In a forensic investigation involving oil, a comparative analysis named oil spill fingerprinting between a source and an oil spill is normally performed. It is based on detecting a certain selection of biomarkers with gas chromatography (GC) coupled to mass spectrometry (MS) which are later divided into diagnostic ratios (DRs). An international guideline formed by European Committee for Standardization (CEN) denoted CEN/TR 15522-2:2012 describes the process of conducting oil spill fingerprinting. This method is currently being inspected and adjusted for standardization into EN 15522-2:2022. One section of the upcoming standard describes sample clean-up which is important to inhibit possible matrix effect that could either enhance or reduce peak intensity in the chromatogram. There is yet no conclusive SPE (Solid Phase Extraction) protocol in the current draft version of EN 15522-2:2022. The aim with this study was to develop such a protocol. Development included comparative testing of the recommended stationary phases silica and Florisil®. Additionally, the effect of both elution solvent and elution volume were investigated. The protocol must pass validation criteria to be implemented at National Forensic Centre (NFC) and possibly be used in the final version of EN 15522-2:2022. A successful method for Heavy Fuel Oil (HFO), diesel and lubricating oil was achieved with activated Florisil® as stationary phase, eluted with 6 ml dichloromethane (DCM). If the evidence material is suspected to contain FAMEs (Fatty Acid Methyl Esters), then 2 % acetone should be added to the DCM. The final SPE column was packed with 0.5 glass wool, 4 cm Florisil® and 0.5 cm sodium sulfate. Based on successful validation result, the SPE protocol should be considered for the final version of EN 15522-2:2022 as well as for implementation at NFC.

A significant issue affecting the aquaculture and water industries is the presence of off-flavour compounds in water, which cause problems by imparting an undesirable earthy/musty flavour and smell to water and fish. Two predominant off-flavour compounds are geosmin (GSM) and 2-methylisoborneol (MIB). These compounds are produced by several varieties of cyanobacteria and actinomycetes as metabolic products and can be detected by humans at concentrations as low as 0.015 mg L-1. Removal of GSM and MIB from potable waters has proven to be inefficient using standard water treatment such as filtration, coagulation, flocculation, sedimentation and chlorination. Activated carbon and membrane processes can physically remove GSM and MIB, but do not destroy them, and ozone treatment can be expensive. Titanium dioxide (TiO2) photocatalysis has recently been demonstrated to rapidly degrade GSM and MIB. When the semiconductor catalyst is illuminated with ultraviolet light simultaneous oxidation and reduction reactions occur. Pollutants are broken down into mineral acids, carbon dioxide and water. This study was conducted to determine if TiO2 photocatalysis, using a pelleted form of TiO2 called Hombikat K01/C, was a suitable method for the treatment of potable water. Additionally an analytical method was developed to rapidily analyse the large number of samples generated. Two reactors, a bench scale batch reactor and pilot scale flow reactor, were developed and used to evaluate the efficacy of Hombikat K01/C TiO2 photocatalysis in degrading GSM. The batch reactor, containing Hombikat K01/C, was used to investigate the effect of numerous experimental variables on the photocatalysis of GSM, including initial substrate concentration, pH, light intensity, aeration rate, the presence of additional reactants, and catalysis conducted in deuterated water. GSM was rapidly degraded using the TiO2 batch reactor, with the rate of GSM degradation most affected by light intensity and additional reactants, though pH also had a notable effect. A kinetic isotope effect of 1.61 was observed for the destruction of GSM using Hombikat K01/C TiO2. The flow reactor was also found to efficiently degrade GSM in raw waters. The rate of GSM destruction was found to be significantly lowered by UV shielding of the catalyst, caused by constituents of raw the water used, and the presence of additional reactants. The pilot scale flow reactor was also successfully evaluated in Denmark using gesomin contaminated water from an eel farm

