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6 protocols using na2b4o7 10h2o

1

UVC-LED Actinometry using KI/KIO3

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Actinometry using KI/KIO3 was performed to measure the fluence delivered by the UVC-LED reactor to the water. The protocol was adapted from [88 (link),89 (link),90 (link),91 (link)] and is shown in greater detail in the Supplementary Materials [68 (link)]. A similar but simpler, laboratory-scale skid was set up to perform actinometry experiments; details are given in the supplemental information Figure S3 and Table S3 [68 (link)]. The setup used consisted of a water bath, a pump, a flowmeter, a pressure sensor and a needle valve. To perform the actinometry experiments, a 0.6 M KI (Merck, Darmstadt, Germany), 0.1 M KIO3 (VWR, Darmstadt, Germany) and 0.01 M Na2B4O7 10 H2O (Sigma-Aldrich, Taufkirchen, Germany) solution was prepared [89 (link)]. The pH of the finished solution was 9–9.2. The solution was adjusted to 23.5 °C in a temperature-controlled water bath, the temperature in the cabinet was set to 15 °C and UVC-LED reactor was turned on for at least 15 min to allow a warm-up period. Within an actinometry experiment, several flow steps were tested, ranging from approximately 1 to 6 L∙h−1 leading to hydraulic retention times in the reactor of 0.7 to 6 s. Samples and blank were taken in triplicates and the absorbance at 352 nm was determined using the DR6000 UV-Vis spectrophotometer (HACH, Düsseldorf, Germany).
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2

Quantitative Analysis of Glyphosate and AMPA

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Millipore® Direct UV-Q water was used to prepare all the solutions in this study. GLY of 99.7% purity, AMPA of 99% purity and 9-flourenylmethlylchloroformate chloride (FMOC) of 97% purity were purchased from Sigma Aldrich® (Seelze, Germany), while acetonitrile was purchased from QREC®, Malaysia. Stock solutions (500 mg L−1) of GLY and AMPA were prepared by quantitatively dissolving their appropriate quantities into Millipore® Direct UV-Q water, while 0.02 M FMOC was prepared in acetonitrile. Analytical reagent grade CaCl2 and KH2PO4 were purchased from Emsure® (Germany) while HgCl2 and Na2B4O7.10H2O were purchased from Sigma Aldrich® (India).
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3

Extraction and Analysis of Natural Compounds

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NaHCO3, Na2B4O7·10H2O, KCl, CH3COOH, CH3COONa, HCl, and
NaOH of analytical grades were purchased from
Merck. NR of grade ribbed smoked sheets 3 (RSS3) and CBD were collected
from PCBL (West Bengal, India) and local tannery (Bantala, Kolkata,
West Bengal, India), respectively. BCB, SF, and chloride salt of Hg(II)
were purchased from Sigma-Aldrich.
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4

Adsorption of Heavy Metals Using Hydrogels

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Na2HPO4, Na2B4O7·10H2O,
HCl, acrylic acid, NIPAm, PN (degree of esterification = 63–66%), N,N′-methylenebisacrylamide (MBA),
potassium persulfate (PPS), and sodium bisulfite (SBS) of analytical
grades were purchased from Merck and used without any further modification.
SF, methyl orange (MO), and nitrate salts of Cd(II), Hg(II), and Cr(III),
used in adsorption studies, were purchased from Sigma-Aldrich.
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5

Synthesis and Characterization of Conductive Polymers

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NaHCO3, Na2B4O7·10H2O, KCl, CH3COOH, CH3COONa, HCl, NaOH, AMPS, AM, STR, MBA,
sodium bisulfite (SBS), and potassium persulfate (PPS) of analytical
grades were purchased from Merck and used without any further modification.
BCB, CV, SbCl3, and Bi(NO3)3 were
purchased from Sigma-Aldrich.
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6

Spectroscopic Analysis of Uranyl Complexes

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CAUTION! Natural uranium consists of radioactive nuclides, including long‐lived α‐emitters (235U, t1/2=7.04×108 years and 238U, t1/2=4.47×109 years) and is also chemically toxic. Special precautions as well as appropriate equipment and facilities for radiation protection are required to handle this material.
Acetonitrile (VWR), chloroform (Sigma–Aldrich), methanol (VWR), NaOH (Merck), UO2(NO3)26 H2O (Chemapol), Eu(NO3)36 H2O (Alfa Aesar), HClO4 (Merck), anhydrous NaClO4 (Alfa Aesar), and Na2B4O710 H2O (Merck) were used as purchased from commercial sources without further purification. For the mobile phase of ESI‐TOF MS, Acetonitrile was obtained from Roth (HPLC grade). In all calorimetric and spectroscopic investigations, the ionic strength was adjusted to 0.01 m NaClO4. Generally, all experiments were performed at (25±0.02) °C under atmospheric conditions. The pH was adjusted by using a WTW pH benchtop meter (Portable meter ProfiLine pH 3110) equipped with a WTW pH microelectrode. A three‐point calibration at room temperature with technical calibration buffers (HANNA instruments) was routinely performed before pH adjustment.
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