Potential contamination from hazardous and solid waste landfills stemming from population increase, rapid industrialization, and the proliferation of assembly plants known as the maquiladoras, are of major concern in the U.S.-Mexican border area. Additionally, historical, current, and future stresses on the Hueco Bolson alluvial aquifer in the El Paso/Ciudad Juarez area due to excessive groundwater withdrawal can affect contaminant migration in the area. In the current study, an updated and improved threedimensional numerical groundwater flow and transport model is developed using a current Hueco Bolson groundwater availability model as its basis. The model with contaminant transport is required to access and characterize the extent of vulnerability of the aquifer to potential contamination from landfills in the El Paso/Ciudad Juarez border area. The model developed in this study is very capable of serving as the basis of future studies for water availability, water quality, and contamination assessments in the Hueco Bolson. The implementation of fate and transport modeling and the incorporation of the Visual MODFLOW® pre and post processor, requiring MODFLOW 2000 data conversion, enabled significant enhancements to the numerical modeling and computing capabilities for the Hueco Bolson. The model in the current research was also developed by employing MT3DMS©, ZONEBUDGET, and Visual PEST® for automated calibrations. Simulation results found that the Hueco Bolson released more water from storage than the aquifer was being recharged in response to increased pumping to supply the growing border area population. Hence, significant head drops and high levels of drawdown were observed in the El Paso/Ciudad Juarez area. Predictive simulations were completed representing scenarios of potential contamination from the border area sites. Fate and transport results were most sensitive to hydraulic conductivities, flow velocities, and directions at the sites. Sites that were located within the vicinity of the El Paso Valley and the Rio Grande River, where head differences and permeabilities were significant, exhibited the highest potentials for contaminant migration.

Many potential small wind turbine locations are near obstacles such as buildings and shelterbelts, which can have a significant, detrimental effect on the local wind climate. This thesis describes the creation of a new model which can predict the wind speed, turbulence intensity, and wind power density at any point in an obstacle’s region of influence, relative to unsheltered conditions. Artificial neural networks were used to learn the relationship between an obstacle’s characteristics and its effects on the local wind. The neural network was trained using measurements collected in the wakes of scale models exposed to a simulated atmospheric boundary layer in a wind tunnel. A field experiment was conducted to validate the wind tunnel measurements. Model predictions are most accurate in the far wake region. The estimated mean uncertainties associated with model predictions of velocity deficit, power density deficit, and turbulence intensity excess are 5.0%, 15%, and 12.8%, respectively. / Industrial collaborators: Weather INnovations Inc., Wenvor Technologies Inc. / Ontario Centre of Excellence for Energy

This manuscript based thesis examines and advances methods for constraining sources of atmospheric trace constituents with a Lagrangian particle dispersion model. The method of Bayesian inversion is demonstrated, and a new method is introduced to a class of similar problems where established methods are not applicable. First, A new regression based methodology was developed and applied to observations of atmospheric methanesulfonic acid mass concentrations at Alert, Nunavut. The methodology was used to compare the importance of phytoplankton blooms vs. the ice-free ocean as sources of the dimethylsulfide precursor, and to compare the importance of bromine monoxide vs. hydroxyl as agents oxidizing dimethylsul de to methanesulfonic acid. These issues are relevant to the application of methanesulfonic acid concentrations in ice cores to determine historic sea ice properties. The analysis indicated that source regions to Alert during the spring are primarily ice-free ocean with a significant contribution from ice edge blooms, and during the summer to be dominated by the ice-free ocean. The model also indicated that oxidation of DMS by BrO was the dominant source of MSA in the spring, while DMS oxidation by OH was the dominant source in the summer. Secondly, Bayesian inversion was applied to observations of atmospheric elemental carbon mass concentrations at Tsinghua University in Beijing, China. The analysis provided evidence that current bottom-up elemental carbon emissions estimates in northern China are likely underpredicted. Global chemical transport models show ubiquitous underestimates of the atmospheric burden of elemental carbon, especially near large sources of emissions. Northern China is among the regions with the most intensive elemental carbon emissions in the world, and an underestimate of emissions in this region may be partially responsible for the global chemical transport model underestimates.