Orientador: Isabel Cristina Sales Fontes Jardim / Dissertação (mestrado) - Universidade Estadual de Campinas, Instituto de Quimica / Made available in DSpace on 2018-08-04T03:19:20Z (GMT). No. of bitstreams: 1 Faria_LeonardoJardimdaSilva_M.pdf: 547743 bytes, checksum: c807d29f792ecf6c57e17ca59816fdfe (MD5) Previous issue date: 2004 / Mestrado / Quimica Analitica / Mestre em Química

Oil spills, especially in water have happened throughout the years. The consequences from this kind of incident have always been a threat to marine life and take a lot of money and time to clean up. The forensic investigations of oil usually focus on oil spill in water, however, this kind of investigation can be applied on more areas, such as in sexual offense cases and arson. The oil from the crime scene and the oil from the suspected source are analyzed and compared to each other to see if the compositions match. The aim of this thesis was to optimize the clean-up process of heavy fuel oil (HFO) using solid-phase extraction (SPE) according to the European Committee for standardization (CEN) 15522-2 method. HFOs are black oils, containing particles and soot which will decrease injector performance. Thus, a cleanup procedure is attractive when analyzing such samples. The three factors of optimization in this study were elution volumes, solvents, and SPE sorbents.The SPE method used in this study was to use the cartridges as a filter; therefore, the samples were both loaded and eluted with an organic solvent, in this case dichloromethane (DCM) or dichloromethane/heptane (DCM/Hp). The gas chromatography mass spectrometry (GC-MS) analysis method used is described in Annex B in the CEN 15522-2 method.Concluding, increasing the eluent volume did not indicate improvement on the extraction method. In terms of the solvents, both dichloromethane and dichloromethane/heptane showed similar results. The percentage weathering plots (PW-plots) showed that the SPE sorbents (dual layer florisil/Na2SO4, florisil and silica gel sorbents) worked similar. The overall conclusion from this thesis work was that further optimization must be made before implementing the method.

Bifenilas policloradas (PCBs) são componentes de óleo ascarel, usado extensamente (no Brasil até os anos 80) como isolante em transformadores de energia devido às suas propriedades físico-químicas como estabilidade térmica e alta constante dielétrica. Apesar de ter sido proibido em todo o mundo devido à alta toxicidade dos PCBs presentes em sua composição, ainda resta grande quantidade de ascarel em circulação como resíduo \"passivo\" e resultante de contaminação em trocas dos fluidos dos transformadores, além de vazamentos. A principal forma de eliminação é por incineração, que, além de ser um processo caro, pode provocar a formação de compostos mais tóxicos, as dioxinas. Por isso é importante o monitoramento da concentração dessas substâncias, a fim de evitar maiores impactos ambientais na sua disposição, bem como em estudos de biodegradação. Esta matriz é extremamente complexa, o que torna a extração e determinação desses analitos um processo trabalhoso e difícil. Neste trabalho avaliaram-se métodos de extração e determinação de PCBs presentes na solução padrão comercial PCB Congener MIX 1, SUPELCO (PCBs 10, 28, 52, 138, 153 e 180). O desenvolvimento de métodos de extração (cromatografia em coluna, extração líquido-líquido (L-L), extração em fase sólida (SPE) e micro-extração em fase sólida - SPME) dos PCBs foi seguido da determinação, por cromatografia gasosa com detector por captura de elétrons (CG/DCE), em três matrizes diferentes: óleo ascarel, amostras provenientes de reatores anaeróbios em batelada e solo. Os métodos cuja purificação e extração diminuíram o efeito dos interferentes da matriz, como SPE - Sulfoxide, cromatografia em coluna de sílica e extração L-L com n-hexano foram validados pela avaliação dos seguintes parâmetros: linearidade e faixa de aplicação; precisão instrumental; limite de detecção, limite de quantificação e recuperação absoluta. O critério de escolha entre os métodos