Academic literature on the topic 'Nitrofuran metabolites'
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Journal articles on the topic "Nitrofuran metabolites"
Bayer, O. V., O. S. Yaremchuk, T. V. Yevtushenko, L. V. Shevchenko, V. M. Mykhalska, Yu V. Dobrozhan, Ya V. Dovhopol, and R. L. Varpikhovskyi. "Розробка та оцінка придатності методу визначення нітрофуранів в меді за допомогою рідинної хроматографії високого тиску – тандемної мас-спектрометрії (UPLC-MS-MS)." Ukrainian Journal of Ecology 8, no. 1 (March 25, 2018): 966–74. http://dx.doi.org/10.15421/2018_300.
Full textAn, Haejung, Lenin Parrales, Kai Wang, Teresa Cain, Ralph Hollins, Douglas Forrest, Benjamin Liao, Han Chol Paek, and Jacqueline Sram. "Quantitative Analysis of Nitrofuran Metabolites and Chloramphenicol in Shrimp Using Acetonitrile Extraction and Liquid Chromatograph-Tandem Mass Spectrometric Detection: A Single Laboratory Validation." Journal of AOAC INTERNATIONAL 98, no. 3 (May 1, 2015): 602–8. http://dx.doi.org/10.5740/jaoacint.14-262.
Full textSmajlovic, Ahmed, Indira Mujezinovic, Vitomir Cupic, and Mehmed Muminovic. "Nitrofurans' residues in food of animal origin." Veterinarski glasnik 65, no. 3-4 (2011): 215–22. http://dx.doi.org/10.2298/vetgl1104215s.
Full textAlkan, Fatih, Arzu Kotan, and Nurullah Ozdemir. "Development and Validation of Confirmatory Method for Analysis of Nitrofuran Metabolites in Milk, Honey, Poultry Meat and Fish by Liquid Chromatography-Mass Spectrometry." Macedonian Veterinary Review 39, no. 1 (March 1, 2016): 15–22. http://dx.doi.org/10.1515/macvetrev-2015-0060.
Full textEl-Demerdash, Aref, Fenhong Song, Robin K. Reel, Judy Hillegas, and Robert E. Smith. "Simultaneous Determination of Nitrofuran Metabolites and Chloramphenicol in Shrimp with a Single Extraction and LC-MS/MS Analysis." Journal of AOAC INTERNATIONAL 98, no. 3 (May 1, 2015): 595–601. http://dx.doi.org/10.5740/jaoacint.14-261.
Full textVeach, Brian T., Chris A. Baker, John H. Kibbey, Andrew Fong, Bryanna J. Broadaway, and Connie P. Drake. "Quantitation of Chloramphenicol and Nitrofuran Metabolites in Aquaculture Products Using Microwave-Assisted Derivatization, Automated SPE, and LC-MS/MS." Journal of AOAC INTERNATIONAL 98, no. 3 (May 1, 2015): 588–94. http://dx.doi.org/10.5740/jaoacint.14-271.
Full textLuo, Xianzhu, Zhiwei Sun, Xu Wang, Yanxin Yu, Zhongyin Ji, Shijuan Zhang, Guoliang Li, and Jinmao You. "Determination of nitrofuran metabolites in marine products by high performance liquid chromatography–fluorescence detection with microwave-assisted derivatization." New Journal of Chemistry 43, no. 6 (2019): 2649–57. http://dx.doi.org/10.1039/c8nj05479g.
Full textAn, Haejung, Mark Henry, Teresa Cain, Bichsa Tran, Han Chol Paek, and Dennis Farley. "Determination of Total Nitrofuran Metabolites in Shrimp Muscle Using Liquid Chromatography/Tandem Mass Spectrometry in the Atmospheric Pressure Chemical Ionization Mode." Journal of AOAC INTERNATIONAL 95, no. 4 (July 1, 2012): 1222–33. http://dx.doi.org/10.5740/jaoacint.11-305.
Full textVeach, Brian T., N. Bandara, B. Broadaway, C. Casey, A. Fong, A. Karmakar, M. Mayweather, et al. "Determination of Chloramphenicol and Nitrofuran Metabolites in Cobia, Croaker, and Shrimp Using Microwave-Assisted Derivatization, Automated SPE, and LC-MS/MS–Results from a U.S. Food and Drug Administration Level Three Inter-Laboratory Study." Journal of AOAC INTERNATIONAL 103, no. 4 (June 4, 2020): 1043–51. http://dx.doi.org/10.1093/jaoacint/qsaa019.
