<p>Over 750 million people, 80% of whom live in rural communities, lack access to improved water sources. Even where an improved water source is easily accessible, recontamination and/or inadequate infrastructure may make it unsafe for human consumption. A lack of safe water leads to elevated rates of waterborne diseases and can exacerbate cycles of poverty by forcing individuals to miss school and work and to travel greater distances to secure better-quality water. Households in rural and remote communities may thus choose to use point-of-use treatment as a means of gaining greater control over their water quality and the health of their families. The BioSand Filter (BSF) is one such technology: it is an intermittently-operated household-scale slow sand filter currently used in over 70 nations around the world.</p> <p>This thesis situates point-of-use water treatment, and specifically the BSF, within the context of the relationship between water and health and the continuum of technologies used for water treatment. From this foundation, it presents the methodology and results of a study carried out to inform best-practices around BSF use by: (a) examining the effects on BSF media and filtration performance of physical disturbances that may commonly occur in the field; and (b) assessing whether the biological community within BSFs promotes nitrification that could produce elevated nitrate/nitrite levels.</p> <p>Results demonstrated that disturbing the filters through moving and side impacts caused marked sand compaction and decreased flow rates for plastic (Hydraid) BSFs. Although these decreased flow rates may contribute to user frustration and disuse, they were not associated with reduced filtration performance. Nitrate and nitrite concentrations were well below WHO guidelines for all samples, but changes in nitrogen speciation suggested that nitrification was mediated by the biological community within the filters. Recommendations for practitioners and for future research are discussed in light of these findings.</p> / Master of Applied Science (MASc)

Os reatores UASB (upflow anaerobic sludge blanket reactors) foram um marco histórico no tratamento de efluentes ao propiciar alta retenção de sólidos e boa mistura entre biomassa e afluente. Apesar de os reatores com a concepção original dos UASB serem usados com sucesso em muitas estações de tratamento de esgoto, algumas questões relacionadas a sua operação, construção e manutenção ainda prevalecem. Sendo assim, novas configurações baseadas na concepção tradicional de reatores de manta de lodo podem simbolizar novas tentativas para sanar essas questões. Neste contexto, uma configuração que emprega manta de lodo, objetivando principalmente a eliminação dos separadores trifásicos e adoção mistura com jatos, é aqui proposta, almejando simplificar a distribuição/mistura do esgoto afluente. A pesquisa foi, assim, realizada primeiramente em escala de bancada para determinar do gradiente de velocidade médio necessário para suspensão de sólidos, resultando em valores favoráveis de até 20 s-1. Na segunda fase, uma instalação piloto de 2,69 m3, construída em acrílico, foi utilizada para o estudo das características do jato e dos bocais, e do regime de mistura proporcionado pelo mesmo. Com auxílio das informações obtidas na primeira e segunda fases, a terceira fase do experimento abrangeu a reforma de um reator UASB tradicional, em escala piloto de 20,8 m3, para a implantação desse novo sistema de tratamento: removeram-se os sistemas para coleta de gases e de distribuição de fundo e implantou-se alimentação intermitente por meio de jatos, além de unidade de decantador de alta taxa. Em essência, o novo sistema foi dividido em duas zonas distintas: uma para as reações e outra provida de decantação laminar para a remoção de sólidos suspensos. Na primeira zona, a entrada de esgoto sanitário deu-se por meio de bocal que proporcionou jato para mistura da manta de lodo através da carga manométrica fornecida por reservatório elevado. A velocidade de entrada no reator e o alcance do jato puderam ser determinados, constatando-se que o número de pontos de entrada no reator pode ser reduzido (em relação ao número de pontos recomendados tradicionalmente: 2 a 4 m2, por ponto). O gradiente de velocidade aplicado durante cada jato (com 30 segundos de duração) foi de 16,6 s-1. Para o reator da terceira fase, na fase estável da operação, obteve-se eficiência de remoção de 52,79%, 70,90 % e 47,00% para DQO, DBO e SST, respectivamente. Adicionalmente, avaliou-se o uso de filtro rápido de camada única de areia para o pós-tratamento do efluente do reator anaeróbio, cujas remoções de DQO, SST e Turbidez (para taxa de aplicação de 100 m3.m-2.dia-1) foram de 54,94%, 84,44% e 81,71% respectivamente. Concluiu-se, desta forma, a