RESUMEN
Selectively and effectively for removal of tetracycline (TC) and its related antibiotic resistance gene from food wastewater matrix with high-salt and high COD characteristics is highly desirable. In this work, novel schwertmannite/graphene oxide (SCH/GO) nanocomposites were synthesized through a facile oxidation-coprecipitation method. The SCH/GO nanocomposites were characterized by TEM, XRD, BET, PL, DRS, XPS and FTIR. In the presence of 1â¯mM H2O2, the SCH/GO catalyzed Fenton-like oxidation can thoroughly degrade TC under visible light irradiation, even under nature sunlight, whose second-order kinetic rate constant was about 15 times higher than that of pure SCH. SCH/GO was capable of highly selectively capturing and effectively degrading TC in the presence of similar concentration of Cl-, NO3-, SO42- and PO43- with that of food wastewater, even at organic matters concentration of 12.5 times than that of TC. At the same time, the removal of total organic carbon (TOC) and chemical oxygen demand (COD) in aforementioned food wastewater in SCH/GO+H2O2+Vis system reached 27.3 % and 34.5 % after 60â¯min, respectively. The inhibition zone experiments authenticated that the removal of drug resistance of bacteria by TC degradation intermediates can be achieved very well without producing secondary contamination in this system.
Asunto(s)
Antibacterianos/química , Tetraciclina/química , Contaminantes del Agua/química , Purificación del Agua/métodos , Antibacterianos/farmacología , Bacillus subtilis/efectos de los fármacos , Catálisis , Farmacorresistencia Microbiana/genética , Alimentos , Genes Bacterianos , Grafito/química , Grafito/efectos de la radiación , Peróxido de Hidrógeno/química , Peróxido de Hidrógeno/efectos de la radiación , Hierro/química , Hierro/efectos de la radiación , Compuestos de Hierro/química , Compuestos de Hierro/efectos de la radiación , Luz , Nanocompuestos/química , Nanocompuestos/efectos de la radiación , Staphylococcus aureus/efectos de los fármacos , Tetraciclina/farmacología , Aguas Residuales , Contaminantes del Agua/farmacologíaRESUMEN
In drinking water treatment, complete mineralization of organophosphorus pesticides (OPPs) by UV-based advanced oxidation processes (UV AOPs) is rarely achieved. The formation of intermediate oxidation byproducts would likely have some profound effects on toxicity of the reaction solutions. This study investigated the intermediate oxidation byproducts, transformation pathway and toxicity of malathion solutions during the treatment processes of UV alone, UV/H2O2, UV/TiO2 and UV/Fenton. The main intermediate oxidation byproducts were derived using ultra-performance liquid chromatography - electrospray - time-of-flight mass spectrometry. Thereby the transformation pathway for each of these treatment processes was proposed. The results indicate that in UV photolysis, the transformation pathway of malathion proceeded initially via cleavage of the phosphorus-sulfur bonds while in photocatalysis, the desulfurization from a PS bond to a PO bond was the primary degradation pathway. Interestingly, only in the UV/TiO2 process a small fraction of malathion was found decomposed via a demethylation reaction. At the same time, a toxicity assessment of the treated solutions was conducted by both luminescence inhibition of Vibrio fischeri and inhibition of acetylcholinesterase (AChE). It was found that after UV AOP treatment, the toxicity of the malathion aqueous solution increased sharply. In contrast, no increase in toxicity was observed for the malathion aqueous solution after UV alone treatment. This study demonstrates that the high removal efficiency achieved by OPPs does not imply that detoxification of the water solution has been achieved. On the contrary, the toxicity of the treated solutions by OPPs may be increased significantly depending on the selected treatment processes.
Asunto(s)
Aliivibrio fischeri/crecimiento & desarrollo , Insecticidas/toxicidad , Malatión/toxicidad , Fotólisis , Rayos Ultravioleta , Contaminantes Químicos del Agua/toxicidad , Purificación del Agua/métodos , Aliivibrio fischeri/efectos de los fármacos , Peróxido de Hidrógeno/química , Peróxido de Hidrógeno/efectos de la radiación , Hierro/química , Hierro/efectos de la radiación , Oxidación-Reducción , Titanio/química , Titanio/efectos de la radiación , Contaminantes Químicos del Agua/químicaRESUMEN
Fast photochemical oxidation of protein (FPOP) has become an important mass spectrometry-based protein footprinting approach. Although the hydroxyl radical (â¢OH) generated by photolysis of hydrogen peroxide (H2O2) is most commonly used, the pathways for its reaction with amino-acid side chains remain unclear. Here, we report a systematic study of â¢OH oxidative modification of 13 amino acid residues by using 18O isotopic labeling. The results differentiate three classes of residues on the basis of their oxygen uptake preference toward different oxygen sources. Histidine, arginine, tyrosine, and phenylalanine residues preferentially take oxygen from H2O2. Methionine residues competitively take oxygen from H2O2 and dissolved oxygen (O2), whereas the remaining residues take oxygen exclusively from O2. Results reported in this work deepen the understanding of â¢OH labeling pathway on a FPOP platform, opening new possibilities for tailoring FPOP conditions in addressing many biological questions in a profound way.