Full textŚniegocki, Tomasz, Marta Giergiel, Bartosz Sell, and Andrzej Posyniak. "New method of analysis of nitrofurans and nitrofuran metabolites in different biological matrices using UHPLC-MS/MS." Journal of Veterinary Research 62, no. 2 (July 7, 2018): 161–66. http://dx.doi.org/10.2478/jvetres-2018-0025.
Full textDissertations / Theses on the topic "Nitrofuran metabolites"
Wickramanayake, Priyanga, and s3028858@student rmit edu au. "Applications of chiral selectors and replaceable supports for capillary electrophoretic separations." RMIT University. Applied Chemistry, 2007. http://adt.lib.rmit.edu.au/adt/public/adt-VIT20080617.115607.
Full textKuo, Yi-Hsin, and 郭宜鑫. "The Effect of Chlorine Dioxide on Nitrofuran Metabolites Degradation in Water and Sediments." Thesis, 2015. http://ndltd.ncl.edu.tw/handle/2d5ak4.
Full text國立臺灣海洋大學
水產養殖學系
103
The objective of this study was to investigate the effect of different concentrations of chlorine dioxide (ClO2) on degradation of four nitrofuran metabolites (AOZ, AMOZ, SC and AH) in freshwater and seawater environments of water and sediments; also to understand the situation of nitrofuran metabolites residues in water and sediments. Experiment consisted of four parts, first was to establish the method for detecting the four nitrofuran metabolites in water and sediments, and the results showed that specificity, recovery, repeatability and limits of quantification were in line with the validation of Method of Test for chemistry in foods of Food and Drug Administration. Limits of quantification of four nitrofuran metabolites in freshwater, seawater and sediments were reached 0.5 ng/mL, and the recovery rate were between 90.10~109.97 %. Second was the different concentrations (1, 5 and 10 mg/L) of chlorine dioxide on 100 ng/mL nitrofuran metabolites degradation in freshwater and seawater. Results showed that 1 mg/L chlorine dioxide was effective immediately in 1 day after treatment for nitrofuran metabolites in freshwater and seawater, and treatment with 10 mg/L chlorine dioxide showed the most significant result both in freshwater and seawater which the concentrations of AOZ, AMOZ, SC and AH were below the limits of quantification after 10 mg/L chlorine dioxide treatment 2 day. Third was the different concentrations (10, 20 and 40 mg/L) of chlorine dioxide on 100 ng/mL nitrofuran metabolites degradation in sediments with freshwater and seawater. Results showed that 40 mg/L chlorine dioxide treatment effect was the most significant and effective immediately in 1 day after treatment for nitrofuran metabolites in sediments with freshwater and seawater. Fourth was to investigate the degradation of 100 ng/mL nitrofuran metabolites in water and sediments during 90 days. In freshwater and seawater, results indicated that AOZ was 42.07 ± 0.80 and 35.10 ± 0.35 ng/mL, AMOZ was 31.23 ± 0.08 and 21.08 ± 0.25 ng/mL, SC was 11.82 ± 0.53 ng/mL and below the quantification limit, and AH was 51.17 ± 0.29 and 7.03 ± 0.53 ng/ mL on ninetieth day; but SC was still 1.09 ± 0.19 ng/mL in seawater on thirtieth day. In sediments, outcome was that four nitrofuran metabolites were degraded immediately in 1 day. The degradation rate of nitrofuran metabolites became slow with time. In sediments with freshwater and seawater on ninetieth day, AOZ was 4.98 ± 0.12 and 5.49 ± 0.73 ng/mL, AMOZ was 31.23 ± 0.08 and 21.08 ± 0.25 ng/mL, SC was 1.52 ± 0.01 and 1.58 ± 0.09 ng/mL, and AH was 1.11 ± 0.03 and 1.31 ± 0.04 ng/mL. This experiment pointed that chlorine dioxide (ClO2) can degrade four nitrofuran metabolites (AOZ, AMOZ, SC and AH) in freshwater and seawater environments, and higher concentration was needed in sediments than in water. Four nitrofuran metabolites would remain in water and sediments for a long period, and the remaining time in seawater is longer than in freshwater.