viabilidade da operação do reator de manta de lodo com alimentação intermitente e sem necessidade de instalação do sistema separador trifásico. / In spite of reactors with the original design of UASB are successfully used in many wastewater treatment plants, some issues regarding the operation, construction and maintenance of these reactors still prevail. Thus, new configurations based on the traditional conception of sludge blanket reactors may signify new tries to solve these issues. In this context, this research proposes a new configuration, using sludge blanket, mainly aiming at the elimination of the three-phase separators and adoption of a mixture through jets in order to simplify distribution / mixing of the influent. Therefore firstly a bench scale study was conducted to determine the required average velocity gradient for suspension of solids, resulting in favorable values up to 20 s-1. In the second phase, a 2.69 m3 pilot plant was built in acrylic to study the characteristics of the jet and the nozzles, and the resulting mixing state. After this stage, and with the contribution of information obtained in the earlier stages, a traditional pilotscale UASB reactor of 20.8 m3 was adapted for the implementation of this new treatment system: the systems for gas collection and distribution of background were removed, and a high-rate sedimentation unit and intermittently feed through jets were introduced. In essence, the new system has been divided into two distinct zones: one for reactions and other provided of laminar decantation to remove suspended solids. In the reaction zone the entry of sewage was given through jet for mixing the sludge blanket. The mixing energy was provided by jet stemmed on an elevated tank, where the sewer was accumulated. The jet range and entry velocity into the reactor could be determined, noting that the number of entry points in the reactor can be reduced (relative to the number of points traditionally recommended: 2 to 4 m2 per point). The velocity gradient applied during each jet (with a 30 seconds duration) was 16.6 s-1. The pilot-scale reactor (third phase), in stable-phase operation, got a removal efficiency of 52.79%, 70.90% and 47.00% for COD, BOD and TSS, respectively. Additionally, were evaluated the use of unique coating rapid sand filter to the post-treatment of the effluent in the anaerobic reactor. The removals obtained for COD, TSS and Turbidity (for application rate of 100 m3.m-2.dia-1) were 54.94%, 84.44% and 81.71% respectively. It was concluded, therefore, the viability of the sludge blanket reactor operation with intermittent feed and without threephase separator system installation.

The fate of antimicrobials entering the aquatic environment is an increasing concern for researchers and regulators, and recent research has focused on antimicrobial contamination from point sources, such as wastewater treatment facility outfalls. The terraccumulation of antimicrobials and mobility in diffuse pollution pathways should not be overlooked as a contributor to the spread of bacterial resistance and the resulting threat to human drug therapy. This review critically examines recent global trends of bacterial resistance, antimicrobial contaminant pathways from agriculture and water treatment processes, and the need to incorporate diffuse pathways into risk assessment and treatment system design. Slow sand filters are used in rural regions where source water may be subjected to antimicrobial contaminant loads from waste discharges and diffuse pollution. A simple model was derived to describe removal efficiencies of antimicrobials in slow sand filtration and calculate antimicrobial concentrations sorbed to the schmutzdecke at the end of a filtration cycle. Input parameters include water quality variables easily quantified by water system personnel and published adsorption, partitioning, and photolysis coefficients. Simulation results for three classes of antimicrobials suggested greater than 4-log removal from 1 ��g/L influent concentrations in the top 30 cm of the sand column, with schmutzdecke concentrations comparable to land-applied biosolids. Sorbed concentrations of the antimicrobial tylosin fed to a pilot filter were within one order of magnitude of the predicted concentration. To investigate the behavior of antimicrobial contaminants during multi-stage filtration, five compounds from four classes of antimicrobials were applied to a mature slow sand filter and roughing filter fed raw water from the Santiam River in Oregon during a 14-day challenge study. Antimicrobial removal efficiency of the filters was calculated from 0.2 mg/L influent concentrations using HPLC MS/MS. and sorption coefficients (K[subscript d], K[subscript oc], K[subscript om]) were calculated for schmutzdecke collected from a mature filter column. Sulfonamides had low sorption coefficients and were largely unaffected by multi-stage filtration. Lincomycin, trimethoprim, and tylosin exhibited higher sorption coefficients and limited mobility within the slow sand filter column. The lack of a significant increase in overall antimicrobial removal efficiency indicated biodegradation is less significant than sorption in multi-stage filtration. / Graduation date: 2004