Asunto(s)
Marcaje Isotópico/métodos , Isótopos de Oxígeno/química , Fragmentos de Péptidos/química , Albúmina Sérica Bovina/química , Aminoácidos/química , Animales , Bovinos , Peróxido de Hidrógeno/química , Peróxido de Hidrógeno/efectos de la radiación , Radical Hidroxilo/química , Oxidación-Reducción , Oxígeno/química , Oxígeno/efectos de la radiación , Fotólisis , Huella de Proteína/métodos , Rayos UltravioletaRESUMEN
Various methods for shifting the optical response of TiO2 into the visible (Vis) range have been reported. Herein, we reported the application of a TiO2/H2O2/Vis process and the effects of TiO2 crystalline structure on the degradation of terbuthylazine. The results indicated that TiO2 crystalline structure and H2O2 addition had significant effects on terbuthylazine degradation: its degradation rate could be increased from 7% to 70% with H2O2 addition after 180â¯min of reaction, the synergistic degradation of terbuthylazine by TiO2-Fe3+ was substantially accelerated, with the degradation rate reaching up to 100% after 20â¯min of reaction, and rutile TiO2 showed better photocatalytic activity and a more obvious synergistic effect than anatase TiO2. The addition of free-radical scavengers (tert-butyl alcohol or methanol) inhibited the degradation efficiency of rutile TiO2, but had a relatively minor effect on anatase TiO2. Fluorescence spectrophotometry analysis indicated that hydroxyl free radicals could be continuously produced when using rutile TiO2 as the photocatalyst. Degradation of terbuthylazine catalyzed by rutile TiO2 occurred mainly in solution, but occurred on the particle surface of the photocatalyst when catalyzed by anatase TiO2. This study provides new insight into the role of TiO2 crystalline structure on the degradation of terbuthylazine and its photocatalytic degradation mechanism.
Asunto(s)
Peróxido de Hidrógeno/química , Titanio/química , Triazinas/química , Contaminantes Químicos del Agua/química , Catálisis , Cristalización , Peróxido de Hidrógeno/efectos de la radiación , Luz , Fotólisis , Titanio/efectos de la radiaciónRESUMEN
The evaluation of the photocatalysis of visible light activated titanium dioxide employed in hydrogen peroxide (H2O2) was carried using seven H2O2 solutions (3.5 and 35%) and/or methylene blue (MB), with or without light irradiation (LI); the absorbance of MB was the bleaching indicator. Color analysis was performed on bovine teeth (n=12) using two different concentrations of H2O2, 6 and 35% associated with titanium dioxide (TiO2). Data were analyzed with one and two-way ANOVA, and significance level of p<0.05. Solutions containing MB, H2O2 at 3.5 or 35%, and TiO2, followed by LI, showed significant difference when compared with other groups. Greater MB reduction was found in 35% concentration. H2O2 35%+TiO2 gel showed no difference in comparison to control group. All groups for the color analysis assay showed ΔE higher than 3.3. In conclusion, TiO2 and H2O2 association is a promisor alternative for reducing the clinical time of in-office dental bleaching.
Asunto(s)
Peróxido de Hidrógeno/efectos de la radiación , Luz , Procesos Fotoquímicos , Titanio/efectos de la radiación , Blanqueadores Dentales/efectos de la radiación , Blanqueamiento de Dientes/instrumentación , Animales , Bovinos , Color , Técnicas In Vitro , Azul de Metileno , SolucionesRESUMEN
Hydrogen peroxide (H2O2) plays an important role in various biological processes in numerous organisms. Depending on the concentration and the distribution within the cell, it can act as stressor or redox signalling molecule. To analyse the effects of H2O2 and its diffusion within the cell we developed the new genetically encoded photosensitizer KillerRed-SOD1 which enables a light-induced spatially and temporally controlled generation of H2O2 in living cells. The KillerRed-SOD1 is a fusion protein of the photosensitizer KillerRed (KR) and the cytosolic superoxide dismutase isoform 1 (SOD1) connected by a helix-forming peptide linker. Light irradiation at a wavelength of 560 nm induced superoxide radical formation at the KR domain which was transformed to H2O2 at the SOD1 domain. H2O2 was specifically detected under live cell conditions using the fluorescent sensor protein HyPer. Genetically encoded photosensitizers have the advantage that appropriate tag sequences can determine the localisation of the protein within the cell. Herein, it was exemplarily shown that the peroxisomal targeting sequence 1 directed the photosensitizer KR-SOD1 to the peroxisomes and enabled H2O2 formation specifically in these organelles. In summary, with the photosensitizer KR-SOD1 a new valuable tool was established which allows a controlled intracellular H2O2 generation for the analysis of H2O2 effects on a subcellular level.
