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Polychlorinated biphenyls (PCBs) are widespread persistent organic pollutants. The metabolism of PCBs by various organisms involves many steps that can lead to the formation of a wide range of metabolites. These metabolites frequently exhibit a toxicity and biodegradability different than the parent compounds. There is currently little information available about the biological effects of PCB hydroxylated metabolites that can be generated by various organisms and potentially released into the environment. The objective of the present research is to compare the toxicity of selected PCB congeners and their corresponding mono-hydroxylated metabolites. To achieve this objective, the following specific aims were performed: (1) to determine the effect of selected PCBs and PCB hydroxylated metabolites on the growth rate of a model PCB-degrading bacterium, Burkholderia xenovorans LB 400, (2) to determine the microbial toxicity of PCBs and PCB metabolites using the bioluminescent assay Microtox®, and (3) to determine the estrogenicity of PCBs and PCB metabolites using the Yeast Estrogen Screen assay (YES). The effects of a range of PCBs (PCB-2, -3, -8, -9, -30, -35, -36, -39, -61, -68, and -79) and their mono-hydroxylated metabolites on the growth rate of the PCB degrader, Burkholderia xenovorans LB400, were recorded. The results showed that the parent PCBs (50 mg L-1) did not affect the growth rate of LB400 although their hydroxylated metabolites strongly inhibited microbial growth. Using Microtox® assay, Parent PCBs (50 mg L-1) did not exhibit observable toxicity, while their hydroxylated metabolites showed a high level of toxicity (EC50 ranges from 2 mg L-1 to 46 mg L-1). Results using the YES assay also showed that the estrogenicity of hydroxylated metabolites of PCBs (50 mg L-1) was higher than the parent PCBs. The results obtained from the present study show that mono-hydroxylated metabolites of PCBs are more toxic than the corresponding parent PCBs. Because hydroxylated PCB derivatives are produced by a range of organisms and potentially released into the environment, this work raises new concerns associated with the environmental fate of PCBs. / Civil Engineering

Amongst the polar organic compounds occurring in unrefined and refined crude oils and the associated polluted production waters, complex mixtures of acids, known historically as naphthenic acids (NAs), have achieved prominence. This is particularly because NAs have been designated a toxicant class of concern in the oil sands process-affected water (OSPW) that has accumulated in vast quantities following exploitation of the oil sands of Northern Alberta, Canada in recent years. However, though there have been calls for NAs to be added to pollutant inventories, at the initiation of the current study, little knowledge existed of the exact composition of refined or unrefined NAs. The overall aim of the current study was therefore to identify individual NAs in refined (commercial) and unrefined (e.g. oil sands process-derived) complex mixtures of acids and then to assess the toxicity of any identified NAs. Individual NAs were tentatively identified by interpretation of the electron ionisation mass spectra of methyl ester derivatives, following comprehensive multidimensional gas chromatography-mass spectrometry (GCxGC-MS). Reference acids were then either purchased, or more commonly, where they were not commercially-available, synthesised, mainly by micro-hydrogenation methods, for co-chromatography and comparison of mass spectra of methyl esters with those of unknowns. The synthetic NAs, purified to >97% were then subjected to toxicological assessments using the Microtox™ assay. In all, 34 compounds were obtained pure enough for testing. Microtox results revealed that the toxicity endpoint (50% Inhibition Concentration, IC50) was between 0.004 and 0.7 mM. Exponential and other correlations were noted between carbon number and toxicity in several of the structural groups of acids assayed, which may be beneficial for predictions of toxicity of non-synthesised acids. Although n-hexanoic acid (IC50 0.7 mM) had the lowest toxicity, adamantane-type acids were the least toxic as a group overall. Conversely, the decahydronaphthalene (decalin)-type acids had the largest range of toxicities (IC50 0.004 to 0.3 mM) and the most toxic acid assayed was 3-decalin-1-yl-propanoic acid. According to USEPA guidelines many individual acids can be said to show low to medium toxicity. Since the acids in commercial and