Condensed phase membrane introduction mass spectrometry
Over the last few decades, membrane introduction mass spectrometry (MIMS) has been established as a robust tool for the on-line continuous monitoring of trace gases and volatile organic compounds. However, the range of amenable anlaytes has been limited by the need for molecules to pervaporate into...
Main Author: | |
---|---|
Other Authors: | |
Language: | English en |
Published: |
2015
|
Subjects: | |
Online Access: | http://hdl.handle.net/1828/6936 |
id |
ndltd-uvic.ca-oai-dspace.library.uvic.ca-1828-6936 |
---|---|
record_format |
oai_dc |
collection |
NDLTD |
language |
English en |
sources |
NDLTD |
topic |
membrane introduction mass spectrometry rapid screening environmental chemistry bioanalytical chemistry naphthenic acids electrospray ionization membrane inlet mass spectrometry reaction monitoring continuous sampling |
spellingShingle |
membrane introduction mass spectrometry rapid screening environmental chemistry bioanalytical chemistry naphthenic acids electrospray ionization membrane inlet mass spectrometry reaction monitoring continuous sampling Duncan, Kyle Daniel Condensed phase membrane introduction mass spectrometry |
description |
Over the last few decades, membrane introduction mass spectrometry (MIMS) has been established as a robust tool for the on-line continuous monitoring of trace gases and volatile organic compounds. However, the range of amenable anlaytes has been limited by the need for molecules to pervaporate into a gaseous acceptor phase, or high vacuum environment of a mass spectrometer. This thesis expands the range of amenable analytes for MIMS to include larger, less volatile molecules (e.g., 200 to 500 Da), such as pharmaceuticals, persistent organic pollutants, and small biomolecules. This was achieved through the use of a liquid|membrane|liquid interface. We distinguish the technique from conventional MIMS, which uses a gaseous acceptor phase, by inserting the prefix ‘condensed phase’ to emphasize the use of a solvent acceptor phase – thus yielding CP-MIMS. An initial flow-cell interface with a methanol acceptor phase was characterized, yielding detection limits for model analytes in pptr to ppb, and analyte response times from 1-10 minutes. The flow cell interface was miniaturized into an immersion style CP-MIMS probe (~2 cm), which allowed for analysis of smaller volume samples and improved membrane washing capabilities. Comparable detection limits were observed for the immersion probe, however, it was noticed that significant analyte depletion was observed for samples under 2 mL. In addition, each of the developed membrane interfaces were observed to suffer from ionization suppression effects from complex samples when paired with ESI. Several strategies for mitigating ionization suppression using CP-MIMS are presented, including the use of a continuously infused internal standard present within the acceptor solvent. The developed CP-MIMS system was challenged with the analysis of naphthenic acids (a complex mixture of aliphatic carboxylic acids) directly in contaminated real-world samples. The method used negative ESI to rapidly screen and mass profile aqueous samples for naphthenic acids (as [M-H]-), with sample duty cycles ~20 min. However, it was found that Negative ESI did not differentiate hydroxylated and carboxylated analytes, and both species contributed signal to the total naphthenic acid concentration. To increase method specificity for carboxylic acids, barium ion chemistry was used in conjunction with positive ion tandem mass spectrometry. Common product ions were used to quantify carboxylated analytes, while a qualifier ion was used to confirm the functionality. The increased selectivity afforded by the barium ion chemistry was at the cost of a modest increase in detection limits. CP-MIMS has been established as a technique capable of the direct analysis of real-world samples, and shows promise as a rapid screening method for amenable environmental contaminants and/or biomolecules. === Graduate === 0486 === 0485 === kyle.duncan@viu.ca |
author2 |
Gill, Christopher |
author_facet |
Gill, Christopher Duncan, Kyle Daniel |
author |
Duncan, Kyle Daniel |
author_sort |
Duncan, Kyle Daniel |
title |
Condensed phase membrane introduction mass spectrometry |
title_short |
Condensed phase membrane introduction mass spectrometry |
title_full |
Condensed phase membrane introduction mass spectrometry |
title_fullStr |
Condensed phase membrane introduction mass spectrometry |
title_full_unstemmed |
Condensed phase membrane introduction mass spectrometry |
title_sort |
condensed phase membrane introduction mass spectrometry |
publishDate |
2015 |
url |
http://hdl.handle.net/1828/6936 |
work_keys_str_mv |
AT duncankyledaniel condensedphasemembraneintroductionmassspectrometry |