Asunto(s)
Peróxido de Hidrógeno/metabolismo , Peróxido de Hidrógeno/efectos de la radiación , Luz , Fármacos Fotosensibilizantes/metabolismo , Superóxido Dismutasa-1/metabolismo , Animales , Muerte Celular , Ingeniería Genética , Células HEK293 , Humanos , Peróxido de Hidrógeno/química , Fármacos Fotosensibilizantes/química , Ratas , Superóxido Dismutasa-1/genéticaRESUMEN
The photolytic and photocatalytic transformation of an antipsychotic drug asenapine with the use of H2O2 and TiO2 was studied. A method employing irradiation with a simulated full solar spectrum in the photostability chamber was applied, then the reverse-phase ultra high performance liquid chromatography with diode array detector, coupled with electrospray quadrupole time-of-flight mass spectrometer (RP-UHPLC-DAD - ESI-Q-TOF) was used for the quantitative and qualitative analysis of the processes. The developed quantitative method was fully validated, according to the International Conference on Harmonization of Technical Requirements for Registration of Pharmaceuticals for Human Use (ICH) guidelines, and the kinetic parameters of asenapine photodecomposition were compared. Nineteen phototransformation products were detected, and their probable structures - mainly hydroxylated and oxidized asenapine derivatives - were suggested. On the basis of the elucidated structures the computational prediction of their toxicity at the various endpoints, as well as bioconcentration factors and biodegradability was performed. The obtained results were then subjected to the principal component analysis (PCA). This chemometric technique facilitated comparison of the applied models, calculated properties of the TPs, and enabled visualization of relationships between them.
Asunto(s)
Antipsicóticos/química , Compuestos Heterocíclicos de 4 o más Anillos/química , Peróxido de Hidrógeno/efectos de la radiación , Luz Solar , Titanio/efectos de la radiación , Contaminantes Químicos del Agua/química , Catálisis , Cromatografía Líquida de Alta Presión/métodos , Simulación por Computador , Dibenzocicloheptenos , Peróxido de Hidrógeno/química , Cinética , Espectrometría de Masas , Oxidación-Reducción , Fotólisis , Titanio/químicaRESUMEN
Readily-available and efficient catalyst is essential for activating oxidants to produce reactive species for deeply remediating water bodies contaminated by antibiotics. In this study, Ferrocene (Fc) was introduced to establish a heterogeneous photo-Fenton system for the degradation of sulfonamide antibiotics, taking sulfamethoxazole as a representative. Results showed that the removal of sulfamethoxazole was effective in Fc-catalyzed photo-Fenton system. Electron spin resonance and radical scavenging experiments verified that there was a photoindued electron transfer process from Fc to H2O2 and dissolved oxygen resulting in the formation of OH that was primarily responsible for the degradation of sulfamethoxazole. The reactions of OH with substructure model compounds of sulfamethoxazole unveiled that aniline moiety was the preferable reaction site of sulfamethoxazole, which was verified by the formation of hydroxylated product and the dimer of sulfamethoxazole in Fc-catalyzed photo-Fenton system. This heterogeneous photo-Fenton system displayed an effective degradation efficiency even in a complex water matrices, and Fc represented a long-term stability by using the catalyst for multiple cycles. These results demonstrate that Fc-catalyzed photo-Fenton oxidation may be an efficient approach for remediation of wastewater containing antibiotics.
Asunto(s)
Antibacterianos/química , Compuestos Ferrosos/química , Peróxido de Hidrógeno/química , Metalocenos/química , Sulfametoxazol/química , Contaminantes Químicos del Agua/química , Catálisis , Compuestos Ferrosos/efectos de la radiación , Peróxido de Hidrógeno/efectos de la radiación , Metalocenos/efectos de la radiación , Fotólisis , Luz Solar , Purificación del Agua/métodosRESUMEN
Transformation products and toxicity patterns of microcystin-LR (MC-LR), a common cyanotoxin in freshwaters, during degradation by solar photo-Fenton process were studied in the absence and presence of two major water components, namely fulvic acid and alkalinity. The transformation products m/z 795, 835, 515/1030 and 532 can be formed through attack of OH on the conjugated carbon double bonds of Adda. Transformation products with m/z 1010, 966 and 513 can be generated through the attack of OH on the methoxy group of Adda. The transformation products m/z 783, 508 and 1012 can be originated from the attack of OH on the cyclic structure of MC-LR. Transformation products (m/z 522, 1028, 1012, 1046 and 514) formed after hydroxylation of the aromatic ring with OH were also identified in this study. The toxicity study revealed that fulvic acid and alkalinity strongly influence the toxicity profiles of solar photo-Fenton treated MC-LR. Fulvic acid enhanced the detoxification whereas low level total alkalinity (1.8â¯mgâ¯L-1 CaCO3) inhibited the detoxification of MC-LR by solar photo-Fenton process as assessed by protein phosphatase-1 (PP-1) inhibition assay. This work provides insights on the utility of solar photo-Fenton destruction of MC-LR in water based on transformation products and toxicity data.
