Entwicklung eines biologischen Verfahrens zur Reduktion des Methanschlupfes von Gasaufbereitungsanlagen mittels Einsatz methanotropher Mikroorganismen

Im Rahmen dieser Arbeit wurde ein biologisches Verfahren zur Reduzierung des Methanschlupfes in Gasaufbereitungsanlagen entwickelt. Der Methanschlupf entsteht, wenn das in Biogasanlagen produzierte Biogas auf normierte Erdgasqualität aufgereinigt wird, welches notwendig ist, um es in das bestehende Erdgasnetz einleiten zu können. Bei dieser Aufreinigung wird aus dem Biogas auch ein Teil des Methans mit ausgewaschen und gelangt mit dem Abgas der Gasaufbereitungsanlage in die Umwelt. Bisher wird dieses methanhaltige Abgas verbrannt, da eine Freisetzung des starken Treibhausgases Methan durch das Erneuerbare-Energien-Gesetz untersagt ist. Dies reduziert die ökologische Bilanz und setzt die Wirtschaftlichkeit der gesamten Biogasanlage herab. rnUm das Methan mit Hilfe eines biologischen Verfahrens zu entfernen, wurden zunächst methanoxidierende Bakterien (MOB) aus verschiedenen Habitaten isoliert, darunter auch erstmalig aus Termiten. Der Nachweis erfolgte durch (quantitative) Polymerase-Kettenreaktion und Fluoreszenz-in-situ-Hybridisierung anhand spezifischer Primer bzw. Sonden für das Gen der partikulären Methanmonoxygenase, ein MOB kennzeichnendes Enzym. Ihr Titer wurde durch qPCR auf 10^2 - 10^3 MOB pro Termitendarm durch qPCR bestimmt. Mit Hilfe einer 16S rDNA Sequenzierung, der (n)SAPD-PCR, der Bestimmung der zellulären Fettsäurezusammensetzung sowie MALDI-TOF-MS-Analysen konnten die Termitenisolate der Gattung Methylocystis zugeordnet werden. Die fehlende Artzuweisung spricht jedoch für die Isolierung einer neuen Art. rnFür den Einsatz der Isolate in Gasaufbereitungsanlagen wurde in Zusammenarbeit mit dem Prüf- und Forschungsinstitut in Pirmasens ein Reaktor im Technikumsmaßstab entwickelt und konstruiert. Der Reaktor wurde mit synthetischen Aufwuchskörper befüllt, diese mit einem neu gewonnenen potenten Termitenisolat besiedelt und der methanhaltige Abgasstrom der Gasaufbereitungsanlage darüber geleitet. Es wurde eine Reduktion des Methans um 68 % innerhalb von 30 Stunden erzielt. Medienoptimierungen wiesen das Potential auf, diesen Verbrauch um das bis zu 4-fache weiter zu steigern. Da durch die Oxidation des Methans im Abgasstrom der Gasaufbereitungsanlage Zellmasse und Polyhydroxybuttersäure (PHB) aufgebaut wurde, können diese als Substrat zurück in die Biogasanlagen geleitet werden und die Wirtschaftlichkeit weiter verbessern. Die Wirksamkeit des in diesem Projekt entwickelten Verfahrens wurde somit eindeutig demonstriert.

Linkage and association of candidate obesity genes in Mexican-Americans from Starr County, Texas

