Övergödning är ett utbrett miljöproblem i hav och sjöar, som yttrar sig i toxiska algblomningar och en minskad biodiversitet. Eftersom kväve är en betydande källa till övergödning, har flera avloppsreningsverk (ARV) krav på kväveavskiljning innan utsläpp i recipient. Tierp ARV omfattas [TA1] för närvarande inte av sådana utsläppskrav på kväve, men förväntas bli det i och med kommande lagstiftning. En utbyggnad av det biologiska reningssteget, som idag endast medför viss kväveavskiljning, kan därför bli nödvändigt för att åstadkomma fullständig kväverening.  Syftet med examensarbetet var att föreslå reningstekniker som kan åstadkomma tillräcklig kväveavskiljning vid Tierp ARV och bedöma vilken av dessa som är mest fördelaktig för implementering. Vidare utvärderades nuvarande reduktion av kväve och organiskt material samt rådande nitrifikation i det biologiska reningssteget. Massbalanser upprättades utifrån provtagning på dessa parametrar. Lämpliga kvävereningstekniker föreslogs med hänsyn till lokala krav och förutsättningar. Dessa tekniker jämfördes därefter i en multikriterieanalys med avseende på platsåtgång, växthusgasutsläpp, drift- och underhållskostnader, kapitalkostnader och arbetsinsats.  Massbalanserna uppvisade en reduktion på 31 % för totalkväve, 10 % för ammoniumkväve, 63 % för nitratkväve, 7 % för nitritkväve, 62 % för COD och 67 % för BOD7. Nuvarande nitrifikation bedömdes vara relativt låg, vilket troligtvis är resultatet av den låga temperaturen på avloppsvattnet, eventuell otillräcklig syretillförsel samt ogynnsamt pH. De reningstekniker som föreslås kunna minska kväveutsläppen från Tierp ARV är aktivslamprocess, membranbioreaktor (MBR) och hybridprocess med biofilmsbärare och aktivslam (IFAS). Utifrån en samlad bedömning av kriterierna i multikriterieanalysen bedömdes IFAS som mest fördelaktig för etablering och MBR som minst gynnsamt. / Eutrophication is a major environmental problem in oceans and lakes, which manifests itself intoxic algal blooms and reduced biodiversity. As nitrogen is a significant contributor toeutrophication, numerous wastewater treatment plants (WTPs) have requirements for nitrogenremoval before discharge into the recipient. Tierp WTP is not currently subject to suchregulation, but is expected to be so with forthcoming legislation. Consequently, an expansion ofthe biological treatment, which presently facilitates only partial nitrogen removal, may becomepertinent to achieve complete nitrogen removal. The objective of this thesis was to propose treatment methods capable of achieving adequatenitrogen removal at Tierp WTP and evaluate the most suitable option for implementation.Furthermore, the current nitrogen and organic material reduction, as well as present nitrificationin the biological treatment, were assessed. Mass balances were established based on sampling ofthese parameters. Suitable nitrogen purification techniques were proposed, considering localrequirements and conditions. These techniques were then compared through a multi-criteriaanalysis, taking into account space occupancy, greenhouse gas emissions, operation andmaintenance costs, capital costs and workload. The mass balances revealed reductions of 31% for total nitrogen, 10% for ammonium nitrogen,63% for nitrate nitrogen, 7% for nitrite nitrogen, 62% for COD and 67% for BOD7. The currentnitrification was assessed as relatively low, likely attributable to the low temperature of thewastewater, possibly insufficient oxygen supply and unfavourable pH. The treatment methodsproposed in the thesis to achieve sufficient nitrogen removal at Tierp WTP are the activatedsludge process, membrane bioreactor (MBR), and hybrid process with biofilm carriers andactivated sludge (IFAS). According to the multicriteria analysis, IFAS was deemed the mostadvantageous option for implementation, while MBR was evaluated as the least favourable.