La réutilisation des eaux usées traitées (REUT) constitue une ressource alternative pérenne et à fort potentiel notamment pour les régions soumises à un stress hydrique. L’objectif général de cette thèse est de définir les conditions nécessaires pour garantir la fiabilité d’une filière de traitement tertiaire pour la réutilisation. La première partie s’intéresse aux limites des méthodes de dénombrement des microorganismes indicateurs couramment employées, notamment en lien avec la contamination particulaire des effluents. Les résultats indiquent qu’il existe un risque de sous-estimation par ces méthodes pour de fortes charges en matières en suspension.La désinfection par rayonnement ultraviolet (UV) est souvent employée pour garantir la qualité sanitaire de l’eau distribuée. La deuxième partie de cette thèse vise à comprendre les mécanismes pouvant affecter l’efficacité des UV. Une corrélation linéaire a pu être mise en évidence entre la contamination particulaire des effluents à traiter et la baisse d’efficacité de la désinfection UV, caractérisée d’une part par la diminution de la constante d’inactivation des microorganismes exposés aux UV et d’autre part par le risque d’apparition d’un effet de traîne (fraction de microorganismes insensibles aux UV).La mise en place d’un prétraitement par filtration s’avère donc nécessaire en amont de la désinfection UV. La troisième partie de cette thèse a permis de définir les paramètres opératoires les plus adaptés à l’effluent. Enfin, le contrôle de la qualité sur l’ensemble de la filière est envisagé, avec notamment la démonstration de faisabilité d’un système de surveillance en continu basé sur la spectrométrie UV/Visible. / Wastewater reclamation is an ongoing and promising alternative resource in a context of water stress. In particular, this is a major issue in the Mediterranean region, and its effects tend to be intensified by global warming. The main objective of this PhD thesis is to define the conditions for ensuring the reliability of a tertiary treatment chain for wastewater reclamation. The first part deals with the limits of the methods used in routine for the enumeration of indicator microorganisms, in relation with particulate contamination. The results indicate that there is a risk of underestimation by these methods for high loads of suspended matter.Ultraviolet (UV) disinfection has been used for years to ensure the biological safety of reclaimed water. The second part of this work aims to understand the mechanisms which may affect the efficiency of UV disinfection. A linear relationship has been observed between the particulate contamination of the effluents to be treated and the disinfection efficiency loss, featured on one hand by the decrease of the inactivation constant of the microorganisms and on the other hand by the risk of tailing (UV-resistant fraction among the microorganisms).The implementation of a pre-filtration is thus necessary before UV disinfection. The third part of this work enabled to identify the filtration parameters suited for the effluents to be treated. Finally, quality control on the whole chain is considered, in particular with the demonstration of feasibility of a continuous control system based on UV/Visible spectrometry.

Made available in DSpace on 2014-07-29T15:01:52Z (GMT). No. of bitstreams: 1 dissertacao daniela camplesi.pdf: 1230668 bytes, checksum: 56ed1f54e5e43d735ad2b69bff069adc (MD5) Previous issue date: 2009-12-18 / The present work has evaluated the efficiency of an MSF system for treating supplying water on a pilot scale. A MSF pilot plant was located in the Water Treatment Station (WTS) area in Goianápolis- GO and fed by Sozinha stream. The plant was comprised of a dynamic prefilter (DPF) and a vertical upflowing pre-filter (VUF) in layers, both of them with different granular compositions; a slow sand filter (SSF); and a slow sand filter with activated carbon (SSFAC), which was called SEQ. 1. The second sequence of the trial, SEQ. 2, was comprised of a dynamic pre-filter (DPF) and a slow sand filter (SSF-2). The filtration rates in use were 24 and 48 m3/m2 a day for DPF, 12 e 24 m3/m2. day for APF; 3 e 6 m3/m2. day for SSF and SSFAC. The efficiency was evaluated by analyzing turbidity, apparent color, total suspended solids (TSS), as well as total thermo tolerant coliforms. The following items