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An overview of analytical methodologies for the determination of antibiotics in environmental waters
Authors:Marcela Seifrtová  Celeste Lino  Petr Solich
Institution:a Department of Analytical Chemistry, Faculty of Pharmacy, Charles University, Heyrovského 1203, 500 05 Hradec Králové, Czech Republic
b Group of Bromatology, Center of Pharmaceutical Studies, University of Coimbra, Coimbra, Portugal
Abstract:The widespread occurrence of antibiotics as contaminants in the aquatic environment has increased attention in the last years. The concern over the release of antibiotics into the environment is related primarily to the potential for the development of antimicrobial resistance among microorganisms. This article presents an overview of analytical methodologies for the determination of quinolone (Qs) and fluoroquinolone (FQs), macrolide (MLs), tetracycline (TCs), sulfonamide (SAs) antibiotics and trimethoprim (TMP) in different environmental waters. The analysis of these antibiotics has usually been carried out by high-performance liquid chromatography (HPLC) coupled to mass spectrometry (MS) or tandem mass spectrometry (MS/MS) and to a lesser extent by ultraviolet (UV) or fluorescence detection (FD). A very important step before LC analysis is sample preparation and extraction leading to elimination of interferences and prevention of matrix effect and preconcentration of target analytes.
Keywords:AcAc  acetic acid  ACN  acetonitrile  AmAc  ammonium acetate  APCI  atmospheric pressure chemical ionization  AZI  azithromycin  CF  concentration factor  CIN  cinoxacin  CIPRO  ciprofloxacin  CLAR  clarithromycin  CLIN  clindamycin  CTC  chlortetracycline  CZE  capillary zone electrophoresis  DAD  diode-array detector  DAN  danofloxacin  DEME  demeclocycline  DIF  difloxacin  DOXY  doxycycline  ENO  enoxacin  ENRO  enrofloxacin  ERY  erythromycin  ESI  electrospray ionization  FAc  formic acid  FD  fluorescence detection  FLE  fleroxacin  FLU  flumequine  FQs  fluoroquinolone antibiotics  GAT  gatifloxacin  HPLC  high-performance liquid chromatography  IS  internal standard  LC  liquid chromatography  LEV  levofloxacin  LLE  liquid-liquid extraction  LOD  limit of detection  LOME  lomefloxacin  LOQ  limit of quantification  MAR  marbofloxacin  MCX  mixed-cation exchange  MECLO  meclocycline  MeOH  methanol  MINO  minocycline  MLs  macrolide antibiotics  MOXI  moxifloxacin  MS  mass spectrometry  MS/MS  tandem mass spectrometry  NAL  nalidixic acid  NOR  norfloxacin  OFLO  ofloxacin  OXO  oxolinic acid  OXY  oxytetracycline  PEFLO  pefloxacin  PIP  pipemidic acid  Qs  quinolone antibiotics  RIA  radioimmunoassay  ROXI  roxithromycin  SAD  sulfanilamide  SARA  sarafloxacin  SAs  sulfonamide antibiotics  SAX  strong-anion exchange  SCP  sulfachloropyridazine  SCT  sulfacetamide  SDM  sulfadimidine  SDT  sulfadimethoxine  SDX  sulfadoxine  SDZ  sulfadiazine  SGN  sulfaguanidine  SIM  selected ion monitoring  SM  sulfameter  SMD  sulfamethoxydiazine  SML  sulfamoxole  SMM  sulfamonomethoxine  SMO  sulfamethoxine  SMP  sulfamethoxypyrazine  SMR  sulfamerazine  SMT  sulfamethizole  SMX  sulfamethoxazole  SMZ  sulfamethazine  SNT  sulfanitran  SPAR  sparfloxacin  SPE  solid-phase extraction  SPIR  spiramycin  SPME  solid-phase microextraction  SPY  sulfapyridine  SQX  sulfaquinoxaline  SRM  selected reaction monitoring  SSM  sulfisomidin  SSX  sulfisoxazole  SSZ  sulfasalazine  STZ  sulfathiazole  TCs  tetracycline antibiotics  TET  tetracycline  TLS  tylosin  TMP  trimethoprim  TOS  tosufloxacin  UHPLC  ultra-high-performance liquid chromatography  UV  ultraviolet  VAN  vancomycin  WCX  weak-cation exchange  WWTPs  wastewater treatment plants
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