Asunto(s)
Peróxido de Hidrógeno , Hierro , Microcistinas , Luz Solar , Contaminantes del Agua , Benzopiranos/química , Supervivencia Celular/efectos de los fármacos , Células Hep G2 , Humanos , Peróxido de Hidrógeno/química , Peróxido de Hidrógeno/efectos de la radiación , Concentración de Iones de Hidrógeno , Hierro/química , Hierro/efectos de la radiación , Toxinas Marinas , Microcistinas/química , Microcistinas/toxicidad , Contaminantes del Agua/química , Contaminantes del Agua/toxicidadRESUMEN
The widespread occurrence of pharmaceuticals and their metabolites in natural waters has raised great concerns about their potential risks on human health and ecological systems. This study systematically investigates the degradation of sulfasalazine (SSZ) and its two human metabolites, sulfapyridine (SPD) and 5-aminosalicylic acid (5-ASA), by UV and UV/peroxydisulfate (UV/PDS) processes. Experimental results show that SPD and 5-ASA were readily degraded upon UV 254â¯nm direct photolysis, with quantum yields measured to be (8.6⯱â¯0.8)â¯×â¯10-3 and (2.4⯱â¯0.1)â¯×â¯10-2â¯molâ¯Einstein-1, respectively. Although SSZ was resistant to direct UV photolysis, it could be effectively removed by both UV/H2O2 and UV/PDS processes, with fluence-based pseudo-first-order rate constants determined to be 0.0030 and 0.0038â¯cm2â¯mJ-1, respectively. Second-order rate constant between SO4â¢- and SSZ was measured as (1.33⯱â¯0.01)â¯×â¯109â¯M-1s-1 by competition kinetic method. A kinetic model was established for predicting the degradation rate of SSZ in the UV/PDS process. Increasing the dosage of PDS significantly enhanced the degradation of SSZ in the UV/PDS process, which can be well predicted by the developed kinetic model. Natural water constituents, such as natural organic matter (NOM) and bicarbonate (HCO3-), influenced the degradation of SSZ differently. The azo functional group of SSZ molecule was predicted as the reactive site susceptible to electrophilic attack by SO4â¢- by frontier electron densities (FEDs) calculations. Four intermediate products arising from azo bond cleavage and SO2 extrusion were identified by solid phase extraction-liquid chromatography-triple quadrupole mass spectrometry (SPE-LC-MS/MS). Based on the products identified, detailed transformation pathways for SSZ degradation in the UV/PDS system were proposed. Results reveal that UV/PDS could be an efficient approach for remediation of water contaminated by SSZ and its metabolites.
Asunto(s)
Compuestos de Sodio/efectos de la radiación , Sulfasalazina/química , Sulfasalazina/efectos de la radiación , Sulfatos/efectos de la radiación , Rayos Ultravioleta , Contaminantes Químicos del Agua/química , Contaminantes Químicos del Agua/efectos de la radiación , Humanos , Peróxido de Hidrógeno/química , Peróxido de Hidrógeno/efectos de la radiación , Cinética , Mesalamina/química , Mesalamina/efectos de la radiación , Oxidación-Reducción , Fotólisis , Compuestos de Sodio/química , Sulfapiridina/química , Sulfapiridina/efectos de la radiación , Sulfatos/química , Purificación del AguaRESUMEN
The concentration of antiretroviral drugs in wastewater treatment plants (WWTP) effluents and surface waters of many countries has increased significantly due to their widespread use for HIV treatment. In this study, the removal of stavudine and zidovudine under UV254 photolysis or UV254/H2O2 was investigated in a microcapillary film (MCF) photoreactor, using minimal water samples quantities. The UV254 quantum yield of zidovudine, (2.357⯱â¯0.0589)·10-2â¯molâ¯ein-1 (pH 4.0-8.0), was 28-fold higher that the yield of stavudine (8.34⯱â¯0.334)·10-4â¯molâ¯ein-1 (pH 6.0-8.0). The second-order rate constant kOH,iof reaction of hydroxyl radical with the antiretrovirals (UV254/H2O2 process) were determined by kinetics modeling: (9.98⯱â¯0.68)·108â¯M-1â¯s-1 (pH 4.0-8.0) for zidovudine and (2.03⯱â¯0.18)·109â¯M-1â¯s-1 (pH 6.0-8.0) for stavudine. A battery of ecotoxicological tests (i.e. inhibition growth, bioluminescence, mutagenic and genotoxic activity) using bacteria (Aliivibrio fischeri, Salmonella typhimurium), crustacean (Daphnia magna) and algae (Raphidocelis subcapitata) revealed a marked influence of the UV dose on the ecotoxicological activity. The UV254/H2O2 treatment process reduced the ecotoxicological risk associated to direct photolysis of the antiretrovirals aqueous solutions, but required significantly higher UV254 doses (≥2000 mJâ¯cm-2) in comparison to common water UV disinfection processes.