I takt med att Uppsala växer behöver kapaciteten för avloppsvattenrening på Kungsängsverket byggas ut. För att möta en framtida ökad belastning bedömer Uppsala Vatten & Avfall AB att en kolkälla kommer behöva tillsättas i den biologiska kvävereningen för att effektivisera den heterotrofa denitrifikationen på Kungsängsverket, som idag sker utan tillsats av kolkälla. Potentialen till förbättrad denitrifikation med olika kolkällor utvärderades genom satsvisa laboratorieförsök och litteraturstudier. Syftet var att bättre förstå de studerade kolkällornas funktion och prestanda i denitrifikation för att ge underlag inför en framtida fullskalig implementering av kolkälla. Det övergripande målet var att identifiera vilken eller vilka kolkällor som är mest fördelaktiga med avseende på reningseffektivitet, processpåverkan, doseringsbehov, ekonomi och miljöpåverkan. Triplikata försök genomfördes som denitrifikationstester med aktivt slam vid en genomsnittlig slamtemperatur på 14 ℃ och pH 7-8, där fem externa kolkällor (etanol, Brenntaplus VP1 och tre industriella restprodukter) samt försedimenterat avloppsvatten testades. I litteraturstudien inkluderades även metanol. Från försöksdata bestämdes specifika denitrifikationshastigheter, COD/N-kvoter och utbyteskoefficienter. Även bieffekter såsom nitritackumulering och fosforsläpp studerades. Därefter uppskattades doseringsbehov och kostnader baserat på erhållna resultat och antaganden om framtida produktionsmål för nitratkväve. En likartad prestanda erhölls med en av restprodukterna (RTP-vätska) och etanol som uppnådde högst denitrifikationshastigheter och reduktionsgrader (98 % respektive 97 %). Doseringsbehovet uppskattades vara 4 gånger högre med RTP-vätska jämfört med etanol. Med de två andra restprodukterna (dextrandrank och sackaroslösning) uppnåddes lägst denitrifikationseffektivitet och reduktionsgraderna uppgick till 79 % respektive 47 %. Vid test av sackaroslösning observerades dessutom ofullständig denitrifikation samt höga fosforsläpp. Dextrandranken uppträdde på liknande sätt. I egenskap av restprodukt är RTP-vätskan intressant för fortsatt utvärdering. Fullskalig implementering av RTP-vätska förutsätter att doseringsbehoven kan tillgodoses samt att lämplig distribuering och lagerhållning kan ordnas på Kungsängsverket. / The city of Uppsala is expanding and consequently enhanced capacity at the wastewater treatment plant of Kungsängen will be required in the future. As for the biological nitrogen removal process, Uppsala Vatten & Avfall AB expects an additional carbon source to be necessary in the future denitrification process. Currently, the nitrogen removal is employed without the addition of a carbon source. The potential of enhancing denitrification with different carbon sources was evaluated by conducting lab-scale batch tests and compiling literature data. The objective of this work was to better understand the performance of the chosen carbon sources as electron donors in heterotrophic denitrification and thereby provide groundwork for a future full-scale implementation of a carbon source. Based on information drawn from batch tests and literature, the carbon sources were evaluated with respect to removal efficiency, process compliance, quantitative dosing requirements, costs, and environmental sustainability. Lab-scale trials were conducted as denitrification tests (triplicate) at a mean sludge temperature of 14 ℃ and pH 7-8 with five external carbon sources (ethanol, Brenntaplus VP1, and three industrial waste products) and pretreated wastewater. In the literature review, methanol was included as well. Results obtained from the batch tests were used to determine kinetic parameters, mainly specific denitrification rates, COD/N ratios, and anoxic yield coefficients. Moreover, unwanted side effects due to addition of carbon sources were examined. Dosing requirements and costs were assessed based on previously determined kinetic parameters and supposed future production guidelines for effluent quality with respect to nitrate concentration. Similar performance was observed with one of the waste products (RTP liquid) and ethanol which achieved the highest denitrification rates and degree of removal (98 and 97 %, respectively). The estimated dosing requirement was 4 times higher with the RTP liquid compared to ethanol. The other two waste products, solutions of fructose (dextran) and sucrose, reached the lowest denitrification efficiency and removal degrees were 79 and 47 %, respectively. During tests with sucrose solution, incomplete denitrification and release of phosphorous were observed. The fructose solution showed somewhat similar behavior but to a lesser degree. Being a waste product, the RTP liquid is interesting for future evaluation. Full-scale implementation needs further considerations regarding dosing requirements, distribution, and storage conditions at the site of Kungsängsverket.

