Spelling suggestions: "subject:"photofenton process"" "subject:"fotofenton process""
11 |
Espécies nitrogenadas em água de chuva de Ribeirão Preto (SP) / Nitrogen species in rainwater of Ribeirão Preto (SP)Cristina Penna Crispim 28 June 2018 (has links)
Espécies nitrogenadas vem sendo adicionadas ao meio ambiente de forma intensa desde o desenvolvimento do processo Haber-Bosch para transformação de N2 em NH3, alterando significativamente o ciclo biogeoquímico do nitrogênio no ambiente. Uma vez na atmosfera, o nitrogênio reativo é depositado de volta à superfície da Terra por processos de deposição úmida e seca. A importância de levar em conta as formas orgânicas de nitrogênio para estimar a deposição de nitrogênio atmosférico pela chuva (úmida) já é conhecida, no entanto, ainda há poucos trabalhos que avaliam essa fração devido às dificuldades e incertezas impostas pelos métodos analíticos disponíveis. Este trabalho traz o desenvolvimento de um novo método, simples e de baixo custo, para a determinação de nitrogênio orgânico (N-org) em água de chuva utilizando o processo foto-Fenton e um foto-reator construído de forma artesanal. Por meio da adição de solução de Fenton (50 µmol L-1 Fe2+ e 2 mmol L-1 H2O2) e 90 min de radiação UV (85 °C) foi possível obter em média 106 ± 8% de recuperação de nitrogênio para soluções contendo 50 µmol N L-1 das moléculas modelos: ureia, serina, glicina e histidina. No caso da arginina, 90 min de radiação foi suficiente para degradar soluções contendo 10 µmol N L-1. O reator comercial se mostrou mais eficiente na degradação dos compostos testados (30 min), no entanto, com um tempo de 75 min, o reator artesanal atingiu os mesmos resultados. Com o uso de 0,2 g L-1 TiO2 e 120 min de radiação UV, também foi possível obter resultados satisfatórios. Porém, esse método possuiu valores de branco elevados, havendo necessidade de filtrar as amostras irradiadas antes da análise, adicionando tempo e custo ao procedimento analítico. O método desenvolvido utilizando foto-Fenton foi aplicado para a determinação de N-org em amostras de água de chuva coletadas na cidade de Ribeirão Preto (SP) de 2013 a 2017. A concentração de N-org variou de 3,5 a 195 µmol N L-1 com concentração média ponderada pelo volume (MPV) de 17,7 ± 1,0 µmol N L-1 (n=236). Essa média foi maior que aquelas obtidas em água de chuva de várias partes do mundo, podendo ser atribuída a elevada queima de biomassa na região de estudo. As concentrações de aminoácidos livres dissolvidos (AA) representaram em média 15 ± 12% (n=144) em relação à fração orgânica de nitrogênio na chuva, enquanto as concentrações de ureia foram próximas ou inferiores ao limite de quantificação do método (0,5 µmol N L-1). Considerando toda série temporal iniciada no mesmo sítio amostral desde 2005, as concentrações MPV calculadas para os íons NH4+ foi de 22,2 ± 1,1 µmol L-1 (n=460), NO3- de 13,3 ± 0,6 µmol L-1 (n=466), sendo que a concentração de NO2- foi irrelevante. Foram obtidas concentrações significativamente mais elevadas (teste-t, P=0,05) de NH4+, NO3-, N-org e AA no período de safra da cana (seco) com relação à entressafra (chuvoso), para todos os anos avaliados. Apesar da colheita manual da cana ter sido drasticamente reduzida, o fato de manter a mesma tendência sazonal desde 2005, demonstra que a prática da queima de biomassa ainda é intensa na região. O uso de fogo para manejo na área rural ainda é comum, além de haver grandes áreas queimadas de forma acidental. A deposição úmida de nitrogênio (N-org + NH4+ + NO3-) para Ribeirão Preto foi de 10,5 kg (N) ha-1 ano-1, sendo que a fração orgânica representou 33% dessa deposição, demonstrando a importância de se determinar N-org para melhor estimar os fluxos atmosféricos de deposição. A massa estimada de nitrogênio depositada pela chuva é cerca de 16% do nitrogênio aplicado por meio de fertilizantes em culturas de cana. Somando as deposições de nitrogênio pelo material particulado, pela fase gasosa, e úmida, esta última representa 71% do fluxo atmosférico de nitrogênio. Nesse contexto, a fração orgânica corresponde a 24% da deposição total, sendo que este valor ainda pode estar sendo subestimado, pois as concentrações de N-org no material particulado não foram determinadas. A simplicidade e exatidão do método aqui proposto pode facilitar a aquisição de dados de N-org na chuva de outras partes do mundo, melhorando assim o conhecimento sobre o ciclo biogeoquímico global do nitrogênio. / Nitrogen species have been intensively added to the environment since the development of Haber-Bosch process for N2 transformation to NH3, significantly altering the biogeochemical cycle of nitrogen. Once in the atmosphere, reactive nitrogen is deposited back to the Earth\'s surface by wet and dry deposition processes. The importance of taking into account the organic forms of nitrogen to estimate atmospheric nitrogen deposition by rain is already known. However, few studies evaluated this fraction due to the difficulties and uncertainties imposed by the available analytical methods. This work presents the development of a new, simple and low-cost method for the determination of organic nitrogen (N-org) in rainwater using photo-Fenton process and a homemade photo-reactor. By adding Fenton solution (50 mol L-1 Fe2+ and 2 mmol L-1 H2O2) and keeping the reaction under UV radiation for 90 min (85 °C), it was possible to obtain an average of 106 ± 8% nitrogen recovery for solutions containing 