para extração dos PCBs do óleo que forneceram maior eficiência (cartucho SPE Sulfoxide e coluna de sílica gel, após lavagem ácida; método da adição de padrão, entre 1,0 e 4,0 mg L-1) deve considerar a disponibilidade de recursos, pois a sílica gel é mais viável economicamente do que o cartucho SPE. Os valores de R2 > 0,99 para o método de extração com sílica, mesmo tendo sido considerados apenas três pontos para a curva de calibração, atestam maior linearidade do que o método com SPE Sulfoxide (R2 entre 0,97 e 0,99). A extração L-L e determinação por CG/DCE dos PCBs (padronização interna) de amostras provenientes de reatores anaeróbios em batelada (aquosas, em matriz extremamente complexa com biomassa e espuma de poliuretano para imobilização de microrganismos) foram eficientes na faixa de concentração entre 0,05 e 0,5 mg L-1. Esse método foi adequado para monitorar PCBs em estudo de degradação anaeróbia e teste de adsorção dos PCBs em espuma; forneceu linearidade com R2 entre 0,93 e 0,96 e limites de detecção de 0,048 a 0,298 mg L-1, além de recuperação absoluta entre 14,1% e 110,7%. As condições testadas por SPME não permitiram a extração dos PCBs de óleo e de solo, principalmente devido à dessorção incompleta dos PCBs da fibra de polidimetil-siloxano, de 100 μm. / Polychlorinated biphenyls (PCBs) are components of ascarel, oil widely used as insulation (until the \'80s in Brazil) due to its physicochemical properties such as thermal stability and high dielectric constant. Despite having been banned worldwide due to the high toxicity of PCBs present in its composition, there are still lots of outstanding ascarel as \"passive\" residue and resulting contamination of fluids in transformers exchanges, plus leaks. The main form of disposal is incineration, which, besides being costly, can cause the formation of more toxic compounds, that is, dioxins. It is therefore important to monitor the concentration of these substances in order to prevent further environmental impacts in their disposal, as well as in studies of biodegradation. This is an extremely complex matrix, which makes the extraction and determination of this analytes very difficult and labor intensive. In this work we have evaluated methods of extraction and determination of the PCBs present in the standard solution Congener MIX 1, SUPELCO (PCBs 10, 28, 52, 138, 153 e 180). The extraction and cleanup developed methods which reduced the effects of interfering matrix as solid phase extraction (SPE) - Sulfoxide, column chromatography on silica and liquid-liquid (L-L) extraction with n-hexane, and solid phase microextraction (SPME) after determination of the PCBs by gas chromatography with electron capture detector (GC/ECD) were validated by assessing the following parameters: linearity and range of application; instrumental precision; detection limit; limit of quantification and absolute recovery. The criterion for choosing between the methods for extraction of PCBs from the oil with a higher efficiency (SPE cartridge Sulfoxide and silica gel column, after acid washing; using the standard addition method, between 1.0 and 4.0 mg L-1) must evaluate the availability resources, since the silica gel is more economically viable than the SPE cartridge. The R2 values > 0.99 for silica extraction method, even though it was considered only three points for the calibration curve, attested higher linearity than the method with SPE Sulfoxide (R2 between 0.97 and 0.99). The L-L extraction and determination by GC/ECD of the PCBs (internal standardization) of samples from batch anaerobic reactors (aqueous, in a very complex matrix with biomass and polyurethane foam for the immobilization of microorganisms) were efficient in the concentration range between 0.05 and 0.5 mg L-1. This method was suitable to monitor PCBs in anaerobic degradation studies and its adsorption on foam; provided R2 linearity between 0.93 and 0.96 and detection limits from 0.048 to 0.298 mg L-1, as well as absolute recovery between 14.1% and 110.7%. The conditions tested for SPME technique did not allow the extraction of the PCBs from the oil and soil, mainly due to the \"incomplete dessorption\" of PCBs from the polydimethylsiloxane fiber of 100 micron.

