This dissertation examines the suitability of Computational Fluid Dynamics (CFD) modelling for the production of realistic flowfields and temperature fields within a series of vortex combustion chambers of differing geometries and operating under various conditions. Initial validation of the CFD predictions was obtained through modelling of a series of isothermal vortex chambers for which a comprehensive set of experimental data was available. It was observed that CFD did indeed produce representative flowfield predictions for chambers of various geometries and operating conditions. A vortex unit used for the incineration of sewage sludge (US Navy Waste Incinerator) was subsequently investigated, and it was shown that due to the high moisture content of the waste material used, temperature profiles obtained with a modified coal combustion model were similar to those obtained with a more straightforward and computationally less expensive spray drier model. Results from both models were similar to experimentally observed conditions. However, comprehensive validation was not possible. In order that full validation could be provided for a CFD model of a vortex combustion unit, a model was developed of a commercial thermal oxidiser used for the incineration of liquid and gaseous wastes. CFD temperature predictions for the BASF Thermal Oxidiser were validated by a series of experimental measurements obtained from the operating unit. In general, it was found that the Reynolds Stress Model for turbulence produced the most representative velocity flowfields, with the less computationally demanding k-e model being applicable only under certain limited circumstances. Furthermore, insufficient grid refinement resulted in significantly distorted velocity profiles.

European legislation has increased pressure on the use of land to represent the major disposal option for sewage sludge. Owing to their importance in regulating soil fertility, much research has been conducted into the effects of sewage sludge application on soil microorganisms. However, little knowledge is known about its effects on community dynamics of the beta-subgroup ammonia oxidising bacteria. This is despite the fact that nitrification activity of these bacteria plays an important role in soil nitrogen cycling. This investigation aimed to examine community dynamics of the beta-subgroup ammonia oxidising bacteria in sewage sludge amended soil by employing recently developed molecular based techniques. Firstly, a soil DNA extraction protocol was identified that allowed routine nested PCR amplification of 16S rDNA using beta-subgroup ammonia oxidiser directed primers. Reproducibility observed in denaturant gradient gel electrophoresis (DGGE) profiles suggested that 0.5 g samples used for DNA extraction allowed consistent detection of dominant beta-subgroup ammonia oxidiser community members. The effects of applying primary treatment sewage sludge to a variety of contrasting soils on (3-subgroup ammonia oxidiser community structure was unclear. This was partially hampered by lack of specificity of PCR primers for non ammonia oxidiser 16S rDNA sequences. Further, through measurement of net nitrification, there was no indication that sewage sludge addition stimulated the activity of nitrifier populations. Nevertheless, this study indicated the usefulness of DGGE for screening multiple environmental samples. A set of hierarchical oligonucleotide probes exhibiting specificity at the group, genus and cluster level were optimised using a non-radioactive system. These probes were used to assess the effects of application of aerobically digested sewage sludge to soil for 4 y on beta-subgroup ammonia oxidiser community structure. Despite significant changes in measurable soil parameters including net nitrification activity no changes were observed in beta-subgroup ammonia oxidiser community structure. This indicated resilience of these communities to change. A final study was conducted examining the effects of application of anaerobically digested sewage sludge to soil on beta-subgroup ammonia oxidiser community structure. Inhibition of nitrification by acetylene indicated the presence of a viable population of ammonia oxidising bacteria in continuously shaken samples of sludge. DGGE and oligonucleotide probing analysis provided evidence that sewage populations had the potential to outcompete indigenous soil populations of beta-subgroup ammonia oxidising bacteria. This was despite the fact that MPN enumeration suggested that soil populations of these bacteria were in some cases 10-fold greater than sludge populations. Evidence was also provided that suggested net nitrification to be an unreliable indicator of ammonia oxidiser activity in soil. It is possible to conclude that community structure of the beta-subgroup ammonia oxidising bacteria may be altered by application of sewage sludge to soil. The effects on community structure are likely to be influenced by both the type and level of sludge applied to soil.