50 mol N L-1 of the model molecules: urea, serine, glycine and histidine. In the case of arginine, 90 min of radiation was sufficient to degrade solutions containing 10 mol N L-1. A commercial reactor showed to be more efficient in degradation of the tested compounds (30 min). However, with a time of 75 min, the homemade reactor achieved the same results. With 0.2 g L-1 TiO2 and 120 min of UV radiation, it was also possible to obtain satisfactory results. Nevertheless, this method had high blank values, and filtration of irradiated samples before the analysis was necessary, which increased time and cost to the analytical procedure. The developed method using photo-Fenton was applied to determine N-org in rainwater samples collected in Ribeirão Preto city (SP) from 2013 to 2017. N-org concentrations ranged from 3.5 to 195 mol N L-1 with a volume-weighted mean concentration (VWM) of 17.7 ± 1.0 mol N L-1 (n = 236). This value was higher than those reported for rainwater from different parts of the world, and this fact can be attributed to the high biomass burning in the study region. Dissolved free amino acids (AA) mean concentrations represented 15 ± 12% (n = 144) of the organic nitrogen fraction in rain, while urea concentrations were close to or below the limit of quantification of the method (0.5 mol N L-1). Considering all temporal series, initiated in 2005 at the same sampling site, the VWM concentration calculated for NH4+ ions was 22.2 ± 1.1 mol L-1 (n = 460) and for NO3- was 13.3 ± 0.6 mol L-1 (n = 466), while NO2- mean concentration was irrelevant. Significantly higher concentrations (t-test, P = 0.05) of NH4+, NO3-, N-org and AA were obtained during the harvest period (dry season) in relation to the non-harvest one (rainy season), for all evaluated years. Although manual harvesting was drastically reduced, the fact that the same seasonal trend has been maintained since 2005 demonstrates that the practice of biomass burning is still intense in the region. In rural area, using fire for land management is still common, in addition to large areas burned by unintentional fires. Nitrogen deposition (N-org + NH4+ + NO3-) in Ribeirão Preto was 10.5 kg (N) ha-1 year-1, and the organic fraction represented 33% of this deposition, demonstrating the importance of determining N-org to better estimate the atmospheric deposition fluxes. The estimated mass of nitrogen deposited by rain represents approximately 16% of the nitrogen introduced by fertilizers in sugarcane crops. Summing up the nitrogen deposition by particulate matter, by gas phase, and by rain, the latter represents 71% of the atmospheric nitrogen flux. In this context, the organic fraction corresponds to 24% of the total deposition, and this value may still be underestimated, since N-org concentrations in particulate matter were not determined. The simplicity and accuracy of the method proposed here may facilitate acquisition of N-org data in rainwater from other parts of the world, thus improving the knowledge on the global biogeochemical cycle of nitrogen.
|
12 |
Aplicação dos processos foto-Fenton e eletrofloculação no tratamento de efluente de curtume / Application of the photo-Fenton and electrocoagulation processes at the tannery effluent treatmentBorba, Fernando Henrique 18 February 2010 (has links)
Made available in DSpace on 2017-07-10T18:08:12Z (GMT). No. of bitstreams: 1
Fernando Henrique Borba.pdf: 3301834 bytes, checksum: 0c5216d667957cc99d5acd2dd5d59c05 (MD5)
Previous issue date: 2010-02-18 / Pollution is a currently environmental problem of world concern. There are many events such as the discharging of untreated effluents in watercourses that cause the eutrophization of water bodies and bad water quality, as well as an inefficiency or lack of a current environmental law. The main goal of this dissertation was the application of solar and artificial-based photo-Fenton processes and aluminum electrodes-based electrocoagulation method in non coupled mode and in an integrated mode for the tannery effluent treatment. These effluent treatments were carried out in lab-scale reactors. In order to evaluate the performance of the reactor experimental conditions of photo-Fenton reactor, a 33 complete experimental design was performed. The lab scale EC reactor was operated at the 4 A electrical current, 4 cm electrode distance and 3 initial pH optimized values, according to the previous results obtained in another work, while the electrolysis time was varied from 5 to 120 min. For EC and photo-Fenton reactors, their performance was evaluated on the removal values of chemical oxygem demand (COD), color, turbidity, total solids (TS), total fixed solids (TFS), total volatile solids (TVS) and metal concentration. Measurements of physico-chemical parameters for untreated and treated effluent samples were performed applying the Standard Method for water analysis, while metal concentrations were determined by the Synchrotron radiation total Reflexion X-ray Fluorescence technique at Brazilian Light Synchrotron Laboratory. By an optimized photon-Fenton process at 0.5 g Fe2+ L-1, 30 g H2O2 L-1, 3 initial pH, and 120 min reaction time, tannery effluent was treated achieving a high performance in pollutant removal as reported by 98.1, 96.4, 98.8, 71.8, 32.1 and 98.5 percent removal for COD, color, turbidity, TS, TFS, and TVS, respectively. As a primer treatment stage, electrocoagulation technique was not achieved a well successful