Asunto(s)
Antirretrovirales , Peróxido de Hidrógeno , Estavudina , Rayos Ultravioleta , Contaminantes Químicos del Agua , Zidovudina , Aliivibrio fischeri/efectos de los fármacos , Aliivibrio fischeri/crecimiento & desarrollo , Animales , Antirretrovirales/química , Antirretrovirales/toxicidad , Daphnia/efectos de los fármacos , Daphnia/fisiología , Ecotoxicología , Peróxido de Hidrógeno/química , Peróxido de Hidrógeno/efectos de la radiación , Cinética , Salmonella typhimurium/efectos de los fármacos , Salmonella typhimurium/genética , Estavudina/química , Estavudina/toxicidad , Contaminantes Químicos del Agua/química , Contaminantes Químicos del Agua/toxicidad , Zidovudina/química , Zidovudina/toxicidadRESUMEN
OBJECTIVE: A systematic review and meta-analysis were performed to answer the following research question: Does light-activated in-office vital bleaching have a greater whitening efficacy and higher tooth sensitivity (TS) in comparison with in-office vital bleaching without light when used in adults? DATA AND SOURCE: Only randomized clinical trials (RCTs) involving adults who had in-office bleaching with and without light activation were included. Controlled vocabulary and keywords were used in a comprehensive search for titles and abstracts in PubMed, and this search was adapted for Scopus, Web of Science, LILACS, BBO, Cochrane Library, and SIGLE without restrictions in May 2016 and was updated in August 2017. IADR abstracts (1990-2016), unpublished- and ongoing-trial registries, dissertations, and theses were also searched. The risk-of-bias tool of the Cochrane Collaboration was used for quality assessment. The quality of the evidence was rated using the Grading of Recommendations: Assessment, Development, and Evaluation approach. Through the use of the random effects model, a meta-analysis with a subgroup analysis (low and high hydrogen peroxide concentration) was conducted for color change (ΔE*, ΔSGU) as well as the risk and intensity of TS. STUDY SELECTION: We retrieved 6663 articles, but after removing duplicates and non-relevant articles, only 21 RCTs remained. No significant difference in ΔE*, ΔSGU, and risk and intensity of TS was observed (pâ¯>â¯.05). For ΔE and risk of TS, the quality of the evidence was graded as moderate whereas the evidence for ΔSGU and intensity of TS was graded as very low and low, respectively. CONCLUSION: Without considering variations in the protocols, the activation of in-office bleaching gel with light does not seem to improve color change or affect tooth sensitivity, regardless of the hydrogen peroxide concentration. (PROSPERO - CRD42016037630). CLINICAL RELEVANCE: Although it is commercially claimed that in-office bleaching associated with light improves and accelerates color change, this study did not confirm this belief for in-office bleaching gels with either high or low levels of hydrogen peroxide.
Asunto(s)
Consultorios Odontológicos , Luz/efectos adversos , Blanqueamiento de Dientes/métodos , Adulto , Bases de Datos Factuales , Sensibilidad de la Dentina , Humanos , Peróxido de Hidrógeno/efectos de la radiación , Peróxido de Hidrógeno/uso terapéutico , Blanqueadores Dentales/efectos de la radiación , Blanqueadores Dentales/uso terapéuticoRESUMEN
We used Ames assays to investigate the effects of ozonation (designated O3), ozonation followed by chlorination (O3/Cl), an advanced oxidation process (AOP, UV/H2O2), and AOP followed by chlorination (AOP/Cl) on the mutagenicity of solutions of 3-methyl-4-nitrophenol (3M4NP), a major environmental degradation product of the organophosphorus insecticide fenitrothion. Whereas O3 did not induce mutagenicity, O3/Cl, AOP, and AOP/Cl converted 3M4NP into mutagenic transformation products (TPs). Using liquid chromatography-mass spectrometry, we detected a total of 138 peaks in the solutions subjected to O3/Cl, AOP, and AOP/Cl. To elucidate the TPs responsible for the observed mutagenicity, we performed simple regression analyses of the relationship between the area of each peak and the observed mutagenicity of samples withdrawn periodically during each oxidation process. The area of each of 10 peaks was found to be positively correlated (r2 ≥ 0.8) with the observed mutagenicity, suggesting that the TPs corresponding to these peaks contributed to the mutagenicity. After taking into account the consistency of mutagenicity induction by the oxidation processes and analyzing the peaks by tandem mass spectrometry, we identified 3 TPs, corresponding to 6 peaks, as candidate mutagens. These TPs were assessed by means of 4 quantitative structure-activity relationship (QSAR) models, and all 3 were predicted to be mutagenic by at least one model. This result was consistent with our assumption that these TPs were mutagens. Ames assays of an authentic sample of one of the 3 TPs revealed that it did not contribute to the mutagenicity. This left 3-methoxy-4-nitrophenol and 2-[(E)-[(2,5-dihydroxyphenyl) methylidene]amino]-5-dihydroxybenzaldehyde on the list of mutagens suspected of contributing to the mutagenicity induced by AOP. No TPs were identified as candidate mutagens responsible for the mutagenicity induced by O3/Cl and AOP/Cl.
