6.91 (Eu), 1.90 (Gd), and 4.11 (Tb).
Recovery of rare earth elements - optimized elemental analysis of fluorescent lamp shredder waste
(2016)
Rare earth elements (REE) are a crucial component of fluorescence lamps. Several procedures have been developed to recovery these technological important elements. Nevertheless, actual REE recycling from fluorescence lamps is scarce so far (recovery rate of less than 1 %), with current recycling approaches concentrating on glass recovery. Since most recycling processes include several, also wet-chemical steps, a complete knowledge of the actual elemental composition of the respective mass flows is necessary for an efficient REE recovery. We tested seven different reagent mixtures for microwave-assisted digestion of fluorescent lamp shredder, including HF, HClO4, and H2O2. We determined the concentrations of 25 of the most relevant rare earth and other trace elements in the respective dilutions. Two independent digestions, one a mixture of perchlorid/nitric/hydrofluoric acid and the other aqua regia, showed the highest concentrations of 23 of these elements, excluding only Sn and Tb. The REE concentrations in the tested lamp shredder sample (stated in g/kg) were 10.2 (Y), 12.1 (La), 7.77 (Ce), 6.91 (Eu), 1.90 (Gd), and 4.11 (Tb).
Phosphorus is essential for all animate beings and not replaceable in its functions. Recovered phosphorus from secondary sources is expected gain importance in the future due to supply risks and environmental concerns regarding fossil phosphate rock, the single source of phosphorus so far. Existing regulations, standards, and analytical methods are basically configured for well-established organic and mineral fertilizer but not for the emerging recycling products. Consequently, the respective procedures have to be adapted, especially in terms of matrix effects and so far not regulated pollutants like uranium and emerging pollutants of concern.