were evaluated: the filtration rates ranging effect onto the MSF unit trial system efficiencies; the MSF system efficiency comparison to the WTS complete cycling treatment; and the correlations between turbidity, color, and coliforms removals and the TSS removals. The results obtained from the trials have shown that DPF and VUF are important units for microorganisms and solid particles retaining, for it prepares the effluent in order to submit it into slow filtration. They have also shown that they make it possible for the roughing filtration to last longer. Generally put, it presents that the slow filters are significantly and above 90% efficient in removing TSS, color and turbidity, and 99% efficient in removing total coliforms and thermotolerant coliforms in all roughing filtration. After comparing the quality of both the water produced by MSF and the one by the complete cycling WTS, it was noticed that MSF produces water with quality similar to the complete cycling WTS. The range for the filtration rates has had significant influence only in the removal efficiencies of color and turbidity. There isn t correlation among the removals of the parameters color, turbidity, TSS and coliforms but for the correlation among apparent color and true color. The experiment results suggest that MSF technology, when suitably operated, it is a viable system for the treatment of supplying water and produced water with low levels of color, turbidity, TSS and coliforms is that 40% of the samples, provided drinking water under conditions compatible to those established by Decree 518/2004 of the Ministry of Health (BRAZIL, 2004) for human consumption / O presente trabalho avaliou a eficiência de um sistema de FiME no tratamento de águas de abastecimento em escala piloto. A instalação piloto FiME, localizada na área da Estação de Tratamento de Água (ETA) de Goianápolis, GO e alimentada pelo Ribeirão Sozinha, era composta de um pré-filtro dinâmico (PFD), um pré-filtro com escoamento vertical ascendente (PFA) em camadas, ambos com composições granulométricas diferenciadas, um filtro lento de areia (FLA) e um filtro lento de areia com carvão ativado (FLAC) e foi denominada SEQ 1. A SEQ 2 do experimento era constituída de um pré-filtro dinâmico (PFD) e um filtro lento de areia (FLA-2). As taxas de filtração utilizadas foram 24 e 48 m3/m2. dia para PFD, 12 e 24 m3/m2. dia para PFA, 3 e 6 m3/m2. dia para FLA e FLAC. A eficiência foi avaliada por meio das análises de turbidez, cor aparente, sólidos suspensos totais (SST) e coliformes totais e termotolerantes. Foi avaliado também o efeito da variação das taxas de filtração nas eficiências das unidades do sistema FiME, a comparação da eficiência do sistema FiME com o tratamento de ciclo completo da ETA e as correlações entre as remoções de turbidez, cor, coliformes e a remoção de SST. Os resultados obtidos nos experimentos demonstraram que o PFD e PFA são unidades importantes para a retenção de partículas sólidas e microorganismos, preparando o afluente para ser submetido à filtração lenta e possibilitam maior duração das carreiras de filtração. De maneira geral, os filtros lentos apresentaram eficiências significativas e superiores a 90% para remoção de cor, turbidez, SST e 99,9% de eficiência para remoção de coliformes totais e termotolerantes em praticamente todas as carreiras de filtração. Quando comparada a qualidade da água produzida pelo sistema FiME com a ETA de ciclo completo, verificou-se que a FiME produz água com qualidade similar à ETA de ciclo completo. As variações das taxas de filtração influenciaram significativamente nas eficiências de remoção de cor e turbidez. Não há correlação entre as remoções dos parâmetros cor, turbidez, SST e coliformes mas há correlação para cor aparente e cor verdadeira. Os resultados obtidos nos experimentos sugerem que a tecnologia de FiME, quando operada adequadamente, é um sistema viável para o tratamento de águas de abastecimento e produziu água com baixos teores de cor, turbidez, SST e coliformes sendo que em 40% das amostras analisadas, proveu água potável em condições compatíveis às estabelecidas pela Portaria 518/2004 do Ministério da Saúde (BRASIL, 2004) para consumo humano