unrefined NAs occur in complex mixtures, an attempt was also made to assess mixture toxicity. Mixtures of individual structural groups of acids (e.g. acyclic isoprenoid acids, n-acids) and a mixture of all 34 acids were assessed. Apart from the adamantane sub-group of acids, all of the mixtures showed toxicities lower than the sum of the parts when calculated using equations for Concentration Addition and Model Deviation Ratios (simply the predicted IC50/Observed IC50). A hypothesis that achievement of a critical micelle concentration is required to produce toxicity was proposed to explain the lower than expected results. Some of the mass spectra of NA present in the commercial and unrefined mixtures were inconsistent with those of any of the alicyclic acids synthesised or purchased. These were hypothesised to be aromatic acids. Fractionation experiments of the NA mixtures using silver ion thin layer chromatography and solid phase extraction (Ag+TLC and Ag+SPE) were carried out in order to provide further evidence for aromatic acids. Ag+TLC allowed separation of a methylated NA mixture from OSPW into three distinct fractions; Ag+SPE resulted in eleven fractions, through the use of a wider range of solvents and differential solvent ratios. Analysis of the fractions by GC-MS revealed that each fraction was largely still made up of unresolved acids (as esters), although one or two fractions revealed some resolved acids. Use of averaged mass spectra and mass chromatography on each fraction revealed further resolved chromatographic peaks and associated interpretable mass spectra. Each of eight of the eleven sub-fractions were examined by GC-MS, in some cases by GCxGC-MS, and all by infrared spectroscopy, ultraviolet visible spectrophotometry and elemental analysis. A number of structures were proposed for the aromatic acids, including those with sulphur-containing moieties. It was noted that far from being minor components, aromatic acids comprised ca.25-40% of the OSPW acid extracts.

Ce travail de recherche porte sur l'application d'un procédé électrochimique d'oxydation avancée, le procédé électro-Fenton, au traitement des eaux usées contenant des polluants organiques persistants tels que les herbicides. En fait, le radical hydroxyle qui est un oxydant fort est généré in situ de manière électrocatalytique. Ce radical est capable d'oxyder n'importe quel molécule organique jusqu'à la minéralisation (transformation en CO2 et H2O).La dégradation/minéralisation de trois herbicides (atrazine, mesotrione et sulcotrione) a fait l'objet de ce travail. L'atrazine est un herbicide qui a été très largement utilisé dans le passé et interdit récemment en France à raison de son impact négatif sur l'environnement. L'atrazine constitue un polluant chroniques des eaux de surfaces et souterrains des deux dernières décennies. L'atrazine et ses métabolites seront présents dans les eaux encore pendant plusieurs années. L'atrazine est bien connu comme herbicide problématique quant à leur traitement. L'atrazine est une des molécules rare qui résiste à la minéralisation par les procédés d'oxydation avancée. Mesotrione et sulcotrione se sont des molécules conçus pour remplacer l'atrazine en tant que herbicides. Après avoir optimisé les paramètres opératoires du procédé électro-Fenton (nature et concentration du catalyseur, l'utilisation d'une anode Pt et une anode BDD en diamant dopé au bore, etc.) afin d'augmenter son efficacité, nous l'avons appliqué au traitement des solutions aqueux des polluants organiques. En premier lieu, nous avons identifié et effectué le suivi quantitatif des intermédiaires réactionnels aromatiques et aliphatiques formés lors du traitement. La libération des ions minéraux a été mise en évidence par chromatographie et leur évolution au cours de l'électrolyse a été suivie. L'efficacité de minéralisation des solutions traitées a été déterminée par l'analyse du carbone organique total. Dans le cas de l'atrazine, un taux de minéralisation de 96 % a été obtenu. Un taux si élevé n'est jamais rapporté par un procédé d'oxydation avancée. L'étude cinétique de la dégradation des herbicides étudiés a permis de déterminer les constantes de réaction apparentes de dégradation par les radicaux hydroxyles. Les constantes de vitesse absolue (kabs) de réaction des radicaux hydroxyles sur les herbicides étudiés ont été mesurées par la mise en oeuvre de la méthode de cinétique de compétition. Les valeurs de ( (1,53 x 108 M-1 s-1 ) ,(1.01 x 109 M-1 s-1 ) et ( 8.20 x 108 M-1 s-1)ont été trouvées respectivement pour l'atrazine, la sulcotrione et la Mesotrione