Barbosa, Jorge Manuel da Silva. "Residues of Furaltadone and Nifursol Nitrofuran Parent Compounds and Metabolites in Feed, Poultry Edible Tissues and Eggs." Doctoral thesis, 2012. http://hdl.handle.net/10316/18276.
Full textCheng, Hsing-Hsiang, and 鄭幸祥. "A study on the analytical methods of antibacterial drugs-nitrofuran and its metabolites residues in cultured fish A study on the analytical methods of antibacterial drugs-nitrofuran and its metabolites residues in cultured fish A study on the analytic." Thesis, 2006. http://ndltd.ncl.edu.tw/handle/74606675622788303476.
Full text國立屏東科技大學
食品科學系
94
The objects of this study were to compare the analytical methods of HPLC and LC-MS for the antibacterial drugs- nitrofuran and its metabolites residues in aquacultural fish and to apply ELISA method to detect AOZ residues in fish tissue. Nitrofuran, which including FZD, FTD, NFZ, and NFT, had been widely used in animal feed additives or aquacultural fish due to their efficiency and cheap price. But, because of the carcinogenic and mutagenic toxicity, its application on animals for food producing in EU was prohibited since 1993. The nitrofurans are characterized by the rapid metabolism with short half-life, but, its metabolites, AOZ, AMOZ, SC, and AH, which are much stable in tissue bounded with protein. Hence, it will be more meaningful to detect the metabolites to monitor the illegal use of nitrofurans. About HPLC method, samples were extracted by adding 1 to 1 ratio of 0.2 % metaphosphate methanol and deionized water solution and ethyl acetate. Mobile phase was mixed with acetonitrile and 0.05 M NaH2PO4 by 20 to 80 ratio at pH 5.1, and could be completely conducted within 20 minutes. The limit of quantification was 0.02 ppm, the recovery was ranged from 63.8- 75.5 %, and the CV was 2.8-7.4 %. About LC-MS analysis, the derivatisation should be done previously by adding 0.125 M HCl and 2-NBA overnight for 16 hours. Then, SPE cartridge was used to clean up and eluted by ethyl acetate. The gradient mobile phase was used, and total analysis could be finished within 30 minutes. The limit of quantification for AMOZ and AOZ were 0.25 ppb, SC and AH were 0.50 ppb, respectively. The recovery was 63.2-77.3 %, and CV was 4.8-8.4 %. Trying to understand whether the different treatment had the effect on the residues or not, the fish samples were stored for 10 days under -18℃ and heated by microwave for 6 minutes, respectively, and the results revealed both the treatments had not the significant effects no destroying metabolite residues. About AOZ-ELISA analysis, the detection limit was 0.2 ppb, recovery was from 82.6- 98.2 %, CV was 0.8-2.9 %, and the total analysis was within 90 minutes. Therefore, AOZ-ELISA kit would be recommended for the screening work on large sample size.
Hsu, Ming-Hui, and 徐名慧. "Analysis of Metabolites of Nitrofurans in Aquatic Animals." Thesis, 2014. http://ndltd.ncl.edu.tw/handle/25np8p.
Full text國立臺灣海洋大學
食品科學系
102
Nitrofurans are synthetic broad spectrum antibacterials that have been used widely in aquatic animals. The use of nitrofurans in aquatic animals has been banned in many countries because of its carcinogenic and mutagenic effects. The aim of this study was to establish a HPLC-UV method analyzing the metabolites of nitrofurans, AOZ (3-amino-2-oxazolidinone), AMOZ (3-amino-5-morpholinomethyl-2-oxazolidinone), SEM (semicarbazide), and AHD (1-aminohydantoin). It included the optimum HPLC condition, derivatization method, and the order of sample treatment. The derivatives of AOZ, AMOZ, SEM, and AHD could be separated effectively when it used acetonitrile and 0.02% acetic acid with gradient elution. The metabolites of nitrofurans were derivatized by water bath derivatization (37oC for 16 hours and 55oC for 4 hours), ultrasonic-assisted derivatization (for 30 and 60 minutes), and microwave-assisted derivatization (100 and 200 W for 5, 6, and 7 minutes), respectively. There was no significant difference between 37 oC water bath for 16 hours and 55 oC water bath for 4 hours, and so were ultrasonic-assisted derivatization for 60 minutes and microwave-assisted derivatization under different conditions. In addition, derivatization yields were not related to microwave time and irradiation power. It was speculated that derivatization by microwaving under 100 W for 10 seconds could achieve the effect by the treatment at 37 oC water bath for 16 hours. Derivatization time was reduced significantly from 16 hours to 10 seconds. Tilapia was treated with HDEC (hydrolysis, derivatization, extraction, and clean-up), HEDC (hydrolysis, extraction, derivatization, and clean-up), and HEDEC (hydrolysis, extraction, derivatization, extraction, and clean-up). AMOZ was not detected in HEDC procedure while the contents of AOZ and AHD were the highest in HDEC procedure. As a result, HDEC was regarded as the optimum order of sample treatment. The method of using HPLC-UV and Inertsil ODS-3 column, and combining with the optimum HPLC condition, derivatization method, and the order of sample treatment that were established by this study was validated. The limit of detection of AOZ, AMOZ, SEM, and AHD in tilapia was ranged from 0.63 to 0.84 ng/g and the recovery was between 64.2 and 131.5%. The contents of the metabolites of nitrofurans in commercial aquatic animals were also determined. No metabolites of nitrofurans were found in the 10 samples we purchased.
