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381 protocols using uv 1700

1

Rumen Fluid NH3-N and VFA Analysis

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Rumen fluid NH3-N was analyzed using a spectrophotometer (UV-1700; Shimazu Corporation, Kyoto, Japan) following the methods described by Broderick and Kang [19 (link)]. The VFA concentrations were determined by gas chromatograph (GC-2014; Shimazu Corporation, Japan) with a capillary column (Rtx-Wax, 30 m long, 0.25 mm diameter, 0.25 μm film). Chromatograph parameters included an injection volume of 0.4 μL with a split ratio of 40:1, column nitrogen flow rate of 2.5 mL/min, injector temperature of 220°C and flame ionization detector temperature of 250°C. The oven temperature program was as follows: initial 110°C for 30 s, up to 120°C at 10°C/min, 120°C hold for 4 min, and continue to 150°C at 10°C/min.
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2

Photocatalytic Degradation of Organic Pollutants

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In the experiment, a 300 W mercury lamp with an irradiation distance of 10 cm was used as the ultraviolet light source as a substitute for a solar light. In order to disperse ultraviolet rays uniformly and improve the utilization rate of light, tin foil was packed inside the reactor. Simulated organic pollutant wastewater (30 mL, 5 g L−1 Na2SO4, 0.2 g L−1 NB) and the Au/TiO2 NTs were placed in a quartz device with circulating water, and the adsorption and desorption equilibrium of the solution was reached by stirring at room temperature for 30 min. A PEC system was used with the Au/TiO2 NTs as the working anode electrode and Pt as the cathode electrode with a bias voltage of 1.2 V. The degradation rate of NB was measured by a UV-vis spectrophotometer (Shimazu, UV-1700) once per 30 min measurement over 2 hours.
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3

Enzymatic Decolorization of Textile Dyes

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The efficiency of the enzymatic treatment was evaluated by monitoring the decolorization of dyes at their maximum absorption wavelength with a UV-Vis spectrophotometer (UV Shimadzu 1700, Shimadzu Corporation, Kyoto, Japan). For this purpose, a solution of 30 mg/L concentration of dyes was scanned over a wavelength range of 200–800 nm and optimum wavelength was determined (λmax⁡—628 nm, absorbance—0.265 for AB 225, and λmax⁡—590 nm, absorbance—0.319 for AV 109). The calculated molar extinction coefficients were 11,019 L mmol−1 cm−1 and 6,053 L mmol−1 cm−1 for AV 109 and AB 225, respectively.
The decolorization in percentage for both dyes was determined, according to the equation [28 (link)]
Decolorization%=A0AtA0×100,
where A0 is the initial absorbance of untreated dye solutions (control) and At is the absorbance of dye solutions after enzymatic treatment.
Experiments were made in triplicates, and standard deviations were calculated.
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4

Comparative Evaluation of Immobilized HRP Activity

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The activity of the free and immobilized HRP was measured first using the standard method with substrate pyrogallol and H2O2 in a reaction medium [50 (link)] consisting of 3 mL of 0.013 M pyrogallol solution in the potassium phosphate buffer (pH 7.0; 0.1 M). Briefly, 2 mg of immobilized enzyme (0.05–10 mg HRP/gcarrier) and 30 µL of H2O2 (3% v/v) were placed in the cuvette. By adding 30 µL of H2O2 (3% v/v), the reaction was started. The oxidation of pyrogallol (yellow) by HRP-MAB to purpurogallin (dark brown) was monitored at 420 nm absorbance (ε(420 nm) = 12 mM−1 cm−1) using a UV–Vis spectrophotometer (UV Shimadzu 1700, Shimadzu Corporation, Kyoto, Japan). The change in absorbance in the sample, against the reagent blank, was recorded each 30 s for 3 min. One unit of activity was defined as the amount of biocatalyst that formed 1.0 mg of purpurogallin from pyrogallol in 20 s at pH 7.0 and 20 °C [51 ]. The activity of HRP-MABs immobilized under optimal conditions was then compared to the activity of the HRP covalently immobilized on the alginate beads in the absence of magnetite under the same conditions, encapsulating HRP into Mag-alginate beads with the same initial enzyme/carrier ratio and free HRP using the standard method.
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5

Quantifying Candida Biofilm Formation

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Candida cell density of each strain was adjusted to 3 × 10 6 cells/mL in BHI broth. Of these suspensions 2 mL were added to each of the four materials in 24 well plates and they were incubated for 48 h at 37 °C. After 48 h, biofilm formation was determined using a crystal violet binding assay (O'Toole, 2011) . Briefly, the materials with the biofilms were gently washed three times with 10 mM potassium phosphate buffer (pH 7) and stained with a 1% (w/v) solution of crystal violet (Merck) in sterile distilled water for 20 min at 25 °C. Subsequently, the materials were gently rinsed with 10 mM potassium phosphate buffer (pH 7) and crystal violet bound to the biofilm was dissolved in ethanol (96% v/v) for 20 min. Quantification of the biofilm was done by measuring the absorbance at 560 nm using a spectrophotometer (UV-Visible Spectrophotometer; Shimadzu UV-1700, Kyoto, Japan). Note, crystal violet binds not only to viable and dead cells but also to extracellular matrix of the biofilms (Kwasny and Opperman, 2010) .
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6