_version_ |
1718154225277468672 |
spelling |
ndltd-uvic.ca-oai-dspace.library.uvic.ca-1828-69362015-12-19T16:55:00Z Condensed phase membrane introduction mass spectrometry Duncan, Kyle Daniel Gill, Christopher Fyles, Thomas M. membrane introduction mass spectrometry rapid screening environmental chemistry bioanalytical chemistry naphthenic acids electrospray ionization membrane inlet mass spectrometry reaction monitoring continuous sampling Over the last few decades, membrane introduction mass spectrometry (MIMS) has been established as a robust tool for the on-line continuous monitoring of trace gases and volatile organic compounds. However, the range of amenable anlaytes has been limited by the need for molecules to pervaporate into a gaseous acceptor phase, or high vacuum environment of a mass spectrometer. This thesis expands the range of amenable analytes for MIMS to include larger, less volatile molecules (e.g., 200 to 500 Da), such as pharmaceuticals, persistent organic pollutants, and small biomolecules. This was achieved through the use of a liquid|membrane|liquid interface. We distinguish the technique from conventional MIMS, which uses a gaseous acceptor phase, by inserting the prefix ‘condensed phase’ to emphasize the use of a solvent acceptor phase – thus yielding CP-MIMS. An initial flow-cell interface with a methanol acceptor phase was characterized, yielding detection limits for model analytes in pptr to ppb, and analyte response times from 1-10 minutes. The flow cell interface was miniaturized into an immersion style CP-MIMS probe (~2 cm), which allowed for analysis of smaller volume samples and improved membrane washing capabilities. Comparable detection limits were observed for the immersion probe, however, it was noticed that significant analyte depletion was observed for samples under 2 mL. In addition, each of the developed membrane interfaces were observed to suffer from ionization suppression effects from complex samples when paired with ESI. Several strategies for mitigating ionization suppression using CP-MIMS are presented, including the use of a continuously infused internal standard present within the acceptor solvent. The developed CP-MIMS system was challenged with the analysis of naphthenic acids (a complex mixture of aliphatic carboxylic acids) directly in contaminated real-world samples. The method used negative ESI to rapidly screen and mass profile aqueous samples for naphthenic acids (as [M-H]-), with sample duty cycles ~20 min. However, it was found that Negative ESI did not differentiate hydroxylated and carboxylated analytes, and both species contributed signal to the total naphthenic acid concentration. To increase method specificity for carboxylic acids, barium ion chemistry was used in conjunction with positive ion tandem mass spectrometry. Common product ions were used to quantify carboxylated analytes, while a qualifier ion was used to confirm the functionality. The increased selectivity afforded by the barium ion chemistry was at the cost of a modest increase in detection limits. CP-MIMS has been established as a technique capable of the direct analysis of real-world samples, and shows promise as a rapid screening method for amenable environmental contaminants and/or biomolecules. Graduate 0486 0485 kyle.duncan@viu.ca 2015-12-17T16:07:22Z 2015-12-17T16:07:22Z 2015 2015-12-17 Thesis http://hdl.handle.net/1828/6936 Duncan, K.; McCauley, E.; Krogh, E.; Gill, C., Characterization of a condensed-phase membrane introduction mass spectrometry (CP-MIMS) interface using a methanol acceptor phase coupled with electrospray ionization for the continuous on-line quantitation of polar, low-volatility analytes at trace levels in complex aqueous samples. Rapid Commun. Mass Spectrom., 25, 1141-1151 (2011). Duncan, K; Willis, M.; Krogh, E.; Gill, C., A miniature condensed-phase membrane introduction mass spectrometry (CP-MIMS) probe for direct and on-line measurements of pharmaceuticals and contaminants in small, complex samples. Rapid Commun. Mass Spectrom., 27, 1213-1221 (2013). Duncan, K.; Vandergrift, G.; Krogh, E.; Gill, C., Ionization suppression effects with condensed phase membrane introduction mass spectrometry: methods to increase the linear dynamic range and sensitivity. J. Mass Spectrom., 50, 437-443 (2015). Duncan, K.; D. Letourneau; Vandergrift, G.; Jobst, K.; Reiner, E.; Gill, C.; Krogh, E., A semi-quantitative approach for the rapid screening and mass profiling of naphthenic acids directly in contaminated aqueous samples. J. Mass Spectrom., 51, 44-52 (2016). Duncan, K.; Volmer, D.; Gill, C.; Krogh, E., Rapid screening of carboxylic acids from waste and surface waters by ESI-MS/MS using barium ion chemistry and on-line membrane sampling. J. Am. Soc. Mass Spectrom., in press (2015). English en Available to the World Wide Web |