En av de vanligaste föroreningarna i mark och grundvatten är aromatiska kolvä- ten såsom bensen, toluen, etylbensen och xylener. Dessa härstammar från ex. ben- sin och har läckt ut till omgivande miljö från drivmedelsanläggningar. I stället för schaktning och bortforsling av de förorenade jordmassorna som mest förekom- mande ex situ-saneringsmetod behövs mer forskning kring in situ-saneringsmetoder där föroreningen alltså kan angripas på plats. I denna rapport undersöks förhöjd biologisk nedbrytning genom att redogöra för de önskvärda (bio)kemiska reak- tionerna i marken, de parametrar som styr den biologiska nedbrytningen samt huruvida dessa parametrars inverkan har kunnat påvisas i tre stycken fallstu- dier där in situ-sanering utförts vid drivmedelsanläggningar. Studien kommer fram till ett antal primära (ursprungliga) variabler såsom föroreningen i fråga, jordtätheten och klimatet, samt ett antal sekundära (förändringsbara) variabler såsom oxidationsmedlet, mikroorganismerna, näringsämnena och markvattnet. Dessa presenterades sedan i en schematisk skiss som visar hur de växelverkar med parametrarna för optimal biologisk nedbrytning, vilka visade sig ha vissa optimala värden. Dessa konstaterades vara föroreningshalten (<5-10 viktprocent torr jord), pH-värdet (6-9), temperaturen (20-35◦C), vattenmättnaden (40-80%), syrehalten (> 2 500 viktprocent kolväten), C:N:P-kvoten (100:10:1) samt koncent- rationen mikroorganismer (> 103 CFU/ml). När de olika parametrarnas inverkan  i fallstudierna undersöktes kunde slutsatsen dras att det skulle behövas ytterliga- re data och mätningar vid varje sanering för att kunna garantera att parametrarna varit inom sina respektive optimala värden. / One of the many goals for a sustainable living and a healthy environment is the reduction of toxic substances in soil and groundwater. Within this ambit, one of the most common pollutants is aromatic hydrocarbons such as benzene, tolue- ne, ethylbenzene and xylenes (BTEX) which are spread from e.g. filling stations for fuel as they are constituents of petrol. These are volatile and can constitute a risk for humans and the environment as they percolate through the soil and groundwater resources as well as can exfiltrate from the ground to surrounding buildings and pollute the indoor air. Once these pollutants are present in the soil, the site needs to be remediated, something which is mainly done ex situ by exca- vating the polluted masses to be sent to a treatment facility. An alternative to this is in situ remediation where the pollution can be treated without being excavated and thus having a smaller impact on the environment.  In this report, one of these techniques called enhanced biodegradation was studied, which implies the application of oxidisers to faciliate microbial activities. It investigated (1) how this remediation technique works and what (bio)chemical reactions are desired in the soil; (2) what are the principal parameters that enable this remediation process and how do they interact with the surrounding factors, and (3) whether the impact of these parameters can be estimated in three case studies where this technique has been used. The three case studies were filling stations located in Sweden, having similar pollutants and geology, and two diffe- rent oxidisers had been used.  The study resulted in the identification of a number of primary (initial) varia- bles such as the pollutant characteristics, the soil density and the climate; as well as a number of secodnary (modifiable) variables such as the oxidiser, microorga- nisms, nutrients and soil moisture. These were then presented in a scheme which shows how their interactions with the parameters for optimal biodegradation. Each parameter was found to have a certain optimum such as the concentration of hydrocarbons (<5-10 mass percent of the dry soil) , pH value (6-9), tempe- rature (20-35◦C), soil water saturation (40-80%), oxygen concentration (> 2,500 mass percent of the hydrocarbons), C:N:P ratio (100:10:1) as well as concentration of microorganisms (> 103 CFU/ml). A negative correlation could be identified between the soil density and the oxygen concentration in the soil, as well as a po- sitive correlation between the soil water saturation in the and the soil moisture, alternatively additional water via irrigation. The impact of each parameter in the case studies of in situ remediation was assessed and the it could be concluded that they would need additional data and measurements for most parameters in order to guarantee that they are within the respective optima.

The aim of the research study was to evaluate the levels of 14C and 3H radionuclides in Hartbeespoort Dam water and to determine if these radionuclides are within regulatory concerns. Water samples from Hartbeespoort Dam were prepared using the Sample Oxidiser Method and measurements of selected radionuclides were done using Liquid Scintillation Counter Quantulus 1220. The results evaluated suggest that water from Hartbeespoort Dam contains levels of 14C and 3H radionuclides that are within regulatory limits. The highest average concentration for 14C measured was 3.77E+01 (+/-2.47E-01) Bq/L, whereas the highest average concentration measured for 3H was 2.74E+01 (+/- 2.30E-01) Bq/L. The observations made regarding the impacts of climate on the 14C radionuclide were that, the concentration levels were higher during winter season when there was a rain than during rainy seasons. Tritium results showed that the climate conditions did not have any significant impacts on the concentration levels. When the concentrations of these radionuclides are above regulatory levels (14C is 100 Bq/L and 3H is10000 Bq/L), their impacts may cause harm to public`s health and the environment. Therefore, Necsa as a nuclear facility owner and National Nuclear Regulator (NNR) as a regulator are responsible for ensuring the public protection from radioactive effluents that contain not just 3H and 14C, but any radionuclide which may cause harm to public`s health. / Environmental Sciences / M. Sc. (Environmental Science)