EPA-OGWDW/TSC: 531.2:  N-Methylcarbamoyloximes and N-Methylcarbamates in Water by HPLC with Post Column Derivitization

  • Summary
  • Analytes
  • Revision
  • Data and Sites
Official Method Name
Measurement of N-Methylcarbamoyloximes and N-Methylcarbamates in Water by Direct Aqueous Injection HPLC With Postcolumn Derivitization
Current Revision
Revision 1.0, September 2001
Media
WATER
Instrumentation
High Performance Chromatography with Post Column Derivitization and Fluorescence Detection
Method Subcategory
Organic
Method Source
  EPA-OGWDW/TSC
Citation
  EPA Web site for Analytical Methods for Drinking Water
Brief Method Summary
A filtered water sample (up to 1.0 mL) is injected into a HPLC system equipped with a reversed phase (C-18) column. After elution from the column, the analytes are hydrolyzed in a postcolumn reaction with sodium hydroxide at 80-100 deg C. to form methyl amine. Methyl amine is reacted with o-phthalaldehyde (OPA) and 2-mercaptoethanol (or N,N-dimethyl-2-mercaptoethylamine) to form a highly fluorescent isoindole which is detected by a fluorescence detector. Analytes are quantitated using the external standard technique.
Scope and Application
Method is applicable to determination of certain N-methylcarbamoyloximes and N-methylcarbamates in finished drinking waters.
Applicable Concentration Range
0.2-10 ug/L
Interferences
Contamination: Interferences may be caused by contaminants, especially amines and ammonia, in solvents, reagents, glassware, and other sample processing apparatus that lead to discrete artifacts or elevated baselines. Samples or the analytical system may be contaminated from being handled with bare fingers. Clean glassware and test for contaminants by analyzing laboratory reagent blanks per the method.
Quality Control Requirements
Initial demonstration of accuracy (average recovery must be + or - 20% of true value), precision (RSD must be <20% ) and low system background are required. Calibration and continuing calibration checks (CCC) are required with a second source standard for the CCC and the Detection Limit must be determined over a 3 day period. A field duplicate (FD) and a Laboratory Fortified Sample Matrix (LFSM) and laboratory reagent blanks (LRB) are required with each analysis batch. Subtracting blank values from sample results is not permitted.
Sample Handling
Amber 40 or 60 mL bottles with PTFE-lined screw caps are used for sample collection. Prior to sample collection potassium dihydrogen citrate is added as a dry solid in sufficient amounts to adjust the sample pH to about 3.8 in order to protect against degradation (especially of oxamyl, 3-hydroxycarbofuran, carbaryl, and methiocarb which hydrolyze in neutral or basic pH water). Also prior to sample collection sodium thiosulfate is added as a dry solid for a dechlorinating agent (especially for aldicarb and methiocarb which rapidly degrade in chlorinated water). Sample bottles thus must not be pre-rinsed before collection. Samples do not need to be collected free of headspace and must be kept cool, not exceeding 10 deg. C during the first 48 hours after collection. The laboratory must confirm receipt of samples at 10 deg. C. or below.
Maximum Holding Time
28 days
Relative Cost
$201 to $400
Sample Preparation Methods