[pt] Este trabalho apresenta resultados de um estudo, executado em laboratório, da mobilidade do herbicida Paraquat, realizado a partir de sua percolação através de amostras de solos retiradas do Campo Experimental de Bom Jardim, RJ. Foram determinadas as propriedades físicas, químicas e mineralógicas das amostras coletadas de maneira a formar um perfil do solo local. Para estes solos, através dos ensaios realizados, tais como o ensaio ADS (em coluna) e o de adsorção em batelada, foi possível determinar parâmetros de transporte do contaminante. Na análise para a quantificação do Paraquat foi adotado um método de coloração por determinação espectrofotométrica. No ensaio ADS foi possível, para apenas um dos solos, a determinação dos parâmetros de transporte em solo saturado, enquanto que no ensaio de adsorção em batelada foi determinada, para todos os solos, a isoterma de adsorção bem como os parâmetros referentes aos modelos de Freudlich e Langmuir. A partir dos resultados do ensaio ADS, verificou-se, a alta capacidade de retenção do Paraquat ao solo, chegando-se à conclusão de que, possíveis problemas de contaminação de águas pelo mesmo venham a estar associados a processos erosivos. / [en] This paper presents results of a study, performed in the laboratory, on the mobility of the herbicide Paraquat, investigated from its percolation through soils samples withdrawn from the Experimental Field of Bom Jardim, RJ. It was determined the physical, chemical and mineralogical properties of samples collected in such manner to form a profile of ground local soil. For these soils, through testings, such as the ADS test (in a special column) and the batchadsorption test, it was possible to determine parameters of the transport of the contaminant. In the analysis for the quantification of Paraquat was adopted a method of staining by spectrophotometric determination. In the ADS test it was possible, for only one of the soil samples, the determination of the parameters of transport with the batch- adsorption test it was determined, for all soils, the isotherm of adsorption as well as the parameters related to the models of Freudlich and Langmuir. From the results the ADS test it was found a high retention of Paraquat to the soil, leading to the conclusion that potential problems of contamination of superficial water at the sitemay be associated with erosive processes.

It is recognised through current literature that contaminantin trusion is a primary threat leading to degradation of water quality and threat to human health. The problem is more serious in developing countries where the water supply is intermittent and water distribution system crisscross with sanitary systems. Therefore there is a need to develop the methodology that enables the decision makers and engineers to undertake actions to minimise the risk of contamination of water. The researchs tudy presentedin this thesis addresses these water quality issues by developing the appropriate modelling tools to minimize the risk of contaminant intrusion. The conceptual framework proposed in this study consists of a risk based approach where the process of contaminant intrusion into the systems is traced to know the hazards of contaminant intrusion and vulnerability of the system. The risk of contaminant intrusion into the pipes of a water distribution system is then estimated as the function of hazards and vulnerability. A suit of four models is developed based on this framework. The first model is a water distribution pipe condition assessment model that simulates the potential pathway for contaminant ingress into water pipes by relating it to the deterioration/condition of the pipes. The condition of each pipe is assessed by means of numerous factors related to physical, environmental and operational aspects of the water distribution system. These factors are grouped into different indicators at three levels, depending on the nature of influence of each factor on the deterioration process of the pipe. The uncertainties inherent in these pipe condition indicators are described with fuzzy set theory. A distance based multi-criteria decision making method-fuzzy composite programming has been applied to combine the multilevel pipe condition indicators to form a single indicator to rank the condition of the pipes. The second model is a water flow and contaminant transport modelling tool. This model predicts the envelope of pollution emanating from pollution sources (contaminant zone) and simulates the seepage and contaminant transport in this zone. It is assumed that the seepage of contaminant from pollution sources such as unlined canal/drains and surface water bodies follow saturated flow while from pollution sources such as sewer pipelines, lined canals/drains follow unsaturated flow. Accordingly Richard/Green Ampt equations (unsaturated flow) and Darcy's equation (saturatedf lows) are coupled with advection-diffusion equations that account for water flow and contaminant transport respectively. The third model, the contaminant ingress model, identifies sections of pipe of water distribution system within contaminant zone by combining the outputs from the contaminant seepage model with spatial analysis. The fourth model, the risk assessment model, identifies the risk of contaminant intrusion into a water distribution system from the outputs of the above three models, namely the vulnerability of the water distribution pipe (pipe condition assessment model), the contaminant concentration(contaminant seepage model) and section of pipe in contaminant zone (contaminant ingress model). All these models have been integrated into ArcView GIS to form a decision support system (Improved Risk Assessment of Water Distribution System) and applied to a real water distribution system in Guntur, India for which water pipe network data and data for pollution sources were collected. The modelling results are presented as risk maps that show the potential areas that are under threat of contamination with relative risk scores. It is envisaged that the developed modelling tools will be used by water utilities in developing countries to improve the water quality management by identifying vulnerable areas and understanding threats that exist to the water distribution systems.

