Benzene is chemically stable as it has no substituents which can be biochemically attacked and a well-known toxic contaminant whose anaerobic degradation pathway is still not fully resolved. As only a very few anaerobic benzene-mineralizing pure cultures have been described yet, research was usually done with enrichment cultures dominated by specific organisms capable of benzene degradation under different electron acceptor conditions. Remarkable progress has been made in recent years with regard to the initial mechanism of benzene transformation especially on the putative genes that are involved in anaerobic carboxylation of benzene and the benzoyl-CoA central pathway. Many phylotypes described to be primary benzene degraders in anaerobic enrichment cultures at various electron acceptor conditions belong to the Peptococcaceae. Here, the thesis focused on characterizing the structure and function of anaerobic benzene-mineralizing microbial communities enriched from two hydrocarbon-contaminated sites: hydrocarbon-contaminated sediment from Ogoni in Niger Delta of Nigeria and a benzene-contaminated aquifer in Zeitz (Germany). The Niger Delta is one of the world’s most damaged ecosystem mainly due to hydrocarbon exploration accidents. The natural attenuation potential of Niger Delta subsurface sediment for anaerobic hydrocarbon degradation was investigated using benzene as a model compound under iron-reducing, sulfate-reducing, and methanogenic conditions. Benzene was slowly mineralized under iron-reducing conditions using Fe(III) chelated with nitrilotriacetic acid, or poorly crystalline Fe(III) oxyhydroxides as electron acceptors, analyzed by measurement of 13CO2 produced from added 13C-labelled benzene. The highest mineralization rates were observed in microcosms amended with Fe(III) oxyhydroxides while microcosms amended with Fe(III) nitrilotriacetic acid produced methane. Abundant phylotypes were affiliated to Betaproteobacteriales, Ignavibacteriales, Desulfuromonadales, and Methanosarcinales of the genera Methanosarcina and Methanothrix, illustrating that the enriched benzene mineralizing communities were diverse and may contain more than a single benzene degrader. The study underpins the importance of microbial ecosystem services in contaminant degradation as a sustainable environmental means of mitigating harmful chemicals. Benzene degradation pathways in a benzene-mineralizing, nitrate-reducing enrichment culture from Zeitz was investigated. Benzene mineralization was dependent on the presence of nitrate and correlated to enrichment of a Peptococcaceae phylotype only distantly related to known anaerobic benzene degraders of this family. Its relative abundance decreased after benzene mineralization had terminated, while other abundant taxa - Ignavibacteriaceae, Rhodanobacteraceae and Brocadiaceae - slightly increased. Generally, the microbial community remained diverse despite amendment of benzene as single organic carbon source, suggesting complex trophic interactions between different functional groups. A subunit of the putative anaerobic benzene carboxylase (AbcA) previously detected in Peptococcaceae was identified by metaproteomic analysis suggesting that benzene was activated by carboxylation. Detection of proteins involved in anaerobic ammonium oxidation (Anammox) indicates that benzene mineralization was accompanied by Anammox, facilitated by nitrite accumulation and the presence of ammonium in the growth medium. The results suggest that benzene was activated by carboxylation and further assimilated by a novel Peptococcaceae phylotype and confirm the hypothesis that Peptococcaceae are important anaerobic benzene degraders. Only a few benzene mineralizing anaerobes have been isolated to date. In an attempt using classical isolation techniques to isolate benzene-mineralizing pure cultures from a benzene-mineralizing nitrate-reducing microbial community, two consortia were gained under nitrate-reducing conditions spiked separately with acetate and benzene as sole sources of carbon and energy with media containing ammonium or without ammonium. Both consortia – Bz4 (with ammonium) and Bz7 (without ammonium) - mineralized 13C-labelled acetate under anoxic conditions at 3.3 and 2.7 µM day-1, respectively, revealed by analysis