Asunto(s)
Cresoles/química , Mutágenos/química , Cromatografía Liquida/métodos , Halogenación , Peróxido de Hidrógeno/química , Peróxido de Hidrógeno/efectos de la radiación , Pruebas de Mutagenicidad , Mutágenos/toxicidad , Oxidantes/química , Oxidación-Reducción , Ozono/química , Relación Estructura-Actividad Cuantitativa , Espectrometría de Masas en Tándem , Rayos Ultravioleta , Purificación del Agua/métodosRESUMEN
OBJECTIVE: The aim of this study was to assess the dental bleaching efficacy of 37.5% hydrogen peroxide (HP), with and without light activation, in HP-exposed and unexposed areas. METHOD: 28 bovine teeth were selected and divided into two groups (n = 14). Crowns were detached and stained with tea. The gingival half was covered with a gingival barrier. In the incisal half, 37.5% HP (Pola Office+, SDI) was applied three times, with a 1-week interval between applications. In HP-A group, the bleaching agent was activated for 3 min with a LED lamp. No light activation was applied in HP-N group. Dental color variation was determined through a spectrophotometer in both halves. Statistical analysis between groups was performed with an ANOVA test, and intragroup differences were evaluated, with an ANOVA test for paired data, with a significance level of P < 0.05. RESULTS: An increase in lightness and a decrease in chroma were found in both groups and halves. No significant differences in ΔE between groups (P > 0.5) were detected in the incisal half. After treatment, a significantly higher ΔE was found in the gingival half for HP-A group (P < 0.05). For the same group, a significantly higher bleaching effect was found in the gingival half, compared with the incisal half (P < 0.05). CONCLUSIONS: LED activation did not have a significant effect in terms of bleaching in the incisal half, but increased clearance in the gingival half. CLINICAL RELEVANCE: HP light activation does not significantly increase the whitening effect, but it can improve the bleaching diffusion to areas where it has not been directly applied.
Asunto(s)
Peróxido de Hidrógeno/farmacocinética , Fotoquimioterapia/métodos , Blanqueadores Dentales/farmacocinética , Blanqueamiento de Dientes/métodos , Animales , Bovinos , Color , Difusión , Peróxido de Hidrógeno/efectos de la radiación , Masculino , Ensayo de Materiales , Espectrofotometría/instrumentación , Factores de Tiempo , Diente/efectos de los fármacos , Diente/metabolismo , Blanqueadores Dentales/efectos de la radiación , Decoloración de Dientes/tratamiento farmacológicoRESUMEN
The use of light sources in the bleaching process reduces the time required and promotes satisfactory results. However, these light sources can cause an increase in the pulp temperature. Objective The purpose of the present study was to measure the increase in intrapulpal temperature induced by different light-activated bleaching procedures with and without the use of a bleaching gel. Material and Methods A human maxillary central incisor was sectioned 2 mm below the cementoenamel junction. A K-type thermocouple probe was introduced into the pulp chamber. A 35% hydrogen peroxide bleaching gel was applied to the vestibular tooth surface. The light units used were a conventional halogen, a hybrid light (only LED and LED/Laser), a high intensity LED, and a green LED light. Temperature increase values were compared by two-way ANOVA and Tukey´s tests (p<0.05). Results There were statistically significant differences in temperature increases between the different light sources used and between the same light sources with and without the use of a bleaching gel. The presence of a bleaching gel generated an increase in intra-pulpal temperature in groups activated with halogen light, hybrid light, and high intensity LED. Compared to the other light sources, the conventional halogen lamp applied over the bleaching gel induced a signiï¬cant increase in temperature (3.83±0.41°C). The green LED unit with and without gel application did not produce any significant intrapulpal temperature variations. Conclusion In the present study, the conventional halogen lamp caused the highest increase in intrapulpal temperature, and the green LED caused the least. There was an increase in temperature with all lights tested and the maximum temperature remained below the critical level (5.5°C). The addition of a bleaching gel led to a higher increase in intrapulpal temperatures.