Eutrophication is one of the key environmental problems of today, both in terms of complexity and magnitude. For the Baltic Sea (BS), eutrophication is an acute problem, leading to hypoxic conditions at the bottom; a situation that is sustained and amplified, when phosphorus is released from hypoxic sediments. Reducing nutrient loading is a top political priority but the present situation is believed to require active measures within the catchments and recipients to reduce both loading and adverse effects. Implementation of effective and cost-efficient abatement methods requires understanding of natural processes in watersheds, streams and recipients as well as technological expertise in order to compare the effects of measures of different kinds and locations. This thesis tries to combine process understanding of catchment transport behaviour, especially in coastal zones, and feasibility of certain technologies for reducing nutrient loading and effects of eutrophication in-situ. The over-arching theme is the fate of the individual contaminant, from injection to removal. Transport and dispersion in catchments are investigated, combining physically-based, distributed, numerical groundwater models with Lagrangian stochastic advective reactive solute (LaSAR) transport modelling. The approach is powerful in the sense that it incorporates catchment structural, geomorphological dispersion in the numerical model with hydrodynamic and sub-scale dispersion as well as uncertainty in the LaSAR framework. The study exemplifies the complex nature of transport time distributions in catchments in general and when varying source size and location, importance of dispersion parameters and retention due to molecular diffusion. It is shown that geomorphological control on dispersion is present even for relatively heterogeneous systems and that neither the mean residence time nor a statistical distribution may provide accurate representations of hydrological systems. To combat internal loading of P from sediments in-situ, large-scale aeration of deep waters, halocline ventilation, has been suggested. This study further investigates the feasibility of wave-powered devices to meet the energy demands for such an operation. It is shown that the required amount of oxygen needed to keep the sediments at oxic conditions could be provided, cheaply and efficiently, through the use of wave power. / QC 20120511

Bioretention is increasingly being employed as a stormwater management tool in urban areas, with the intent of using infiltration to address both water quantity and quality concerns. However, bioretention soil media (BSM) has limited removal capacity for dissolved contaminants; hence, amendments may be justified to improve performance. In this study, the potential of five low-cost sorbents as BSM amendments – waste tire crumb rubber (WTCR), coconut coir fiber (CCF), blast furnace slag (BFS), biochar (BC) and iron coated biochar (FeBC) – were investigated for removing several classes of contaminants from simulated stormwater (SSW). The contaminated SSW contained a mixture of metals (Cr, Cd, Cu, Pb, Ni and Zn), nutrients (ammonium, nitrate, and phosphate) and PAHs (pyrene (PYR), phenanthrene (PHE), acenaphthylene (ACY) and naphthalene (NAP)). First, batch studies were used to investigate the sorption capacities, kinetics, and the effects of different water quality parameters on sorbents performance. Then, a long-term vegetated column study was conducted to investigate the performance of three amendments (CCF, WTCR, and BFS) under intermittent runoff condition considering different runoff intensities and antecedent dry periods (ADP). The long-term effects of amendments on plant health and infiltration rate of all media were also investigated. Finally, HYDRUS-1D and a cost model were used to investigate longevity and cost-effectiveness of all BSM. Batch test results revealed that among all sorbents, BC and FeBC were only effective for removing PAHs; CFF had high sorption capacity for both metals and PAHs; BFS was very effective for metals; and WTCR was effective for some of metals and PAHs. Metal removal by BFS occurred primarily via precipitation was due to the BFS mineral structure and high/alkaline pH. The effectiveness of CCF for removing both metals and PAHs was due to its lignocellulose structure and diverse functional groups. CCF could remove metals through several mechanisms including cation exchange, complexation, and electrostatic attraction, and remove PAHs through hydrophobic interaction. Biochar in this study had a highly aromatic structure with less O-containing functional groups, and PAHs were sorbed through hydrophobic pi-pi interactions. The selectivity orders of sorbents for the removal of different metals and PAHs were Cr~Cu~Pb > Ni > Cd > Zn and PYR > PHE > ACY > NAP. This selectivity was mainly caused by differences in properties of metal ions (e.g., ionic radius, hydrogen energy, etc.) and PAHs (e.g., hydrophobicity). Phosphate was removed by BFS due to its Al, Fe and Ca contents, but the other sorbents were ineffective for nutrient removal. Metals sorption capacity of sorbents was greater at higher pH, lower salinity and lower DOC; however, PAHs sorption capacity of sorbents was generally not sensitive to water quality parameters. Column experiments showed that almost all amended and non-amended BSM were able to remove > 99% of influent metals over the 7-month experiment period (except Zn in WTCR media). Cu and Cr effluent concentrations in all media (except BFS media) increased to ~ 10% of influent concentrations during heavy rainfall which was probably due to decomposition of Cu/Cr-organic matter complexes. All bioretention columns removed > 99% of PHE and PYR (higher molecular weight PAHs) regardless of rain intensity and ADP, while the performance of different media for removing the lower molecular weight PAHs (NAP and ACY) varied with the rain intensity, and removal decreased when larger storms were experimentally simulated. For nutrients, among all media, BFS-amended media had high phosphate removal capacity (> 90%). Nitrate removal in all columns was notably affected by changes in stormwater intensity and ADP, likely due to difference in degree of saturation and the potential that anoxic conditions were created, which are favorable for denitrification. All media were ineffective in ammonium removal, and ammonium production occurred throughout experiment which might be due to the lack of nitrifiers in the media. Hydraulic properties of all media were appropriate over the entire experiment. BFS-amended media had the greatest negative effect on plant health, while CCF-amended media was supportive for plants. The transport model results showed that the predicted metal breakthrough times (according to EPA criteria) for different media were 6 years for non-amended media, 7 years for WTCR media, 25 years for CCF media, and 70 years for BFS media. Modeling PAHs, nutrients and some metals (Cr and Cu) under intermittent flow conditions are complicated and other processes and models need to be investigated as future study. Finally, cost analysis results showed that among all bioretention media, CCF- and BFS-amended media with the lowest capital and maintenance costs were the most cost-effective BSM. This research will improve our understanding of BSM amendments that will improve water quality while simultaneously support bioretention system hydrologic function as well as estimating costs of bioretention systems for a long-term application. / Civil Engineering