En aquest estudi, la toxicitat de diversos metalls pesants i l'arsènic va ser analitzada utilitzant diferents models biològics.En la primera part d'aquest treball, el bioassaig de toxicitat Microtox, el qual està basat en la variació de l'emissió lumínica del bacteri luminiscent Vibrio fischeri, va ser utilitzat per establir les corbes dosi-resposta de diferents elements tòxics com el Zn(II), Pb(II), Cu(II), Hg(II), Ag(I), Co(II), Cd(II), Cr(VI), As(V) i As(III) en solucions aquoses. Els experiments es varen portar a terme a pH 6.0 i 7.0 per tal de mostrar que el pH pot influir en la toxicitat final mesurada d'alguns metalls degut als canvis relacionats amb la seva especiació química. Es varen trobar diferents tipus de corbes dosi-resposta depenent del metall analitzat i el pH del medi. En el cas de l'arsènic, l'efecte del pH en la toxicitat de l'arsenat i l'arsenit es va investigar utilitzant l'assaig Microtox en un rang de pHs comprès entre pH 5.0 i 9.0. Els valors d'EC50 determinats per l'As(V) disminueixen, reflectint un augment de la toxicitat, a mesura que el pH de la solució augmenta mentre que, en el cas de l'As(III), els valors d'EC50 quasi bé no varien entre pH 6.0 i 8.0 i només disminueixen a pH 9.0. HAsO42- i H2AsO3- es varen definir com les espècies més tòxiques. Així mateix, una anàlisi estadística va revelar un efecte antagònic entre les espècies químiques d'arsenat que es troben conjuntament a pH 6.0 i 7.0.D'altra banda, els resultats de dos mètodes estadístics per predir la toxicitat i les possibles interaccions entre el Co(II), Cd(II), Cu(II), Zn(II) i Pb(II) en mescles binàries equitòxiques es varen comparar amb la toxicitat observada sobre el bacteri Vibrio fischeri. L'efecte combinat d'aquests metalls va resultar ser antagònic per les mescles de Co(II)-Cd(II), Cd(II)-Zn(II), Cd(II)-Pb(II) i Cu(II)-Pb(II), sinèrgic per Co(II)-Cu(II) i Zn(II)-Pb(II) i additiu en els altres casos, revelant un patró complex de possibles interaccions. L'efecte sinèrgic de la combinació Co(II)-Cu(II) i la forta disminució de la toxicitat del Pb(II) quan es troba en presència de Cd(II) hauria de merèixer més atenció quan s'estableixen les normatives de seguretat ambiental.La sensibilitat de l'assaig Microtox també va ser determinada. Els valors d'EC20, els quals representen la toxicitat llindar mesurable, varen ser determinats per cada element individualment i es va veure que augmenten de la següent manera: Pb(II) < Ag(I) < Hg(II) &#61627; Cu(II) < Zn(II) < As(V) < Cd(II) &#61627; Co(II) < As(III) < Cr(VI). Aquests valors es varen comparar amb les concentracions permeses en aigues residuals industrials establertes per la normativa oficial de Catalunya (Espanya). L'assaig Microtox va resultar ser suficientment sensible per detectar els elements assajats respecte a les normes oficials referents al control de la contaminació, excepte en el cas del cadmi, mercuri, arsenat, arsenit i cromat. En la segona part d'aquest treball, com a resultats complementaris dels resultats previs obtinguts utilitzant l'assaig de toxicitat aguda Microtox, els efectes crònics del Cd(II), Cr(VI) i As(V) es varen analitzar sobre la taxa de creixement i la viabilitat en el mateix model biològic. Sorprenentment, aquests productes químics nocius varen resultar ser poc tòxics per aquest bacteri quan es mesura el seu efecte després de temps d'exposició llargs. Tot i això, en el cas del Cr(VI), l'assaig d'inhibició de la viabilitat va resultar ser més sensible que l'assaig de toxicitat aguda Microtox. Així mateix, també va ser possible observar un clar fenomen d'hormesis, especialment en el cas del Cd(II), quan s'utilitza l'assaig d'inhibició de la viabilitat. A més a més, diversos experiments es varen portar a terme per intentar explicar la manca de toxicitat de Cr(VI) mostrada pel bacteri Vibrio fischeri. La resistència mostrada per aquest bacteri podria ser atribuïda a la capacitat d'aquest bacteri de convertir el Cr(VI) a la forma menys tòxica de Cr(III). Es va trobar que aquesta capacitat de reducció depèn de la composició del medi de cultiu, de la concentració inicial de Cr(VI), del temps d'incubació i de la presència d'una font de carboni. En la tercera part d'aquest treball, la línia cel·lular humana HT29 i cultius primaris de cèl·lules sanguínies de Sparus sarba es varen utilitzar in vitro per detectar la toxicitat llindar de metalls mesurant la sobreexpressió de proteines d'estrès. Extractes de fangs precedents de diverses plantes de tractament d'aigues residuals i diferents metalls, individualment