result based on the physico-chemical parameter values reduction as compared with photo-Fenton process. However, an integrated solar irradiation-based photo-Fenton and Al electrodes-based electrocoagulation with 15 min electrolysis time has achieved recommended values by the Brazilian environmental law for Cr concentration (0.24 mg Cr L-1) and DQO (107 mg O2 L-1). Considering both the costs of electrical energy and material and the generated sludge discharging, one m3 of tannery effluent should cost R$ 56.30 for a treatment system based on an integrated and optimized photo Fenton and electrocoagulation processes. Finally, the integrated solar-based photo Fenton and electrocoagulation method is suggested as an efficient one, instead to apply a unique process. / A poluição ambiental é um dos grandes problemas nos países desenvolvidos e em desenvolvimento. Isto é decorrente de uma série de fatores, como o despejo de efluentes não tratados em corpos hídricos e a ineficiência e/ou a falta de legislação ambiental vigente. O objetivo principal deste trabalho é aplicar os processos foto-Fenton com irradiação solar e/ou artificial, a técnica da eletrofloculação e a integração destes processos no tratamento de efluente de curtume. Ambos os processos de tratamento do foto-Fenton e da eletrofloculação foram conduzidos em reatores a escala laboratorial. Para a técnica da eletrofloculação foi utilizado um par de placas de alumínio como eletrodos no reator de eletrofloculação. Para avaliar as melhores condições de processo do sistema foto-Fenton, foi aplicado um planejamento experimental 33 completo. Para a técnica da eletrofloculação manteve-se constante a intensidade de corrente, pH inicial do efluente bruto e distância entre os eletrodos, variando-se o tempo de eletrólise de 5 à 120 min. A eficiência de ambos os processos foram avaliadas com base na redução de Demanda química de oxigênio (DQO), cor, turbidez, sólidos totais (ST), sólidos totais fixos (STF), sólidos totais voláteis (STV). Para a técnica da eletrofloculação e dos processos integrados também foram avaliados a redução da concentração dos metais pesados. Todas as medidas dos parâmetros físico-químicos foram realizadas aplicando os métodos padrões do Standard Methods for the Examination of Water and Wastewater para amostra não tratada e tratada. As concentrações dos metais pesados foram determinadas usando a técnica de fluorescência de raio X por reflexão total, na linha de Luz (D09-XRF) do Laboratório Nacional de Luz Synchrotron. A maior eficiência na redução dos poluentes verificada no processo foto-Fenton foi de 98,1, 96,4, 98,8, 71,8, 32,1 e 98,5 para valores da DQO, cor, turbidez, ST, STF e STV, respectivamente, nas condições operacionais do reator: concentração de ferro de 0,5 gL-1, concentração de peróxido de hidrogênio de 30 gL-1, pH inicial 3 e tempo reacional de 120 min. No entanto a técnica da eletrofloculação não apresentou boa redução nos valores dos parâmetros físico-químicos. Após a aplicação dos processos integrados do foto-Fenton com irradiação solar e da eletrofloculação em tempo de eletrólise de 15 min, foi alcançado valores mínimos de Cr e DQO no efluente tratado, contendo 0,24 mg Cr L-1 e 107 mg O2 L-1 da DQO. O custo do tratamento do efluente e da disposição final do lodo gerado no processo integrado FFs→EF foi de R$ 56,30 m3 do efluente de curtume tratado. Este processo integrado reduziu as concentrações de cromo, ferro e DQO, a níveis permitidos pelas legislações ambientais. Baseada na redução da matéria orgânica e inorgânica, o método integrado FFs→EF pode ser recomendado como uma substituição eficiente ao método individual.
|
13 |
Tratamento de efluente têxtil utilizando o processo foto-fenton / Treatment of textile effluent using photo-fenton processManenti, Diego Ricieri 25 February 2011 (has links)
Made available in DSpace on 2017-07-10T18:08:15Z (GMT). No. of bitstreams: 1
Diego Ricieri Manenti.pdf: 2926963 bytes, checksum: 74aa89bdde44c5ef6942846129864678 (MD5)
Previous issue date: 2011-02-25 / Coordenação de Aperfeiçoamento de Pessoal de Nível Superior / The aim of this work was to study the performance of the photo-Fenton process using both the artificial UV and solar sources on the textile effluent treatments. Preliminary photo-Fenton experiments for mineralization and degradation of organic and inorganic pollutants as well as of synthetic dyes were carried out in order to assess the best experimental conditions by photo-Fenton process. As synthetic textile effluent a mixture of six dyes: Solophenyl orange TGL (C25H33ClN6O6S2), Solophenyl blue 71 (C40H23N7Na4O13S4), Solophenyl scarlet BNLE (C44H32N10Na4O16S4), Solophenyl yellow ARL (C48H26N8Na6O18S6), Solophenyl black FR (C44H32N13Na3O11S3) e Navy Blue 98 (C38H24N5Na3O13S3) that contained 50 mg L-1 concentration was prepared and diluted in distillated water. The photo-Fenton experiments by using a set of high-pressure mercury lamps and solar light as artificial and natural UV irradiation sources were performed in laboratory scale. As reactor operational parameters to be optimized by a 33 full factorial experimental design: hydrogen peroxide and divalent iron ion as well as the initial solution pH were chosen as variables, keeping constant a reaction time of 120 min that was enough to warrant the maximum (chemical oxygen demand) COD and color removal. The efficiency of photo-Fenton process applied in the treatment of synthetic and real effluents, was