Os reatores UASB (upflow anaerobic sludge blanket reactors) foram um marco histórico no tratamento de efluentes ao propiciar alta retenção de sólidos e boa mistura entre biomassa e afluente. Apesar de os reatores com a concepção original dos UASB serem usados com sucesso em muitas estações de tratamento de esgoto, algumas questões relacionadas a sua operação, construção e manutenção ainda prevalecem. Sendo assim, novas configurações baseadas na concepção tradicional de reatores de manta de lodo podem simbolizar novas tentativas para sanar essas questões. Neste contexto, uma configuração que emprega manta de lodo, objetivando principalmente a eliminação dos separadores trifásicos e adoção mistura com jatos, é aqui proposta, almejando simplificar a distribuição/mistura do esgoto afluente. A pesquisa foi, assim, realizada primeiramente em escala de bancada para determinar do gradiente de velocidade médio necessário para suspensão de sólidos, resultando em valores favoráveis de até 20 s-1. Na segunda fase, uma instalação piloto de 2,69 m3, construída em acrílico, foi utilizada para o estudo das características do jato e dos bocais, e do regime de mistura proporcionado pelo mesmo. Com auxílio das informações obtidas na primeira e segunda fases, a terceira fase do experimento abrangeu a reforma de um reator UASB tradicional, em escala piloto de 20,8 m3, para a implantação desse novo sistema de tratamento: removeram-se os sistemas para coleta de gases e de distribuição de fundo e implantou-se alimentação intermitente por meio de jatos, além de unidade de decantador de alta taxa. Em essência, o novo sistema foi dividido em duas zonas distintas: uma para as reações e outra provida de decantação laminar para a remoção de sólidos suspensos. Na primeira zona, a entrada de esgoto sanitário deu-se por meio de bocal que proporcionou jato para mistura da manta de lodo através da carga manométrica fornecida por reservatório elevado. A velocidade de entrada no reator e o alcance do jato puderam ser determinados, constatando-se que o número de pontos de entrada no reator pode ser reduzido (em relação ao número de pontos recomendados tradicionalmente: 2 a 4 m2, por ponto). O gradiente de velocidade aplicado durante cada jato (com 30 segundos de duração) foi de 16,6 s-1. Para o reator da terceira fase, na fase estável da operação, obteve-se eficiência de remoção de 52,79%, 70,90 % e 47,00% para DQO, DBO e SST, respectivamente. Adicionalmente, avaliou-se o uso de filtro rápido de camada única de areia para o pós-tratamento do efluente do reator anaeróbio, cujas remoções de DQO, SST e Turbidez (para taxa de aplicação de 100 m3.m-2.dia-1) foram de 54,94%, 84,44% e 81,71% respectivamente. Concluiu-se, desta forma, a viabilidade da operação do reator de manta de lodo com alimentação intermitente e sem necessidade de instalação do sistema separador trifásico. / In spite of reactors with the original design of UASB are successfully used in many wastewater treatment plants, some issues regarding the operation, construction and maintenance of these reactors still prevail. Thus, new configurations based on the traditional conception of sludge blanket reactors may signify new tries to solve these issues. In this context, this research proposes a new configuration, using sludge blanket, mainly aiming at the elimination of the three-phase separators and adoption of a mixture through jets in order to simplify distribution / mixing of the influent. Therefore firstly a bench scale study was conducted to determine the required average velocity gradient for suspension of solids, resulting in favorable values up to 20 s-1. In the second phase, a 2.69 m3 pilot plant was built in acrylic to study the characteristics of the jet and the nozzles, and the resulting mixing state. After this stage, and with the contribution of information obtained in the earlier stages, a traditional pilotscale UASB reactor of 20.8 m3 was adapted for the implementation of this new treatment system: the systems for gas collection and distribution of background were removed, and a high-rate sedimentation unit and intermittently feed through jets were introduced. In essence, the new system has been divided into two distinct zones: one for reactions and other provided of laminar decantation to remove suspended solids. In the reaction zone the entry of sewage was given through jet for mixing the sludge blanket. The mixing energy was provided by jet stemmed on an elevated tank, where the sewer was accumulated. The jet range and entry velocity into the reactor could be determined, noting that the number of entry points in the reactor can be reduced (relative to the number of points traditionally recommended: 2 to 4 m2 per point). The velocity gradient applied during each jet (with a 30 seconds duration) was 16.6 s-1. The pilot-scale reactor (third phase), in stable-phase operation, got a removal efficiency of 52.79%, 70.90% and 47.00% for COD, BOD and TSS, respectively. Additionally, were evaluated the use of unique coating rapid sand filter to the post-treatment of the effluent in the anaerobic reactor. The removals obtained for COD, TSS and Turbidity (for application rate of 100 m3.m-2.dia-1) were 54.94%, 84.44% and 81.71% respectively. It was concluded, therefore, the viability of the sludge blanket reactor operation with intermittent feed and without threephase separator system installation.

