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Mikroorganismen in geothermischen Aquiferen : Einfluss mikrobieller Prozesse auf den Anlagenbetrieb
(2012)
In Fluid-, Filter- und Sedimentproben von vier geothermischen Anlagen des Norddeutschen Beckens wurden mit molekulargenetischen Verfahren unterschiedliche mikrobielle Gemeinschaften nachgewiesen. Die mikrobielle Zusammensetzung in den Prozesswässern wurde dabei durch die Aquiferteufe, die Salinität, die Temperatur und den verfügbaren Elektronendonatoren und -akzeptoren beeinflusst. Die in den anoxischen Prozesswässern identifizierten Organismen zeichneten sich durch einen chemoheterotrophen oder chemoautotrophen Stoffwechsel aus, wobei Nitrat, Sulfat, Eisen (III) oder Bikarbonat als terminale Elektronenakzeptoren fungierten. Mikroorganismen beeinflussten den Betrieb von zwei Anlagen negativ. So reduzierten im Prozesswasser des Kältespeichers am Berliner Reichstag vorhandene Eisenoxidierer, nahe verwandt zu der Gattung Gallionella, die Injektivität der Bohrungen durch Eisenhydroxidausfällungen in den Filterschlitzen. Biofilme, die von schwefeloxidierenden Bakterien der Gattung Thiothrix in den Filtern der obertägigen Anlage gebildet wurden, führten ebenfalls zu Betriebsstörungen, indem sie die Injektion des Fluids in den Aquifer behinderten. Beim Wärmespeicher in Neubrandenburg waren Sulfatreduzierer vermutlich an der Bildung von Eisensulfidausfällungen in den obertägigen Filtern und im bohrlochnahen Bereich beteiligt und verstärkten Korrosionsprozesse an der Pumpe im Bohrloch der kalten Aquiferseite. Organische Säuren in den Fluiden sowie mineralische Ausfällungen in den Filtern der obertägigen Anlagen waren Belege für die Aktivität der in den verschiedenen Anlagen vorhandenen Mikroorganismen. Es wurde zudem deutlich, dass Mikroorganismen auf Grund der hohen Durchflussraten in den Anlagen chemische Veränderungen in den Prozesswässern deutlich sensitiver anzeigen als chemische Analyseverfahren. So deuteten Änderungen in der Zusammensetzung der mikrobiellen Biozönosen und speziell die Identifikation von Indikatororganismen wie Eisen- und Schwefeloxidierern, fermentativen Bakterien und Sulfatreduzierern auf eine erhöhte Verfügbarkeit von Elektronendonatoren oder akzeptoren in den Prozesswässern hin. Die Ursachen für die an den Geothermieanlagen auftretenden Betriebsstörungen konnten dadurch erkannt werden.
The presented study investigated the influence of microbial and biogeochemical processes on the physical transport related properties and the fate of microplastics in freshwater reservoirs. The overarching goal was to elucidate the mechanisms leading to sedimentation and deposition of microplastics in such environments. This is of importance, as large amounts of initially buoyant microplastics are found in reservoir sediments worldwide. However, the transport processes which lead to microplastics accumulation in sediments, were up to now understudied.
The impact of biofilm formation on the density and subsequent sedimentation of microplastics was investigated in the eutrophic Bautzen reservoirs (Chapter 2). Biofilms are complex microbial communities fixed to submerged surfaces through a slimy organic film. The mineral calcite was detected in the biofilms, which led to the
sinking of the overgrown microplastic particles. The calcite was of biogenic origin, most likely precipitated by sessile cyanobacteria within the biofilms.
Biofilm formation was also studied in the mesotrophic Malter reservoir. Unlike in Bautzen reservoir, biofilm formation did not govern the sedimentation of different microplastics in Malter reservoir (Chapter 3). Instead autumnal lake mixing led to
the formation of sinking aggregates of microplastics and iron colloids. Such colloids form when anoxic, iron-rich water from the hypolimnion mixes with the oxygenated epilimnetic waters. The colloids bind organic material from the lake water, which leads to the formation of large and sinking iron-organo flocs.
Hence, iron-organo floc formation and their influence on the buoyancy or burial of microplastics into sediments of Bautzen reservoir was studied in laboratory experiments (Chapter 4). Microplastics of different shapes (fiber, fragment, sphere) and sizes were readily incorporated into sinking iron-organo flocs. By this initially buoyant polyethylene microplastics were transported on top of sediments from Bautzen reservoir. Shortly after deposition, the microplastic bearing flocs started to subside and transported the pollutants into deeper sediment layers. The microplastics were not released from the sediments within two months of laboratory incubation.
The stability of floc microplastic deposition was further investigated employing experiments with the iron reducing model organism Shewanella oneidensis (Chapter 5). It was shown, that reduction or re-mineralization of the iron minerals did not affect the integrity of the iron-organo flocs. The organic matrix was stable under iron reducing conditions. Hence, no incorporated microplastics were released from the flocs. As similar processes are likely to take place in natural sediments, this might explain the previous described low microplastic release from the sediments.
This thesis introduced different mechanisms leading to the sedimentation of initially buoyant microplastics and to their subsequent deposition in freshwater reservoirs. Novel processes such as the aggregation with iron-organo flocs were identified and the understudied issue of biofilm densification through biogenic mineral formation was further investigated. The findings might have implications for the fate of microplastics within the river-reservoir system and outline the role of freshwater reservoirs as important accumulation zone for microplastics. Microplastics deposited in the sediments of reservoirs might not be transported further by through flowing river. Hence the study might contribute to better risk assessment and transport balances of these anthropogenic contaminants.