evaluated based on the parameters: values of COD, color, turbidity, total organic carbon (TOC), absorbance at a wavelength of maximum absorption for the dyes and simple aromatic compounds and conjugated reductions, as well as behavior analysis of the evolution the sulfate, nitrate inorganic, organic nitrogen and ammonia concentrations. Second-degree models for the COD and color removal percents were proposed to model the photo-Fenton experiments data in order to reduce the cost of running such a photo-Fenton experiment as well as to obtain optimum values of the reactor operating parameters. Second-degree models were also validated by ANOVA. Predicted yields showed good validation with experimental yields. The values of the optimized reactor operational parameters were 3.0, 6.0 g L-1, and 0.05 g L-1 for initial pH, hydrogen peroxide and divalent iron concentrations, respectively, for both photo-Fenton processes. Based on this optimized experimental conditions, almost 100% removals of physico-chemical parameter such as COD, color, turbidity and COT for real textile effluents. The aromatics compounds were showed more resistant to reaction, persisting for longer. It can be noticed that the degradtion of the organic and inorganic matters were verified by the nitrification process and, the sulfates formation and reduction. The process presented similar efficiencies with both solar and artificial irradiation, thus suggesting the use of solar photo-Fenton, as it proved to be an efficient alternative besides using a source of clean and renewable energy. / O objetivo deste trabalho é avaliar o desempenho do processo foto-Fenton, utilizando energia solar e artificial como fontes de irradiação UV, no tratamento de efluentes têxteis. Foram realizados experimentos preliminares para avaliar a eficiência do processo foto-Fenton na mineralização e degradação dos poluentes orgânicos e inorgânicos, bem como dos corantes sintéticos. Para tanto, foi preparado o efluente têxtil sintético pela mistura de seis corantes: Laranja TGL (C25H33ClN6O6S2), Azul FGLE (C40H23N7Na4O13S4), Escarlate BNLE (C44H32N10Na4O16S4), Amarelo ARLE (C48H26N8Na6O18S6), Preto FR (C44H32N13Na3O11S3) e Marinho BLE (C38H24N5Na3O13S3), em água destilada, com concentração de 50 mg L-1. Os experimentos foram realizados em reatores de escala laboratorial utilizando fontes de irradiação UV natural e artificial. Os parâmetros operacionais dos reatores: pH inicial e a concentração dos reagentes H2O2 e Fe2+, foram otimizados baseados nos valores da demanda química de oxigênio (DQO) e descoloração, a partir de um planejamento fatorial 33 completo com o tempo de irradiação constante em 120 minutos. A eficiência do processo foto-Fenton, aplicado no tratamento dos efluentes sintético e real, foi avaliada baseada nos parâmetros: redução dos valores da DQO, cor, turbidez, carbono orgânico total (COT), absorvância nos comprimentos de onda de máxima absorção relativos aos corantes e aos compostos aromáticos simples e conjugados, além da análise do comportamento da evolução das concentrações de sulfato, nitrato inorgânico, nitrogênio orgânico e amoniacal. Para auxiliar na obtenção das condições ótimas dos parâmetros operacionais do reator e redução dos custos do processo foto-Fenton, as respostas experimentais para a redução da DQO e da cor foram ajustados por um modelo previsto de segunda ordem, o qual apresentou uma boa modelagem dos dados, validado pela ANOVA. Os valores ótimos operacionais do reator, para ambos os processos foto-Fenton no tratamento do efluente real, foram: pH = 3,0, concentração de H2O2 = 6,0 g L-1 e concentração de Fe2+ = 0,05 g L-1. Nestas condições, foram obtidos valores próximos a 100% de redução dos parâmetros físico-químicos DQO, cor, turbidez e COT. Os compostos aromáticos se mostraram mais resistentes a reação, persistindo por mais tempo. A degradação da matéria orgânica e inorgânica foi verificada analisando a evolução do processo de nitrificação e a formação ou redução de sulfatos. Os processos apresentaram eficiências similares tanto com irradiação solar como artificial, desta forma, sugere-se a utilização do processo foto-Fenton solar, pois mostrou ser uma alternativa eficiente além de utilizar uma fonte de energia limpa e renovável.
|
14 |
Voltametrijske metode zasnovane na primeni jednostavnih i savremenih elektroda/senzora na bazi ugljeničnih materijala za određivanje vodonik-peroksida u odabranim uzorcima / Voltammetric methods based on the application of simple and contemporary carbonaceousmaterials-based electrodes/sensors for the determination of hydrogen-peroxide in the selected samplesAnojčić Jasmina 22 November 2018 (has links)