No description available.

É crescente a demanda por materiais que atendam as exigências para construção de barreiras selantes (liners) em obras para disposição de resíduos. A utilização de solos tropicais para esta finalidade só não é maior por falta de conhecimento sobre muitas de suas características técnicas, principalmente a migração de contaminantes. Tentativas de melhoria das qualidades de solos supostamente inadequados também são importantes. Esta tese apresenta estudos sobre a migração dos íons \'CD POT.2+\', \'K POT.+\', \'CL POT.1-\' e \'F POT.-\' em latossolos residuais das formações Botucatu e Serra Geral e três diferentes misturas destes solos, com ênfase nos processos de sorção e difusão molecular. O potencial de retenção dos íons é avaliado através da construção de 33 isotermas de sorção resultantes de ensaios de equilíbrio em lote. Seus parâmetros são obtidos da adequação dos modelos linear, Freundlich e Langmuir as isotermas. O potencial de transporte dos íons é avaliado através de ensaios de difusão em colunas estanques, onde curvas teóricas produzidas no programa POLLUTE são ajustadas aos dados de concentração para a estimativa dos parâmetros de difusão. Os resultados dos estudos de retenção mostram que o \'CL POT.-\' experimenta sorção sob certas condições, o \'K POT.+\' e \'F POT.-\' possuem taxas semelhantes de retenção, e que a sorção do \'CD POT.2+\' se mostrou altamente dependente da composição da solução contaminante. Os ensaios de difusão resultaram em vários valores para o coeficiente de difusão efetiva (D*), mostrando que o fluxo difusivo dos íons diminui para solos mais argilosos. / There is a growing demand for materials that can be used in lining systems for waste disposal facilities. The use of tropical soils for this purpose is restricted due to the lack of technical knowledge about this type of material. Attempts to improve the quality of supposed unsuitable soils play also an important role. This thesis presents studies concerning the migration of the ions \'CD POT.2+\', \'K POT.+\', \'CL POT.-\' and \'F POT.-\' in latosoils from the Botucatu and Serra Geral formations and three different mixtures of these soils, with emphasis on sorption and molecular diffusion. Batch equilibrium tests were conduced to examine the retention capacity of the soils, and the sorption parameters are estimated by fitting the linear, Freundlich and Langmuir models to the experimental isotherm plots. The potential for these soils to transport ions is evaluated by diffusion tests, where theoretical curves produced in the POLLUTE code are used to estimate the effective diffusion coefficients (D*). The results show that the \'CL POT.-\' is sorbed under specific conditions and, therefore, it can not always be used as a conservative ion (i.e. nonreactive ion), \'K POT.+\' and \'F POT.-\' are sorbed in similar amounts, and that the \'CD POT.2+\' sorption is highly dependent on the contaminant solution composition. Several D* values are reported, showing that the diffusion rates are decreased for soils with more clay.