Asunto(s)
Pulpa Dental/efectos de la radiación , Calor , Láseres de Semiconductores , Luz , Blanqueamiento de Dientes/métodos , Análisis de Varianza , Pulpa Dental/efectos de los fármacos , Geles , Humanos , Peróxido de Hidrógeno/efectos de la radiación , Oxidantes/efectos de la radiación , Valores de Referencia , Reproducibilidad de los Resultados , Blanqueamiento de Dientes/instrumentaciónRESUMEN
ABSTRACT The use of light sources in the bleaching process reduces the time required and promotes satisfactory results. However, these light sources can cause an increase in the pulp temperature. Objective The purpose of the present study was to measure the increase in intrapulpal temperature induced by different light-activated bleaching procedures with and without the use of a bleaching gel. Material and Methods A human maxillary central incisor was sectioned 2 mm below the cementoenamel junction. A K-type thermocouple probe was introduced into the pulp chamber. A 35% hydrogen peroxide bleaching gel was applied to the vestibular tooth surface. The light units used were a conventional halogen, a hybrid light (only LED and LED/Laser), a high intensity LED, and a green LED light. Temperature increase values were compared by two-way ANOVA and Tukey´s tests (p<0.05). Results There were statistically significant differences in temperature increases between the different light sources used and between the same light sources with and without the use of a bleaching gel. The presence of a bleaching gel generated an increase in intra-pulpal temperature in groups activated with halogen light, hybrid light, and high intensity LED. Compared to the other light sources, the conventional halogen lamp applied over the bleaching gel induced a significant increase in temperature (3.83±0.41°C). The green LED unit with and without gel application did not produce any significant intrapulpal temperature variations. Conclusion In the present study, the conventional halogen lamp caused the highest increase in intrapulpal temperature, and the green LED caused the least. There was an increase in temperature with all lights tested and the maximum temperature remained below the critical level (5.5°C). The addition of a bleaching gel led to a higher increase in intrapulpal temperatures.
Asunto(s)
Humanos , Pulpa Dental/efectos de la radiación , Láseres de Semiconductores , Luz , Blanqueamiento de Dientes/métodos , Análisis de Varianza , Pulpa Dental/efectos de los fármacos , Geles , Calor , Peróxido de Hidrógeno/efectos de la radiación , Oxidantes/efectos de la radiación , Valores de Referencia , Reproducibilidad de los Resultados , Blanqueamiento de Dientes/instrumentaciónRESUMEN
The removal of Bisphenol-A (BPA) from contaminated water using advanced oxidation methods such as UV-C assisted oxidation by hydrogen peroxide (H2O2) and sodium persulfate (SPS) has been reported by the authors earlier (Sharma et al., 2015a). In the present study, the authors report the removal of BPA from aqueous solution by the above two methods and its degradation mechanism. UV-C light (254 nm wavelength, 40 W power) was applied to BPA contaminated water at natural pH (pHN) under room temperature conditions. Experiments were carried out with the initial BPA concentration in the range of 0.04 mM-0.31 mM and the oxidant/BPA molar ratio in the range of 294:1-38:1 for UV-C/H2O2 and 31.5-4.06:1 for UV-C/SPS systems. The removal of BPA enhanced with decreasing BPA concentration. The total organic carbon also decreased with the UV-C irradiation time under optimum conditions ([H2O2]0 = 11.76 mM; [SPS]0 = 1.26 mM; temperature (29 ± 3 °C). Competition of BPA for reaction with HO or [Formula: see text] radicals at its higher concentrations results in a decrease in the removal of BPA. The intermediates with smaller and higher molecular weights than that of BPA were found in the treated water. Based on GC-MS and FTIR spectra of the reaction mixture, the formation of hydroxylated by-products testified the HO mediated oxidation pathway in the BPA degradation, while the formation of quinones and phenoxy phenols pointed to the [Formula: see text] dominating pathway through the formation of hydroxycyclohexadienyl (HCHD) and BPA phenoxyl radicals. The main route of BPA degradation is the hydroxylation followed by dehydration, coupling and ring opening reactions.