<p>Cilj ove doktorske disertacije je bio razvoj brzih i pouzdanih voltametrijskih metoda zasnovanih na primeni jednostavnih i savremenih elektroda/senzora na bazi ugljeničnih materijala (ugljenične paste napravljene od grafitnog praha i parafinskog ulja i štampanih ugljeničnih elektroda) za određivanje H <sub>2</sub>O<sub>2 </sub>u odabranim složenim model i realnim uzorcima. U tu svrhu, ispitana je primenljivost različitih radnih elektroda. Amperometrijska metoda zasnovana na elektrodi od ugljenične paste (CPE) zapreminski modifikovane sa 5% (m:m) MnO2 je, pri optimizovanim uslovima i pri radnom potencijalu od 0,40 V u odnosu na zasićenu kalomelovu elektrodu (ZKE) u fosfatnom puferu pH 7,50 kao pomoćnom elektrolitu, omogućila kvantifikaciju H <sub>2</sub>O<sub>2</sub> u opsegu koncentracija od 1,4 do 65 µg mL -1 sa relativnom standardnom devijacijom (RSD) manjom od 10%. Ova metoda je primenjena za određivanje sadržaja H <sub>2</sub>O<sub>2 </sub>u uzorcima podzemne vode iz centralnog Banata (Pokrajina Vojvodina, Srbija) tretirane Fentonovim (Fe<sup> 2+</sup> i H <sub>2</sub>O<sub>2</sub> ) i Fentonu-sličnim (Fe <sup>3+</sup> i H <sub>2</sub>O<sub>2</sub> ) reagensima u cilju uklanjanja prirodnih organskih materija (POM) pri čemu su korišćene različite početne koncentracije gvožđa i različiti odnosi molarnih koncentracija gvožđa i H <sub>2</sub>O<sub>2</sub> . Utvrđeno je da oksidaciono stanje gvožđe (Fe<sup> 2+</sup> ili Fe <sup>3+</sup>) i molarni odnos jona Fe i H<sub> 2</sub>O<sub>2</sub> utiču na stepen potrošnje/razgradnje H<sub> 2</sub>O<sub>2</sub><br />u podzemnoj vodi sa visokim sadržajem POM. Takođe, u slučaju Fentonu-sličnog procesa, za sve početne koncentracije Fe <sup>3+</sup> i H <sub>2</sub>O<sub>2 ,</sub> signifikantna količina H <sub>2</sub>O<sub>2 </sub>ostaje neiskorišćena, što ukazuje na nižu efikasnost ovakvog sistema u poređenju sa Fentonovim procesom.Štampana ugljenična elektroda (SPCE) zapreminski modifikovana sa MnO 2 kao medijatorom je primenjena za određivanje sadržaja H<sub> 2</sub>O<sub>2</sub> u toku Fentonovog (Fe <sup>2+</sup> , H<sub>2</sub>O<sub>2</sub> ) i vidljivom svetlošću potpomognutog foto-Fentonovog (Fe<sup> 2+ </sup>, H <sub>2</sub>O<sub>2 </sub>, hν) procesa uklanjanja neonikotinoidnog insekticida acetamiprida (ACT). Pri optimizovanim uslovima (radni potencijal 0,40 V u odnosu na ZKE, fosfatni pufer pH 7,50 kao pomoćni elektrolit) amperometrijskog određivanja H <sub>2</sub>O<sub>2</sub> , postignuta je linearnost u opsegu koncentracija 0,01–1,24 mmol L-1(0,34– 42,2 µg mL -1<br />) i vrednost RSD nije prelazila 4,2%. U ispitivanimuzorcima (nakon odgovarajućeg<br />podešavanja pH vrednosti od 2,8 do 7,5 odmah nakon uzorkovanja radi stopiranja ili maksimalnog usporavanja procesa oksidacije, filtriranja, zamrzavanja i odmrzavanja neposredno pre merenja) sadržaj H <sub>2</sub>O<sub>2</sub> je određen metodom standardnog dodatka analiziranjem odgovarajućih amperometrijskih krivi. Paralelna HPLC-DAD merenja su vršena u cilju praćenja koncentracije/uklanjanja ACT. U slučaju foto-Fentonovog procesa (početne koncentracije 0,31; 2,0 i 3,0 mmol L -1 (70,0; 111,7 i 102,1 µg mL -1 ) za ACT, Fe<br /><sup>2+</sup> i H <sub>2</sub>O<sub>2</sub>, redom) nakon 10 min H <sub>2</sub>O<sub>2 </sub>je izreagovao, a može se smatrati da je ACT uklonjen nakon 5 min. U toku Fentonovog procesa ACT je uklonjen nakon 20 min tretmana i oko 10% početne koncentracije H <sub>2</sub>O<sub>2</sub> je ostalo u sistemu<br />neiskorišćeno.CPE je površinski modifikovane kompozitom na bazi nanočestica Pt (< 5 nm) i grafitizovanog ugljenika (Pt-C, 10% Pt na Vulkanu XC72) etodom nanošenja kapi. Nemodifikovana CPE i modifikovana (Pt-C/CPE) su okarakterisane primenom SEM/EDS i CV merenja. Pt-C/CPE je pokazala izuzetne elektrokatalitičke osobine u pogledu elektrohemijskeredoks reakcije H<br /><sub>2</sub>O<sub>2</sub> u poređenju sa nemodifikovanom CPE u fosfatnom puferu (0,1 mol L -1 ;<br />pH 7,50), a takođe i u acetatnom puferu (0,1 mol L -1 ; pH 4,50) kao pomoćnim elektrolitima. Prilikom amperometrijskog određivanja H <sub>2</sub>O<sub>2</sub> primenom Pt-C/CPE u model sistemima, zadovoljavajuća linearnost je postignuta u koncentracionom opseguH<sub>2</sub>O<sub>2</sub>od 0,15 do 1,45 µg mL -1 ,dok su vrednosti GO iznosile 0,06 µg mL -1 (pH 7,50, radni potencijal 0,20 V) i 0,10 µg mL -1 (pH<br />4,50, radni potencijal 0,50 V). Optimizovane analitičke metode su primenjene za određivanje sadržaja H <sub>2</sub>O<sub>2</sub> u komercijalno dostupnim proizvodima za ličnu negu: rastvoru za dezinfekciju (pH 7,50) i rastvoru za čišćenje kontaktnih sočiva (pH 4,50). Amperometrijski dobijeni rezultati su u dobrom slaganju sa rezultatima dobijenim primenom tradicionalne spektrofotometrijske metode bazirane na titanijum-sulfatu kao reagensu sa određenim koncentracijama 2,91% i 2,94% za<br />dezinfekcioni rastvor i 3,04% i 3,17% za rastvor zakontaktna sočiva, redom. RSD je bila manja od 2%. Postignuti rezultati su u dobrom slaganju sa sadržajem H<br /><sub>2</sub>O<sub>2 </sub>deklarisanim od strane proizvođača (3%) u oba ispitivana uzorka. Pt-C/CPE je takođe testirana za praćenje koncentracije H<sub>2</sub>O<sub>2</sub> u rastvoru za kontaktna sočiva u toku procesa njegove neutralizacije/razgradnje. Nakon 6 h procesa neutralizacije, 24,68 µg mL -1 je bila određena koncentracija H <sub>2</sub>O<sub>2 ,</sub> što je ispod dozvoljene<br />H<sub>2</sub>O<sub>2 </sub>koncentracije u rastvoru za kontaktna sočiva imajući u vidu granicu koja izaziva iritaciju oka. CPE je površinski modifikovana višezidnim ugljeničnim nanocevima (MWCNT) i kompozitima MnO 2 -MWCNT ili Pt-MWCNT metodom nanošenja kapi radi pripreme jednostavnih, osetljivih i pouzdanih voltametrijskih senzora za određivanje H <sub>2</sub>O<sub>2 </sub>u odabranom uzorku. Rezultati SEM/EDS analize kompozitnih materijala su potvrdili da su medijatori, čestice MnO 2 i Pt, nasumično raspoređeni na površini MWCNT i zastupljeni sa blizu 5% (m:m) u kompozitu izraženo<br />preko Mn i Pt. CV merenja su vršena sa pripremljenim radnim elektrodama u acetatnom (pH 4,50), fosfatnom (pH 7,50) i boratnom (pH 9,18) puferu kako bi se okarakterisalo osnovno elektrohemijsko ponašanje H <sub>2</sub>O<sub>2 </sub>i odabrali