Tsai, Chung-Wei, and 蔡仲偉. "Studies in Determination and Residues of Nitrofurans and Corresponding Metabolites by LC-MS/MS in Tilapia." Thesis, 2009. http://ndltd.ncl.edu.tw/handle/6b5zgu.
Full text國立中山大學
海洋生物科技暨資源學系研究所
97
Nitrofurans have been widely used either in waterbath or feed additives for the prevention and treatment of aquatic products. The European Union was able to assign a maximum residue limit and prohibited nitrofurans used to animals in 1995, because of the potential carcinogenic effects of their residues on human health. This study is focusing on the analytical method of four kinds of commonly used nitrofurans and corresponding residual metabolites by LC-MS/MS. The detection limits of furazolidone, furaltadone, nitrofurazone and nitrofurntoin were 6.11, 3.63, 4.52 and 6.20 μg kg-1,respectively. The detection limits of AOZ, AMOZ, SC and AH were 0.23, 0.30, 0.36, 0.53 μg kg-1, respectively. The lightness is the main factor to cause the decomposition of nitrofurans. It is not significant for temperature to depredate nitrofurans. The adsorbtion of metabolites by the plastic tube was in the extraction procedure. Equipments in glass are suggested to be used for the sample pretreatment and plastic meterials are averted to be exercised. About the comparation of determination of AOZ by ELISA and LC-MS/MS. The result demonstrated that the ELISA method might overestimate the residual AOZ content at low concentrations. The detection limit and recovery of the known addition were 0.05 μg kg-1 and 108% for the LC-MS/MS method and 0.31 μg kg-1 and 305% for the ELISA method, respectively. The amounts of residual nitrofurans and metabolites in muscle, liver, gill and skin tissue of tilapia which were treated in different conditions were compared. The depletion data of bathing treatment group obtained showed similar be haviors of furazolidone, furaltadone, nitrofurazone, nitrofurantoin in tilapia which the residual time was less than 24 hr. The amounts of residual nitrofurans appeared the highest concentration in gill and the lowest concentration in muscle. Bonded residues of metabolites can be detected for at least 4 weeks after administration in muscle, skin, liver and gill. The concentrations of residual bonded metabolites were higher than non-bonded metabolites in gill and muscle besides liver during depletion periods. After bathing medication, there were more residual nitrofurans and corresponding metabolites in sea water tilapia than fresh water group, because sea water fish survives in high osmotic condition to reduce their urination. Nitrofurans and metabolites were deconstructed by enzyme in gills, livers, intestines and muscles. Then tissues of fish accumulated nitrofurans and metabolites soon after medication. The maturity of fish is one of facters to effect different residual concentration during depletion periods. Liver is the main tissue to deconstruct nitrofurans and metabolites for the bathing medication and intestine is the major tissue to decompose antibiotics for the feeding medicaton. In this research, we built a completed way to determine nitrofurans and corresponding metatbolites. Comparation of fish in different conditions and different medicative ways were in this investigation. These results could be helpful for aquacultures and government institutions.
Books on the topic "Nitrofuran metabolites"
Nazrul, Islam Md. Analysis of pond water and soil/sediment of shrimp farms and hatcheries for nitrofuran metabolites and chloramphenicol. Mymensingh: Department of Fisheries Technology, Faculty of Fisheries, Bangladesh Agricultural University, 2010.
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