o en combinació, es varen analitzar sobre cultius cel·lulars humans per avaluar el seu efecte sobre la taxa de creixement i la capacitat d'induir la síntesi de les proteïnes Hsp72 relacionades amb l'estrès cel·lular. No es varen trobar efectes adversos significatius quan els components s'analitzen individualment. Nogensmenys, quan es troben conjuntament, es produeix un afecte advers sobre tan la taxa de creixement com en l'expressió de proteins d'estrès. D'altra banda, cèl·lules sanguínies procedents de Sparus sarba es varen exposar in vitro a diferents concentracions de cadmi, plom i crom. La proteïna d'estrès HSP70 es va sobreexpressar significativament després de l'exposició a concentracions tan febles com 0.1 &#61549;M. Sota les nostres condicions de treball, no es va evidenciar una sobreexpressió de metal·lotioneïnes. Nogensmenys, les cèl·lules sanguínies de peix varen resultar ser un model biològic interessant per a ser utilitzat en anàlisis de toxicitat. Ambdós models biològics varen resultar ser molt adequats per a detectar acuradament la toxicitat produïda per metalls. En general, l'avaluació de la toxicitat basada en l'anàlisi de la sobreexpressió de proteïnes d'estrès és més sensible que l'avaluació de la toxicitat realitzada a nivell d'organisme.A partir dels resultats obtinguts, podem concloure que una bateria de bioassaigs és realment necessària per avaluar acuradament la toxicitat de metalls ja que existeixen grans variacions entre els valors de toxicitat obtinguts emprant diferents organismes i molts factors ambientals poden influir i modificar els resultats obtinguts. / In this study, the toxicity of some metals and arsenic was investigated using three different biological models. In the first part of this work, the Microtox® bioassay, which is based on variation in light emission by Vibrio fischeri luminescent bacteria, was used to establish dose-response curves for several toxic elements, namely, Zn(II), Pb(II), Cu(II), Hg(II), Ag(I), Co(II), Cd(II), Cr(VI), As(V), and As(III), in aqueous solutions. Experiments were carried out at either pH 6.0 or pH 7.0 to indicate that pH may influence the measured toxicity of some elements due to pH-related changes in their chemical speciation. Different types of dose-response curves were found depending on the analyzed metal and pH. In the case of arsenic, effect of pH on either arsenate or arsenite toxicity, was investigated using the Microtox® bioassay within a 5.0 - 9.0 pH range. EC50 values for As(V) were found to decrease, reflecting an increase in toxicity, as pH became basic, whereas in the case of As(III), EC50 values were almost unchanged within a 6.0 - 8.0 pH range and lowered at pH 9.0 only. HAsO42- and H2AsO3- were found to be the most toxic species. A statistical approach revealed an antagonistic effect between the arsenate chemical species found in combination at pH 6.0 or 7.0.On the other hand, results from two mathematical approaches to predict the toxicity of all the possible binary equitoxic mixtures of Co(II), Cd(II), Cu(II), Zn(II), and Pb(II) were compared to the observed toxicity of these mixtures to Vibrio fischeri bacteria. Combined effect of the metals was found to be antagonistic for Co(II)-Cd(II), Cd(II)-Zn(II), Cd(II)-Pb(II), and Cu(II)-Pb(II), synergistic for Co(II)-Cu(II) and Zn(II)-Pb(II) and merely additive in other cases, revealing a complex pattern of possible interactions. The synergistic effect of the Co(II)-Cu(II) combination and the strong decrease of Pb(II) toxicity when in the presence of Cd(II) should deserve much attention when establishing environmental safety regulations. Microtox bioassay sensitivity was also analyzed. EC20 values, which represent a measurable threshold of toxicity, were determined for each element individually and were found to rank as Pb(II) < Ag(I) < Hg(II) &#61627; Cu(II) < Zn(II) < As(V) < Cd(II) &#61627; Co(II) < As(III) < Cr(VI). These values were compared to the concentration levels allowed in industrial wastewater according to the official regulations in Catalonia (Spain). It appears that the Microtox® test is sensitive enough to detect the tested elements with respect to official regulations dealing with pollution control, with the exception of cadmium, mercury, arsenate, arsenite and chromate.In the second part of this work, as a complement to previous results obtained using the standard Microtox® acute toxicity test, the long-term effects of Cd(II), Cr(VI), and As(V) were studied on growth rate and viability of the same biological model. Surprisingly, these poisonous