pogodni radni potencijali za amperometrijsko određivanje ovog ciljnog analita. Pt- WCNT/CPE je primenljiva za rad kako u fosfatnom puferu pH 7,50 tako i u acetatnom puferu pH 4,50 V kako pri negativnim tako i pri pozitivnim radnim<br />potencijalima, pri čemu su vrednosti RSD uglavnom ispod 2,5%. U slučaju MnO 2<br />-MWCNT/CPE, na potencijalu 0,30 V i višim vrednostima, oksidacioni signali H<br /><sub>2</sub>O<sub>2</sub> su signifikantni u blago alkalnoj sredini (pH 7,50), pri pH 4,50 ova elektroda pokazuje nezadovoljavajuće ponašanje, dok pri pH 9,18 ima prihvatljive performanse. Granice određivanja (GO) su bile u oblasti µg mL -1 . H <sub>2</sub>O<sub>2</sub> je određen u spajkovanom uzorku mleka metodom standardnog dodatka nakon odgovarajuće pripreme uzorka (pH podešavanje i centrifugiranje) i primenom optimizovane amperometrijske procedure (acetatni pufer pH 4,50, radni potencijal-0,75 V) koristeći Pt-MWCNT/CPE kao radnu elektrodu. RSD za tri ponovljena merenja je iznosila 2,5%, dok je prinos metode bio nešto veći od 71%.<br />Kompozitni materijali koji se sastoje od MWCNT i čestica na bazi Pd (Pd-MWCNT) ili Pt (Pt-MWCNT) su primenjeni za pripremu zapreminski modifikovanih SPCE (Pd-MWCNT-SPCE i Pt-MWCNT-SPCE) i površinski modifikovane SPCE (Pd-MWCNT/SPCE). Ove elektrode, kao i nemodifikovana SPCE i MWCNT-SPCE, su okarakterisane primenom CV i amperometrije u fosfatnom puferu pH 7,50 radi određivanja H <sub>2</sub>O<sub>2</sub> . Pd-MWCNT-SPCE i Pd-MWCNT/SPCE su se pokazale pogodnim za određivanje H <sub>2</sub>O<sub>2</sub> na radnim potencijalima između -0,50 i 0,50 V, a PtMWCNT-SPCE na ispitivanim radnim potencijalima od -0,80 do 0,70 V. Ove elektrode su zatim modifikovane enzimom glukoza oksidazom (GOx) metodom nanošenja kapi rastvora GOx i Nafion ® -a na njihovu površinu, pri čemu je optimizovana količina nanetog biofilma. GOx/PdMWCNT-SPCE je pokazala bolje analitičke performanse za određivanje glukoze u poređenju sa GOx/Pd- WCNT/SPCE. Kao optimalan radni potencijal GOx/Pd-MWCNT-SPCE je odabrana<br />vrednost potencijala -0,40 V u odnosu na ZKE, sa zadovoljavajućom linearnošću u ispitivanom opsegu koncentracija glukoze od 0,16 do 0,97 mmol L -1 (od 29,1 do 174 µg mL -1), dok je GO iznosila 0,14 mmol L -1 (25 µg mL<br />-1 ). Optimizovana metoda zasnovana na GOx/Pd-MWCNT-SPCE je uspešno primenjena za određivanje glukoze u uzorku livadskog meda. Dobijeni rezultati su u dobroj saglasnosti sa onima dobijenim primenom komercijalno dostupnog aparata za merenje glukoze. Pogodan radni potencijal za GOx/Pt-MWCNT-SPCE je bio -0,50 V u odnosu na ZKE, pri čemu je zadovoljavajuća linearnost postignuta u ispitivanom opsegu koncentracija glukoze od 65,8 do 260,6 µg mL -1 , sa GO 35 µg mL -1 . Optimizovana metoda zasnovana na GOx/Pt-MWCNT-SPCE je uspešno primenjena za određivanje glukoze u u uzorku belog grožđa i uzorku tableta (Traubenzucker-bonbons), pri čemu su dobijeni rezultati u dobroj saglasnosti sa rezultatima dobijenim primenom Accu-Chek aparata.<br />Na osnovu dobijenih rezultata može se zaključiti da su razvijene analitičke metode pre svega jednostavne, pouzdane i pogodne za dobijanje brzih informacija o sadržaju H <sub>2</sub>O<sub>2</sub> u različitim tipovima uzoraka. Svakako odabir pogodne radne elektrode, kao i optimizacija eksperimentalnih uslova su ključni faktori za uspešno određivanje H <sub>2</sub>O<sub>2</sub></p> / null / <p>The aim of this doctoral dissertation was the development of fast and reliable voltammetric methods based on the application of simple and contemporary electrodes/sensors based on carbonaceous materials (carbon paste made of graphite powder and paraffin oil and screen printed carbon electrodes) for the determination of H <span id="cke_bm_571S" style="display: none;"> </span><sub>2</sub><span id="cke_bm_571E" style="display: none;"> </span>O<sub>2</sub> in the selected complex model and real samples.For this purpose, applicability of different working electrodes was investigated.The amperometric method based on carbon paste electrode (CPE) bulk- modified with 5% (m:m) MnO 2 , under optimized conditions, with a working potential of 0.40 V vs. the saturated calomel elect<span id="cke_bm_572E" style="display: none;"> </span>rode (SCE) and a phosphate buffer solution (pH 7.50) as supporting electrolyte, enabled the quantitation of H <span id="cke_bm_577S" style="display: none;"> </span><sub>2</sub><span id="cke_bm_577E" style="display: none;"> </span>O<sub>2</sub>in the concentration interval from 1.4 to 65 µg mL −1 with a relative standard deviation (RSD) of less than 10%. This meth<span id="cke_bm_578E" style="display: none;"> </span>od was applied for the determination of the H<span id="cke_bm_583S" style="display: none;"> </span><sub>2</sub><span id="cke_bm_583E" style="display: none;"> </span>O<sub>2 </sub>consumption in samples of groundwater fro<span id="cke_bm_584E" style="display: none;"> </span>m the Central Banat region (Province of Vojvodina, Serbia) treated by the Fenton (Fe <sup>2+ </sup>and H <sub>2</sub>O<sub>2</sub> ) and Fenton- like (Fe <sup>3+</sup>and H <sub>2</sub>O<sub>2</sub> ) reagents to remove natural organic matter (NOM) at differentinitial concentrations of iron species, and of their molar ratios to the initial concentration of H<sub>2</sub>O<sub>2</sub> . It was found that the form of Fe (Fe <sup>2+</sup> or Fe <sup>3+</sup> )and the molar ratio to H <sub>2</sub>O<sub>2</sub>influenced the degree of the H<sub> 