Asunto(s)
Compuestos de Bencidrilo/química , Peróxido de Hidrógeno/química , Fenoles/química , Compuestos de Sodio/química , Sulfatos/química , Rayos Ultravioleta , Contaminantes Químicos del Agua/química , Purificación del Agua/métodos , Compuestos de Bencidrilo/análisis , Radicales Libres/química , Radicales Libres/efectos de la radiación , Cromatografía de Gases y Espectrometría de Masas , Peróxido de Hidrógeno/efectos de la radiación , Oxidantes , Oxidación-Reducción , Fenoles/análisis , Compuestos de Sodio/efectos de la radiación , Sulfatos/efectos de la radiación , Contaminantes Químicos del Agua/análisisRESUMEN
The highly sensitive, interference-free and non-enzymatic optical sensing of glucose has been made possible for the first time using the hydrothermally synthesized ZnO nanorods. The UV irradiation of glucose-treated ZnO nanorods decomposes glucose into hydrogen peroxide (H2O2) and gluconic acid by UV oxidation. The ZnO nanorods play the role of a catalyst similar to the oxidase used in the enzymatic glucose sensors. The photoluminescence (PL) intensity of the near-band edge emission of the ZnO nanorods linearly decreased with the increased concentration of H2O2. Therefore, the glucose concentration is monitored over the wide range of 0.5-30 mM, corresponding to 9-540 mg/dL. The concentration range of the linear region in the calibration curve is suitable for its clinical use as a glucose sensor, because the glucose concentration of human serum is typically in the range of 80-120 mg/dL. In addition, the optical glucose sensor made of the ZnO nanorods is free from interference by bovin serum albumin, ascorbic acid or uric acid, which are also present in human blood. The non-enzymatic ZnO-nanorod sensor has been demonstrated with human serum samples from both normal persons and diabetic patients. There is a good agreement between the glucose concentrations measured by the PL quenching and standard clinical methods.
Asunto(s)
Técnicas Biosensibles/instrumentación , Glucosa/análisis , Nanotubos/química , Dispositivos Ópticos , Óxido de Zinc/química , Análisis Químico de la Sangre/instrumentación , Glucemia/análisis , Diabetes Mellitus/sangre , Gluconatos/química , Gluconatos/efectos de la radiación , Glucosa/química , Glucosa/efectos de la radiación , Humanos , Peróxido de Hidrógeno/química , Peróxido de Hidrógeno/efectos de la radiación , Membranas Artificiales , Rayos UltravioletaRESUMEN
In this study, UV light was adopted to make it possible to attain sufficiently high extraction efficiency even with a minimal amount of H2O2. The Fenton-like reaction showed 80% of lipid extraction efficiency with 0.5% H2O2, whereas the provision of 16 W UV increased efficiency to 85% and decreased H2O2 consumption to 0.3%. This oxidation-based lipid extraction means have one fortuitous yet beneficial effect to remove chlorophylls, which are known to degrade the quality of the final product like biodiesel. The UV-Fenton-like reaction was found to eliminate 77% of chlorophylls. Such oxidation-based lipid extraction approaches as the Fenton-like reaction appear to have the sure application potential; and it is more so with the help of UV.
Asunto(s)
Fraccionamiento Celular/métodos , Peróxido de Hidrógeno/química , Hierro/química , Lípidos/aislamiento & purificación , Extracción Líquido-Líquido/métodos , Microalgas/química , Microalgas/efectos de la radiación , Biocombustibles/microbiología , Peróxido de Hidrógeno/efectos de la radiación , Hierro/efectos de la radiación , Lípidos/química , Lípidos/efectos de la radiación , Dosis de Radiación , Rayos UltravioletaRESUMEN
This work reports on the removal and mineralization of an endocrine disrupting chemical, Bisphenol A (BPA) at a concentration of 0.22 mM in aqueous solution using inorganic oxidants (hydrogen peroxide, H2O2 and sodium persulfate, Na2S2O8;S2O8(2-)) under UV irradiation at a wavelength of 254 nm and 40 W power (Io = 1.26 × 10(-6) E s(-1)) at its natural pH and a temperature of 29 ± 3 °C. With an optimum persulfate concentration of 1.26 mM, the UV/S2O8(2-) process resulted in â¼95% BPA removal after 240 min of irradiation. The optimum BPA removal was found to be â¼85% with a H2O2 concentration of 11.76 mM. At higher concentrations, either of the oxidants showed an adverse effect because of the quenching of the hydroxyl or sulfate radicals in the BPA solution. The sulfate-based oxidation process could be used over a wider initial pH range of 3-12, but the hydroxyl radical-based oxidation of BPA should be carried out in the acidic pH range only. The water matrix components (bicarbonate, chloride and humic acid) showed higher scavenging effect in hydroxyl radical-based oxidation than that in the sulfate radical-based oxidation of BPA. UV/S2O8(2-) oxidation system utilized less energy (307 kWh/m(3)) EE/O in comparison to UV/H2O2 system (509 kWh/m(3)) under optimum operating conditions. The cost of UV irradiation far outweighed the cost of the oxidants in the process. However, the total cost of treatment of persulfate-based system was much lower than that of H2O2-based oxidation system.