Bifenilas policloradas (PCBs) são componentes de óleo ascarel, usado extensamente (no Brasil até os anos 80) como isolante em transformadores de energia devido às suas propriedades físico-químicas como estabilidade térmica e alta constante dielétrica. Apesar de ter sido proibido em todo o mundo devido à alta toxicidade dos PCBs presentes em sua composição, ainda resta grande quantidade de ascarel em circulação como resíduo \"passivo\" e resultante de contaminação em trocas dos fluidos dos transformadores, além de vazamentos. A principal forma de eliminação é por incineração, que, além de ser um processo caro, pode provocar a formação de compostos mais tóxicos, as dioxinas. Por isso é importante o monitoramento da concentração dessas substâncias, a fim de evitar maiores impactos ambientais na sua disposição, bem como em estudos de biodegradação. Esta matriz é extremamente complexa, o que torna a extração e determinação desses analitos um processo trabalhoso e difícil. Neste trabalho avaliaram-se métodos de extração e determinação de PCBs presentes na solução padrão comercial PCB Congener MIX 1, SUPELCO (PCBs 10, 28, 52, 138, 153 e 180). O desenvolvimento de métodos de extração (cromatografia em coluna, extração líquido-líquido (L-L), extração em fase sólida (SPE) e micro-extração em fase sólida - SPME) dos PCBs foi seguido da determinação, por cromatografia gasosa com detector por captura de elétrons (CG/DCE), em três matrizes diferentes: óleo ascarel, amostras provenientes de reatores anaeróbios em batelada e solo. Os métodos cuja purificação e extração diminuíram o efeito dos interferentes da matriz, como SPE - Sulfoxide, cromatografia em coluna de sílica e extração L-L com n-hexano foram validados pela avaliação dos seguintes parâmetros: linearidade e faixa de aplicação; precisão instrumental; limite de detecção, limite de quantificação e recuperação absoluta. O critério de escolha entre os métodos para extração dos PCBs do óleo que forneceram maior eficiência (cartucho SPE Sulfoxide e coluna de sílica gel, após lavagem ácida; método da adição de padrão, entre 1,0 e 4,0 mg L-1) deve considerar a disponibilidade de recursos, pois a sílica gel é mais viável economicamente do que o cartucho SPE. Os valores de R2 > 0,99 para o método de extração com sílica, mesmo tendo sido considerados apenas três pontos para a curva de calibração, atestam maior linearidade do que o método com SPE Sulfoxide (R2 entre 0,97 e 0,99). A extração L-L e determinação por CG/DCE dos PCBs (padronização interna) de amostras provenientes de reatores anaeróbios em batelada (aquosas, em matriz extremamente complexa com biomassa e espuma de poliuretano para imobilização de microrganismos) foram eficientes na faixa de concentração entre 0,05 e 0,5 mg L-1. Esse método foi adequado para monitorar PCBs em estudo de degradação anaeróbia e teste de adsorção dos PCBs em espuma; forneceu linearidade com R2 entre 0,93 e 0,96 e limites de detecção de 0,048 a 0,298 mg L-1, além de recuperação absoluta entre 14,1% e 110,7%. As condições testadas por SPME não permitiram a extração dos PCBs de óleo e de solo, principalmente devido à dessorção incompleta dos PCBs da fibra de polidimetil-siloxano, de 100 μm. / Polychlorinated biphenyls (PCBs) are components of ascarel, oil widely used as insulation (until the \'80s in Brazil) due to its physicochemical properties such as thermal stability and high dielectric constant. Despite having been banned worldwide due to the high toxicity of PCBs present in its composition, there are still lots of outstanding ascarel as \"passive\" residue and resulting contamination of fluids in transformers exchanges, plus leaks. The main form of disposal is incineration, which, besides being costly, can cause the formation of more toxic compounds, that is, dioxins. It is therefore important to monitor the concentration of these substances in order to prevent further environmental impacts in their disposal, as well as in studies of biodegradation. This is an extremely complex matrix, which makes the extraction and determination of this analytes very difficult and labor intensive. In this work we have evaluated methods of extraction and determination of the PCBs present in the standard solution Congener MIX 1, SUPELCO (PCBs 10, 28, 52, 138, 153 e 180). The extraction and cleanup developed methods which reduced the effects of interfering matrix as solid phase extraction (SPE) - Sulfoxide, column chromatography on silica and liquid-liquid (L-L) extraction with n-hexane, and solid phase microextraction (SPME) after determination of the PCBs by gas chromatography with electron capture detector (GC/ECD) were validated by assessing the following parameters: linearity and range of application; instrumental precision; detection limit; limit of quantification and absolute recovery. The criterion for choosing between the methods for extraction of PCBs from the oil with a higher efficiency (SPE cartridge Sulfoxide and silica gel column, after acid washing; using the standard addition method, between 1.0 and 4.0 mg L-1) must evaluate the availability resources, since the silica gel is more economically viable than the SPE cartridge. The R2 values > 0.99 for silica extraction method, even though it was considered only three points for the calibration curve, attested higher linearity than the method with SPE Sulfoxide (R2 between 0.97 and 0.99). The L-L extraction and determination by GC/ECD of the PCBs (internal standardization) of samples from batch anaerobic reactors (aqueous, in a very complex matrix with biomass and polyurethane foam for the immobilization of microorganisms) were efficient in the concentration range between 0.05 and 0.5 mg L-1. This method was suitable to monitor PCBs in anaerobic degradation studies and its adsorption on foam; provided R2 linearity between 0.93 and 0.96 and detection limits from 0.048 to 0.298 mg L-1, as well as absolute recovery between 14.1% and 110.7%. The conditions tested for SPME technique did not allow the extraction of the PCBs from the oil and soil, mainly due to the \"incomplete dessorption\" of PCBs from the polydimethylsiloxane fiber of 100 micron.