Made available in DSpace on 2014-12-17T15:03:34Z (GMT). No. of bitstreams: 1 DanilloLMF_DISSERT.pdf: 2643693 bytes, checksum: e8aa0f4d4535d4002a68928f7529ab75 (MD5) Previous issue date: 2014-03-07 / In the state of Rio Grande do Norte (RN), Brazil, there are about 80 sewage treatment systems being the predominant technology waste stabilization ponds. The Baldo s WWTP , due to its location and low availability of area, was designed as a hybrid conventional system (UASB reactor followed by activated sludge with biodiscs) at a tertiary level, being the most advanced WWTP in the State and also with the larger treatment capacity (1620 m3/h) .The paper presents the results of its performance based on samples collections from May to December 2012. Composite samples of the effluent of the grit chamber, UASB reactors, anoxic chambers, aeration tanks and treated effluent were collected weekly, every 4 hours for 24 hours. The results showed that the WWTP effluent presented adequate ranges of temperatures, pH and DO, however removal efficiencies of BOD and TSS were below the predicted by design. The UASB reactors also showed removals of BOD and TSS less than expected, due to the accumulation of sludge in the reactors, which eventually, was washed out in the effluent. The nitrification process was not satisfactory mainly due to problems in the oxygen distribution in the aeration tanks. The removal of ammonia and TKN were high, probably by the assimilation process / No Rio Grande do Norte (RN), Brasil existe cerca de 80 sistemas de tratamento de esgotos sendo a tecnologia das lagoas de estabiliza??o a predominantemente utilizada. A ETE do Baldo, devido a sua localiza??o e disponibilidade de ?rea foi concebida como um sistema convencional h?brido (UASB lodos ativados com biodiscos) em n?vel terci?rio, sendo a ETE mais avan?ada do Estado e com maior capacidade de tratamento (1620 m 3 /h). O trabalho apresenta os resultados do seu monitoramento, atrav?s de coletas realizadas semanalmente no per?odo de junho a dezembro de 2012, com base em amostras compostas coletadas a cada 4 horas, durante 24 horas, do efluente da caixa de areia, reatores UASB, c?maras an?xicas, tanques de aera??o e efluente tratado. Os resultados mostraram que a ETE apresentou efluentes com temperaturas, pH e OD adequados, entretanto efici?ncias abaixo do projetado para os par?metros DBO e SST. Os reatores UASB tamb?m apresentaram remo??es de DBO e SST abaixo do esperado, devido ao ac?mulo de lodo nos reatores, uma vez que, este era expelido no efluente. O processo de nitrifica??o n?o foi satisfat?rio, pelas baixas concentra??es de nitrato encontradas nos efluentes dos tanques de aera??o, provavelmente por problemas no sistema de aera??o. As remo??es de am?nia e NTK foram altas, provavelmente pelo processo de assimila??o

Thesis (PhD (Chemical Engineering))--Cape Peninsula University of Technology, 2019 / Simultaneous nitrification and aerobic denitrification (SNaD) is a preferred method for single stage total nitrogen (TN) removal, which was recently proposed to improve wastewater treatment plant design. However, SNaD processes are prone to inhibition by toxicant loading with free cyanide (CN-) possessing the highest inhibitory effect on such processes, rendering these processes ineffective. Despite the best efforts of regulators to limit toxicant disposal into municipal wastewater sewage systems (MWSSs), free cyanide (CN-) still enters MWSSs through various pathways; hence, it has been suggested that CN- resistant or tolerant microorganisms be utilized for processes such as SNaD. To mitigate toxicant loading, organisms in SNaD have been observed to adopt a multiphase growth strategy to sequentially degrade CN- during primary growth and subsequently degrade TN during the secondary growth phase. However, CN- degrading microorganisms are not widely used for SNaD in MWSSs due to the inadequate application of suitable microorganisms (Chromobacterium violaceum, Pseudomonas aeruginosa, Thiobacillus denitrificans, Rhodospirillum palustris, Klebsiella pneumoniae, and Alcaligenes faecalis) commonly used in single-stage SNaD. The use of CN- degrading or resistant microorganisms for SNaD is a cost-effective method compared to the use of other methods of CN- removal prior to TN removal, as they involve multi-stage systems (as currently observed in MWSSs). The use of CN- degrading microorganisms, particularly when used as a consortium, presents a promising and sustainable resolution to mitigate inhibitory effects of CN- in SNaD. However, SNaD is known to be completely inhibited by CN- thus it is imperative to also study some thermodynamic parameters of SNaD under high CN- conditions to see the feasibility of the process. The Gibbs free energy is significant to understand the feasibility of SNaD, it is also vital to study Gibbs free energy to determine whether or not the biological reaction is plausible. The relationship between the rate of nitrification and Gibbs free energy was also investigated. The attained results showed that up to 37.55 mg CN-/L did not have an effect on SNaD. The consortia degraded CN- and achieved SNaD, with degradation efficiency of 92.9 and 97.7% while the degradation rate of 0.0234 and 0.139 mg/L/hr for ammonium-nitrogen (NH4-N) and CN- respectively. Moreover, all the free Gibbs energy was describing the individual processes