Integrated Algae Pond Systems (IAPS) are a derivation of the Oswald designed Algal Integrated Wastewater Pond Systems (AIWPS®) and combine the use of anaerobic and aerobic bioprocesses to effect wastewater treatment. IAPS technology was introduced to South Africa in 1996 and a pilot plant designed and commissioned at the Belmont Valley WWTW in Grahamstown. The system has been in continual use since implementation and affords a secondarily treated water for reclamation according to its design specifications which most closely resemble those of the AIWPS® Advanced Secondary Process developed by Oswald. As a consequence, and as might be expected, while the technology performed well and delivered a final effluent superior to most pond systems deployed in South Africa it was unable to meet The Department of Water Affairs General Standard for nutrient removal and effluent discharge. The work described in this thesis involved the design, construction, and evaluation of several tertiary treatment units (TTU') for incorporation into the IAPS process design. Included were; Maturation Ponds (MP), Slow Sand Filter (SSF) and Rock Filters (RF). Three MP's were constructed in series with a 12 day retention time and operated in parallel with a two-layered SSF and a three-stage RF. Water quality of the effluent emerging from each of these TTU's was monitored over a 10 month period. Significant decreases in the chemical oxygen demand (COD), ammonium-N, phosphate-P, nitrate-N, faecal coliforms (FC) and total coliforms (TC) were achieved by these TTU's. On average, throughout the testing period, water quality was within the statutory limit for discharge to a water course that is not a listed water course, with the exception of the total suspended solids (TSS). The RF was determined as the most suitable TTU for commercial use due to production of a better quality water, smaller footprint, lower construction costs and less maintenance required. From the results of this investigation it is concluded that commercial deployment of IAPS for the treatment of municipal sewage requires the inclusion of a suitable TTU. Furthermore, and based on the findings presented, RF appears most appropriate to ensure that quality of the final effluent meets the standard for discharge.

The quality of raw water is deteriorating with the continuous increase in environmental pollution. Raw water is being modified to drinking water by technological processes, and it is therefore necessary to put increased demands on the efficiency of these technological processes and their possible innovation. Due to the fact that raw water is contaminated with different types of pollutants, it is necessary to continuously control the drinking water supplied to the public distribution network in order to ensure its quality. Drinking water treatment is still unable to treat the raw water perfectly, its pollution is only reduced to acceptable standards. For this reason, it is indispensable that the quality of drinking water is being checked regularly and at the same time the efficiency of individual technological processes of drinking water treatment is assessed. This includes screening analysis or eventually ecotoxicological tests. The thesis focuses on the efficiency of technological processes of drinking water treatment. Within the experimental part, samples of raw water and samples of water after each separation stage have been collected at the drinking water treatment plant in the Czech Republic. These samples have been subjected to ecotoxicological tests and screening analysis. Based on the ecotoxicological tests carried out on Thamnocephalus platyurus, Lemna minor and Vibrio fischeri, we can assume the emergence of harmful chlorinated by-products, resulting to nearly 100% mortality in T. platyurus. The results of the screening analysis carried out indicate, after the extraction of specimens by the SPE method using HPLC/MS, that the most effective method for the removal of hormonal substances is ozonization.

Arbetet studerade skillnaderna mellan en användning av kalciumhydroxid samtnatriumhydroxid som pH-reglerande kemikalie i en kemisk vattenreningsanläggning.Samt dess påverkan på filtreringssteg som sandfilter, aktivkol filtrering samt jonbytarfiltrering. Det behandlade hur reningsgraden påverkas sett till metallreduktion av;krom, nickel, koppar och zink. Hur slammängderna är i förhållande tillvarandramellan de olika pH-reglernade kemikalierna och slutligen hur filtreringsstegenpåverkas beroende på vilken pH-reglerande kemikalie som doserats. Resultatet förarbetet har visat på att reningsgraden minskar vid användning av natriumhydroxidsom pH-reglerande kemikalie vilket besvarar en del av syftet samt frågeställningenmed arbetet. Ytterligare har resultatet påvisat att de efterkommande filtreringsstegensom i en eventuell framtid kan implementeras leder till en reducering avmetallhalterna i vattnet, vanligen gick reduceringen inte att statistiskt säkerställa