chemicals were found not to be very toxic to these bacteria when measuring their effect on viability or growth after long periods of exposure. Nevertheless, in the case of Cr(VI), the inhibition viability assay resulted to be more sensitive than the Microtox acute toxicity test was. Interestingly, it was possible to observe a clear hormesis phenomenon, especially for Cd(II), under the conditions of the viability assay. In addition, several experiments were performed as an attempt to explain the lack of Cr(VI) toxicity shown by Vibrio fischeri bacteria. The resistance shown by Vibrio fischeri bacteria could be attributed to the capacity of the bacteria to convert Cr(VI) ions into less toxic Cr(III) ions. This capacity of reduction was found to depend on culture medium composition, initial concentration of chromium, incubation time, and the presence of a carbon source. In the third part of this work, the HT29 human cell line and primary cultures of Sparus sarba blood cells were used in vitro to detect metal toxicity thresholds by measuring the overexpression of stress proteins. Sludge extracts from several wastewater treatment plants and metals, individually or in combination, were tested on human cultured cells for evaluating their ability to affect the growth rate and trigger a synthesis of the stress-related HSP72i proteins. No significant adverse effects were found when given individually. When given in combination, they were however found to affect both cell growth and stress proteins expression. On the other hand, blood cells freshly collected from Sparus sarba were exposed in vitro to different concentrations of cadmium, lead or chromium(VI). HSP70 stress protein was significantly overexpressed after exposure to a metal concentration as low as 0.1 µM. Under our experimental conditions, no overexpression of metallothioneins was evidenced. Nevertheless, fish blood cells appear as an interesting biological model for experimental toxicology.Both biological models were found convenient to detect toxicity produced by metals. In general, evaluation of toxicity based on stress proteins overexpression was found to be more sensitive than evaluation of toxicity performed at the organism level.Based on the results, it can be concluded that a battery of bioassays is necessary to accurately evaluate toxicity of metals since important variations between different organisms can be found and a lot of environmental factors may influence as well as modify the obtained results.

Made available in DSpace on 2016-06-02T19:31:43Z (GMT). No. of bitstreams: 1 2493.pdf: 1820155 bytes, checksum: c4fbdc0a3fdb7a9316ba5c6c6a6905c8 (MD5) Previous issue date: 2009-05-15 / Universidade Federal de Sao Carlos / The objective of the present dissertation was to make a toxicity assessment of the application of calcium nitrate solution as a remediation procedure for sediments of a eutrophic aquatic ecosystem. The study was carried out using microcosms with superficial sediments and water from sediment-water interface of the Ibirité Reservoir located in the metropolitan area of Belo Horizonte (Minas Gerais, SE Brazil). The experiment lasted 135 days and the following treatment or incubation periods were applied: t=0, t=5, t=10, t=25, t=50, t=85 and t=135 days. In each period, one controlmicrocosm and three treatment-microcosms were disassembled and, chemically and ecotoxicologically analyzed. The organisms Ceriodaphnia silvestrii and Vibrio fischeri (Microtox® System) were used for the acute toxicity assessment of the water from sediment-water interface and the pore water of sediments, whereas the organism Chironomus xanthus was used for the toxicity assessment of bulk sediment. The toxicity tests were run in parallel with chemical analyzes of dissolved inorganic nitrogen species (nitrate, nitrate and ammonium), sulfate, and metals in the interface sediment-water and interstitial water samples. Acid volatile sulfide (AVS), simultaneously extracted metal (SEM) and potentially bioavailable metals were analyzed in bulk sediment. The overall results indicate that nitrate whose concentration reached 1,200 mg N-NO3 - L-1 in sediment pore water samples from treatment-microcosms is the most probable compound causing toxicity to the tests organisms. For Chironomus xanthus sediments were deleterious to the exposed organisms in all microcosm run, except in the period of t= 135 days. For the experimental conditions of this work, the application of calcium nitrate as a remediation procedure for sediments from Ibirité Reservoir indicated to be inadequate