Obesity and related chronic diseases represent a tremendous public health burden among Mexican Americans, a young and rapidly-expanding population. This study investigated the impact of variation within eight candidate obesity genes, which include leptin (LEP), leptin receptor (LEPR), neuropeptide Y (NPY), NPYY1 receptor (NPYY1), glucagon-like peptide-1 (GLP-1), GLP-1 receptor (GLP1R), beta-3 adrenergic receptor (β3AR), and uncoupling protein (UCP1), on variation in human obesity status and/or quantitative traits related to obesity in Mexican Americans from Starr County, Texas. The Trp64Arg polymorphism within β3AR was typed in 820 random individuals and 240 pedigrees (N = 2,044). The Arg allele frequency was significantly greater in obese versus non-obese individuals (0.20 versus 0. 15, respectively). In addition, within the random sample, the Arg allele was associated with significantly greater body weight (p = 0.031) and body mass index (BMI, p = 0.008) than the Trp allele. In the family sample, the Trp64Arg locus was also linked to percent fat (p = 0.045) but not to body weight or BMI. No linkage between obesity, diabetes, hypertension, or gallbladder disease and the Trp64Arg mutation was observed in families using affected sib pair linkage analysis or the transmission disequilibrium test. Microsatellite markers proximate to the remaining seven genes were typed in 302 individuals from 59 families. Sib pair linkage analysis provided evidence for linkage between obesity and NPY within affected sibling pairs (p = 0.042; n = 170 pairs). NPY was also linked to weight (p = 0.020), abdominal circumference (p = 0.031), hip circumference (p = 0.012), DBP (p ≤ 0.005), and a composite measure of body mass/fat (p ≤ 0.048) in all sibling pairs (n = 545 pairs). Additionally, LEP was linked to waist/hip ratio (p ≤ 0.009), total cholesterol (p ≤ 0.030), and HDL cholesterol (p ≤ 0.026), and LEPR was linked to fasting blood glucose (p ≤ 0.018) and DBP (p ≤ 0.003). Subsequent to the linkage analyses, the NPY gene was sequenced and eight variant sites identified. Two variant sites (-880I/D and 69I/D) were typed in a random sample of 914 individuals. The 880I/D variant was significantly associated with waist/hip ratio (p = 0.035) in the entire sample (N = 914) and with BMI (p = 0. 031), abdominal circumference (p = 0.044), and waist/hip ratio (p = 0.041) in a non-obese subsample (BW < 30 kg/m2, n = 594). The 69I/D variant was a rare mutation observed in only one pedigree and was not associated with obesity or body size/mass within this pedigree. Results of this study indicate that variation at or near β3AR, LEP, LEPR, and NPY may exert effects which increase obesity susceptibility and influence obesity-related measures in this population. ^

Respiration and ingestion rates of calanoid copepod in the northern Benguela Current System measured ex situ during the RSS Discovery D356 cruise in 2010

Respiration rates of 16 calanoid copepod species from the northern Benguela upwelling system were measured on board RRS Discovery in September/October 2010 to determine their energy requirements and assess their significance in the carbon cycle. Copepod species were sampled by different net types. Immediately after the hauls, samples were sorted to species and stages (16 species; females, males and C5 copepodids) according to Bradford-Grieve et al. (1999). Specimens were kept in temperature-controlled refrigerators for at least 12 h before they were used in experiments. Respiration rates of different copepod species were measured onboard by optode respirometry (for details see Köster et al., 2008) with a 10-channel optode respirometer (PreSens Precision Sensing Oxy-10 Mini, Regensburg, Germany) under simulated in situ conditions in temperature-controlled refrigerators. Experiments were run in gas-tight glass bottles (12-13 ml). For each set of experiments, two controls without animals were measured under exactly the same conditions to compensate for potential bias. The number of animals per bottle depended on the copepods size, stage and metabolic activity. Animals were not fed during the experiments but they showed natural species-specific movements. Immediately after the experiments, all specimens were deep-frozen at - 80 °C for later dry mass determination (after lyophilisation for 48 h) in the home lab. The carbon content (% of dry mass) of each species was measured by mass-spectrometry in association with stable isotope analysis and body dry mass was converted to units of carbon. For species without available carbon data, the mean value of all copepod species (44% dry mass) was applied. For the estimation of carbon requirements of copepod species, individual oxygen consumption rates were converted to carbon units, assuming that the expiration of 1 ml oxygen mobilises 0.44 mg of organic carbon by using a respiratory quotient (RQ) of 0.82 for a mixed diet consisting of proteins (RQ = 0.8-1.0), lipids (RQ = 0.7) and carbohydrates (RQ = 1.0) (Auel and Werner, 2003). The carbon ingestion rates were calculated using the energy budget and the potential maximum ingestion rate approach. To allow for physiological comparisons of respiration rates of deep- and shallow-living copepod species without the effects of ambient temperature and different individual body mass, individual respiration rates were temperature- (15°C, Q10=2) and size-adjusted. The scaling coefficient of 0.76 (R2=0.556) is used for the standardisation of body dry mass to 0.3 mg (mean dry mass of all analysed copepods), applying the allometric equation R= (R15°C/M0.76)×0.30.76, where R is respiration and M is individual dry mass in mg.