of evolved 13CO2. However, only Bz4 mineralized 13C-labelled benzene (0.298 µM benzene mineralized day-1) generated up to 960.2 ± 0.3 ‰ ẟ13C-CO2 during 184 days while producing only slight amounts of nitrite (4.60 ± 0.004 µM). By 16S rRNA gene amplicon sequencing was determined that the isolated cultures were not pure cultures but still contained several different phylotypes. The gained Bz4 consortium that mineralized benzene under anoxic conditions can be further purified and explored for their metabolic potentials.:Acknowledgments ………………………………………………………................. ii Table of Contents …………………………………………………………………… iii Dissertation Summary ……………………………………………………………… vi Dissertation Zusammenfassung …………………………………………………… viii List of Tables ………………………………………………………………………… x List of Figures ……………………………………………………………………….. xi List of Appendices ………………………………………………………………….. xiii Abbreviations .………………………………………………………….................... xv Chapter 1: Introduction and Research Objectives ……………………………… 1 1.1 Introduction ……………………………………………………………… 2 1.2 Aims and Objectives ………………………………………………….... 4 Chapter 2: Anaerobic Benzene Degradation by Microbial Communities and Pure Cultures …… 6 2.1 Anaerobic benzene degradation – a brief introduction ...…………… 7 2.2 Anaerobic benzene degradation under different electron acceptor conditions … 9 2.2.1 Benzene degradation under methanogenic conditions ……… 9 2.2.2 Benzene degradation under sulfate-reducing conditions …… 14 2.2.3 Benzene degradation under nitrate-reducing conditions …… 20 2.2.4 Benzene degradation under iron-reducing conditions ……… 25 2.3 Anaerobic benzene degradation by pure cultures ………………… 26 2.4 Anaerobic benzene activation mechanisms and associated genes……………… 28 2.4.1 Hydroxylation of benzene …………………………………….… 30 2.4.2 Methylation of benzene ………………………………..………… 34 2.4.3 Carboxylation of benzene ……………………………....………. 34 2.5 Benzoyl-CoA central metabolic pathways ………………………… 37 2.6 Syntrophic interactions in benzene-degrading communities ……… 42 2.7 Prospects for the future ……..……………………………………………… 43 Chapter 3: Anaerobic Benzene Mineralization by Natural Microbial Communities from Niger Delta …………………………………………………………………........... 44 3.1 Introduction …………………………………………………………..... 45 3.2 Materials and Methods ……………………………………………….. 46 3.2.1 Chemicals ………………………………………………………... 46 3.2.2 Site description and sampling procedure ……………………… 47 3.2.3 Setup of enrichment cultures …………………………………… 47 3.2.4 Chemical and microscopic analysis …………………………… 48 3.2.5 Microbial community analysis …………………………………… 49 3.3 Results and Discussion …………………………………………………. 50 3.3.1 Mineralization of benzene at different electron-acceptor conditions …………... 50 3.3.2 Microbial community structure at different electron-acceptor conditions ……... 53 3.4 Conclusion ………………………………………….…………………… 61 Chapter 4: Structure and Functional Capacity of a Benzene-mineralizing, and Nitrate-reducing Microbial Community ……………………………………………......... 62 4.1 Introduction …………………………………………………………..... 63 4.2 Materials and methods ……………………………………………..... 64 4.2.1 Chemicals ………………………………………………………... 64 4.2.2 Microcosm setup and sampling ………………………………… 64 4.2.3 Chemical and physiochemical analyses ……………………… 66 4.2.4 Amplicon and metagenome sequencing ……………………… 67 4.2.5 Protein mass spectrometry ……………………………………. 67 4.2.6 Metaproteome analysis ………………………………………… 68 4.2.7 Cloning and sequencing of putative nitric oxide dismutase (nod) genes ………. 68 4.2.8 Data availability …………………………………………………… 69 4.3 Results …………………………………………………………………………. 70 4.3.1 Benzene mineralization under nitrate-reducing conditions …… 70 4.3.2 Changes in microbial diversity during benzene mineralization . 71 4.3.3 Metaproteome composition ……………………………………… 74 4.3.4 Presence of putative nitric oxide dismutase genes (nod) ……. 76 4.4 Discussion ……………………………………………………………... 76 4.4.1 Putative pathways for nitrate reduction coupled with benzene mineralization … 76 4.4.2 Elucidation of the benzene activation step ……………………… 78 4.4.3 Benzoyl-CoA central pathway ……………………………………. 79 4.4.4 Peptococcacea as putative primary benzene degraders ……… 80 4.4.5 Metabolic function of Anammox bacteria in the community …… 81 Chapter 5: Consortia Dominated by Gammaproteobacteria Isolated from a Denitrifying Benzene-degrading Enrichment Culture and their Capacity to Mineralize Benzene...................... 