Inhibition of Fungal Biofilm Formation

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Inhibition of biofilm formation of the fungal pathogen CRP1 by EA extract of CNE6 was checked in 24-well polystyrene cell culture plates. Similar to the previous description, fungal conidia were inoculated in 1 mL of ME broth and then added to each well. EA extract of CNE6 dissolved in 10% sterilized DMSO (100 μL) was added at different concentrations (0 to 1,000 μg/mL) to different wells and incubated for 24 h at 28°C. After that, broth was removed from each well and the wells were carefully washed twice with PBS. Biofilms were fixed with 95% ethanol for 15 min at 37°C and finally stained with 1 mL of 0.1% safranin (54 (link)) and left for 5 min. Excessive safranin was eluted from the wells by washing with sterilized distilled water and air dried again. To extract the bound safranin from the fungal cells, 1 mL of 30% glacial acetic acid was added to each well and left at room temperature for 5 min. Color changes of the acetic acid solution were measured at 490 nm with the help of a UV-Vis spectrophotometer (Shimadzu; UV-1700).
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7

Analytical Methods for API Characterization

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UV-Visible double beam spectrophotometer (UV 1700, Shimadzu, Japan) with 1 cm matched quartz cells, Micropipette of variable volumes (Microlit, India), and Digital balance (Denver Instrument, Germany) were used for the UV-Spectrophotometric method. The HPLC experiment was executed on WATERS HPLC system which is compiled of 515 HPLC pump, arrayed with Rheodyne injection valve with loop having 20 µl capacity. Detection was performed by WATERS 2489 UV-Visible detector. EMPOWER-2 software was used to record and process the chromatographic data. PCI analytics Ultrabath sonicator with 3.5 L capacity was used for mixing and sonication purposes. Agilent Cary 360 FT-IR spectrometer with micro lab software was used to record IR spectra of API. Analytical Balance Mettler Toledo, AB204-S/FACT was used for weighing purposes.
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8

Determination of Molar Extinction Coefficients

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A concentrated
solution of each dye was prepared by weighting the dye (5–7
mg) and dissolving it into 10 mL of absolute ethanol (EtOH). Three
diluted solution (25 mL) of EtOH were prepared by taking aliquots
(0.2, 0.1, and 0.05 mL) of the stock solution. The diluted solutions
were measured by steady-state UV–visible absorption spectroscopy
(Shimadzu UV-1700) using a quartz cuvette (1 cm pathway length). The
absorbance intensities of each solution at the λmax were plotted versus the sample concentration. A linear fit was applied
to determine the molar extinction coefficient (ε) using the
Beer–Lambert equation. The analysis was duplicated. The obtained
data were considered acceptable when the difference between the determined
log ε was less or equal to 0.02 in respect to their average.
Otherwise, new concentrated dye stock solution in absolute EtOH was
prepared and the protocol repeated.
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9

Quantifying Polyphenols and Flavonoids in Chrysanthemum Tea

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To determine total polyphenols and total flavonoids, 3.0 ± 0.01 g of each chrysanthemum tea powder sample was mixed with 120 mL of distilled water in a 250 mL round-bottomed flask and extracted at 90 °C for 40 min in a water bath. After extraction, each extracted solution was centrifuged at 5000 r/min for 5 min, concentrated at 65 °C under reduced pressure for 1 h, and then freeze-dried. After drying, the extracted powder was stored immediately at −20 °C for future analysis. The total polyphenol contents of the chrysanthemum tea samples were measured according to the Folin-Denis method. Briefly, 0.01 g of each extracted chrysanthemum tea powder was mixed with 1.0 mL of Folin-Ciocâlteu reagent (1.0 mol/L) and reacted at room temperature for 1 min. Then, 8 mL of 10% sodium carbonate (100 g/L) was mixed well, and the mixture was left in a dark place for 2 h. The absorbance was measured at 760 nm using a spectrophotometer (UV-1700, Shimadzu, Kyoto, Japan). The results were expressed as milligrams of gallic acid equivalents per gram of dry matter (mg GAE/g), using gallic acid as a reference standard. The total flavonoid contents of the chrysanthemum tea samples were determined according to the aluminum chloride complex formation method and expressed as milligrams of rutin equivalents per gram of extracted chrysanthemum tea powder in dry weight (mg RE/g).
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10

Photostability Assessment of Pigments

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A photostability study was carried out by dissolving the pigments in acetone and illuminating them continuously with LEDs for 60 min at room temperature. The evolution of the electronic absorption spectrum was recorded periodically using a UV-visible spectrophotometer (UV-1700, Shimadzu, Kyoto, Japan) and examined for any decrease or shift in the absorption peaks or shoulders. Since remnant of plant carotenes might be present, the photostability of pigments was also evaluated using β-carotene as standard reference (Chameleon Reagent, Osaka, Japan).
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