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5 protocols using norfloxacin

1

Magnetic Molecularly Imprinted Polymers for Fluoroquinolone Analysis

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Water-compatible commercial molecularly imprinted polymers (MIPs) material, named SupelMIPTM SPE-Fluoroquinolones, was purchased from Sigma–Aldrich (St.Louis, MO, USA). Fe3O4 magnetite nanocomposites (MNPs) were prepared according to previous studies46 (link),66 (link) (detailed in Supplementary). Fluoroquinolones (norfloxacin, enoxacin, and fleroxacin, purity 98%) were purchased from J&K Scientific Ltd. (Shanghai, China). The individual stock solutions of norfloxacin, enoxacin, and fleroxacin were prepared in methanol at a concentration of 0.1 mg mL−1 and stored at 4 °C before use. Both Methanol and acetonitrile were HPLC grade and purchased from Merck KGaA (Darmstadt, Germany). Ammonium hydroxide solution (suitability for use in UPLC/LC-MS, NH3, w/w 20%) was bought from CNW Technologies GmbH (Düsseldorf, Germany). Ethylene glycol, ethylene diamine, ferric trichloride hexahydrate (FeCl3·6H2O), and sodium acetate (NaAc) were purchased from Sinopharm Chemical Reagent Co. Ltd. (Shanghai, China). Ultrapure water obtained from a Millipore water purification system (Milli-Q, Millipore; Bedford, MA, USA).
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Electrochemical Wastewater Treatment

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A Nafion-117 cation exchange membrane for separating catholyte and anolyte was manufactured by Du Pont de Nemours & Co., Ltd. (Wilmington, DE, USA). A potentiostat providing direct current (DC) power was purchased from Shanghai Chenhua Science Technology Corp., Ltd., Shanghai, China. Unless otherwise specified, all chemical reagents were acquired from commercial suppliers and utilized without further purification. Sodium persulfate (PS, ≥99.5%), carbamazepine, norfloxacin, atrazine, phonel, methanol (99%), bisphenol A (BPA), sodium hydroxide (NaOH), atrazine, sulfuric acid (H2SO4), sodium sulfate (Na2SO4, ≥99.0%), Diammonium 2,2′-azino-bis (3-ethylbenzothiazoline-6-sulfonate) (ABTS), potassium titanium (IV) oxalate, tert-butanol (TBA, 99%), and boron-doped diamond electrode (BDD) electrodes (800 ppm boron, bipolar, 1 mm coating thickness) were obtained from J&K Chemical (Beijing, China). Activated carbon fiber (ACF) electrodes and platinum-plated titanium electrodes (25 mm × 50 mm × 1 mm) were obtained from Shanxi Kaida Chemical Ltd., Lvliang, China. DC power supply was obtained from Zhejiang Sako Electrical Group Co., Ltd., Leqing, China.
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Radiolabeling and Evaluation of Norfloxacin

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Norfloxacin was purchased from J&K chemical, Beijing, China. All other reagents were of reagent grade and were used without further purification. [99mTc]NaTcO4 was obtained from a 99Mo/99mTc generator purchased from Atomic High Tech Co. Ltd., Beijing, China. NMR spectra were recorded on a 400 MHz and 600 MHz JNM-ECS spectrophotometer (JEOL, Tokyo, Japan). ESI-MS spectra were recorded on an LC–MS Shimadzu 2010 series. HPLC analysis was performed on a Waters 2489 UV system and a Gabi raytest radioactivity detector using an analytical column (C-18, Kromasil, 100–5 μm, 250 × 4.6 mm). The centrifuge model was 800-1 (Ronghua, Jintan, China). The radioactivity was measured by WIZARD2 2480 Automatic Gamma Counter (PerkinElmer, Waltham, MA, USA), an HRS-2000 technetium analyzer (Huaruisen, Beijing, China), and RW-905A radioactivity meter (Hechang, Beijing, China). SPECT/CT imaging was performed on micro SPECT/CT equipment with 930 collimator (Trifoil, Chatswort, CA, USA). The SPECT technical parameters were as follows: native resolution ≤ 1.6 mm; detection area ≥ 128 mm × 128 mm; and sensitivity ≥ 4800 cps/MBq. Animal studies were performed in accordance with the Regulations on Laboratory Animals of Beijing Municipality and the guidelines of the Ethics Committee of Beijing Normal University (permit no. CLS-EAW-2018-001, June 2018).
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4

Analytical Standards for Quinolone Antibiotics

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Analytical standards for fleroxacin (FLE), ofloxacin (OFL), norfloxacin (NOR), ciprofloxacin (CIP) and enrofloxacin (ENR) were purchased from J&K Chemical, China and used without further purification. HPLC-grade ethanol, methanol, ethyl acetate, acetonitrile and acetone were sourced from Merck (www.merck.com.cn). Salts (magnesium sulfate (MgSO 4 ), sodium sulfate (Na 2 SO4), sodium acetate (CH 3 COONa), ammonium sulfate ((NH 4 ) 2 SO 4 ) and ammonium acetate (CH 3 COONH 4 )) with purities ≥99% were obtained from Aladdin Industrial Co. Ltd.
Stock standard solutions (1000 g mL -1 ) for each FQ were prepared by dissolving each compound in methanol and stored at 4 • C. Stock solutions were diluted with methanol to prepare a secondary mixed stock solution of 10 g mL -1 . Mixtures of standard working solutions for extraction at different concentrations were prepared daily by dilution with Milli-Q ultrapure water (Millipore, Bedford, USA).
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5

Quantification of Antibiotics and Fatty Acids in Coastal Environments

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Analytical standards included six antibiotics, ofloxacin (OFL), norfloxacin (NOR), ciprofloxacin (CIP), enrofloxacin (ENR), oxytetracycline (OTC), and tetracycline (TC) with purity >99.0%, and five medium-chain fatty acids, pentanoic acid, hexanoic acid, heptanoic acid, octanoic acid, and nonanoic acid, all purchased from J&K Chemical, Shanghai, China.
Stock standard solutions (1000 μg mL -1 ) for the six antibiotics were prepared every month by dissolving each compound in methanol and stored at 4 o C for further use. Working solutions were diluted with Milli-Q ultrapure water (Millipore, Bedford, MA, USA) and methanol (v/v = 50:50) to prepare a secondary mixed stock solution of 10 μg mL -1 . All of the working solutions were prepared every week and stored at 4 o C for further use.
summer of 2017. The seawater sample was filtered through a 0.45-μm membrane filter and stored at -4 o C until analysis. The sediment sample was air-dried at room temperature before grinding and sieving. Fish, shrimp, shellfish, and squid were purchased from local fishing boats (Weifang, China) and stored at -20 o C after grinding (JX-FSTPRP-24 grinder, Shanghai, China). All samples were analyzed within 1 wk of sample collection.
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