83 5.1 Introduction ……………………………………………………………… 84 5.2 Materials and methods ………………………………………………… 85 5.2.1 Chemicals ………………………………………………………… 85 5.2.2 Isolation procedure …………………………………………………… 85 5.2.3 Mineralization and nitrite analyses ……………………..……… 86 5.2.4 Genomic DNA extraction and 16S rRNA gene sequencing … 87 5.3 Results …………………………………………………………………. 87 5.4 Discussions …………………………………………………………… 91 Chapter 6: General Conclusions and Outlook …..……………………………… 95 6.1 Conclusions and novelty of the research …………………………… 96 6.2 Ignavibacteriales as benzene degrading consortia under iron-reducing conditions 96 6.3 Insights into benzene activation via carboxylation by Peptococcaceae … 97 6.4 Unraveling growth of Anammox bacteria during benzene mineralization … 98 6.5 Study significance ……………………………………………………… 99 6.6 General outlook ………………………………………………………… 100 References ………………………………………………………………………… 101 Appendices ………………………………………………………………………… 120 Contributions of other Authors …………………………………………………… 160

This qualitative study has evaluated the economic development progression in the Russian Arctic over the 2008-2020 time-period. Departing from the qualitatively formulated official objectives in the Russian Federation’s Policy for the Arctic to 2020 (signed in 2008), this investigation sought to trace the implementation process and analyse the extent in which they have been met. A geoeconomic theoretical framework was used to guide this study through a dual case-centric process tracing and policy evaluation methodology. The data in this investigation mainly originated from news sources, think tanks, Arctic-specific foundations, and official reports from the Arctic Council and the Nordic Council of Ministers. The investigation was not hypothesis driven but rather attempted to assess the extent to which Russia’s stated objectives corresponded with the economic reality in the Russian Arctic region. The investigation has focused on three separate but interrelated elements of the regional economic development, namely maritime activity, hydrocarbon resource development and demographic trajectory. The analysis found that economic activity in the Russian Arctic regions has increased over the time-period and the stated policy objectives are to be considered fulfilled.

Ph. D. (Department of Biotechnology, Faculty of Applied and Computer Sciences), Vaal University of Technology. / Hydrocarbon pollution is becoming a growing environmental concern in South Africa and globally. This inadvertently supports the need to identify enzymes for their targeted degradation. The search for novel biocatalysts such as monooxygenases, alcohol dehydrogenases and aldehyde dehydrogenases, have relied on conventional culture-based techniques but this allows sourcing of the biomolecules from only 1-10 % of the microbial population leaving the majority of the biomolecules unaccounted for in 90-99 % of the microbial community. The implementation of a metagenomics approach, a culture-independent technique, ensures that more or less than 100 % of the microbial community is assessed. This increases the chance of finding novel enzymes with superior physico-chemical and catalytic traits. Hydrocarbon polluted soils present a rich environment with an adapted microbial diversity. It was thus extrapolated that it could be a potential source of novel monooxygenases, alcohol dehydrogenases (ADH) and aldehyde dehydrogenases (ALDH) involved in hydrocarbon degradation pathways. Therefore, the aim of the study was to extract metagenomic DNA from hydrocarbon contaminated soils and construct a metagenomic fosmid library and screen the library for monooxygenases, alcohol dehydrogenases (ADH) and aldehyde dehydrogenases (ALDH). Accordingly, the fosmid library was constructed from metagenome of hydrocarbon-contaminated soil. Then the library was functionally screened using hexadecane, octadecene and cyclohexane as substrates and fifteen positive clones were selected. The fosmid constructs of the positive clones were sequenced using PacBio next generation sequencing platform. The sequences were de novo assembled and analysed using CLC Genomic Workbench. The open reading frames (ORF) of the contigs were identified by blasting the contigs