Deponering är globalt sett det vanligaste sättet att hantera avfall, men i Sverige får sedan 2001 enbart avfall som inte kan återanvändas deponeras. Innan deponiförordningen trädde i kraft 2001 deponerades många olika typer av avfall. En deponi används idag som ett slutförvar för avfall och för att minimera infiltration av regnvatten och eventuell föroreningsspridning sluttäcks gamla deponier. Sluttäckningen består av flera skikt som tillsammans ska täta deponin och leda bort vatten. Att förvara avfall i en sluttäckt deponi är miljöfarlig verksamhet och det är därför av intresse att kontrollera omgivningarna under och efter sluttäckning för att säkerställa att eventuell föroreningsspridning minskar. På Hovgårdens avfallsanläggning i Uppsala kommun har en deponi som använts sedan 1971 sluttäckts under hösten 2018. I två provtagningsrör vid deponin, i vilka provtagning och analys skett regelbundet sedan 1991, har förhöjda halter av vissa ämnen kunnat uppmätas efter att arbetet med sluttäckningen påbörjades. Syftet med detta examensarbete var att få ökad förståelse för trender i ämneshalter samt att utreda hur sluttäckning påverkar grundvattennivåer och ämneskoncentrationer runt deponin. Uppmätta halter i provtagningsrören sammanställdes och trender analyserades med statistiska verktyg i mjukvaran R. Dessutom konstruerades en grundvattenmodell över avfallsanläggningen i MODFLOW och MT3DMS. Stationära flödessimuleringar och transportsimuleringar med klorid utfördes. Tolv av 33 analyserade ämnen och parametrar uppvisar statistiskt signifikanta ökningar i antingen ett av provtagningsrören, båda eller båda analyserade tillsammans. Dessa är alkalinitet, elektrisk konduktivitet, sulfat, klorid, kalcium, natrium, svavel, kalium, magnesium, strontium, barium, och nitratkväve. Sex av dem minskar statistiskt signifikant och dessa är pH-värdet, kadmium, zink, kvicksilver, bly och arsenik. Grundvattenmodellen visar att grundvattnet under etapp 1 flödar mot resten av anläggningen men att flöden ut från deponin finns i de sydvästra och sydöstra hörnen. Sluttäckningen leder till lägre nivåer och en förändrad grundvattendelare vilket kommer minska läckaget, främst i den sydvästra delen. Modellsimuleringar med olika grundvattenbildningsmängder och kloridkoncentrationer visade att ökningar av kloridhalter inte kan förklaras med minskad grundvattenbildning i kombination med förhöjda koncentrationer. Förklaringen bör därmed vara andra fysikaliska och eventuellt kemiska processer som skett samtidigt som sluttäckningen. De parametrar som påverkade simulerade ämneshalter mest var konduktansen i diken och dränering samt moränens hydrauliska konduktivitet. / Landfills are globally the most common waste treatment method but in Sweden the method is since 2001 used only for waste that cannot be reused in any way. Before 2001, almost any type of waste could be landfilled. Today a landfill is used as a final storage and old landfills are capped to minimize infiltration and contaminant transport. A capping consists of several layers which together seal and drain the landfill surface. Storing waste in a capped landfill is considered an environmentally hazardous activity, therefore it is of great interest to monitor the surrounding groundwater during and after capping to make sure that any contaminant concentrations decreases. At Hovgården waste treatment plant in Uppsala, Sweden, a landfill used since 1971 was capped during 2018. Elevated contaminant concentrations have been measured in two monitoring wells close to the landfill after the capping procedure started. The aim of this master thesis was to increase the understanding of trends in contaminant concentrations and to investigate how capping affects groundwater levels and concentrations. Concentration data were compiled and statistical tools in R were used to analyze trends. Additionally, a groundwater model of the area was created in MODFLOW and MT3DMS. The model was used to simulate different steady state scenarios with and without chloride transport. Twelve of 33 analyzed substances and parameters show a statistically significant increase. These are alkalinity, electrical conductance, sulphate, chloride, calcium, sodium, sulfur, potassium, magnesium, strontium, barium and nitrate. Six show a decrease, these are pH, cadmium, zinc, mercury, lead and arsenic. The groundwater model indicates that the groundwater flow in the landfill is directed towards the rest of the waste treatment plant except for two places where leakage occurs: the southwest and southeast corners of the landfill. The capping results in lower groundwater levels and an altered groundwater divide, which will reduce the contaminant leakage, particularly in the southwest part. Model simulations with varying recharge and chloride concentrations showed that the increase in chloride levels cannot be explained with only decreased infiltration combined with increased concentrations. Therefore, the explanation is assumed to be other physical processes and possibly chemical reactions due to or at the same time as the capping. The model parameters that effected the simulated concentrations to the greatest extent are the conductances in drains, and the hydraulic conductivity of the till soil.