2</sub>O<sub>2</sub> decomposition in the groundwater with high NOM content. Besides, in the case of the Fenton-like process, for all initial doses of Fe <sup>3+</sup> and H<span id="cke_bm_604S" style="display: none;"> </span><sub> 2</sub><span id="cke_bm_604E" style="display: none;"> </span>O<sub>2</sub>, a sign<span id="cke_bm_605E" style="display: none;"> </span>ificant amount of H<span id="cke_bm_610S" style="display: none;"> </span><sub> 2</sub><span id="cke_bm_610E" style="display: none;"> </span>O<sub>2</sub> remained unused, whi<span id="cke_bm_611E" style="display: none;"> </span>ch also indicates a lower efficiency of such system compared to the Fenton process. Screen printed carbon electrode (SPCE) bulk-modified with MnO <sub> 2</sub> as a mediator was applied for amperometric determination of the H <span id="cke_bm_617S" style="display: none;"> </span><sub>2</sub><span id="cke_bm_617E" style="display: none;"> </span>O<sub>2</sub> content during the Fenton (Fe <sup>2+</sup> , H <span id="cke_bm_624S" style="display: none;"> </span><sub>2</sub><span id="cke_bm_624E" style="display: none;"> </span>O<sub>2 </sub>) and <span id="cke_bm_625E" style="display: none;"> </span>visible light-assisted<span id="cke_bm_618E" style="display: none;"> </span>, photo-Fenton (Fe <sup>2+ </sup> , H <span id="cke_bm_631S" style="display: none;"> </span><sub>2</sub><span id="cke_bm_631E" style="display: none;"> </span>O<sub>2</sub> , hν)<span id="cke_bm_632E" style="display: none;"> </span> based removal of neonicotinoid insecticide acetamiprid (ACT). Under optimized conditions (working potential of 0.40 V vs. SCE, phosphate buffer pH 7.50 as supporting electrolyte) amperometric determination of H <span id="cke_bm_637S" style="display: none;"> </span><sub>2</sub><span id="cke_bm_637E" style="display: none;"> </span>O<sub>2 </sub>showed a linear dynamic range from 0.01 to 1.24 mmol L -1 (from 0.34 to 42.2 µg mL -1) and the RSD did not exceed 4.2%. In the investigated samples (after appropriate pH adjustment from 2.8 to 7.5 instantly after the sampling<span id="cke_bm_638E" style="display: none;"> </span> to stop or maximum decelerate the oxidation processes, filtering, and storage of the deep- frozen sample with defrosting immediately before the measurements) the H <span id="cke_bm_643S" style="display: none;"> </span><sub>2</sub><span id="cke_bm_643E" style="display: none;"> </span>O<sub>2</sub> contents were determined by the standard addition method by analyzing the corresponding amperometric curves. Parallel HPLC-DAD measurements were performed to monito<span id="cke_bm_644E" style="display: none;"> </span>r the concentration/removal of ACT. In the case of the photo- Fenton process (initial concentrations: 0.31; 2.0 and 3.0 mmol L -1 (70.0; 111.7 and 102.1 µg mL -1 ) of ACT, Fe<sup> 2+</sup> and H <span id="cke_bm_650S" style="display: none;"> </span><sub>2</sub><span id="cke_bm_650E" style="display: none;"> </span>O<sub>2</sub>, respec<span id="cke_bm_651E" style="display: none;"> </span>tively) after 10 min of irradiation H <span id="cke_bm_656S" style="display: none;"> </span><sub>2</sub><span id="cke_bm_656E" style="display: none;"> </span>O<sub>2</sub> was consumed and it can be consi<span id="cke_bm_657E" style="display: none;"> </span>dered that ACT was removed after 5 min. During the Fenton process ACT was removed after 20 min of treatment and around 10% of the initial concentration of the H 2O2 remained still unused.<br />CPE was surface modified with a composite of Pt nanoparticles (< 5 nm) on graphitized carbon (Pt-C, 10% Pt on Vulcan XC72) by simply dropcoating method. The unmodified CPE and the modified one (Pt-C/CPE) were characterized by EM/EDS and CV measurements. The PtC/CPE showed remarkable electrocatalytic propertiestoward the electrochemical redox reaction of H<span id="cke_bm_662S" style="display: none;"> </span><sub>2</sub><span id="cke_bm_662E" style="display: none;"> </span>O<sub>2</sub> compared to modified CPE in phosphate buffer (0.1 mol L -1 ; pH 7.50), as well in acetatebuffer (0.1 mol L -1 ; pH .50) supporting electrolytes. Amperometry of H2O2 in the concentration range from 0.15 to 1.45 µg mL -1 with the Pt-C/CPE showed acceptable linearity, while the obtained values of LOQs were 0.06 µg mL -1 (pH 7.50, working potential 0.20 V) and 0.10 µg mL -1 (pH 4<span id="cke_bm_663E" style="display: none;"> </span>.50, working potential 0.50 V). The proposed analytical methods were applied to the determination of the H 2O2 content in commercially available personal care products; i.e., disinfection (pH 7.50) and contact lens cleaning solutions (pH 4.50). The obtained amperometric results are in good agreement with those measured by traditional titanium sulfatereagent based spectrophotometric method with determined concentrations as 2.91% and 2.94% for the disinfection product, and 3.04% and 3.17% for the contact lens solution, respectively. RSD was lower than 2%. The obtained results are in a good agreement with the amounts of the H<span id="cke_bm_668S" style="display: none;"> </span><sub> 2</sub><span id="cke_bm_668E" style="display: none;"> </span>O<sub>2 </sub>declared by producers (3%) in the both investigated samples. The Pt-C/CPE was also tested for monitoring of the H<span id="cke_bm_674S" style="display: none;"> </span><sub> 2</sub><span id="cke_bm_674E" style="display: none;"> </span>O<sub>2</sub> residual concentration in contact lens solution during its