This diploma thesis is focused on the issue of nonylphenol, degradation product of surfactants. Nonylphenol however most often arises in wastewater treatment plants predominantly during the microbial degradation of nonylphenol ethoxylates used in industry. It is a substance highly bioaccumulative, toxic predominantly to aquatic organisms. Furthermore, it belongs among hormone disruptors. The detailed research was prepared, on the basis which experimental part of diploma thesis was solved. Nonylphenol was determined in samples of the wastewater. The solid phase extraction (SPE) was used for the isolation of the analyte and purification of the extract. The final determination was performed on the gas chromatography with tandem mass spectrometry with time of flight analyzer (TOF). All steps of the preanalytical and the analytical procedure were optimized.

This diploma thesis deals with the determination of macrolide antibiotics in wastewater, especially with erythromycin, clarithromycin and roxithromycin. In this time are these pharmaceuticals prescribed quite frequently. Solid phase extraction (SPE) was used for the isolation and the purification of selected analytes from an aqueous matrix; as the suitable procedure was found the using Oasis HLB cartridges. High performance liquid chromatography with mass spectrometry detection (HPLC-MS) was optimized for its analysis of selected pharmaceuticals. The optimized method was used for the determination of pharmaceuticals in real water samples, which was taken at the inflow and the outflow of the urban wastewater treatment plant in Brno-Modřice.

A ocorrência de fármacos residuais no meio ambiente pode levar a efeitos adversos, tanto em organismos aquáticos como em terrestres. Os fármacos, tanto humanos como de uso veterinário, são absorvidos pelo organismo e estão sujeitos a reações metabólicas e, uma quantidade significativa dessas substâncias, tanto a original como seus metabólitos, são excretadas. Por não serem facilmente biodegradáveis, terem propriedades farmacológicas danosas quando administrados indevidamente, através de água contaminada, é crescente a preocupação com o destino destes fármacos residuais, principalmente com relação à avaliação de risco ambiental. A ocorrência destes resíduos, principalmente em águas superficiais e sistemas de abastecimento, vem sendo objeto de estudos em diversos países, principalmente na Europa. Por isso, a detecção, a eliminação e a investigação do destino destes compostos estrógenos em ecossistemas aquáticos têm tido prioridade na química ambiental. Estes produtos são encontrados nos corpos d\'água em baixas concentrações, de \'mü\'g L-1 a \'eta\'g L-1 e, mesmo assim, podem afetar os organismos por meio da bioacumulação. Estudos toxicológicos relacionados a efeitos crônicos em organismos expostos, são escassos. O objetivo do projeto foi adaptar e validar a metodologia analítica, e monitorar a presença de resíduos de hormônios nas águas dos Rios Corumbataí e Piracicaba e amostras de água de abastecimento da cidade de Piracicaba, SP, Brasil. Foram coletadas amostras de água bruta dos Rios Piracicaba e Corumbataí e água de abastecimento residencial da cidade de Piracicaba, SP, no período de novembro de 2007 a abril de 2009. Dentre os hormônios estudados estão o 17\'alfa\'-etinilestradiol (17\'alfa\'-EE2), 17\'beta\'-estradiol (17\'beta\'-E2) e estriol (E3). O método foi baseado na extração em fase sólida (SPE) e cromatografia líquida de alta eficiência (HPLC-DAD) / The occurrence of drug residues in the environment may lead to adverse effects, both on land and aquatic organisms. The drugs, for human and veterinary use, are absorbed by the organism and are subjected to metabolic reactions and a significant amount of these substances, both the original and its metabolites are excreted. By being not easily biodegradable and by having harmful pharmacological properties when administered through contaminated water, there is a growing concern about the fate of these residual drugs, especially in respect to the assessment of environmental risks. The occurrence of these residues, especially in surface Waters and water supplies has been the subject of studies in several countries, mainly in Europe. Therefore, detection, investigation and disposal of the fate of these estrogens compounds in aquatic ecosystems have a high priority in the field of environmental chemistry. These products are found in water bodies in low concentrations, from \'mü\'g L-1 a \'eta\'g L-1 and