from the ecotoxicological pint of view. / O presente trabalho visou à avaliação da toxicidade da aplicação de solução de nitrato de cálcio, como procedimento de intervenção para remediação de sedimentos de um ambiente aquático eutrofizado. O estudo foi realizado através de microcosmos com sedimento e água de interface sedimento-água da Represa Ibirité, situada na região metropolitana de Belo Horizonte (Minas Gerais, Brasil). Os experimentos tiveram a duração total de 135 dias, divididos nos tempos de tratamento ou incubação de: t=0, t=5; t=10; t=25; t=50; t=85 e t=135 dias. Em cada tempo de tratamento foram analisados um microcosmo-controle e três microcosmostratamento. Os organismos Ceriodaphnia silvestrii e Vibrio fischeri (Sistema Microtox®) foram utilizados para avaliação da toxicidade aguda das águas de interface sedimento-água e intersticial dos sedimentos, enquanto o organismo Chironomus xanthus para avaliação do sedimento integral. Em paralelo aos testes de toxicidade foram realizadas análises químicas da série nitrogenada (nitrato, nitrito e amônia), sulfato, e metais nas amostras de água de interface sedimento-água e intersticial dos sedimentos, sulfetos volatilizáveis por acidificação (SVA), metais extraídos simultaneamente (MES) e metais potencialmente biodisponíveis nos sedimentos. Os resultados mostraram que o nitrato, chegando a concentração superior a 1.200 mg N-NO3 - L-1 nas amostras de água intersticial dos sedimentos dos microcosmos-tratamentos, foi considerado o causador mais provável da toxicidade das amostras dos microcosmos-tratamento para os organismos-teste empregados. Para o organismo Chironomus xanthus, os sedimentos em tratamento foram deletérios aos organismos expostos em todos os tempos de incubação, exceto no tempo t=135 dias. Estritamente do ponto de vista ecotoxicológico e para as condições experimentais deste trabalho, a aplicação do nitrato como forma de intervenção para remediação dos sedimentos da Represa Ibirité não se mostrou adequada.

This project focus on investigating the dissolution of low water-soluble intermediate organic compounds called active pharmaceutical ingredients (API) and organic substances that are manufactured by a pharmaceutical company, Cambrex Karlskoga in Sweden. Several dissolution methods were used and evaluated using methods including total organic carbon (TOC), chemical oxygen demand (COD), biochemical oxygen demand (BOD) and Microtox toxicity test. The selection of solvents were based on previous studies and specifications from the Swedish Institute of Standards, SIS.The performance of eight solvents for different organic substances were evaluated using the above mentioned methods. Solvents that are highly volatile and have low solubility in water were excluded. Therefore, dimethyl sulfoxide (DMSO), dimethylformamide (DMF) and Pluronic F-68, that had highest water solubility, low acute toxicity and not degradable by microorganisms, were further used to dissolve four organic substances. Furthermore, DMSO and DMF were then also used to dissolve four censored chemicals with addition of physical treatment and solvent mixtures (DMF:DMSO with ratio 1:2).Results from each method were discussed and statistical tests were also performed in order to compare different dissolution methods. In addition, quality control and quality assurance were made in order to ensure the quality of measured values from analytical methods. Four organic substances were dissolve in DMSO, DMF and Pluronic F-68 with dissolution ≥79% using six ratios of DMSO and DMF and five ratios of Pluronic F-68 which were analyzed using TOC. Physical treatment increased dissolution of two APIs with 40%. Using BOD, para-aminobenzonic acid (PABA) and 5-nitroisophthalic acid (5-NIPA) had values higher than the guideline values, which indicate high biodegradability of these organic substances. PABA, 5-NIPA and bupivacaine base were acute toxic where PABA showed EC50 values of 27.9 mg/L using DMSO and 36.0 mg/L using DMF, and EC50 values of 5-NIPA were 102 mg/L using DMSO and 84.0 mg/L using DMF, and bupivacaine base had EC50 value of 174 mg/L using solvent mixture (DMF:DMSO with ratio 1:2). With increasing amount of Pluronic F-68, 5-NIPA had increased values of EC50, thereby Pluronic F-68 was not appropriate to use.In conclusion, DMSO and DMF were most appropriate solvents to use in order to dissolve APIs and organic substances with analyte: DMSO ratio of 1:0.5 and analyte: DMF ratio of 1:0.25. In addition, physical treatment could be used in order to increase dissolution of the APIs.