mentendenser på en reducering påvisades. Även de erhållna slammängdernareducerades vid användning av natriumhydroxid som pH-reglerande kemikalie vilketvar ett förväntat resultat sett till hypotes och litteratur. Ytterligare minskadeturbiditeten för klarfasproverna vid en natriumhydroxiddosering i förhållande till enkalciumhydroxiddosering. Arbetets resultat har således påvisat den goda möjlighetenatt ersätta den manuella doseringen av solid kalciumhydroxid som pH-reglerandekemikalie emot en automatisk dosering av natriumhydroxid erhållen i vätskeform. / This work studied the differences between the use of calcium hydroxide and sodiumhydroxide as a pH-regulating chemical in a chemical water treatment plant. As wellas its impact on filtration steps such as sand filter, activated carbon filtration and ionexchange filtration. It dealt with how the degree of purification is affected in terms ofmetal reduction of; chromium, nickel, copper and zinc. How the sludge amounts arein relation to each other between the different pH-regulated chemicals and finallyhow the filtration steps are affected depending on which pH-regulating chemical hasbeen dosed. The results for the work have shown that the degree of purificationdecreases when using sodium hydroxide as a pH-regulating chemical, whichanswers part of the purpose and the question of the work. Furthermore, the resultshave shown that the subsequent filtration steps that can be implemented in thepossible future lead to a reduction of the metal contents in the water, usually thereduction could not be statistically confirmed but tendencies of a reduction wereshown. The amounts of sludge obtained were also reduced by using sodiumhydroxide as a pH-regulating chemical, which was an expected result in terms ofhypothesis and literature. Furthermore, the turbidity of the clear phase samplesdecreased at a sodium hydroxide dosage relative to a calcium hydroxide dosage.The results of the work have thus demonstrated the good possibility of replacing themanual dosing of solid calcium hydroxide as a pH-regulating chemical with anautomatic dosing of sodium hydroxide obtained in liquid form.

Dans les dernières décennies, la plupart des pays du monde ont connu une pénurie d'eau et l’augmentation du taux de consommation. Aujourd'hui, tous les pays dans le monde essayent de trouver des alternatives pour remédier à cette pénurie. Une solution consiste en la réutilisation des eaux grises (GW) pour l'irrigation après traitement. Les GW correspondent aux eaux usées générée dans une maison à l'exception de l'eau des toilettes. Les risques associés à la réutilisation de ces eaux est la présence de microorganismes pathogènes qui peuvent infecter les humains, les animaux et les plantes. Dans cette thèse centrée sur l'étude de la survie des représentants d'agents pathogènes, comme E. coli, P. aeruginosa, et le bactériophage MS2 qui sont trouvés dans les eaux grises. Il a été étudié l’effet de quelques facteurs physico-chimiques tels que; température (6 ± 2,23 ± 2 et 42 ± 2 ° C), la salinité (1,75 and 3.5% de NaCl), de l'oxygène (aérobie et anaérobie), des éléments nutritifs (milieu riche et de milieux pauvres), la lumière avec la photocatalyse (lampes UV et visible) et filtre à sable lent (sable du désert égyptien et le sable piscine). Une combinaison de la température, la lumière du soleil et de haute photocatlysis sont principalement responsables de la baisse rapide des bactéries et du coliphage MS2. Le filtre à sable lent a une influence nettement moindre sur la survie des bactéries dans les eaux grises, mais il est efficace pour diminuer la turbidité et de la DCO. / In recent decades, most countries of the world have experienced a shortage of water and increase its rate of consumption. Today, every country in the world are interested in this problem by trying to find alternatives to address this shortage. One solution is reuse greywater (GW) for irrigation after treatment. GW is all water generated from Household except toilet water. The risks associated with the reuse of these waters are the presence of pathogens that can infect humans, animals and plants. In this thesis focused on studying treatment by slow sand filtration and the survival of representatives of pathogens, such as E. Coli, P. aeruginosa , E. Faecalis and Bacteriophage MS2 which could be found in the greywater. The study factors was a physico-chemicals factors such as; temperature (6±2,23±2,42±2°c), salinity (1.75 and 3.5% Nacl), oxygen (aerobic and anaerobic condition), nutrient ( rich media , 50%: 50% salt and poor media ), light with photocatalysis ( UV and Visible lights) and slow sand filter (Egyptian desert sand and swimming pool sand). A combination of high temperature, sunlight and photocatlysis are mainly responsible for the rapid decline of bacteria and MS2 coliphage. Slow sand filter have clearly less influence on the survival of bacteria in the greywater, but it effective to decline turbidity and COD for short times.