against uniport database. Accordingly, four novel genes namely amo-vut1, aol-vut3, dhy-sc-vut5 and dhy-g-vut7 that showed close similarity with our target enzymes were further analysed in silico and codon-optimized as per Escherichia coli codon preference. The codon adjusted sequences were synthesised and cloned into pET30a(+) expression vector. However, it is worth noting that expression of amo-vut1 was not successful since it was later identified to be a multi-pass member protein, which made it insoluble despite the use of detergent to the effect. There is a need to meticulously genetically engineer amo-vut1 to remove the signal and other membrane-bound peptides while maintaining its activity. Yet the other three constructs were successfully transformed and expressed in E. coli BL21 (DE3). The enzymes were purified and characterized and cocktail for hydrolysis of hexanol was succesfully engineered based on AOL-VUT3, DHY-SC-VUT5 and DHY-G-VUT7. Therefore, novel enzymes were mined from metagenome of fossil-oil contaminated soil and effective hydrocarbon-degrading enzyme cocktails containing their combination were successfully engineered.

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<p> Globally, millions of people rely upon plumbing to help store and deliver safe water to building inhabitants. This water is used for drinking, cooking, washing, appliances, and other activities to protect public health and support economic activity. Water softeners are common devices used to remove minerals from water to limit scale formation in plumbing thereby protecting appliances and improving drinking water taste. Despite tens of millions of these devices in U.S. homes, little is known about how these devices impact chemical drinking water quality. Further, many homes that have softeners have been impacted by disasters such as chemical spills and wildfires and encountered hydrocarbon contaminated drinking water. At present, no information is available about hydrocarbon fate in softeners and how to decontaminate these devices. The objectives of the first chapter were to (1) determine how bench-scale and full-scale water softeners impact drinking water organic carbon, chlorine disinfectant, total cell count, and sulfur concentrations, and (2) assess the softener’s ability to be decontaminated by water flushing after hydrocarbon contamination. The objectives of the second chapter were to (1) better understand the effect wildfires have on private drinking water well infrastructure, water quality, and (2) identify practical research needs. Chapter 1 experiments revealed that both new and aged softener resins leached organic carbon compounds into drinking water, and this prompted notable reductions of drinking water free chlorine disinfectant levels. Newly installed water softeners caused first flushed water to have high levels of organic carbon (934 mg/L) with about 40% particulate organic carbon. Total sulfur concentration was also elevated. After 1 week of use, water softeners caused drinking water to have 4-8 mg/L organic carbon levels. When exposed to hydrocarbon contaminated drinking water, resins absorbed and leached benzene, toluene, ethylbenzene, and total xylenes (BTEX) for more than 2 weeks. Chapter 2 results revealed that for the private drinking water wells sampled after the 2021 Marshall Fire, semi-volatile organic compound (SVOC); No SVOCs exceeded health-based drinking water limits. No volatile organic compounds were found in either shallow or deep wells or within homeowner plumbing. Heavy metals (Li and V) were found in several wells, but these contaminants were not associated with the fire. A private well water system serving 8 properties was damaged, lost pressure, and had not been flushed or repaired 7 months after the fire due to financial and technical challenges. Thesis results provide new knowledge for utilities, health officials, and building owners who desire to better understand commercially available softeners and wildfire damage considerations for private drinking water wells. Results described here can be used to inform communications with homeowners, public health recommendations regarding plumbing safety and water use decisions following suspected or confirmed building chemical contamination and wildfires. </p>