can still affect the organisms due to bioaccumulation. Toxicological studies related to chronic effects in the exposed organisms are scarce. The goals of this project was to adapt and validate the analytical methodology, and monitor the presence of hormone residues in the Waters of the Corumbataí and Piracicaba rivers and samples of water supply from the city of Piracicaba, SP, Brazil. We collected samples of raw water from the rivers of Piracicaba and Corumbataí and residential water supply from the city of Piracicaba in the period November 2007 to April 2009. Among the hormones studied are the 17\'alfa\'-ethinylestradiol (17\'alfa\'-EE2), 17\'beta\'-estradiol (17\'beta\'-E2) and estriol (E3). The method is based on solid phase extraction (SPE) and high performance liquid chromatography (HPLC-DAD)

A ocorrência de fármacos residuais no meio ambiente pode levar a efeitos adversos, tanto em organismos aquáticos como em terrestres. Os fármacos, tanto humanos como de uso veterinário, são absorvidos pelo organismo e estão sujeitos a reações metabólicas e, uma quantidade significativa dessas substâncias, tanto a original como seus metabólitos, são excretadas. Por não serem facilmente biodegradáveis, terem propriedades farmacológicas danosas quando administrados indevidamente, através de água contaminada, é crescente a preocupação com o destino destes fármacos residuais, principalmente com relação à avaliação de risco ambiental. A ocorrência destes resíduos, principalmente em águas superficiais e sistemas de abastecimento, vem sendo objeto de estudos em diversos países, principalmente na Europa. Por isso, a detecção, a eliminação e a investigação do destino destes compostos estrógenos em ecossistemas aquáticos têm tido prioridade na química ambiental. Estes produtos são encontrados nos corpos d\'água em baixas concentrações, de \'mü\'g L-1 a \'eta\'g L-1 e, mesmo assim, podem afetar os organismos por meio da bioacumulação. Estudos toxicológicos relacionados a efeitos crônicos em organismos expostos, são escassos. O objetivo do projeto foi adaptar e validar a metodologia analítica, e monitorar a presença de resíduos de hormônios nas águas dos Rios Corumbataí e Piracicaba e amostras de água de abastecimento da cidade de Piracicaba, SP, Brasil. Foram coletadas amostras de água bruta dos Rios Piracicaba e Corumbataí e água de abastecimento residencial da cidade de Piracicaba, SP, no período de novembro de 2007 a abril de 2009. Dentre os hormônios estudados estão o 17\'alfa\'-etinilestradiol (17\'alfa\'-EE2), 17\'beta\'-estradiol (17\'beta\'-E2) e estriol (E3). O método foi baseado na extração em fase sólida (SPE) e cromatografia líquida de alta eficiência (HPLC-DAD) / The occurrence of drug residues in the environment may lead to adverse effects, both on land and aquatic organisms. The drugs, for human and veterinary use, are absorbed by the organism and are subjected to metabolic reactions and a significant amount of these substances, both the original and its metabolites are excreted. By being not easily biodegradable and by having harmful pharmacological properties when administered through contaminated water, there is a growing concern about the fate of these residual drugs, especially in respect to the assessment of environmental risks. The occurrence of these residues, especially in surface Waters and water supplies has been the subject of studies in several countries, mainly in Europe. Therefore, detection, investigation and disposal of the fate of these estrogens compounds in aquatic ecosystems have a high priority in the field of environmental chemistry. These products are found in water bodies in low concentrations, from \'mü\'g L-1 a \'eta\'g L-1 and can still affect the organisms due to bioaccumulation. Toxicological studies related to chronic effects in the exposed organisms are scarce. The goals of this project was to adapt and validate the analytical methodology, and monitor the presence of hormone residues in the Waters of the Corumbataí and Piracicaba rivers and samples of water supply from the city of Piracicaba, SP, Brazil. We collected samples of raw water from the rivers of Piracicaba and Corumbataí and residential water supply from the city of Piracicaba in the period November 2007 to April 2009. Among the hormones studied are the 17\'alfa\'-ethinylestradiol (17\'alfa\'-EE2), 17\'beta\'-estradiol (17\'beta\'-E2) and estriol (E3). The method is based on solid phase extraction (SPE) and high performance liquid chromatography (HPLC-DAD)