Evaluation of the use of performance reference compounds in an Oasis-HLB adsorbent based passive sampler for improving water concentration estimates of polar herbicides in freshwater.

Passive samplers such as the Polar Organic Chemical Integrative Sampler (POCIS) are useful tools for monitoring trace levels of polar organic chemicals in aquatic environments. The use of performance reference compounds (PRC) spiked into the POCIS adsorbent for in situ calibration may improve the semiquantitative nature of water concentration estimates based on this type of sampler. In this work, deuterium labeled atrazine-desisopropyl (DIA-d5) was chosen as PRC because of its relatively high fugacity from Oasis HLB (the POCIS adsorbent used) and our earlier evidence of its isotropic exchange. In situ calibration of POCIS spiked with DIA-d5 was performed, and the resulting time-weighted average concentration estimates were compared with similar values from an automatic sampler equipped with Oasis HLB cartridges. Before PRC correction, water concentration estimates based on POCIS data sampling rates from a laboratory calibration exposure were systematically lower than the reference concentrations obtained with the automatic sampler. Use of the DIA-d5 PRC data to correct POCIS sampling rates narrowed differences between corresponding values derived from the two methods. Application of PRCs for in situ calibration seems promising for improving POCIS-derived concentration estimates of polar pesticides. However, careful attention must be paid to the minimization of matrix effects when the quantification is performed by HPLC-ESI-MS/MS.

[1]  Charles S Wong,et al.  Laboratory calibration and field deployment of the Polar organic chemical integrative sampler for pharmaceuticals and personal care products in wastewater and surface water , 2007, Environmental toxicology and chemistry.

[2]  P. Leonards,et al.  Modelling and field application of the Chemcatcher passive sampler calibration data for the monitoring of hydrophobic organic pollutants in water. , 2007, Environmental pollution.

[3]  J. Hernández-Méndez,et al.  Determination of herbicides, including thermally labile phenylureas, by solid-phase microextraction and gas chromatography-mass spectrometry. , 2003, Journal of chromatography. A.

[4]  R. Gale,et al.  Considerations involved with the use of semipermeable membrane devices for monitoring environmental contaminants. , 2000, Journal of chromatography. A.

[5]  I. Allan,et al.  Passive sampling techniques for monitoring pollutants in water , 2005 .

[6]  J. Huckins,et al.  Determination of uptake kinetics (sampling rates) by lipid-containing semipermeable membrane devices (SPMDs) for polycyclic aromatic hydrocarbons (PAHs) in water , 1999 .

[7]  Foppe Smedes,et al.  Spiking of performance reference compounds in low density polyethylene and silicone passive water samplers. , 2002, Chemosphere.

[8]  G. Schüürmann,et al.  Calibration of the Chemcatcher® passive sampler for monitoring selected polar and semi-polar pesticides in surface water , 2008 .

[9]  Thorsten Reemtsma,et al.  Evaluation of three calibration methods to compensate matrix effects in environmental analysis with LC-ESI-MS , 2004, Analytical and bioanalytical chemistry.

[10]  Jung-Hwan Kwon,et al.  The role of hydrodynamics, matrix and sampling duration in passive sampling of polar compounds with Empore SDB-RPS disks. , 2008, Journal of environmental monitoring : JEM.

[11]  J. Hajšlová,et al.  Alternative calibration approaches to compensate the effect of co-extracted matrix components in liquid chromatography-electrospray ionisation tandem mass spectrometry analysis of pesticide residues in plant materials. , 2002, Journal of chromatography. A.

[12]  W. Jarman,et al.  Passive water sampling via semipermfable membrane devices (SPMDS) in concert with bivalves in the Sacramento/San Joaquin River Delta , 1992 .

[13]  R. Gale Three-Compartment Model for Contaminant Accumulation by Semipermeable Membrane Devices , 1998 .

[14]  J. Pawliszyn Sample preparation: quo vadis? , 2003, Analytical chemistry.

[15]  C. Madigou,et al.  Investigation of the matrix effects on a HPLC-ESI-MS/MS method and application for monitoring triazine, phenylurea and chloroacetanilide concentrations in fresh and estuarine waters. , 2009, Journal of environmental monitoring : JEM.

[16]  N. Mazzella,et al.  Comparison between the polar organic chemical integrative sampler and the solid-phase extraction for estimating herbicide time-weighted average concentrations during a microcosm experiment. , 2008, Chemosphere.

[17]  W. Cranor,et al.  Development of the permeability/performance reference compound approach for in situ calibration of semipermeable membrane devices. , 2002, Environmental science & technology.

[18]  B. Vrana,et al.  Calibration of the Chemcatcher passive sampler for the monitoring of priority organic pollutants in water. , 2006, Environmental pollution.

[19]  R. Bossi,et al.  Analysis of polar pesticides in rainwater in Denmark by liquid chromatography-tandem mass spectrometry. , 2002, Journal of chromatography. A.

[20]  J. Pawliszyn,et al.  Theory of analyte extraction by selected porous polymer SPME fibres , 1999 .

[21]  Jimmie D. Petty,et al.  Lipid-containing semipermeable membrane devices for monitoring organic contaminants in water , 1993 .

[22]  François Delmas,et al.  Determination of kinetic and equilibrium regimes in the operation of polar organic chemical integrative samplers. Application to the passive sampling of the polar herbicides in aquatic environments. , 2007, Journal of chromatography. A.

[23]  K. Chamberlain,et al.  Validation of pH-Metric Technique for Measurement of pKa and log Pow of Ionizable Herbicides , 1995 .

[24]  S. Chiron,et al.  Comparing pharmaceutical and pesticide loads into a small Mediterranean river. , 2005, The Science of the total environment.

[25]  T. Reemtsma The use of liquid chromatography-atmospheric pressure ionization-mass spectrometry in water analysis – Part II: Obstacles , 2001 .