neutralization/decomposition rocess. At 6 h of<span id="cke_bm_675E" style="display: none;"> </span> neutralization treatment 24.68 µg mL -1 of the H <span id="cke_bm_680S" style="display: none;"> </span><sub>2</sub><span id="cke_bm_680E" style="display: none;"> </span>O<sub>2 </sub>was determined which is almost half of the allowedH2<span id="cke_bm_681E" style="display: none;"> </span>O2 concentration in the case of the contact lens solution concerningthe limit of eye irritation. CPE was surface modified with multiwalled carbon nanotubes (MWCNT) and with composites of MnO<sub> 2 </sub>-MWCNT or Pt-MWCNT by drop coating method to prepare simply, sensitive and reliable volta<span id="cke_bm_669E" style="display: none;"> </span>mmetric sensors for the determination of H <span id="cke_bm_687S" style="display: none;"> </span><sub>2</sub><span id="cke_bm_687E" style="display: none;"> </span>O<sub>2 </sub>in selected sample. The results of the SEM/<span id="cke_bm_688E" style="display: none;"> </span>EDS analysis of composite materials have confirmed that the mediators, MnO <sub>2</sub> and Pt articles, are randomly distributed on the surface of MWCNT and represent nearly 5% (m:m) of the composite expressed as Mn and Pt. CV measurements were performed with prepared electrodes in acetate (pH 4.50), phosphate (pH 7.50) and borate (pH 9.18) buffers to characterize the basic electrochemical behavior of H <span id="cke_bm_694S" style="display: none;"> </span><sub>2</sub><span id="cke_bm_694E" style="display: none;"> </span>O<sub>2</sub> and to select the working potentials suitable for amperometric determination of this target analyte. The Pt-MWCNT/CPE performs well in phosphate buffer pH .50 and acetate buffer solution pH 4.50 in the negative as well as in the positive polarization range with RSD mainly lower than 2.5%. In case of MnO<sub> 2 </sub>-MWCNT/CPE at <span id="cke_bm_695E" style="display: none;"> </span>0.30 V and above the H<span id="cke_bm_701S" style="display: none;"> </span><sub>2</sub><span id="cke_bm_701E" style="display: none;"> </span>O<sub>2 </sub>oxidation signal is rem<span id="cke_bm_702E" style="display: none;"> </span>arkable in slightly alkaline media (pH 7.50), at pH 4.50 this electrode showed poor behavior and at pH 9.18 offered acceptable performance. LOQs were in the µg mL -1 concentration range. H<span id="cke_bm_707S" style="display: none;"> </span><sub>2</sub><span id="cke_bm_707E" style="display: none;"> </span>O<sub>2 </sub>was determined in a spiked milk sample by standard addition method after appropriate sample preparation (pH adjustment and centrifugation) and using optimized amperometric p<span id="cke_bm_708E" style="display: none;"> </span>rocedure (acetate buffer pH 4.50, working potential -0.75 V) by Pt-MWCNT/CPE as a working electrode. RSD for three repeated measurements was 2.5%, while the recovery of the method was a bit higher than 71%. The composite materials consisting of MWCNT and Pd (Pd-MWCNT) or Pt containing particles (Pt-WCNT) were applied to the preparation of bulk- modified SPCEs (Pd-MWCNTSPCE and Pt-MWCNT-SPCE) and surface modifiedSPCE (Pd- MWCNT/SPCE). These electrodes, as well as unmodified SPCE and MWCNT-SPCE, were characterized by CV and amperometry in phosphate buffer solution of pH 7.50 for the H<span id="cke_bm_713S" style="display: none;"> </span><sub> 2</sub><span id="cke_bm_713E" style="display: none;"> </span>O<sub>2 </sub>determination. Pd-MWCNT-SPCE and PdMWCNT/SPCEare convenient for the etermination of H 2O2 at working potentials from -0.50 to 0.50 V, and Pt-MWCNT-SPCE at investigated working potentials in the range from -0.80 to 0.70 V. These electrodes were then modified with glucose oxidase (GOx) by drop coating a solution of GOxand Nafion ® on their surface, whereby the applied amount of biococktail was optimized. GOx/PdMWCNT-SPCE showed better analytical performance for glucose determination in comparison with GOx/Pd-MWCNT/SPCE. The optimal working potential for GOx/Pd-MWCNT- SPCE was -0.40 V vs. SCE and <span id="cke_bm_714E" style="display: none;"> </span>satisfactory linearity was obtained in the investigated glucose concentration range from 0.16 to 0.97 mmol L -1 (from 29.1 to 174 µg mL -1 ), hile the LOQ was 0.14 mmol L -1 (25 µg mL -1 ). The optimized method based on GOx/Pd-MWCNT-SPCE was successfully applied to the determination of glucose in multifloral honey sample. The results are in a good agreement with those obtained by commercially available equipment for determination of glucose. Optimal working potential for GOx/Pt-MWCNT-SPCE was -0.50 V vs. SCE, and the satisfactory linearity was obtained in the investigated concentration range ofglucose from 65.8 to 260.6 µg mL -1 , with LOQ of 35 µg mL -1 . The optimized method based on GOx/Pt- MWCNT-SPCE was successfully applied for determination of glucose in white grape and glucose tablets (Traubenzucker-bonbons) samples, whereby the obtained results were in a good agreement with the results obtained by Accu-Chek device. Based on the results, the developed analytical methods are first of all simple, reliable and suitable for obtaining fast information about the content of H <sub>2</sub>O<sub>2</sub> in different types of samples. Certainly the selection of a suitable working electrode, as well as the optimization of experimental conditions are key factors for the successful determination of H<sub>2</sub>O<sub>2 </sub>.</p>
|
Page generated in 0.0499 seconds