were found to be negative, with the lowest Gibbs free energy being -756.4 and -1830.9 Kcal/mol for nitritation and nitratation in the first 48 h of the biological, reaction respectively. Additionally, a linear relationship between the rate of NH4-N and nitrite-nitrogen (NO2-N) degradation with their respective Gibbs free energy was observed. Linear model was also used to predict the relationship between NH4-N, NO2-N degradation and Gibbs free energy. These results obtained showed a good correlation between the models and the experimental data with correlation efficiency being 0.94 and 0.93 for nitritation, and nitratation, respectively. From the results found it can be deduced that SNaD is plausible under high cyanide conditions when cyanide degrading or tolerant microorganisms are employed. This can be a sustainable solution to SNaD inhibition by CN- compounds during wastewater treatment. Furthermore, a single strain was purified from the consortium and identified as Acinetobacter courvalinii. This bacterial strain was found to be able to perform sequential CN- degradation, and SNaD; an ability associated with multiphase growth strategy of the microorganism when provided with multiple nitrogenous sources, i.e. CN- and TN. The effect of CN- on nitrification and aerobic denitrification including enzyme expression, activity and protein functionality of Acinetobacter courvalinii was investigated. It was found that CN- concentration of up to 5.8 mg CN-/L did not affect the growth of Acinetobacter courvalinii. In cultures whereby the A. courvalinii isolate was used, degradation rates of CN- and NH4-N were found to be 2.2 mg CN-/L/h and 0.40 mg NH4-N/L/h, respectively. Moreover, the effect of CN- on NH4-N, nitrate-nitrogen (NO3-N) and NO2-N oxidizing enzymes was investigated, with findings indicating CN- did not affect the expression and activity of ammonia monooxygenase (AMO), but affected the activity of nitrate reductase (NaR) and nitrite reductase (NiR). Nevertheless, a slow decrease in NO2-N was observed after the addition of CN- thus confirming the activity of NaR and the activation of the denitrification pathway by the CN-. Moreover, five models’ (Monod, Moser, Rate law, Haldane, and Andrew’s model) ability to predict SNaD under CN- conditions, indicated that only Rate law, Haldane and Andrew’s models, were suited to predict both SNaD and CN- degradation. Due to low degradation rates of NH4-N and CN-, optimization of SNaD was essential. Therefore, response surface methodology was used to optimize the SNaD under CN- conditions. The physiological parameters that were considered for optimization were temperature and pH; with the result showing that the optimum for pH and temperature was 6.5 and 36.5oC respectively, with NH4-N and CN- degradation efficiency of 50 and 80.2%, respectively. Furthermore, the degradation kinetics of NH4-N and CN- were also studied under the optimum conditions in batch culture reactors, and the results showed that up to 70.6% and 97.3% of NH4-N and CN- were simultaneously degraded with degradation rates of 0.66 and 0.41 mg/L/h, respectively. The predictive ability of RSM was further compared with cybernetic models, and cybernetic models were found to better predict SNaD under CN- conditions. These results exhibited a promising solution in the management of inhibition effected of CN- towards SNaD at an industrial scale.

En aquesta tesi es presenten dues propostes de Sistemes de Control basats en Lògica Difusa (SCLD), des del seu disseny fins a la seva implementació i validació en dues instal·lacions: l'EDAR Granollers i l'EDAR Taradell.El capítol 1 explica els conceptes bàsics per comprendre el desenvolupament dels dos SCLD i el resum d'una revisió d'articles que relacionen la lògica difusa amb aigües residuals. A continuació, s'estableixen els objectius. En el capítol 3 es presenten els materials i mètodes. Els capítols 4 i 5 exposen el treball realitzat per arribar a la implementació dels dos SCLD. Ambdós capítols presenten la mateixa estructura: presentació, definició dels objectius del SCLD, descripció de l'EDAR on s'implementa el SCLD, desenvolupament d'índexs d'avaluació, explicació del disseny del SCLD i la seva avaluació mitjançant estudis de simulació, implementació i validació del SCLD a l'EDAR i, finalment discussió del treball realitzat. En el capítol 6 s'enumeren les conclusions obtingudes. / This thesis presents two proposals of Fuzzy Logic Control Systems (FLCS's), from their design to their implementation and validation in two facilities: Granollers and Taradell WWTP. The fundamental concepts to understand the FLCS's development are explained in the first chapter with a summary of scientific papers related to fuzzy logic applications in the wastewater treatment. The objectives are established in Chapter 2 and the materials and methods are described in Chapter 3.In Chapters 4 and 5, the work to design, implement and validate the FLCS's is presented. Both chapters have the same structure: a presentation, a goal definition of FLCS, a description of the WWTP, the evaluation index development, a detailed explanation about designing the FLCS process and its evaluation by simulation studies, the implementation of FLCS to WWTPs and their validation and, finally, a discussion of the work carried out is presented. The main conclusions are enumerated in Chapter 6.